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UniAtgedenSctaytes Environmental Protection
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1650 Arch Street
Philadelphia, PA
19103-2029
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UMnairtyedDoStmaitneisaEknvironmental Protection
OffiAcgeenOcFyPollution, Prevention and Toxics
Chemical Control Division
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FThEeDEHRonAoLraEbXlPeREJoShSn D. Ashcroft SAt1t1o1rnMeayiGneSnterreaeltoBfutihlediUnngited States. W1a0tshhiSntgreteotn,anDdCCon2s0t5i3tu0tion Avenue, N.W.
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USEPA 6461
March 6, 2001 Page 2
RCEERTTUIRFNIERDECMEAILPLTNROE:Q7U00E0S0T60E0D002406963524 Michael O. Callahan DiWreescttVoirrginia Divisionof Environmental Protection 10 McJunkin Road
Nitro, WV 25143
FEDERAL EXPRESS William Wentworth Project Manager United States Environmental Protection
Agency Region IIT 1630 Arch Street Philadelphia, PA 19103-2029 FEDERAL EXPRESS `West Virginia Health & Human Resources
Department State Capital Complex. Building 3, Room 206 Charleston, WV 25305
AFlElDyEnRTAuLmeErXPRESS Mike Zeto WatEenrviRreosnomuerncteasl/WEansftoercMeamneangtement West Virginia Division of Environmental
Protection
1356 Hansford Street
Charleston, WV 25301-1401 FEDERAL EXPRESS Darrell V. McGraw, Esq. West Virginia Attomey General's Office State Capital Building Room 26E 1900 Kanawha Blvd., East Charleston, WV 25305
Re: Request For Immediate Governmental Action/Regulation Relating To DuPont's C-8 Releases In Wood County, West Virginia And Notice Of Intent To Sue Under The Federal Clean Water Act, Toxic Substances Control Act, And Resource Conservation And Recovery Act - NOTE: For Inclusion In USEPA Docket No. OPPTS-S0639A
Ladies and Gentlemen:
Our law firm represents Wilbur Earl Tennant and Sandra K. Tennant (Route 3, Box 17, Washington, WV 26181, (304) 863-8787), James David Tennant and Della Maric Tennant (Route 3, Box 372, Parkersburg, WV 26101, (304) 863-5428), and Erwin Jackson Tennant (Route 3, Box 17A, Washington, WV 26181, (304) 863-6977) (collectively, the "Tennants") in connection with a lawsuit that is currently pending against E.I. duPontde Nemours & Co., Inc. ("DuPont") in Federal Court in Parkersburg, West Virginia, styled Tennant v. E.L duPont de Nemours & Co., Inc., Civil Action No. 6:99.0488 (S.D. W.Va). The Tennants have sued DuPont in connection with the releaseofvarious pollutants and contaminants from DuPont's Dry Run Landfill in Wood County, West Virginia. (See Exhibit 133.) The Tennants believe that
00027
March 6, 2001 Page 3 such releases have resulted in and continue to result in personal injury and property damage to the Tennants, including the deathofseveral hundred headofthe Tenants' cattle and serious health problems for the Tennants
During the courseofthe ligation, we have confirmed that the chemicals and pollutants released into the environment by DuPont at its Dry Run Landfill and other nearby DuPont-owned facilities may pose an imminent and substantial threat to healthorthe environment. More specifically, information currently available to the Tennants confirms that DuPont has been releasing and continues to release into the air, land, and water, including human drinking water supplies, an essentially unregulated, confirmed animal carcinogen known as ammonium perfluorooctanoate (a/k/a C-8/FC-143/APFO/PFOA) (CAS No. 3825-26-1) (hereinafter "C-8")." Hundreds of headof cattle, along with numerous deer, fish, frogs, and other animals, have died in the area affected by the C-8 releases, and area residents exposed to the C-8 releases have been suffering ill health effects that are believed to be associated with C-8 exposure. For example, oneof our clients, Wilbur Earl Tennant, has been in and out of the hospital repeatedly over the last few years suffering from respiratory problems, chemical burns, and other health problems after exposure to materials from the Dry Run Landfill.
For the reasons discussed in more detail below, the Tennants hereby request that each of `your agencies intervene in the Tenants' pending lawsuit and order the immediate investigation, `assessment, containment, removal, and remediation of DuPont's C- releases into the environment from the Dry Run Landfill, includingan order that DuPont immediately cease and desist all C-8 releases and that appropriate medicalcare testingevaluation be provided to the Tennants. The Tennants also request that DuPont's permit to operate the Dry Run Landfill be immediately revoked and that all operations at that landSill be suspended until adequate scientific demonstrations are made to prove that the C-8 releases have been abated and will not recur.
In addition, the Tennants specifically request that USEPA exercise its authority under TSCA to order DuPont to immediately cease all manufacturing activities involving C-8 until DuPont can prove through appropriate scientific testing and research that its usage of C- does not pose an unreasonable riskofinjury to health or the environment. In the meantime, the Tennants request that your agencies take those steps necessary to begin regulating C-8 releases into the environment. In that regard, the Tennants request that, at a minimum, USEPA include C8 among the chemicals that it proposed in October of 2000 to regulate under TSCA on the `grounds that the chemicals "may be hazardous to human health and the environment." (See Exhibit 123.) The Tennants believe that the information recently obtained from DuPont regarding C-' potential threat to human health,(sce&.g., Exhibits 71, 125, and 126), warrants regulation of C-8 atleastas aggressively as the related perflourinated chemicals manufactured by 3M.
' Curcently available information also indicates unusual levelsof iodide/iodine, along with Triton in Dry Run Creek. (See Exhibit 91.) 000007
March 6, 2001 Page 4
This letter also constitutes notice on behalf of the Tennants and a class of other individuals similarly situatedoftheir intent to bring citizen suit claims against DuPont in
connection with DuPont's C-8 releases into air, land, and water from DuPont's Washington
Works facility in Wood County, West Virginia under the Federal Clean Water Act ("CWA"), Toxic Substances Control Act ("TSCA"), and Resource Conservation and Recovery Act ("RCRA") The factual and legal basis of such citizen suit claims is explained in detail below.
Additional documentation in supportofthe basic facts summarized below is available at our offices in Cincinnati, including a chronologically-organized databaseofthe over 110,000 pages of documents producedto date by DuPont on this topic. L DuPont Has Used C-8 Primarily At Its Washington Works Plant In Wood County,
West Virginia. C-81is a perfluorinated detergenvsurfactant manufactured in the United States by 3M. Company that DuPont uses in connection with its manufactureofTeflon-related products. (See Exhibits 1 and 118.) DuPont has used C-8 as a reaction aid in its production of polytetrafluoroethylene (PTFE) and tetrafluoroethylene (TFE) co-polymers at its Washington Works facility outside Parkersburg, West Virginia since the early 1950s. (See Exhibit 118.) `Wastes from the Washington Works' C-8 processes are either vented to the air following incineration, dumped into the Ohio River, sent to DuPont's Chambers Works facility in Deepwater, New Jersey for treatment and discharge, or disposedofat landfills. (See id) The polymer product manufacturedatthe Washington Works is either sold directly to DuPont's customers (in the United States and abroad) or transferred to DuPont's Spruance Plant in Richmond, Virginia for use in the production of Teflon and PTFE~coated fibers or transferred to DuPont's Parlin Plant in Parlin, New Jersey for use in the productionof Teflon finishes, some of which is then used in consumer cookware. (See id.) C-8 may remain in someofthe products sold from DuPont's Washington Works, Spruance Plant, and Parlin Plant.(Seeid) Some of DuPont's Teflon materials have been used in medical implants that are inserted directly into the human body. (See Exhibit 132.)
Please note that, although the Tennants already have filed claims against DuPont under the CWA and RCRA, these pending claims relate only to releases from DuPont's Dry Run Landfill. This letter provides noticeofthe Teanants' intention to also bring separate claims against DuPont under the CWA, TSCA, and RCRA with respect to releases from DuPont's nearby Washington Works plant in Wood County, West Virginia, onbehalfof themselves and a classofothers similarly situated.
> DuPont's registered trademark. 06042%
March 6, 2001 Page 5
I. DuPont Has Known That Excessive Exposure To C- Causes Adverse Effects.
DuPont has worked closely with 3M since at least the 1970s to investigate the toxic and carcinogenic effects of C-8 on animal and human health. (See id. and Exhibits 2, 24, and 49.) Through such company-sponsored studies, DuPont acquired knowledge by at least the early 1980s that C-8 was toxic and carcinogenic to animals, whether through inhalation, direct skin contact, or ingestion. (See Exhibits 12,49, and 71.) Around the same time, DuPont also became aware that C-8 is biopersistentbioaccumulative in animals and humans. (See Exhibits 30, 49 and 71)"
In response to the mounting toxicity data on C-8, and because C-8 was essentially an
unregulated chemical that, according to USEPA, had simply "sail[ed] under the agency
regulatory radar screen" for decades, (see Exhibit 114), DuPont established in the 1980s its own
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For human exposure to C-8 through contaminated water, DuPont established a CEG of | ppb.
(See id.) DuPont also employes, including
began routine monitoring employees at Washington
ofthe levelsof Works, as early
C-8 as
in the blood of its 1981, (see Exhibit
own 118),
and
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Later in 1993, a study conducted by the University of Minnesota linked C-8 exposure
with also
increased prostate had been informed
cancer among that new tests
human males. (See were linking C-8 to
Exhibits 47 and 51.) DNA damage. (See
By 1996, DuPont Exhibit 60.) In
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1998, DuPont knew that oneofthe monkeys Suffering severe health effects. (See Exhibit
in 90.)
the study receiving a 30 By February of 1999,
mg/kg dose of C- DuPont knew that
was one of
the monkeys involved in the C-8 testing receiving the lowest doseofC-8 (3 mg/kg) had suffered
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exposure levels. (See id. and Exhibits 125 and 126.) Thus, because even exposure to the lowest
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0060.25
March 6, 2001 Page 6
doseof C-8 during the studies (3 mg/kg) produced adverse observable effects, a "no observable effects level" (NOEL) could not be found for C- in primates. (See Exhibits 105, 126.)
3M eventually notified USEPA of the preliminary results of the monkey study ina filing under TSCA, Section 8(e) during November of 1999. (See Exhibit 111.) Within only a few months, USEPA notified 3M that it intended to pursue more rigorous regulationofthe perfluorinated chemicals manufactured by 3M. (See Exhibits 113 and 120.) Soon thereafter, 3M publicly announced that it would "voluntarily" withdraw from the market allofits perfluorinated chemical products, including the C-8 that i sells to DuPont for use in DuPont's Teflon products, and the chemicals 3M uses to make its Scotchguard products. (See Exhibits 113 and 114)
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and that it had released C-8 into the air, water, and land at the Washington Works, into water at
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letter in Novemberof a letter dated January
2000, DuPont sent revised C-8 usage and release 25, 2001. (See Exhibit 136) Asoftoday's date,
information to USEPA however, the Tennants
in
are not aware of the results of the C-8 monkey studies having been "finalized" or published.
IL DuPontPromisedNot ToDisposeOf ToxinsLikeC-8In Its DryRunLandfill.
of
the
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seeking to buy several hundred acres landfill near the base of Dry Run
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be disposed of in the proposed landfill andthatthe Tennants would be permitted to graze their
5 3M's registered trademark.
0090.07
March 6, 2001 Page 7 cattle along the adjacent Dry Run Creek," the Tennants eventually agreed to sell a portionoftheir property to DuPont for constructionofthe "non-hazardous" landfill. DuPont received a permit to operate the Dry Run Landfill as an unlined, non-hazardous, solid waste landfill in 1982, and began actual landfilling operations at the Landfill in 1984. (See Exhibit 5.) IV. DuPont Has Dumped Thousands Of Tons Of C-8 Wastes Into The Dry Run
Landfill Soon after DuPont began operating the Dry Run Landfill in 1984, DuPont received the results of intemal sampling confirming that C- was leaching into groundwater beneath three old, unlined anaerobic digestion ponds at the Washington Works that DuPont previously had used for the disposal of thousandsof tons of C-8-soaked sludges. (See Exhibits 9, 17, 20, and 31.) DuPont's internal sampling indicated that, not only was C-8 getting into the groundwater that DuPont used for the Washington Works" drinking water, but C-8 also was migrating through the `groundwater under the Washington Works and into the Lubeck Public Service District's ("Lubeck PSD's") immediately-adjacent public drinking water wells. (See Exhibits 17, 18, 20, and 31.) Internal DuPont sampling confirmed C-8 in the Lubeck PSD community drinking water supply as high as 1.5 ppb in 1984, (see Exhibits 17, 18, and 20), increasing to as high as 1.9 ppb in 1987, (see Exhibits 19and 20), and further increasing to as high as 2.2 ppb in 1988 (see Exhibits 27 and 28. Seealso Exhibit 33.) Allofthese levels exceedDuPont's own | ppb CEG for community drinking water. (See Exhibits 2-4, and 9.) Upon receipt of those results, DuPont decided to try to remove the sourceofthe C-8 in the public and company drinking water supplies by digging up and removing the sludges from `Washington Works' three anaerobic digestion ponds and dumping the tons of C-8-contaminated sludge' into the Dry Run Landfill. (See Exhibits 20, 21, 22,23, and 26) After DuPont submitted data to the West Virginia Division for Environmental Protection ("WVDEP") asserting that the sludges were "non-hazardous" under RCRA, WVDEP granted DuPont permission to dispose of approximately 7,100 tonsofthe sludge in the unlined Dry Run Landfill. (See Exhibits 21,23, and 25.) DuPont completed the sludge disposal in 1988. (See Exhibit 6.) Rather than abate the presence of DuPont's C-8 in the public drinking water supply, DuPont simply purchased the Lubeck PSD well property and the wells were moved approximately two miles further down-gradient from the Washington Works. (See Exhibits 9, 30,31, and 97.) DuPont then notified its employees to immediately cease all samplingof the
DuPont even agreed to lease back totheTennants for cattle pasture significant portions of the landfill property along the Dry Run Creek. Those leases remained in effect until the Tennants began complaining about the Dry Run Landfill to USEPA. (See Exhibit 5.)
7 DuPont confirmed C-8 levels as high as 610 ppminthe sludge taken from the three ponds. (See Exhibit 9.)
009.
March 6, 2001
-
Page 8
former Lubeck PSD wells and to destroy all previously-drawn, unanalyzed Lubeck PSD well samples. (See Exhibit 29.)
Also in 1989, WVDEP informed DuPont that new landfill regulations had gone into effect in the State of West Virginia requiring existing, unlined landfills to be upgraded with more: rigorous waste containment mechanisms, including liners and more extensive groundwater monitoring well systems. (Ses Exhibit 32.) In response, DuPont installed a seriesof new groundwater monitoring wells at its Dry Run Landfill and at its nearby, unlined Letart Landfill in Mason County, West Virginia where DuPont had been disposing of mostofits Teflon and other C-8 wastes from the Washington Works as non-hazardous solid waste since the 1960s. (See Exhibit 121.) After DuPont's initial groundwater sampling at the Letart Landfill confirmed the presence of C-8 at 0.7 ppm, (see Exhibit 9), DuPont began investigating whether any C-8 also was leaching outofthe waste at the Dry Run Landfill. (See Exhibit 6) By April of 1990, DuPont had confirmed that C-8 was, in fact, leaching from the Dry Run Landfill and discharging directly into the Dry Run Creek at levasehligsh as 1.6ppm ~more than100times DuPont's `own intemal standard for drinking water of 1 ppb. (See Exhibits 9, 35, 37, 41, and 136.) Soon thereafter, DuPont abandoned its effortto seek anew permit for the Letart Landfill, and notified WVDEP that it had decided, instead, to simply close that landfill "for economic reasons." (Sec Exhibits 74 and 121.)" DuPont proceeded, however, with its efforts to geta revised permit for the Dry Run Landfill that would allow DuPont to continue to operate the landfill without having to installa liner. (See Exhibit 50.)
`After confirming elevated C- levels in the water at Dry Run, DuPont began investigating how to get rid ofthe approximately 7,100 tonsof C-8~contaminated sludge that it dumped into the landsill in 1988, which DuPont assumedwas a source of the C-8 being detected in Dry Run Creek. (See Exhibits 7, 8 and 38) Although DuPont initially notified WVDEP that it would remove the C-8-contaminated sludges from the Dry Run Landfill and disposeofthe material at its Letart Landfill, (see Exhibits 36 and 39), DuPont simply moved the sludges to another location within the Dry Run Landfill in 1991. (See Exhibits 5 and 6.)
By the summer of 1993, WVDEP inspectors noticed increasingly excessive amounts of Sediment and discoloration building up in the leachate collection ponds at the Dry Run Landfill. (See Exhibit 44.) In response, DuPont, despite knowledge that the leachate contained high levels of C-8 and despite knowledge thatthe Tennants' cattle were drinking the water in Dry Run Creek, ordered the drains on its leachate collection ponds opened for more than two weeks (after `monthly sampling had been completed (see Exhibit 45)), 50 that the leachate could flow out of
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--_--
* S<DPoupnPasorennetntstalonsfototihocereds{ee0rdoeirdmeptnehtreamtliaisnosdnfiioplnolndfdrraocimonuWolpVdeDfnEleodwidnir1e9c8tl9yainndtoaDgariynRiun n19C9r5eesko,twhiatthtohuetany P. (See Exhibits 34 and 55.)
* D1i9s9c5o,lo1r9e9d6,, f1o9a97m,in1g99w8a,tearndcoinnttionu1e9d99i.n) D(rSyeeRuExnhiCbrietcsk6t2h,r6o3u.gh8o9,utanthde9r5em)ainder of
000.57
March 6, 2001 Page 10
iron sulfide and 78)"
levels
that
had
been
fully
addressed
and
completely
resolved.
(See
Exhibits
5,74,
obfedienaitdiaictnaintOglcetaonabniednrsdpoeefcctt1i9ion9n6t,hofUtaShrEeeaPDoArfyctRohnuetnDacrLtyaendRdfuDinullPCorinenetrk.easnpd(oSniesneefoE(r0xmhtiehbdeittrhseecconomrpeaponrytsthoafthiutnwdorueldds
{SAoVyDDpEotPeE'ntsiaWwlaeatnefttoharDticveDimusePinootnn)atcftIoieroawnmaberyddeoUdfStUEoSPDEAuPPAo'nst paednrdaitngcoimnpslpeacitniton1, Ealiid5.MD6c4u,Cbouyyy(1v6di8it)fhfuOsnintghe
SLaaitncdhfaitnlhg.eeSt(faoStreeeDauEnPxdohniebtni'ttsesreSdaandco6n5s.e)ntWdietchrieneatomrabetlataretirfonugrftwthoeerethkgeosvd,eisDrcnuhmPaeornngttealpcroeomnbpflloeermtcseedmate1ntntheeggoDptriysatRiuonns
wSoouolndtahsesriesatRDeurPMorn.tMicnCcpooamyypmlleeynfittnWtgoVwWDitVEhDPtEhaePncdoonbfseaegn$at2n0dw0eo,crr0ke0ei0n-pgfePnoaolttthye.est&s(aSaemAeetsEDxohcuiibaoiitesss 5c.on6s7u,ltaanndt6t9h.a)t
7)
(See Exhibit
eimdpilteemdeAnustnipdnaegrrtuotphfgetrhSatedaetDsee'tcsoeltmahnbedefDirlrly1r9Reg9uunlsaeLttaitnoldneismleslni,tncsweuict1hh98aW8s,ViDansnEtdPacl,oatnDisuotPnruoocnfttitohfneintaylpye oafgrmeeedrtsoboesgoirns Egifouslplboeincoetcinaockneesdwyaistststeeemcs.oal(toSgteihceeaElDxrrhyiisbkRituassns6Le6asnsadmnfeidnllt6.9.)(SDeeuPiodn)tTahlusso,fibnyaltlhyeatgirmeeedUStoEoPcfeAaa.salecetfuaeacldlhiysposal of L{DiauenPndsofpinoltrltaalnldegheaddlyalhlaedgesdtloyppbeedgudniscpoolsliencgtoifngaciCts-i8vCi--tc8ioe-nsctoianntmtihanemaitDneradtyelRdeuabcnihoaLctaaenkdfeirisolllmuadtrgheeea1aaitnhm1e9y9D7fr,oyrRun (See Exhibtiottsh5e,W7a0s,hainndgt7o2.n)Works for treatment and discharge directly nto the Ohio Riven
aRdevpeorrstefBioymrpttahhceetsDernwyderoRefunc1l9eL9aa7rn,ldyfUielSvlEi.dPe(AnStereaelmEexoahnsiegbdinttuo7mD5eu)roPuUosSnEaatPniAdmr'aaslfst,orefpotrst EicnodilcoagtiecdalthRatia,slktAhsosuegshsment csrheeecamoiomcfmatelhneadsDetrdhyefuRcrlutenhaerrCcraaesuesskee,sosUfmStehnEetPoAbsheardvneodtpbreoeblneambsl.e t(oSeiedeindt.ifaytpa5lan2n)ytsUp,aSraEtniPdcAuol.tathrheekrrnesofwoinr,ee,regulcahteed ithmatbemiugnhdtsb"etchoantthriabdutbienegntdoettheectperadonbidnleivdmaesrn.itoifu(isSceaeetniivoidnr)oonfImnneurnmetseaplroonmusesedi"otaentitnhattsihveuegalgryeesdatoeifnoDtnirfaiytcfdRuun Creek -- f"eoovlelrabmoernattiavle"inevfefsorttigtaotifounr,thDeurPionnvetstiimgmaetdeicaotnedliytiroenqsueisnttehdeaanrdeaUoSfEDPryARagereGerdetcohd(isScueses 5
"DuPy9o1vn8ietFt.'ySsuopfppirt.asc1pt5ir2co4edsu(cwMti.stDhw.areGssapa.edcd1tr9e9tso5s)mea(dckoiinunrdgtetipamuiblploiisnc[etdnhroeevceEor.m$p1da0un0Py'osntkdneowNleemdogueorsft&heCo,
against DuPont).
million in sanesiors
000 :5
March 6, 2001 Page 11
d0EiiscblitohtseesDm7ro9yr.aeRnufdnul83lL.)yantdhPeialprlrteotcfhiatstheaDitudPecnootlnilttaibehsoaorfdaetniaovtce heofffotrtheinvcalruidoeuds DtuyPpoensto'fscahgermeiecmaelnstitthhaatd itduwomupledd
cP5e3o.tn)sfeiAnrtlmitenhdotCuh-eg8hDirDnyutPRhoeunnwtaLthaeanrd cbaecehntmiomnei,tDoruiPnogntC-ep8vreelnvetivueoalulsslliyyniiDddreenynttiRiffuiieneddCCfoo5nrc(hcsSfpboreeiy.negaro(snSlaeyned"Ephxohasidsbiibtly
almost 83)"
a
year
after
the
dfill USEPA
ina had
lcisotmopfldeotzeednisosfdrcahfetmRiicsaklAsstshcastoimt esnenytRepoUrtS.EP(ASeien
late
" 1998
Exhibit
KfiulnldinagnhiiuenncvdearsuetsdiegsoaotffioUhnSeiaEndPtoAof'tthsheepheeTraselitnshtonefanttnhcteocnaTcteetnrlnneasn(ttshcse:t
Esxohmiebtihti7n8g).i
the Dry ypu
Run also
Creek agreed
was to jointly
TiSmepreai,mnghowoawfsev1ce9or9m,9prtlieosscserdteohatfaent.are"fCeeawttdloezTeenaomft"hteo T"einnndaenptesn'dcecanattttltllyee"wiSenpvreecesitfeiivcgaaanltlesysi,ulDcushPliossnsutes`a.TghreBeyeCadttthianltethe
eaExnmhipimlbaoilysefeorwhmoanhyadyebaerse,n sienevoElxvvheetidebriinitnD2au4r)Pi,aonnastns'deslteihcnrtteeeerdnvaebltyeirDniuvnPeasortniiatgn.astisinoecnllsousdmtiyongegbpGyirUeegSffESePyckAtesos,faC-D8uPoonnt
T32enDnuaPnottsn9t5.cb)oywDtsehsewpeirrteceeeDndtruiPCno-kn8itn'mgsoonkukntoeofwyDlsretdyugdeyRutrhenastuClCrt-es(e8ske,we, aea.tgo,sxEixchiabniitmsa87caarucsin1o6g6e)n),(ta.hsart(etSeheneeforced
m2T3ee.nm)nbaCenortnsssoedfqouteehsnetnloCyta,titnldeiTcaetaemthdautrainnygotnhee fcrouormsDeoufPotnhte eCtavhteetrljedoifTsoecrlamomast'eisdonim,nuvcceuhsrtrfieagncatttsliyo1n0a.vtah(ielSaeobtelheEexrthoibtihet
iDmupPaocnttowfeCll-8beofnortehetthTheeernfeninaiansltnsCo'atecvlaitetdlTeene,cadeemstpRhiettpetohtrehteCwaratestllereaesTleoeeafastmehdeeivnCeDn-ceomnocsnikodeeyrssttuhdeyproetseunlttisalto
CUEaxSthEtiPlbAei-tTae1p0ap9mo.)i"niAtngedadeipnCe,antdDtelunePtTolyne"taimknevmpeetsmtcibogemaprtlesettwheoeluhylesdailltehnotfotnhethTeeCn-n8anises:uecaattnleu, seovbrean1c9tk9h9ao.nudg(hlSeettheethe
cs.
never have any reason oese 0 think to look at
tchoellTaebnonrOaavntetirsveht"haevefelfaosbrtetsetenoveiarndadalrnyedesaosruest,onvfwihtriholenemheDonustpPaioltnaptlrswouabfslfeewrmoisnrgikninthgewairtehsOUfSDErPyARounntChreerek, several of
_--
from respiratory problems, chemical
* DpArotynadrRoduurnnaidCnrtoehpeeeksnaewdmh,eer5te0imttehh,eatDftuePhwornfetomu,ala-igsnamiiennlg,lihonergdaedcroendtetnhtesDcroyulRdudnisLcahnadrfgielldisreedcitmlyenitnattoitohne in the stream just beyond the fence." (See Exhiobfitthse$1Teannnda8n2t,s "(ej weeswallowing
"AtlCheraeaveeskc.tom(tpSwleoeaioEntxehhdeirbtihltaostca5tlh4eriaersnicddaet1nt1tl7se.,a)ipnpcelaurditonghaatveeabsetenonheacrumrerdenbtyDsuoPmoentthienmgplionyDere,y aRlusno
009: 5%
March 6, Page 12
2001
ldbeiuasmccshh,aatreagnecdoflorlteohcmetriDouhnePasolyntstht'pesrmDotrbhlyateRmwusansafLtearnhdaiv,ingMobreeeonveexrp,odseesdpittoefiungsittailvleataiiornesmeivsesriaolnyscaanrd liquid
SSfuriomnmmgegertintotifong1t9hi9en9tDo,rtyheRDurnyCRrueenkCwrietehk,srueDpsuupPlotossnetads'tshoicpgarhceyavsemnotn7ictPoopnrbtianimgnintrhaeenpotcrstsfrcoomnftihremDtrhyatRCun8s [iaagsonsodfia
CcloiompeessDuePoonfnitt'ms tChaEat,nGddfeaossrpihCti-eg8hiinansstwa2al7tle.art6.iopnp(obSfeadeurpEixunhrgipbotirhytee1Fda3l4l)ofTh2u0s0,0D~urPeoraendeitkn,'gasoswmrnoercmeeonnttilhytyotarwsietnnhgety
Crenetki.nuing,
ongoing
discharge
ofhigh
levels
of
(of
fonleeachD.rycoRlluenctLiaonndfsiylslteimn,tothDerrye
is a Run
v. unt KaenThatsC8WassHaeLeach nt Driking wat,
eCfaftetcltes TuIepnoaanmddwmietiimlobndetrloosifDtutfhPheeoefnutCl'-l s8exifttaeihnlatusroebfteoiatnsdiksncolwosleedtogethreegTaerndnianngtsthoerntahteurUeS,EePxtAe-natp, paouiglnitkeedly
kfCunrloelewykld,eidstghceleooisfneftdohtreomafUtuSliloEnePxActu,ernrWenVtDlyEaPv,ailJaobglae] tSoroe(vlneeeamsTmieenngnntaaannldtscenoitnnitdtiiicneasu,teesiststtonheartieglDheuabPsoerosni,nttoalDsroyhaRsunyot
tofthe impact of 1s C5. wastes on local drinking watoer,the publi its
vTaorsttehemWaAanssahpgaiernmtgeotnfotintusWnoietfrsfk,osri,tnscDtluouPdcoionnmgtpltwehaetsethrirteseqeuRiCreRdAgo.FiacnivleisttyigIantveewsthiegtahteironaRneypoofrtis("fRoFrImeRrepsoolritdy
iatXrsePROcFSoIInntergfifaborunttysi,pnegDrutsoPoonansntytorteoulonekraesaesoofnawbalsetehseaolnttho.reninsekie.grhgb(ioSreeiedniEggxpehrsiotbpiieotrnstpi9eo8snadansnddth9wa9ht.e)wtehIrener calnoysewdasitnes19a8r3e,
fp{ohrraatintisgteoudswefsorfotrhedrsianmkpilnignwgaotfergmraotorutenhsdeawPmalptalee.rsou(fnSdetechetEhxgherionbueinitdgshwb1a0ot,reir1n1u,n7d6e,ratnhde 9W9a.s)hiDnugPtcooonnntnWeacoltsriokosn swiitteh
nWeaisghhibnogrtinnognpGlWaoEnrtkPdslra"isndikrciisnngdkriwinangtkewirna.gt(weSaotaeserhExishguihpbpailsts3.130
os PPL
11) and
SamgplGiEngPlcaosntficisrmPeladnCt-t8haitn as higahs 0.71 ppb in the
GE the
uses
_--
y. (Sen Exhibits 10, 11, 43, 76, 96, 99, 102, 104,
"ti+WssassulhtnisonttgeotdUotnShaEWto,PraAklstihn(oiwutesglhRlFsDIu3P3R1oe,nt33h2a,dabnede3n36s)a,mphleinsg othrceaemderitnikmiengtowaactteuralwleyllrsepaotrtthe
ccooponlevsern,wieenlnoltrltdyhiaddtidhandotpreevveinoussalmyppyloieretlt,dheeDduweCpl-olnstrtehwsaatuslttrcaldaoiftsi)otnhaalsylay|mhppapdlbey(iowenellldly 3t3h6e),drainndkingthe
h9e9)s.ultYoeft, w1.h9 pepnb,DeuvDPeuonPnotthnetrewfpeaolbrlrtiwtcihatethseedthaheingeCh.wer3r.ree0saudpliptnstgsintfraodiptiFonRalelpyorbt.elo(wSeed1eptEhpxebhhiyibigiehtlesdre7dC6,.3g96,
ohawvninpglatnotrderfienrkeinncgewaantyerd.ri(nSkeiengExwhaitbeirtr9e9s)u.lts excee"dsicnrgeeDnuiPngonlte'vesl"owfonr C1 -p8pbtoCaEvoGidin its
Gain
March 6, 2001 Page 13 106, 110 and 129.) DuPont even found C-8 as high as 0.8 ppb in the new Lubeck PSD drinking water wells, which are now located approximately two miles farther away from the Washington Works site. (See Exhibits 10-11, 40, and 41.)" Recent sampling of the private drinking water wells on the Tennants' property down-gradient from the Dry Run Landfill also has now cwohnaftiCr-m8edleCv-e8lsimnitghhotsebderiprneksienngtwaattvearrwieolulss.cit(iSeseealEoxnhgibtihte 1O3h1i.)o RiDvuePro,nbtasheads uevpeonn iDnuvPeosntitg'asteodngoing releasesofC-8 into the River from the Washington Works facility. (See Exhibits 40, 100, and 118.) Approximately 24,000 pounds ofC-8 also is discharged directly into the air every year from the Washington Works Site, although it is not clear that C-8 is actually permitted for Such air discharge by DuPont. (See Exhibits 101 and 118)
Thus, it is evident that the residents living ina least the area near DuPont's Washington Works facility, Letart Landfill, and Dry Run Landfill (the "DuPont Sites") may have been and may continue to be exposed to DuPont's C-8 through DuPont's on-going and continuous releases of C8 into the air, land, and water at and/or around those Sites, (se Exhibit 80), including direct ingestion of C-8 in the C-8-contaminated drinking water extracted from wells at the Washington Works Plant, the neighboring GE Plastics Plant, the Lubeck PSD well fields, and private residential and agricultural properties near DuPont's Sites." Local wildlife and the environment may be similarly exposed. Despite DuPont's knowledge for years of the nature, extent, and effectofthese C-8 releases on human health and the environment, including the
Sampling results from 1991 confirmed C-8 at2.4ppb in the new Lubeck wells with C-8 levels ashighas 3.9ppb in the tap water of several local, Lubeck-area homes. (See Exhibit 128.) Sampling in Augustof 2000 confirmed C-8 still present in the new Lubeck PSD wells at levels as high as 0.59 ppb. (See Exhibit 119.) "DuPont has been evaluating the levels of C-8 in the Ohio River, which is a source of drinking water for numerous communities, since at least 1982.(See Exhibit 15.) "In August of 2000, after the Tenants had made it known to DuPont that they had become awareofthe C-8 in the Lubeck PSD wells, DuPont drafted a letter for the Lubeck PSD to send to its water customers to "disclose" the existenceofthe C-8. (See Exhibit 124) In that letter, however, DuPont was very careful to refer only to thecurrent C-8 levels in the `current Lubeck PSD wells, and avoided any mention whatsoever ofthe earlier C- readings that were substantially above DuPont's 1 ppb CEG.(Seeid.) DuPont again was careful to avoid any public disclosure of its knowledge of earlier C-8 drinking water results that were well-above DuPont's | ppb CEG in recent statements provided to local Parkersburg newspapers, even though DuPont had received in November adraft of this letter referencing the higher C-8 levels. (See Exhibit 135)
060017
March 6, 2001 Page 14 bioaccumulative/biopersistent nature of the material," it appears that DuPont has allowed and continues to allow these releases to occur unabated for fear of not being able to continue to make its Teflon products,ifit cannot use C-8. This situation is particularly disturbing, given that DuPont apparently has knownofways to remediate C-8-laden soils since the early 1990s but because of the expense, chose to do nothing "pending further actions that may be dictated by the EPA for remediation of the Washington Works site." (See Exhibit 122.) Even more disturbing is the fact that DuPont has known for years that C-8 levels in the Washington Works and old Lubeck PSD drinking water wells far exceeded its own | ppb CEG but has done absolutely nothing in response. DuPont has chosen, instead, to focus either on current, somewhat lower C- levels, or to simply fabricate a totally new drinking water "screening level" of3 ppb for the Washington Works Plant when faced with havingto disclose to USEPA in its RFI report for the Washington Works the existenceof C-8 in the Plant's drinking water at levels well above 1 ppb. (See Exhibits 99 and 124.) VL DuPont Should Be Ordered To Remediate Its C-8 Releases And To Immediately
Shut Down Its Manufacturing Processes Involving C-8 Until Adequate Demonstrations Are Made That There Is No Unreasonable Risk To Health Or The
Envienmeet,
Over the years, DuPont has successfully avoided fully disclosing thenatureand extent of the C-8 problem at its Dry Run Landfill by characterizing C-8 as an unregulated "non-hazardous" waste and/or substance under applicable law. Consequently, when the Federal and State agencies have asked questions about the nature and quantityoftoxic wastes handled by DuPont at the Dry Run Landfill, DuPonthas omitted any comprehensive discussionof C-8 on the grounds that itis nota "hazardous waste," "hazardous substance," or otherwise listed or regulated waste under current laws. DuPont shrewdly avoided any permit limits on its C-8 emissions and/or dumping atits Washington Works facility and Dry Run Landfill through similar corporate strategies. "Thus, although DuPont has known for years that C-8isan animal carcinogen and bioaccumulative/biopersistent substance, it has continued to knowingly dump thousandsoftons ofthe waste into the environmenat unlined, uncontrolled landfills and has allowed the waste to be disposed directly into the air, Ohio River, and local drinking water supplies, arguing that there has not been any improper disposal and/or release ofany regulated material.
In addition, DuPont has been careful to refer to the chemical in conflicting, inconsistent ways in its filings with regulatory agencies - sometimes calling it "C-8," sometimes calling it "FC-143," sometimes calling it "PFOA," sometimes calling it "APFO," and sometimes calling it by its full chemical name- "ammonium perfluorooctanoate" - thereby making it difficult for the agencies to understand how all the information interrelates. As confirmed by USEPA's recent
"DuPont's own employees even raised concerns about Teflon customer exposure to C-8 as early as 1983. (See Exhibits 16 and 52.)
06a 4
March 6, 2001 Page IS proposal to begin regulating 3M's previously-unregulated perfluorinated chemicals, DuPont's past corporate strategy for diverting regulatory attention away from C-8 should stop now.
Based upon the foregoing facts, the Tennants hereby respectfully request that your agencies intervene in the Tenants' pending Federal Court litigation and order the immediate investigation, assessment, containment, removal, and remediationof DuPont's on-going C-8 releases into the environment by virtue of the authority granted to your agencies under at least the following laws and their implementing regulations:
+ The Toxic Substances Control Act, as amended, 15 U.S.C. 2601-2692; + The Federal Clean Water Act, as amended, 33 U.S.C. 1251-1387; + The Safe Drinking Water Act, as amended, 42 U.S.C. 300-300}-26; + The Federal Clean Air Act, as amended, 42 U.S.C. 7401-7671; + The Resource Conservation and Recovery Act, as amended, 42 U.S.C.
6901-6992k;
+ The Comprehensive Environmental Response, Compensation and Liability Act, as amended, 42 U.S.C. 9601-9675;
+ The West Virginia Air Pollution Control Act, W.Va. Code 22-5-1 through 25-18;
+ The West Virginia Water Pollution Control Act, W.Va. Code 22-11-1 through 22-11-28;
The West Virginia Groundwater Protection Act, W.Va. Code 22-12-1through 22-12-14;
The West Virginia Natural Streams Preservation Act, W.Va. Code 22-13-1 through 22-13-15;
+ The West Virginia Solid Waste Management Act, W.Va. Code 22-15-1 through 22-15-21;
+ The West Virginia Hazardous Waste Management Act, W.Va. Code 22-18-1 through 22-18-25; and
00035
March 6, 2001 Page 16
+ The West Virginia Hazardous Waste Emergency Response Fund Laws, W.Va. Code 2219-1 through 22-19-6.
`The Tennants also request that your agencies exercise their respective authority under the referenced laws to order DuPont to immediately cease and desist its C-8 releases into the environment, as addressed in this letter and to provide for immediate, appropriate medical careftesting/evaluation ofthe Tenants. The Tennants further request that DuPont's permit to operate the Dry Run Landfill be immediately revoked until adequate scientific demonstrations are made to prove that the C-8 releases have been abated, will not recur, and pose no unreasonable risk to human or animal healthorthe environment.
`With respect to minimizing harm to the public health and the environment from future C8 releases, the Tennants hereby specifically request that USEPA exercise its authority under the Toxic Substances Control Act to order DuPont to immediately cease all manufacturing activities using C-8, including DuPont's Teflon manufacturing operations, until DuPont either confirms that it has stopped its usageof C-8 entirely or has made adequate scientific demonstrations to prove that ts continued usage of C-8 (whether from 3M or any other source) does not pose an unreasonable risk of injury to heaolrtthhe environment. In the meantime, the Tennants request that your agencies take these steps necessary to regulate C-8 emissions/releases to the environment. As mentioned above, the Tennants believe that such steps should include, at a minimum, including C-8 among the list ofperfluorinated chemicals that USEPA proposed in Octoberofthis year to begin regulating under TSCA on the basis that the chemicals "may be hazardous to humanhealthand the environment." (See Exhibit 123.) VIL The Tennants Intend To Bring Citizen Suit Claims Against DuPont Under The
CWA, TSCA, And RCRAIf Appropriate Action Is Not Taken Immediately To
Abate AndRemediateDuPont'sC-8ReleasesFromItsWashingtonWorksFacility.
As explained above, DuPonthas beenandcontinues to discharge C-8 from its `Washington Works Facility in Wood County, West Virginia into the air, groundwater, and Ohio River. Moreover, the C-8 discharged by DuPont has been contaminating and continues to contaminate the land, air,and human and animal drinking water supplies.
A. DV uPointo ls latTihen CWg A.
Section 505(a)(1)ofthe Clean Water Act ("CWA") permits citizens to commence a civil action against "any person ... who is alleged to be in violationof (A)aneffluent standard or limitation under this chapter." 33 U.S.C. 1365(a)(1). "Effluent standard or limitation" is defined under the CWA to include, among other things, "a permit or conditionthereof issued under Section 1342 of this tile," such as state-issued but federally-enforceable NPDES discharge permits. 1d. at 1365(F). Based upon information currently-available to the Tennant, DuPont's NPDES permit for its Washington Works facility specifies that DuPont shall not discharge any
006uis
March 6, 2001 Page 17 effluent in violationof applicable Water Quality Standards. (See, e.., WV/NPDES Permit No. SWtVa0n0da0r1d2s7p9r,ohCiobintdiDtuiPoonsntA.f1ro-mA.d1i0s,chCa.r1g2i,nganindtoH.s2)u.rfaTcheeorWgersotunVdirwgaitneirasWaantyer"mQautaelriitayls in concentrations which are harmful, hazardous, or toxic to man, animal, or aquatic life." W. Va. Code St. R. tt. 46, 46-1-3.2 (2000). Based upon currently-available information, as described above, DuPont has been discharging and continues to discharge C-8 into surface and groundwater in concentrations exceeding DuPont's own CEG for human drinking water and at concentrations that are otherwise harmful, hazardous, or toxic to man, animal, or aquatic life, constitutinag continuing violationofthe West Virginia Water Quality Standards, and thereby constituting a continuing violationof DuPont's NPDES permit terms and the CWA. See, e.2., 33 USS.C. 1311(a), 1342. Notice is, therefore, hereby provided that the Tenants, onbehalfof themselves and a class of others similarly situated, intend to file suit against DuPont, pursuant to Section 505(a)(1) of the CWA, within sixty (60) days of this notice to obtain appropriate relief for the violationsofthe CWA referenced herein.
B. DuPontlsViolatingTSCA.
Section 20(a)(1)ofthe Toxic Substances Control Act ("TSCA") permits citizens to commence a civil action against "any person. . who is alleged to be in violation of [TSCA] or any rule promulgated under Sections 2603, 2604,or 2605 of [TSCA], or Subchapters Il or IV of [TSCA]" 15 US.C. 2619(2)(1). TSCA requires any "person who manufactures, processes, or distributes in commerce a chemical substance or mixture and who obtains information which reasonably supports the conclusion that such substance or mixture presents a substantial risk of injury to health or the environment" to "immediately" inform USEPA of "such information, unless such person has actual knowledge that" USEPA has been adequately informed of such information. Id, at 2607(e). TSCA also requires each person who manufactures or processes a chemical substance to comply with the regulations adopted by USEPA under TSCA governing the reporting to USEPAofcertain research and adverse health effects information relating to such chemical substances. See id. at 2607(a), (c), (4; 40 CF R. Parts 716 and 717. Failure to comply with such TSCA requirements constitutes a violation of TSCA. See 15 U.S.C. 2614. As indicated above, the information currently available to the Tennants indicates that DuPont has not reported to USEPA all information within DuPont's possession regarding C-8 that is required to be reported to USEPA under Section 8(a), (), (), and (e) of TSCA, 15 US.C. 2607 (a), ), (4), and (e), such as the resultsofthe C-8 monkey studies andtheTennants' allegations of adverse health effects among themselves, their cattle, and area wildlife arising from exposure to DuPont's C-8. Notice is, therefore, hereby provided that the Tenants, on beohfthaemslelvfes and a classofothers similarly situated, intend to file suit against DuPont, pursuant to Section 20(a)(1)of TSCA, within sixty (60) days of this notice to obtain appropriate relief for the violationsof TSCA referenced herein.
000417
March 6, 2001 Page 13
UIDnumdPmoeinrnteR'nsCtRCAA-n.8dRSeulbesatsaenstFiarloEmnIdtas nWgaesrhmienngttoTnoWHoerakltshFOacrilTirtyeEMnavyirPornesmeennttAn
permits
Section citizens
7t0o0c2(oam)m(e1)n(cBe)ofactihviel
RaecstioounrcageaCinosnts:ervation
and
Recovery
Act
("RCRA")
pr[reaealstneymneptnettr,rsaosnntsoproar. ,gteeir,n,colorurddpiiasnspgtoasonarlyppfraaecssitleinottry,opwrwenhseoernhtoargseocnpoeenrrtaarttoiorbr,utopafastor tirsacnosnptorritbauttioinn,g oor dtihseppoassaltoofrapnreysesnotlihdanodrlhinagz,arsdtooruasgew,asttreeeadwthomirecnhwt,,ho moratyhepreensveinrtonamnenitm,minent and substantial endangerment to healt
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naogtaiicnesttoDuoPbtoanitn,appuprrsouparnitatteoreSleiceftifoonra7nt0h0dae2(icaml)am(si1sno)e(fnBo)ttoharenrdRsCssuRibAmsit,laanwrtilitayhlsiientnundaitanenedgt,eyir(nm9te0en)ntddatyosfiolfe stuhiits
herein.
referenced
rreegdaureds,t pPflloeeraayssoeeulcreotinunfsviorklmnvaoesmwiesfnotyonoinuastwhpiioslsismiinpbtolerertvhaenontwepiyunobultihrcerTheeesapnlentcahtnitavsnedageennvciireosnpmleannttsopasddsr:ess Ionurthat ' Federal Capps proceedings or if
0060618
March 6, 2001 Page 19 yCionuciwnonualtdi olfifkiecetso. reWveiewwoaunlydofbtehheapapddyittioomnaeletbawciktuhpydooucautmyeonutratoifofnicmesaitnotdaiisnceudsshetrheisatmaotutrer in more detail. Thank you.
Onbehalfof the Tennants,
4 A. Bilott
RAB/mdm
Enclosures ce: Larry
A.
Winter,
Esq.
(West
Virginia Counsel
for
the
Tennants)
(w/o
encls.)
Paula Durst Gills, Esq. (Counsel for DuPont) (w/ encls.)
(by CREERGTIISFTIEERDEMDAMIALINLON:O:700R0401600000090229490,69R6E3T53U1R,NRERTECUERINPRTERCEEQIUPETSRTEEQD)UESTED &
Reg(isCtTerCeodrpAogreanttiofnorSEy.sL.tedmu,P7o0n7t dVierNgienmioauSrtsree&t,CEoas,t,InCch.a(rlwe/sotoennc,lsW.)V 25301
by CERTIFIED MAIL NO: 70000600002406963500)
HATENNANTReqs wd
069013
1 00629
w" --
oss73515
Material Dsuapfoentty.Data Sheet TTTo
Revised soiar-1999
Page 1 --
Pristed 6-MAT-1999
CHEMICAL PRCOonpD ANYTU omRICITIE GATI) ON TTT
Tradeames aad Syacarms
TT
200 Ammonium Perflucrooctancate Solution
Company Idestification
KANUPACTURER DIS`TDRuIpoBnUtTOR
W1i0l0a7inMgatrokne,t OSFtre1e3t898
PHTPONrrEaondsuwpcuotMrBtEIRnESfmoerrmgaetnicoyn :i C1H-E8M0T0R-E4C41-17-581050-424-9300
Medicil Pmergeacy |: 1-800-441-3637
CoFOSTTION)INFORKATION ONINGREDIENTS Components
TTT
WRaEteSrHR pereivorosctancate
S3hii-mieers 830
EAZARDSIDENTIFICATION
oT
Potential Health Effects
asSamksoihun.ntcsoEnCtvaaicpdtaebsclmeea'yosficsagpuesrseoedsusckihinnagcLtehsreeiitneatfpifoaencttewsaittoihfonsdyisSsticeaommifscoercturorin
toxicity.
SEyheaecionngtacStr mBaylEctanugsteoreye iiroritation with discomfort,
PIanshsaalgaetsi;onWimatyh Ccoauugsehinigrraintdatdiiosncoomftotrhse. uTpTp"er resplrato:Sl
aaIbbnnngooerrsmmtaaillonbllsioavoyedrcaffuousrnemcitgniagosncsryaossltndetemetseftcuitnnecadellbotyhrwalacibttohraLtaeonrreiyatlaat:itoenssts; or
ctTchohoinemstp,aobcloufotdn.o"dmpohAuasnsntidrmaeaailmsloafannbgosdlholhraoblwiefimd-nalgbifyeexInptgehierensitebtinohocden,eyblaiionnnoddhdia,mclaaatytaeinbodtnehmodeartyetestbckhetiiesnd in
i)
00902
g EID087263
W?o essasis
Material sDaufpeotnytData Sheet
Re 2
(HAZARDS IDENTIFICATION = Continued)
detected years after exposure.
meIaxnccdzeiosvwsiidmvueaaylsexhpwaoivsteuhriepnsrc.ereexaissetdinsgusdciespetaisbeislitoyf ftohethLeivetro,xiocritbyonofe
carcaogenicity Information
.
NSPoqenuaeaiol'fnotoohfedGceornmaptoenrenttshapnreOs-e1n%tarien tlhiisstemdatbeyriIaAlRC,atNTcPo,ncOeSnHtAratoiFonAsCGIH
FIRST AID WEASURES
TT
rice Ad
INHALATION
C1aacleliL?oiahaclipehadyl,sirceriseapmnio:cvaetitoon.fresIhf barlre.athiInfgnoits AbLrEefaitchuilntg,, ggiivveeoxygen.
SKIN coNTACT
sIhn0o:ecsaa.tse 1oC0faalsltcona1t5apchmtyi,sniuctLiemasend.wihaitlWeealsyhLecmfoolnvutisahnmgisnckaiotnnetudaimccihnlaopttlehadinnccgylbooecffhoiurnegsearrenudse.
Eve contact
Ifnorcaatseloefastcon1t5acmti,nuttemse.disCtaallly'sfplhuysshiceiyaens.wich plenty of water
GESTION
CIvatolmilst'uissnlgPl.ohvyesdiN,ceivaeLnrm.egdilvaetealnyytghiivneg 2byglmaosustehstoofawnatuenrconasncdioiunsducpeerson.
FIREFIGHTINGKEASURES
CT
Flammable Properties
Non-tlamable.
HmZoaonzroamxceidddoeud,surdhiyendcgroomcgpoemobnnuiscfttliouononr,ipdreo,dTuhcettsossxicpLrnogcdalusucedtsisnogrmcaapyzarbctoainucsledeisosxeiavadeyer',ebeceyaez,bon
nose, and thioat irritation of toxic effects:
8
00c5n02n5
EID087264
8
:.ossrasis
Dupont.
Material safety Data Sheet
Page 3
(FIRE PIcHTING MEASURES - Continued)
9
Extiaguisnisg Kedia
Water Spray, Foss, bry Cheatcal, coz.
Fire Pightisg Instructions
eHqeuairpmseenltf.-contained breathing apparatus (SCEA) and full protective
ACCIDENTAL RELEASE MEASURES
CTT
Safeguards (Personnel)
NPsOEeTRcESt:OiNoAnRLsevsPiRetOwoTrEFeCIpTRIErVoEFcIeGEnQHdUTiIIPnNMGgEVNKITEAhdSuURCrEilSnegaannculdpg:iHnA-NuUDpsLeeINaGpp(rPoEpRrSiOaNtNEeL)
TT
bErveaactuhaitnegpearpspoanrnaatlu,s. thoroughly ventilate ases, use self-contained
Initial containment
Dike spill.
pull clean up
Soak up with sawdust, sand, ofl dry of other abeorbent material.
EANDLINGAND STORAGE
CT
CT
Eandiiag (Perscanel)
vcWMaeoisnkrhteci,ultnahfstootirhaoaonlnucagsthailnedytnh,aTateftspepArirvrooadhltuadoncrdecloinrantregaes.cptuisreawWdbia.lesenh apcylaeorstt,hiicnlsgeksinaufscolerecscssloetsehaiintgva.boiisd
Eandling (Physical Aspects)
Keep container tightly closed.
storage
Store in a well ventilated place.
99
g
0090335
EID087265
2
: oss73s15
Material DsuafpeocnytData Sheet
rage 4
ZXPOSURS CONTROLS/PERSONALPROTECTION| Eagineeriag Controls
TT
Svgparrneeayonhleeyqdueiewpdimcehenxttardaa uefdqeuraltoOsescvC"e3hnhatvnielra6t0Sioopnat.i,caunad.tdeexhwaourskt'areGsuc.a ts, Ddd orinopt Epalnse, 2ofnaootvheerrspdreasyi]gn features to minimize worker exposire th Personal Protective Equipment
EYE/FACE PROTECTION
Wear safety glasses or coverall cheaical splash goggles.
RESPIRATORS
Wear NIOSH approved respiratory protection, as appropriate. PROTECTIVE CLOTHING
Wa3h"eraepprtohperrieatLes poLtmepnetriviaolusfgolrovseksi,n capornotna,ctpahnatvse, avanadilajbaclkeeta.nd wear Exposure Guidelines
ARppalniocnaibulne FEexfpfoisuuorreooLcitmaintcsate
ATESVLL + (((aDocusspuiol)n)t)
+i+ 00N17on00e11 amEggs//taaa33b,,li8s8hfHerrd.. TTHHAA,, SSkkiinn, A3
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PEYSICAL ANDCEEWICAL PROPERTIES Physical Data
FFBororelmeliznigngPPooiinntt
irPoLiicqeuimd.onun
CT
g
g
EID07266 009034
SL osssis
Material DsuafreotaytData Sheet
N SIE REIS
Page 5
fae mmspees chitin ioe tise Ghaxical seability
EE
Stable at normal temperatures and storage conditions.
Incompatibility with Other Materials
None reasonably foreseeable.
Decomposition
Hazardous decomposition products including carbon dioxide, carbon
fnoosrem,edandduritnhgioactombiursrtiitoant.ionThoefsstoppircoduecftfsecmtasy cause Severs sya,
Polymerization
Polymerization will not occur.
ToTicorooToAL TWPORGAEION
Animal Daca
-
Ansontun Pesfluorooctanoate:
iImnahlale3at5io%mn 4 ehoursLCSO: 9g80earamhg/mml inanernaattes , Nok
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dfceoarnsmspailar"nadtsoupbPeeruirteaclupelrneso,du`cdeldanandroinhlsaispv;eecrlieeftnihcaragfyf,ecitansbtorsXsidchsbirn1e2glawetehiigshgt
aR1neodspse;accyda'ndgousesixstp:reonAciensstineapgsarlt]oeduiLcnregideisttalitioivenorn,exanpKdiodsneuenryle,arrfgeaesndscirtLaeisdvseri,nanudeight
tdieensnctoiendsaetnrccaheatneogfeusbm;eonriaigngneamnitiaecstainacdcutlicayvrai,ntoyspiabsna.csreeTdaetsoitncs,anIannimdnaclr1eeivaersraetds
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Ganairmaaglee.in Bacterial cell culbures but has nat been Cested ln
3g
0090i5.5
EID087267
4 osstsis
Material sDaufpeotnytData Sheet
Sin eee
rage 6 enna
Ecotoxlcological Taformation
on
Az18mohnoiuura P0e5r0f,luofraotohcetaadnciantnao:va: 1,500 og/L.
.
DISPOSALCONSIDERATIONS Waste Disposal
CT
TCareceqcauotirmadetanintoc,nes.wsittohragdep,p1itcraanbsipsorFteadteiroanl,, aSntdatdei/s?poovsianlcimauls,t baandiLnocal
REGULATORY INPORKAZION
Cm
015. Federal Regulations
TSCA Inventory status : Listed. TITLE IIT RAZARD CLASSIFICATIONS SECTIONS 311, 312
AFCcihuriteoenic i|i nYYoeosn
PReraecstsiuvriet|y i: NNoo
.
OTHER INPORKATION
Cr
NFPA, NPCA-ENIS
~
HFNePlaCalAtm-haHbNtIiSteRyating
i:3o
Reactivity
to
cPoenrdsiotniaolnsP.rotection rating to be supplied by user depending on use
Tshpeecdiaftiac miantetrhiiaslNadteesriiganlateSdafehteyreiDnataandShedeotesrenloatterselaotnelytotoutsheein COmbination with any other material of in any process.
Responsibility Address
for
MSDS
+
CDJ.hiaraoSb.retcCao'SaptWeeocsrikaslty
Chemicals
Telephone
809-546-3281
g9S g
0650625
EID087268
: - osanas 15
Material DsaufpeotnytData Sheet (Cont tnued) 2nd of KsDS
rageve 7
39
g
EID087269
=
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t
2
prrAcH MENT Z js TSCA cB
pen 30! ooooold
No san Fired Versiom was provided.
CoGL2%
3
66023
) 0A8n/t0h4o7n2y00J0 P0l:a0yt4isAM
Toi H David Ramsey/AEDuPoni@OuPort
Subject: C-8 Exposure Linits
:
FE
.
Hethreinefor'matsion on C-8,aka ammonium perfuorooctancats.
Du Pont Acceptable Exposure Limit (AEL)
0.01 mg/m3,8-hrTWA (skin); "oNrotdeevlelyoptmoebnetaalhtuoxmian"n carcinogen
Du Pont Community Exposure Guidelines (CEG)
>
ADrbinokmineg Water 01.u0g0i0L3 mgim3
ACGIH Threshold Limit Value (TLV)
0.01 mgim3 TWA (skin, A3); The A3 notation means the folowing:
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OSHA Pemnissible Exposure Limit (PEL)
None established.
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REASONING BENIND AEL
INHALATION NDAEL 1 Mo/M3 EFFECTS AT 8 MG/M3 MILD, REVERSIBLE
LOW LEVEL (?) ACTIVITY IN [ESTES (TUMORS)
30 PPM IN DIET = 1.5 MG/KG/DAY
.
100% 10.5 warm ABSORPTION OF JNHALED DOSE, 70 KG WORKER =
THIS IS 1) EFFECT LEVEL 2) HUMAN CLEARANCE FROM BODY SLOW
SAFETY (UNCERTAINTY) FACTOR SHOULD BE LARGE (1000)
RECOMMEND 0.01 MG/M>
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AS FOR THE AEL (0.01 MG/M3, ADDITIONAL FACTORS 1) 24 HR EXPOSURE IN COMMUNITY VS 8 HR AT WORK 2) DIVERSE POPULATION IN COMMUNITY 3) BIO-PERSISTENCE IN MAN
RECOMMEND 0.0003 MG/u> (33 FOLD REDUCTION)
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HUMAN EXPOSURE
Source
Air Skin Adsorption
Ingestion
PreventativeMethod
* Reduce Air Levels
* Breathing Protection
* C-8 in Solution * Chemical Gloves * TYVEK Clothing
* Reduce Concentration in Drinking Water
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DRY RUN LANDFILL CHRONOLOGY -- 1995-1398
August 1994 January 1995 MFaerbcrhuar1y9/95early M1a9r95ch/April
March 23, 1995 May 1995
May 3 June 1995
October 1995 November 1995 February 1996 October 15, 1996 November 1996 December 31, 1996
Filter cake begins to be landfilled at Dry Run TSiSrstexnceoetdiecneceo;f s*tbalratckofwahtiegrh BOD/COD results; Pond Improvement Team organized Addition of antifoam
Wdiattcehresdraainndagferenicmhprdorveamiennstsi:nstdailvleerdsion bCaehngetuminiocaa(mls)ultfrecaotnmternotl,ofhyfdilrlogearneap,eropxoindde,, outfall
Cindy Musser inspection and recommendations Bcoelgliencntiinognofonewneheaknlceydbmaosinsitoring and data
Second sedimentation pond installed Cindy Musser inspection: progress noted tLoabhitgehstTiOnCg pcroonbfliermmsed filter cake contribution
24-hour aeration begun in lower pond Algae control: copper sulfate treatment Lower pond visually improved WIAP-TV news story
Mfuasvsoerra/bBlyritivmepcresisnesdpewcittihonpr(oagtreosusr invitation): aZentdo,HilHlillo,f MLuasndsfeirllinosppeercattiioonnto acquaint Zeto maDecEetPtioinnseswudueed80ltlioedtWtavesarhsitoenfgtmioannntaegWnoetrmketsno't fsfitlaaeinlducarirevdislto Pinal filtercake disposal at Landfill DtEoPseitstslueemdenOtrdeofr aalnld Wiasssuheisn,gtoinncWlourdkisngapgaryemeednt of $250,000
c
EID089743
&
009025
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cDeocnetmibneured31, 1996,
February 1997 March 1397
June 1997 July 1997 December 1997
EDnuvPiornotnmaenndtatlhePWreosttecVtiirognin(iWaVDEDPi)viseinotneroefd a
ospeetrtalteimoenntaangdrmeeamiennttenapnecretaiofnintghe tDorytheRun
aLgarnedefmielnlt., DAsuPpoanrttaogfreethde toseptetrlfeomernmtadditional
mdiaticnhteesn,ancteranosnpoerxtistlianngdfiwlalterledaicvhaetresioton
Washington Works for improvements planned
tforreattmheentlanudnftiillldeasreign
cfoimlptleertceadk,e ainnd thsetopladnidsfiplolsaluntoifl pdlaenstign
ciommpprloevteemde.nts planned for the landfill are
Acaultfo)psyredfeornse itno B*eelmparcei,atiOoHn,(6p-omoorntnhu-torlidtibounlall state; intestinal parasites.
Autopsies (2 older cows) done for EPA:
i1.n t"Thheeseontlwoy asniigmnailfsicwaanst tloowxiccoolpopgeirc finding dcoinecteanrtyraptrioobnl.em, Sainnacleystihsisofmayfeeidndiiscate a r2.eco"mNmoensdiegdn.ificant pathologic findings." i3.n t"hNeo tliovxeirc, ckoimdpnoeuyn,ds uwreirnee doretefcatt.e"d by GC/MS*
EPA ecosystem study
vPeutbelircinaherairainngi;nteirnpcrleutdiendg taeusttoipmsonyydaoftaloacnadl acnoinmcallusd,ingbasnoedLaonndfiinlflo ienffetchte oanutotphesyaurteopporstised
Draft report of EPA ecosystem study
Doc 60531
9
2
EID089744
g=
3
000046
DRY RON LANDPILL EVENTS TIMELINE
++ NAUMECROUQSLDERUAYSREIUS.NR.P.R.OErPvEvR+DT<Y......0.0.0.i.i.u.i.u.s.e.s.s.i.i.ieioeosooeioeeesoseenenninoiL..Ll..
1982-1983 1983-1986
TcEoNwANsT
+ BEGAKNAULFAMNADNFILL OPERATION............eeveesessnnnnnnnneaeeen. 1984
DISPOAL RELOCATIOONFOFTFETFPEOPNODNSDEMDAITMEERNTI.A.L..(.S.U.P.E.RN.A.T.E.)..T.O..L.I.N.E.Dc.CoEeLcLc.c.c.c... 11908/925/91 ++ DSITSAPTEOSAINLSPOEFCFTLIUODNG.E..OF.D.RY.RvUsNeSTsAeRTsEDi.u..v.e..s..e.e..ii.i.i.ii..i.ii(oSriUeMieMeiEnRsn)s 9035/O1R69/944 ++ BEFIGLATNEDRIPSRPEOSSSALINOSFTAFLILLETDEARTCAWKAESTEINDWARTYERRUTNR.E.R.T.M.E.N.T..P.L.A.N.T.................. 0098//9944
+ BLACKWATERAPPEARED...............ccovsreeesnnsssssnaaannns ++ TEINNANNTMSADBEPYSSTTE RAETAEC MDVEIT PDTEEOINSV.O ...N .....PR.OT.N...........................c....i...i..i........... ++ RIONSUPTEICNTEIOINNSPBYECSTTIAOTNE.O.F.D.O.W.N.S.T.R..E.A.M.B.E.G.A.N..............o.c.c.c.o.i.e.i.i.i.i.i.i.i.i.l... ++ BILNASCPKEWCTAITOENRPBYROSBTLAETME SEONLVFEDO..R..C.E.&.M.P.EE.R.NM.I.TT...W.R.I.T.E.R.............................. + TENPNOAINSTONCIONNGTDAECTEERD"D&NWR V(EDLEKPITNSOFOFAFGI.C.E.).rAeBeOsUoTsr"vSeTeReEsAMsssnunnnnns + TENANT BEGAN TALKING IN COMMUNITY ABOUT CATTLE LOSSES........
01/95 A0P3-/M2Y39/S95 0055//9053/95 1005//9955 192S/P9M5-96AM
+ DISCUSSION WITHWV DEPT OF AG VET, WV EXT SERV AGENT, &
++ EWPAASHISNOGITLON&WWAOTREKRS CSAOMMPMLUINNIGT.Y..R.E.S.P.O.N.S.I.B.L.EerCsAsR0EeeTeEeAeMenSnTnAnRnTnEeDs.s.s.s.s.s.. 0101//9262/96
++ FDRREASFDTOMCOMOPFLAIINNFTOFRMRAOTMIOWNVADCETP.R.E.Q.U.E.S.T..B.Y..D ....U ...7.0P .E.P.A.O ........N ........T ...... 1101//9066/36
++ TBEERGRAANDODNI/SPPOOTSEASLTAO.F..F.I.LT.E.R.oCrAeKeEenAsTssNcOeRTsHeWeEuSsTsnLsAaNeDeFnILnLn.n.s.n.n.s.s.s.s.s.s.
11/96 12/96
+ ADMVIINOLSAETTITOLNE.NENeTe ReEnAsCsHvEsDssWeIsTnHnsWnVssDnEnPnsCnOsNnCsEnRsNeInNaGnnAsLssLnEnGnEnDseeenns 12/96
+* DIBESGSAENCTTRIUOCNKOIFNCGLAETATCLHEAVTIEDBEOA.C.K..T.O.P:L:A.N.Tsi.c.i.i.i.i.i.i.e.eoessssvsvevisseirieensesnnns
+* NROETSIPFOINCSAETTIOONBPBAY..EP.A..O.F.C.OrNsCoEeReNsSiQaUaEnSsTsIaOeNn..i.i.i.e.i.i.e.e.i.i..e.s.e.i.o.s.e.s.,.
* MESWIT T(HLCEIOGMISMNLUANTIGOTRYS L-EACDOMEMRUSN.I.T.Y..A.W.A.R.E.?...-.E.C.C.)...............
++ ETPOAPEENHVIORUOSNEM"EFNOTRALCORMIMSUKNAISTSYESASTMDERNYTSRAUMNP.L.I.N.G........................................
+
LFLEUTOTREIRDTEOSSAIMTPELEESMPTLAOKYEENESBYBDYuPPOLNATN.T.M.A.N.A.G.E.M.E.N.T.....................................
* PERMITAPPLICATION PUBLICHEARING.............................
0021//9977 02/97 0053//3270/37 0066//9977 0076//2273//9977 07/97
+* CSEPAESLETDERDIBSEPCOASMAELOISFSAUBS.B.E.S.T.O.S..A.T..D.R.Y..R.U.N....................c.o.o.i.i.i.s.o.e.n.s.s.s.s.s 0031//9081/58
++ BIENGSPAENCSTEICOUNRBIYTYSTPAATTBR.O.L.S..O.N.W.E.E.K.E.N.DcS..c(cCeOeNiTReAeCuTreAeGaEsNeCsYa)e.i.i.i.i.i.o.n.n.s. 0067//9087/98
.Z
* MEETTHIENMG WIINTEHBWAVACDTEIPVIOTFYF.I.C.E vOvFtvWvAeTeEaRnQ nssUssAsnTLnOsnIEnNnT GnAsGYsEessneeens 07/98
S
EID089745
O5LLY
6
009015
DL DRRYRRA UUNN LN ANDFD ILL:F CC--8I HHIISSL TORYL SSUue: umRyY
SUPERMATE POND SOIL DISPOSAL: ~O7F1N0E0ATRONTSHEOBFOSTOTIOLMCOOFNTTAHIENLINAGND~FI8L5LPP1M1/8C8-.8 DISPOSED ~TAHNIDS BSUORIILEDWAISN MAOVCELDAYT-OLITNHEEDTSOEPPAORFATTEHECELLALND1F0I/L91L.
O C-8 GROUMDNATER AND SURFACE VATER MONITORING: ~ BEGAN MONITORING ANNUALLY FOR C-8 IN 1991. ~ GROUWDUATER CONCENTRATIONS RANGE <1 - 15 PPB. ~ LEACHATE CONC. AT O.F. 001 RANGES 30 - 200 PP. PRARNOGPEESRT2Y -BO2U5NDAPRPBY.STREAM CONCENTRATION
~ D1A9T91A RAENPMOURATLEDREAPNORNTU.ALLY TO WVDEP BEGINNING WITH * 1998 RESULTS: OLUETALGEUTTE001 == 1567 PPPrBB SSTTRREEAAMM ##12 == 41.6 ePPBB PROP. BID. = 0.88 PPB
77 POUND/YR C-8 DISPOSED OF WITH BIOCAKE (930 pes). O 610/9M6;PODUONEDSS/MYORTOCFONFTALIN UC-8G. ROWAPSTEODILSPOYSAML REEGRAN
006G19
EEZy
EIDO78867
2
|
C-8HISTORICALPROSPECTIVE
+ Known Contaminant Sources - Supernate Ponds (Closed 1988) (Excavated Soll removed to Dry Run Landfill) Excavated Soil Levels - 234 ppm Max Residual Level in Remaining Riverbank Soil-173 ppm Max
- Lubeck Public Service Division
Test Well 27 - 1-2 ppb
Employee Water Taps - 1-2 ppb
= Letart Landfill Landfill Leachate - 3 ppm
Groundwater Wells - 1.6 ppm (Poss. Construction Cont.)
- Dry Run Landfill Landfill Leachate - 0.7 ppm Leachate Stream at Property Line = 0.1 ppm
+ Regulatory Knowledge
- EPA SWMU Survey - 6/5/85 C-8 in trace levels in Supernate waste C-8 found in ppb levels in aquifer
- NPDES Permit Application - 9/2/86
Surfactants In 002/005 Discharge (Not specific mention)
- Supernate Sludge Disposal Request - 7/30/87, 8/23/90
Supernate Sludge contained 85 ppm C-8
= Lubeck Public Service Division - 6/13/89 C-8 has been found In aquifer in ppb levels Stated no health hazard
- Letart Landfill Permit Application - 9/21/89
C-8 in stream and wells reported in required analysis
[EERE
EID080125
]
Am TahneacacienptoafbltehislemveeletionfgC-i8s tion bdiostchusssurwfhaacte wsahtoeurldabned cgornosuindderweadter 2cnodnttaomindaetvieolnopatathpelanDtrysRturnatelgayndffiolrl.dealing with the C-8
Review:
Discuss:
AGENDA .
Cc--88 -- wOhvaetrviieswito?f limits and guides SSouuprecrenatoef pC-o8ndcosnltudagmeina-ti1o4n,00at0,0D0r0y Rpuonund-s = cL-o8cactioonncenatndrataimoounnt- 2o7f5cpuprmrent known contamination
wWahtaetr?is an acceptable level of C-8 in surface Wwhaatter?is an acceptable level of C-8 in ground Baacsteidonontothbeesetakleevnelast, DwrhyatRunisatthethiaspptroipmreiate
Some
optiNoonsA:ction,
monitor
for
further
cCaopntmaamtienraitailonin place, monitor for
MfouvrethmeartecroinatlamtionatLieotnart landfill
NIenwcinteercahtneology
cRaOlcining
Ton Exchange
000633
EID0S0103
ATTACH MENT 9
is TS cA
eB IL:
074
G30!ti020e040version
ben
No
sani
was PT vided.
009654
|
PFOA Concentrations
Washington Works drinking water
1999
02-05 ppb (building samples)
1899
0.082 ppb (drinking water wells)
1998
w1e.l9,ls1).0, and 0.4 ppb (drinking water
Outall 005
1890's 5060 pp
GE Plastics drinking water
1999
0.5 ppb (drinkingwaterwell)
Lubeck Public Service District OI LPSD we+lWWlwesll 27
2000
1992 198488
2144QQ:: 00381,50,440.,51a6n,da0n.d3103.2p1pbp.pb 02,0.4,a0d0.09 ppb 9samples ranging from 1.02.2 ppb
Ory Run Landfil
1089
Leachate
34pp0
Outet 001
66 ppb
Stream Sampling Staton No. 1
054 ppb
Stream Sampling Station No.2
87ppb
Property Line
3990
Letart Lanett
2000
MonitZoorniengAwells are identifiedby Zones, with A ne.arestthe surface and Fthdeepest.
MwWt
17.400 ppd 219 ppd
Zone OEM3
2100 ppb
Zone FMw
172 ppb
MMW.254B
1045330p0p8d
MWS
34pm
Blood Monitoring Data
1995
None higher than ppm. Previously, levels had been detected up to 33 ppm.
EID089310
005036
oO
PFOA Concentrations
Washington Works drinking water
19w9o9
1998
Outta 001
Gopte | , 1999
a dig
GE Plastics inking water
1999
Lubeck Public Service Distict
1230200
1982
Ory Run Landfil
1959
Leachate
Outeton
Stream Sampling Station No. 1
StreamSampling StationNo.2 Property Line
02-05 ppb (building samples)
:
ooszess (nngvarve 1%
19 ppb arinang water wet) pTPb.
vet Git
wr
66pm
wr
0.5 ppb (drinking water wel)
rE 3
&
08,044, and0313pe
02.04,009 ppb #2Ww
34ppb
spp
0.54 ppb
87 ppb 9pp0
= alr
Lethe
ee OT
en Tp
Letart Landfit
2000
MoniZtoorniengAwells are identified by Zones, with A nearest the surface andF the deepest.
wWeTt
17,241080 ppppbb
Zone DIEws
2,100 ppb
ZoneFMw
172 poo
MMWWAB
1,405330 ppppbb
MWS
34 ppb
Blood Monitoring Data
1905
Nonehigherthan pp. Previously,levelshad been detected upt33 ppm.
0090 :5
EIDO8SS16
|
000:9
|
=
:
-
cc: CRl. JR.. CBaumrpgebrell J3.. RL.. GBrraonaqduwiasyt R2.I JT.hisztilpefetlon GC.. AH.. RSotboiltnzson 3K. FGl. RDrooungbhetryg
C-8 COMMUNICATIONS MEETING OUTLINE, TALK & CHARTS
ii
C7./31E./80STEINER
:
!
PERSONAL & CONFIDENTIAL
3
i
.
EID079399
t
0g
:
TTT
c. E. steiner
. INTRODUCTION
SCh-o8r'ts dC-e8sirhaibslteoryproicnesTsFEqu&alFiEtPieMsanufacture
TOXICITY
oral toxicity - slightly toxic
e Compare to other compounds
skin contact - slightly to moderately toxic
Inhalation toxicity - highly toxic
ee CCoonmcpeanrterattoioontsherfocuonmdpoiunndasrea are lower
:
INITIAL BLOOD TESTS
OuMrDaRteasults
RECOGNIZING EXPECTED OPERATOR QUESTIONS - A transition
ssohmoertdihsibsetloiryeveofbcahseemdicoanlspasitn eixnpdeursiterynceshowing why we are careful
MEDICAL RECORD STUDIES
Nsotudeiveisdentcheoroofughhealth problem
PROVISIONAL AEL
NAoEtL cyoemtmiftitremeAEhaLs set provisional AEL of 0.55 mpb This vdearyy low number is to protect people who work with C-8 ever The lorweapsroonviwseioanraelmAaEkLingandchagnogaelstoinreeqduuciepmebnltoodandflpuroorciendeuriess.the
EQUIPMENT TMPROVEMENTS
GIonaglredtoienrtesducaeddietxipoonsurheoodtoansdolisdtaCc-k8, airborn C-8 and C-8 solutic
RElaiimsiinnagteDryWeerigAhiinrgsCuiptprliycIAncliedtsin C-8 hood
SAdedailtDiornyaelr DLeraykesr Windo; ws
RIenmcorevaisneg VC-e8ntfirloamtiDornyeDrurEixnhgausOtustages
. 006.5
EID079400
:
.
2
:
PROTECTIVE EQUIPMENT
Clothing and Gloves
Needs to be disposable to prevent secondary contamination. An EOD is being prepared to evaluate clothing.
Different protection levels for 3 exposure classes
Breathing
cEqounicpemnetnrtatiiomnpsrowvielmlentsstiwllillremraeidnuceinaisrobmoernaereaCs-.8 but high C-8
@ Breathing air will be installed - ultimate: solution.
Comfo II air respirator with GMAH cartridge acceptable.
TESTING Personal Air Samples Will Resample. Blood Samples FBrleoqoudenstamspalmipnlgiwnigllisbenotrenseumceeds.sary. Area Air Samples OWfitllenceoxncteineudeprtoovidseifoinnaelpArEogLrebsesf.ore
improvements.
SUMMARY
C-8 is People
wtoorxikcinbgutwitchanC:b8e
ghaenndelreadllysaafeclcyu.mulate
organic
fluorine
in
ptohteenbtliooadl,. and levels generally correlate with job exposure
Although not
this has caused tolerable.
no
health
effects
continued
exposure
is
our
basic AEL,
agnodalsto arreedutcoe roerdguacneicexpfolsuuorreisne tolebveellsowinthbelopordoviosfional
This weixlplosreedquwiorrekeresquiapndmenprtecvheanntgeasccutmhautlaatrieonbeiinnngedwomweo.rkers.
It
will of
barlesoathrienqguiarieruosre
orfesdpiirsaptoosrasblefoprrocteercttaiivne jcoblso.thing
and
us
One otchoenrtroilnlgirnegditehnitsiehnatzairsd.needed- -- your cooperation in
~ 06503
&/570 EID079401
'
=8 COMMUNICATIONMEETING
The purpose of this meeting is to bring everyone up to
date on our findings regarding C-8, our immediate program , and
our long term plans.
Most of you know that C-8 is a fluorochemical surfactant that is used for producing fine powder, dispersion, granular and
FEP. It has unique properties that allow it to wet Teflon's
surface, shorten reaction cycle time, stabilize dispersions and
provide sites for reactions. It has been used for Teflon manufactu:
for over 25 years. Other chemicals have been tested but none
match C-8's properties. Four years ago it was introduced in
|
FEP manufacture where it was a manufacturing improvement.
Let's look over the highlights of the Technical history of C-8. In 1965 tests showed that C-8 was slightly toxic when
swallowed. This was not surprising. There is a dose level where
almost every chemical becomes poisonous, even water. (Chart 1). This chart shows the oral toxicity of C-8 relative to some common
chemicals. These tests were done on animals, and represent what
dose would kill 50% of the animals tested. I've scaled up the
dose from test data to animal weights comparable to an operator's
weight. You can see that C-8 is not as toxic as acetone. It has a lower toxicity like table salt.
C-8, like table salt, can also be absorbed through the
skin where it is about as toxic as it is orally. But, based on
this low toxicity, no change in our safety program was necessary.
. 009083
EID079402
Sa.
In 1969 it was found that C-8 was more toxic by inhalation,
Chart 2. This second chart shows the approximate concentration
that will kill test animals in a
4 hour period. This
approximate lethal concentration for rats exceeds anything we have
measured in the plant.
plant is about 1/4 of
at the feed end of No.
The highest level ever measured in the
that level -- and that a 1.lmpm leak
3 dryer which has been repaired. The other
C-8 concentrations are generally about 1,000 to 10,000 times lower
than this so people working in the area see no immediate effect. (.004-
mm
However, since 3M informed us in 1978 of organic fluorine
being detected in the blood of their employees who worked with C-8, we have been reviewing and expanding our C-8 program. We have
concluded that personnel routinely exposed to C-8 will absorb it
in their body. Tests at Washington Works show that blood fluorine
levels which indicate C-8 levels generally correlate with
potential job exposure.
result in accumulation of C-8
that we are studying with the
is eliminated from the body.
Repeated exposures can
in the blood. One of the things
blood samples is the rate that C-8
Some of theoldtimers remember when C-8 was treated
with less respect and they wonder "Why is it suddenly harmful now?"
0050as
EID079403
.
a.
Throughout the chemical industries over the last S50
years this story has been repeated with the same disbelief but
often with more drastic consequences.
For example, carbon tetrachloride was used to clean
auto parts and as a fire extinguisher for years, and now it
is known to cause damage in some people and is used with care.
The same story has been repeated several times for things like
.
chloroform (which was used in cough suryp), methyl alcohol and
other chemicals.
|
The difference between the ending of the C-8 story and
the others is that Du Pont is reacting while C-8 levels in the
blood are low and before any damage is done in the body.
The `medical data show that no one has been injured by
C-8 (Chart 4). The Medical Division after a thorough study has concluded that ". . .there is no conclusive evidence of an
occupationally related health problem among workers exposed to
C-8." All that was noted was a small increase in two liver
enzyme levels. After 25 years of handling C-8 we see no damage
among the workers. However, the potential is there -- C-8 has
accumulated in the blood. Because of this accumulation we have decided to undertake programs to minimize accumulation of C-8 in the blood of new workers.
+
086025
EID079404
a-
The AEL Committee of Haskell Laboratories has set a
provisional Allowable Exposure Limit or "AEL" at 0.55 mpb of C-8 in air. This very low proposal is based on a safety factor
of 800 below the level where reversible liver effects were
observed. An AEL is the same thing as a TLV or EGL -- it is a
safe concentration in the air of a working environment.
In order to meet the expected low AEL, equipment changes
are necessary to protect from solid, liquid and airbora C-8.
The next transparencies show the changes that have been
made recently to protect against C-8 exposure. To date we have:
.
Modified the Fine Powder/Dispersion ingredients
addition hood to reduce C-8 emissions and bring
the mixing operations into the hood. C-8 tools
will also be stored in the hood where possible.
.
Improved the C-8 addition hood exhaust stack.
`The hood exhaust stackwas close to an H & V inlet
on the roof.
. Removed operations that don't have to be done in
the C-8 hood -- like citric acid weighing. This
has reduced exposure of concentration to the operators
The dryers have been improved also:
Air supply inlets have been raised to remove
C-8 rich air from the ceiling.
000033"
EID079405
e Seals of No. 3 dryer doors and seams have been improved.
Inspection windows have been added to reduce need to open dryer doors.
We have also put guards inside the dryer that will permit
using the exhaust fans to remove C-8 when dryers are being cleaned.
This has reduced some C-8 concentrations, but more work is to be
done; for example, we plan to cover injection pump tanks, seal
openings in floor and vent oscillating feeder compartments, sealing
.
No. 3 dryer fans.
The next chart shows the three
different protection
levels required for three exposure classes: Low dry exposure,
high dry exposure and wet exposure. A disposable garpentsof the
appropriate design, gloves and air protection are recommended for
each of these exposure classes. Sample gaments have been selected
and an EOD will be run to evaluate this clothing. Tyveke was
selected over cloth or paper gaments because it is light fairly
resistant to tearing, a good filter and disposable. Disposability
is required to prevent secondary contamination when laundering.
During this EOD, sample gaments will be tried and evaluated by
operators and mechanics.
C-8 will permeate all glove materials over a period of time. New flock lined latex gloves will be used in jobs where C-8 exposure is likely. Even these gloves will be permeated
by C-8 over a period of time, so these gloves will be disposed of after each shift.
0055
EID079406
-
-6-
Breathing protection is very important to reducing c-g
exposures. Equipment improvements will reduce airborn C-8 in
most areas but there will still be areas where exposure is possible. A COMFO II air respirator with a special GMAH cartridge is required as a minimum. Breathing air is better and will be available soon.
The yellow 3M masks are not acceptable.
I've had some questions on future C-8 air samples and
blood samples. We now have our baseline data and have mapped
out the problem areas. The procedures are modified and
equipment improved so C-8 exposures will be reduced.
.
Blood sampling will probably be done on
an annual basis in the future to define the real improvements
in C-8 control.
Let me summarize the items covered:
.
C-8 is toxic, but it can be used and controlled below
the proposed toxic limit.
In the past, people working with C-8 have
accumulated organic fluorine in the blood and levels
generally correlate with job exposure potential.
.
Although this has caused no health effects, continued
exposure should be minimized .with controls.
. Our objective is to reduce exposures to below the
provisional AEL, and to reduce organic fluorine levels
in blood of exposed workers and to limit accumulation
in new workers.
.
06s
EIDO79407
-7-
This will require equipment changes that are partially comp It will also require use of disposable protective clothing
and use of breathing air or respirators for certain jobs. One other ingredient is needed -- Total Division
cooperation in controlling this material.
065035
2 EIDO79408
13 069579
t
Lo
|i
~
(
M4 a
we
AwE t oa r
8 BLOOD S:
NG RES!
Births and
Cnt) PPM C-8 a one
0.45
Pregnancies
.
wo,
Status
TNorramnaslfercrheilddou- tboorfn FJluunoer1oc9a8r0b.ons
4/79.
0.28 0.078
1.5 0.013 2.5%
Normal child - born April 1981..
Normal child Umbilical cord
born Apr 1981. blood .055 ppm.
Fimvoencha--pregnant. On PUfHAr%Lupe
Sis gonchnprsgans. Tm child 2h I
CUhniclodnfi- rm2epdluesyeyeaanrds.tear duct defect.
0.048
20007
BChEilIdSos- cFr&iJhleanntdBieo,egyeoarf defect.
pa il =Arhm wh 19
#C`buerfroernetpbrleogondanclye.vel - in fluorocarbons area only one month
Berd ON EE
009.71
E1D07e: 7
yO
\
ie,
1.
e = - a a1
i
i
cc: JW..TF: AF..AgTBeeohwoemra~s
sils" 37.00.00
September 21, 1981
1
TO:
J. J. DI NICOLA
crow: D. u. snvoerCif
I
'
msaicron oaks
LANDFILL FACT SHEET
1
Ref:
((21))
JLL.eettttL.eerr,StD.oC.weHl.Wl.,SCnry9/od1we1er/8tt1oo,
CE.. WR..
same
KCirmomweel,9/A1./81L,.
title.
Sskaimnenetritlaen.d
|
reviewed
Attached by phone
is on
a copy of 9/16/81.
the Landfill Fact Sheet which we It will be used by J. R. Draper of
|
octwhonenetraRsce.tasl wEistthatelanDdiovwinseirosn. ofItGeniesrailn Sreersvpiocnesse tDoeparreqtumeesntts inbyhissome
|
this with C.botW.h CLreogwael oafnd thPeubDleicparAtfmfeanirtsa.l ETnhgeiynehearsveOfafpipcreoverdeviietweedase.
);
/3as(1669)
Attachment
|
I
i EXHIBIT
0656s
g
EID022224
LANDFILL INFORMATION
The landfill will contain nonhazardous wastes only, including ash from plant boilers, waste plastics, glass, scrap metal, paper, and trash, all transported by covered truck or closed containers.
It will be designed and operated with full consideration for neighbors. The ash will be wetted, and the road will be paved to control dust and mud. The fill will be covered with dirt at the end of each day.
|
Daytime only operation is planned. The site could receive
'
10 to 14 truckloads per day.
The probable start-up date is late 1983.
CIE
EID02225
15
000675
The miracles of science'
Study Title MODELING RELEASES OF AMMONIUM PERFLUOROOCTANOATE INTO THE OHIO RIVER
Author William R. Berti
Draft Report Completed on
May 22, 2000
Performing Laboratory
E. I. du Pont de Nemours and Company Environmental and Microbiological Sciences & Engineering
Corporate Center for Engineering Research
Central Research & Development
Glasgow, Building 300, P.O. Box 6101
Newark, DE 19714-6101
Report No. EMSE-054-00
4 CCR
4 CORPORATE CENTER FOR ENGINEERING RESEARCH
,
Page10f8
EID108608,
`CONTAINS CONFIDENTIAL BUSINESS INFORMATION
009673
DuPont EMSE Report No. 054-00 GENERAL INFORMATION
ChemicalStudied: Ammonium perfluorooctanoate Synonyms/Codes: C-8, FC-143
DuPont Notebook No.: Not Applicable Sponsor; ER.ob1.erdtuPPionncthdote Nemours and Company BARLML CRP-711/2210-B
Study Initiated/Completed: September 1999 to May 2000
Z g
Page 20f
EID108609
CONTAINS CONFIDENTIAL BUSINESS INFORMATION
00077
DuPont EMSE Report No. 054-00
AMMONIUM PERFMLOUDOERLOIONCGTARNELOEAATSEEISNOTFO THE OHIO RIVER
SUMMARY the timePdDurMinigndtihceatyeeadr.thCat-8C-c8onccoenncternattriaotnisoonfsionft1h.e0 rgivCe-r8w/oLulwdouelxdcebeede0x.1c"eegdeC-d8a/Lb.ou9t05%o0%ftohfe time during the year and 10g C-8/L about 2.2%ofthe time during the year. Excel spArveeardasgheeeatnwnauasl0C.-4823cogncCe-n8t/rLa.tiMoonsdeilnetdheCO-hicoonRcievnetrractailocnuslaitnedthbeyriuvseirngraangMeidcrforsoomfta hliogwhoafn0d.1l9o9w rgivCe-r8f/lLowisn,Mraerspcehcttiovealhy.igAhvoerfag0e.9O65higoCR-i8veLrifnlSoewpstaenmdbevro,lwuhmiecdhatcaorcraelcsuploantdedto `fPmlraoondtme.lt,TheThihUseSrBiGevleelorelvfoilgloilwceadDlaatSamurisivstehoyenwctalhosesecOsohtlilleooccRtaeitdvieoartn dt1h3oewmBnieslltelrsevediaolmlwenfDsrtoarmmetahamenodfpltuahsnetedwWihanesrthheienthsgiptsroetnaydpWseoheorefkts information is available.
StRuedpyorCtonPrdeupacrteedd nbdy:
eport Prep
WSeinliloiramReRs. eaBrecrht Biologist
-- @ae)
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EID108610
CONTAINS CONFIDENTIAL BUSINESS INFORMATION
009078
DuPont EMSE Report No. 054-00
INTRODUCTION/PURPOSE manufacCt-u8ri(nagomfmoTneifulmonperaftlWuaosrohoicnagttaononaWteo)rkiss.a AflupoorritniaotnedthseurCf-a8ct(a1nt8,u4s1e6dkign itnhe1996) was Trehleeamsoeldetcoultahre wOehiigohRtiovferC-a8s pisar4to31f.a0n98NgP/mDoEleS. pOetrhmeirttperdopreerlteiaesse offorCt-h8eafraecilliistiyed(WbVe0lo0w0.1279).
HMeaadltehbryat3inMg Coof2mpany Exposure limits 0.01 mg/m' skin 8 hr LBDO,Dac=unteiloral rat = 680 mgrkg +BiBodCeFgr=a1dation = nil MpolHec~u5la(0r.f5o%ramquuleaoCuFs),(CF,,COONH," + pMeKlat=i2ng38po(i-ntCO=O5H6)-58C (-COOH) COD =700 mgke + WaKtoecr=2s5olubility > 1000 mg C-81L Vapor pressure (at 220) = 7.1 * 10% mm Hg. expecteOdutro oobcjceucrtiivnethweasOhtioocaRlicvuelratdeotwhnesctornecaemntorfattihoenNsoPfDCE-S8 ptehartmictotuelddoruetafaslolnaatbltyhebeDuPont Washington Works.
MATERIALS/METHOD WashingRteolenaWseosrokfsaPmlmaontriwieruemmpoedrfellueodrouoscitnagnotahteeP(roCb-a8b)iltiostthiec ODihliuotiRoinveMrodferlom(tPheDMDuBPeotnat cVoenrsstirounct4e.d0 MBiectraoJsuonfet11E,x1c9e9l9s,pUreSadEsPheAetOfmfoidceel.ofCP-o8llruetlieoansePdraetvaefnotiron19a9n6dwTeorxeicuss)edanidn aboth modeling exercises. numberoPfD0M50i3np0u2t0s2i0n3c9l,udaemdetahenNsPtrDeEamSflnouwmobfe4r.7of5EW+V00040m1i2l7li9o.n lTihtiersscpoerrrdeasypo(nMdLsDt)o,a arelaocwh Srtelreeaasmefdl3o3w5ofda9y9s8/0y.ea4r7,MthLeDloaanddinagnweafsfl5ue5n.t13f8lokwgo/fda2y1,6a.n7d5 tMhLeDw.astWeewaatsersutmreedattmheanttCe-f8fiwciaesncy 1w0a5s00%g. CW-8e/LthteondveatreiremditnheetCh-e8CcOonCcepnetrrcaetnitonofaysetahreeCxocneceednetnrcaet.ion of Concern (COC) from 0.1 (USGS:M<ichrpowsaofttedEaxtcealusspgrseagdsohveiemtvuissewd/WrivVerdfaltoawcdoamtpaofnreonmt thie sUScgGseoaltooguimca=l03S1u5rv9e5y30-), T1h0i/s1/i1s9t7h4e 1m0e9a/n30d/a1i9l8y5r.ivTehre BfleolwleivniclulbeiDcafmeeisseocnmtehaesOuhrieodRaitvtehre 1B3elmlievlielsledoDwanmstfrreoammofthe zg wWhaesrheintghtisontyWpeorokfsinPflaonrtm.atTihoinsirsiavvearifllabolwe.daTthaisisrtihveerclfolsoewstdalotcaactoiomnpadroewsnswterlleawmitfhrOomhitoheRpilvaenrt 23 m`AomnntyhCloyrapvseroafgEengfilnoewesrast (Pfiittpsib/u/rwgwhw,.PrAd,-wHeu.nutsiancgetaornm,y.WVmi,l/aMnodntChilncyi_nhniamt/i),.OTHhefraovemrtahgeeUdSaily 2 trihveenrcfolnovwerftoredthteo mthoentavhewraagsecmalecausluarteedd ffrloomw pavearimloanblteh.daWtaebaestsweuemnedthtohseeCt-w8owdaatsesd.isTchhiasrgweadsto the river at a constant rate except for the monthofOctober when production at Washington
Page 40f8
CONTAINS CONFIDENTIAL BUSINESS INFORMATION
0967Y
EID1086 1
DuPont EMSE Report No. 054-00 W18o,r4k1s6 iksgusCu-a8ll(y40s,u6s0p0enIbdsedC-f8o)r adninvuiadledmbayin1t1enmaonncteh.s.WeTaablsesusmheodwtshatthtehreestuolttaslodfitshcihsargeofwas spreadsheet model
RESULTS/DISCUSSION
the timePdDurMinigndtihceatyeeadrt.hCat-8C-c8onccoenncternattriaotnisonosfoinft1h.e0 rgivCe-r8w/oLulwdouelxdcebeede0x.c1eegdCed-8a/bLou9t05%0o%fotfhe stihmoewsdumroidngelthienypeuta/rouatnpdut.10. C-81 about 22% ofthe time dring the yar (Table 1) Figure |
using aAMviecrraogseofatnnuEaxlceCl-8spcroenacdesnhtereattimoondseilnwtahesO0h.i4o23RigveCr-8c/alLcu(lTaatbeldeb2y).cMoonsdterluectdiCng-8and concentrations intheriverranged from a lowof0.199 g C-8/L in March to a high of 0.965
g
C-
SRIiLveirnfSleopwtsemabnedrv,owlhuimcehdcaotrarceaslpcounldatteodhfirgohmatnhdelUoSw Grievoelrogfliocwasl,Sruerspveecytiwvealsy.coAlvleecrtaegdeatOhthieo
BmeillleesvidlolwenDsatrmeaamnodfustehde WinasthheinsgptreoandsWhoeretksmoPdlealn.t.TThheisBreilvleervifllloewDdaamtaoins tthheecOlhoiseostRilvoecarti1o3n
downstream from the plant where this type of information is available
=
Page Sof 8
EID108612
(CONTAINS CONFIDENTIAL BUSINESS INFORMATION
00963G
TABLE 1:
DuPont EMSE Report No. 054-00
Pyreoabrabtihlatistthiec cDoinlcuetniiornatMioodneolf(CP-D8Mw)illrebsueltesxocfeeCd-e8d cionntcheentOrhaitoioRnisvaern.d percent of `SonfceCn8ation|| Pceorncceennttrofatyieoanr exceeded
----1
1
Css]
TT rr
Te]
eT el 1]
C TS or 07
50
70
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EID108613
CONTAINS CONFIDENTIAL BUSINESS INFORMATION
000CEL
Table 2.
2
DuPont EMSE Report No. 054-00 OMihciroosRoifvterExcel spreadsheet calculationsof modeled C-8 concentrations in the STE Tow| Measured Tow|CH serge Oo| ESmated C3
River in 1996 River concentration in Ohio
rrrr
LeE y 5 oes weer[LeSOm 2 0 B-- [Oewber|Ssow-- |[ vZS|UoE ooR
r II .r .%2. 50 1 vas
=
Page7 of 8
EID108614
CONTAINS CONFIDENTIAL BUSINESS INFORMATION
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EID108615
005a5
.
PERANSDCOONFNIDEANTILAL
TRP..NAT,.hisFTotaslyteletorro'n October 13, 1982
To: Re 0. 2IPFEL Frou: 0. G. LoscHIAv) QH.oX.
ESTIMATE OF HUMAN C-8 EXPOSURE RESULTING FROM DRINKING OHIO RIVER WATER
drinkingAs Oyhofuo rReiqvueerstweadt,er.T esAtsimaateredsuhlutm,anI'evxeposfouurned thoumCa-n8 eaxspoasurreesutlot Co-f8 tFoinebePvoedreyr lDorwy.er Uesxihnagus1t9)8,2 pmearnsuofnasctwuoruilndg bceonedxiptoisoends t(oanad Cn-o'B sdcorsuebbrionugghloyf Jeeqcutievdalemnatnuftoact0u.r0i8n%g ocfontdhietioancscepftoarble198e7xpos(wuirteh lsicmriutbbi(nAgEL)o.f FiUnsiengPowpdreortDorye0r.3e8x%haoufstt)h,e pAeErLs.ons Itwouslhdoulbde aelxspoosebde tmenatoionCe-8d dtohsaet rCo.u8ghlisy meoqrueivatloexnitc vWioauldtheTnianchtaulaaltiitoyn breouteeventhalnovterh,e oral route. Therefore, these percentages of condiHtuinoanns:C-8 exposure calculations were made using three separate sets
o oCfasethe1 -FineRefPolwedcetrs D1r9y8e2r meaxnhuafuasctt.uring conditions with no scrubbing o tChaeseFi2ne- PoRwedfelrecDtrsye1r96e2xhmaaunsut.facturing conditions with scrubbing of oCsacsreubb3ing- ofRetfhleecFtisne pProowjdeecrteDdrye1r987exhmaaunsutf.acturing con.ditions with Table. TMhye craelscuulltastioonfs amrye aclaslocualtattaicohnesd. are contained in the attached
J167L9:9s-d1e
0068:
EIDO79287
TABLE 1. Estimated Ohio River C-8 Concentrations and Human C-8 Exposure Reflecting 1982 and 1987 Manufacturing Conditions
Case Mo.
1 2
3
R-i8verConWcateenrtra(tpioomn byinwt.)
0.8 x 10-4 L1x 10-4
3.5 x 10-4
AovferCa-g8e IDnagielsytedAmo(usngt) A%cLofDoEsqeuivalent
0.08
0.08
0.11
0.11
0.35
0.35
179%8-2
s
00Gean"
3 EID079288
CALCULATIONS
General Assumptions:
o An average person drinks 1 liter of water per day.
o fn average person inhales 1013 of air over an 8-hour shift.
Average Ohio River flow rate is 13,880,000,000 1b. water per hour.
The scrubber on the Fine Powder Oryer stacks would be 90% efficient.
When the Fine Powder Dryer exhaust is not scrubbed, 3% of the total C-8 added to Fine Powder/Dispersion goes to the River.
When the Fine Powder Dryer exhaust is scrubbed, 31% of the total C-8 added to Fine Powder/Dispersion goes to the River.
Approximately 81% of the total C-8 added to FEP goes to the River.
Specific Case Assumptions:
cas1e
Fine Powder/Dispersion will manufacture 6.9 MMAP during 1982.
An average of 0.0022 1b. of C-8 is added to make each pound of Fine Powder/Dispersion (35% solids).
FEP will manufacture 6.7 MMAP during 1982
A(nTowavCe-r8agreec0i.p0e0)1.6 1b. of C-8 is added to make each pound of FEP
Case?
o Same as above except the Fine Powder Dryer exhaust fis scrubbed throughout 1982.
cas3e
Fine Powder/Dispersion will manufacture 16 MMAP during 1987.
Jo average 0.0053 lo. of wilbe added to make each pound of
FEP will manufacture 11 MMAP during 1987.
* AFnEP a(vheirgahgeC-08.0r0e3c0ip1eb).. of C-8 will be added to make each pound of
17938-3
R 0096E%
EIDO75289
:
Case 1 Calculations
Fine Powder/Dispersion:
Ce x 106 1b. Irae) (B-0022 1b. C-8 = (9)
re
Tb. TEFLO!
365 days x 26 hr.
yee
day
= 0.051b.C-8 nr.
goes to River
FEP:
er x 106 1b. Erion) (o-0me 1b. C8 ) (2)
re
Tb. TEFLON,
365 dyarys x 24 Ghry.
= 1.001b.C8 goes to[ARiver
Total C-8 going to the River per hour = 1.00 + 0.05 = 1.05 "1b.hCe-8
C-8RivCeornce(nwttr.a/twito.n) in 613,880,10.0050,01b0.0 C1-b.8/hwra.ter/hr I 106 = 8 x 10-5 ppm
AnDoruinntkionfgC-W8ateIrngeEsacthed Dwayith
= Titer of ater) (love gn ater) 6 x10-5)(109) Titer water,
= 8x 10-8 gn. or 0.0u8g of C-8
Amount of C-8 Inhaled at the
,
A8-EhLr.ConScheinfttration over an = (10 srg aofrCc-8)a)) (1003 of aif)) = 100 ~4g of C-8
Ingesting 0.08 4g of C-8 is equivalent to:
0.08 ,g of C-8 x 100 = 0.08% of the AEL
y
1004g of C-8
17998-4
.
00008
EID079290
Case 2 Calculations
Fine Powder/Dispersion:
e x 106 1b. TEFLow) (o.02 1b. C-8 = (3)
yr
Tb. TEFLO
365 days x 24 hr.
re
day
= 0.54 1b. C8 hr.
going to River
FEP: same as shown in Case 1.
Total C-8 going to the River per hour = 1.00 + 0.54 = 1.54 "1b.hCr-8
C-8 Concentration in = 1.54 1b. C-8/hr. x 106 = 1 x 10-4 ppm
River (wt./wt.)
3,880,000,000 1b. water/hr.
AnoDurnitnkoifngC-M8ateIrngEeascthedDawyith = ( Titer of ater) G3Teermn aatteerr)(1.1 x 10-4 om) Gs
= 11x 10-7 gn. or 0.11 xg of C-8
Anoouvnetr. aonf 8C--h8ouIrnhSahliefdtat the AEL Concentration = 100 ug of C-8
Ingesting 0.11pg of C-8 is equivalent to: 0.1149 of C-8 x 100 = 0.11% of the AEL 100sg of C-8
17998-5
00508%
;
EIDO79291
:3
}
CCasael3culations
Fine Powder/Dispersion:
( x 106 1b. Jr) (0-00
ye.
1b. C-8 ) (o-)
Tb. TEFLONS:
1.851b.C8
365 days x 24 hr.
hr.
yr
dy
going to River
FEP:
TM x 106 1b. TEFL) {pom 1b. C-8 ) (2)
yr.
1b. TEFLON,
365
days re
x
26 fr2.
= 3.061b.C-8 golag htro.River
Total C-8 going to the River per hour = 1.85 + 3.06 = 4.91 h 1b. eC-8
-8 Concentration in G 4.91 1b. C-8/hr. x 106 = 3.5 x 10-4 ppm
River (wt./wt.)
3,880,000,000 1b. water/hr
AmoDurnitn.kionfgC-W8ateIrngEeascthedDwaiyth = Titer of ater)(10T0i0taenr wwatder))
= 3.5 x 10-7 gn. or0.35 ug of C-8
x 10-4 on) (ro
Amoouvnetr oanf CB--h8ouIrnhaSlheidftat the AEL Concentration = 100 4g of C-8
Ingesting 0.11 4g of C-8 fs equivalent to:
0.35 4g of C-8 x 100 = 0.35% of the AEL
:
100 4g of C-8
17998-6
006088
EID079292
18
000420
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17 005023
PERSONAL % CONFIDENTIAL
6/13/88
70: HM. V. BRADLEY DT.. GM.o WKIEKMAP T. Li SCHRENK
FROM: J. A. SCHMID
r-8aIrN WeATrER
.
BELOW IS A COMPARISON BETWEEN THE 3/15/84 SAMPLES, AND THOSE TAKEN ON 6/4/84.
LaOxCaArTaIrOeNx LLIUTBTELCEK WHAOTCEKRING
* POWELLS STORE
3/15/84 c-8 IN PPB 6/4/84
rx0s.x8aasx
NrOaTarDaEiTeECTED
1.2
1.0
* LUBECK HILL
NOT SAMPLED
1.5
HOCKING, THI EWOCU-L8DDHRAOVPEPEDTOBECLOONWCLUTDHEE DTHEATTECTIINONTHELICMAISTEOFOF0L.I6TTPLPEE. ATLESSOT,'SRSEECNOSGINTIIZVIINTGY,THATTHEWEBESATREWEOPECRAANTISNAGY AATBOUTTHETHEEXTRLEUMBEECKOFWATHTEER IS THAT IT IS PRESENT IN THE 1.0 PPB RANGE.
REV.6/14/84 - 6/13/84 DATA WAS REPORTED AS FLUORINE NOT C-8.
0EeLE. L \
p07"73
o
--
PERSONAL AND CONFIDENTIAL
TO: J. A. Schmid FROM: J.Fe Toh
CC: T. A. Foster
June 14,198
UPDATE on C-8 IN WATER SAMPLES
The attached
recent data.
table shows
I conclude
the
the
C-8
new
diantwaatceornfdiartmatihenclourdiignignalthdeatmao,st
a1.ndThtehe DusamPpolntingdatsaystsehmowsdoetshatnotthecontetsatmidnoaetse
not
the
sseaemplCe-.8
up
river
, c2.onTtheent saescontdheWafisrhsitn.gton sample had essentially the same C-8
3. The new Lubeck sample shows essentially the same concentration
2s the Lubeck
Washington sample. Thus the Water System as I suspect or
Washington sample is at least the Lubeck
from
the
the same concentration.
system has
bd4.eetlTeohcwetitohoneridgleiitnmeailcttLifioortntllteihmeiHtot.ceskti.ng Tshaempcleoncwaesntrvaetriyonclonsoew atpopetahres to be
I do not plan to do additional
airseneneodtedc.auseTheforconcocnecnetrrna.tions
sampling are very
unless further information low and in my judgement
000035
1007927!
Y
LOCATION
DISTANCE (MILES)
SIDE
ppb C-BhAk
PARKERSBURG
7.5 up stream
1
ND
DU PON(T3/15/84) 0.5 up stream w ND
(6/4/84)
ND
DISTRIBUTION
0.25 down streank WV
ND
CENTER OF
:
"PARKERSBURG
VASHINGTON
0.25 down stream WV
|
(3/15/84)
1.2
(6/4/84)
:
1.0
LUBECK
0.25 down stream WV
(6/4/88)
1.5
LITTLE HOCKING
3 down stream
OHIO
(3/15/84)
0.8
(6/4/84)
ND
BELLEVILLE
12 down stream WW
ND
*
REEDSVILLE
14 down stream
OHIO
ND
'RAVENSWOOD
29 down stream
Ww
ND
RACINE
50 down stream OHIO
ND
POINT PLEASANT
74 down stream
Ww
uD
4% GALLIPOLIS
79 down stream
OHIO
HD
#well is back from the river
AAELirst community to take water directly from the river
#xivalues obtained from Experimental Station multiplied by 1.5 to
i
convert to C-8 vs F content originally reported
i
ND = below the detection limit of 0.6 as C-8 (0.4 as F)
0006370
EID079272
19
000085
|
DuPont
INTEROFFICE MEMORANDUM
DFartoems: TDeelptsNo:
T1o2n-yMayP-L1AY9T8I7S03:06pm EST TPELFATYETCIHS 2775
TO: ROGER ZIPFEL
ZIPFEL >
cCi JOHN CRUM
CRU >
Subject: C8 In Water
whichAtatraechieddent1i3fiaedcopays fofolltohwes.smalytical report for our five water samples, #1 - Washington Works drinking fountain, 83. #2 - Pouell's General Store, Washington WJ 7 - Lubeck Pennzoil, Lubeck WV #4 - Masons Village Market, Little Hocking OW #5 - 812 20th Street, Vienna WV Ca.plLa.stHiicllbootbttlaeinefdillseadmpwlietsh1-d4rinbykindgriwvaitnegr.to Seaamcphlelo5cawtaison taaknedn absykiDn.g Kt.o have Moore at his home. ALL samples were taken on 3/13/87. the rNeostuelt tohfat 1.t3hepprbesubletcsomeasre1e.x9prpepsb.sedTahsispprbesFu.lt Wihsenhigchoenrverttheadn ttohospepb fCr8o,m 1d9i8f4f,erbeuntcecoinssipdreorbianbglyhonwotclsoisgeniwfeicaanrte. to the detection limit of the test, the
Z
g
035:
EIDO79091
PRoelsyemaerrchPr&odDuecvteslopDmeepnatrtmDeinvtision Experinental Station
ce: MSs.. AR.. KLaaiasser -Z 225566
MB..SL.ombsahrespkaird ._- 236293
GR.ALJ. FiSlleoan S- 2a56
Ic.
Sa
ANALYTICAL REPORT
ray 7, 1987
To: A. J. Playtis - PPD, Washington Works
From: M. J. Vilone and R. N, Vasta - PED, ESL 269
mgt
ow
(36h No. 870-441;PEPRRFALLUCNRoOsO.CT8A7N-O2A9T3E3(-C8)293I7N, WANoTtEeRbook No. E4875)
by electroFnivceapstaumrpelesgasofcwhartoemratohgarvaephbye.en aMneatlhyozdedES-f5o6r7pwearsfluuosreodocwtiatnhoatthee (C8) hfooulrlso;wincgonmcoednitfriactaitoinonosf:pesrafmlpuloerosdiezceanwcaaste10ingt;ernlaylophsitlainzdaartdiownevsasdec-r1e8a-s2e0d 10 wfoelrde.'exaSmpiinkeedd. stAandraerpdrsoduactibcloencdeenttercattaibolnes opfeak0.4w,as0.o5b,se0r.v8e,d 1f.o0r a0n.4d 1p.p9b papnbd we hsatvaenduascdesd t<h.i4sppabs.ourFodrettehectiqounantliimtiatt.ionNoveC8hapdealkinveaasr dceatleicbtreadtioinn ctuhrevesspikoevder atnhaelyrzaengdeionfdu0.p4lictaote1,.9 pTphbe. reTshueltssaamrpelesexwperreessefrdeeazseppdrbiefdl,uodreirdievivthiezceed, and 6b F = 0.688 x ppb perfluocooctancate. questions,Thedonr'etsulhtessiatcaetegitvoencaliln. the attached table. If you have any
Roemtachnent. Keyowords:
wPaetcetrluocooctancate
0095.56
EIDO79092
RAL
a7-2033
87-2934
a7-203
87-2936
a1-20m7
Pecfluorooctancate in Water
Designation
n
ngF/g. B,0 (ppb) * .
n.d.
2
1a 9 et <<
La 9 es
#
n.d.
is
nd.
* n.d. = none detected; detection limit = 0.4 ppb
FYse =F
000504
BiDossass
LuFont TO: ROGER ZIFFEL
INTEROFFICE MEMORANDUM
FDartoem:: DTeeplt:No:
4TO=NaYy=F1L9A9Y7TIS02:0%m 37 ETLEAFYTTEICSH 2775
CzieFEL
Subject: C3 in Watar
by theTheendfoloflowtihnegwereeks.ultsThehadveetebceteinonrecleiimvietdofbythpehontee:st iasl0a.t4terppbw.ill
sacele
seb_CB
duraisnhiiinnggtonfouWnotrakisn, ES
0.4
Ftioawsehliln'gstonGenWeYral Stere,
13
Lubeck Fennzeil, Lubeck wv
3
LMiatstolne'sHVociklilnaggeOHMarket,
0.4
312 20th Strest, Vienna WY
0.4
fallen
Zz
00912. \
EID079094
20
0001.03
|
C-8 REDUCTION & CONTROL PROGRAMS STATUS
R. J. ZIPFEL 6-11-87
003546-19 - 06/09/87 - RJZ:kat
~ 009:
EIDO79685
:
WASHINGTON WORKS
OFF PLANT EMISSIONS
WATER
POUNDS C-8
1983
1986
- + 21,700
19,100
AIR
12,700
16,200
PRODUCT
8,000
8,300
OFF-PLANT DISPOSAL
7,700
8,300
50,100
51,900
003546-10611 ~ 06/03/87 - RiZskst 000125
EIDO79694
C-8 LEVELS IN DRINKING WATER
PARKERSBURG WASH. WORKS
LUBECK WATER DISTRICT
LITTLE HOCKING RAVENSWOOD
DISTANCE
FROM NO. 5 OUTFALL
(miles)
C-8 LEVEL - PPB 1984 1987
7.50 UPSTREAM
ND
ND
0.50 UPSTREAM
NR
ND
0.25 DOWNSTREAM 1.1
1.9
0.25 DOWNSTREAM 1.5
1.9
3.00 DOWNSTREAM 0.6
ND
29.0 DOWNSTREAM ND
-
ND = NOT DETECTABLE
003546-7 - 06/10/87 - RJZikst
.
003185
EID079695
SUPERNATE POND ELIMINATION
BENEFIT ~ ELIMINATE C-8 CONTAMINATION OF LUBECK WATER SYSTEM AQUIFER FROM THESE PONDS
STATUS ~ PROJECT APPROVED (320M) 11/86 ~ PERMIT APPROVAL 3Q87 ~ START-UP 11/87
003546-33 - 06/10/87 - RJZ:kst
Q00i5
Emorsron
21
000108
-----
--
Sro-- y bm 17 E. |. ou Pont og Nemours & Company rouvmEn sours SErARTIENE
Tres r on rage us
CC: R. V. Mihaflovich,
U8P.a1Si.lcahEdePeAsitsnnRuitse,BsiPdAts.a19r10t7 Biv of tater Resources Greg Menger, Acting Supvr.
6321 Emerson Avenue Parkersburg, WY 26101
CERTIFIED MAIL RETURN RECEIPT REQUESTED
June 15, 1987
Mr. David W. Robinson, Chief WY Division of Water Resources 1201 Greenbrier Street Charleston, West Virginia 25311
Attention: Industrial Waste Section
Dear Mr. Robinson:
De Bor and 008. The changes planned vere reviewed in a telephone This letter is to comply with
WY0001279, and Section D.1, Page 17 of
Section D.1. hud of NPDES Permit WV Permit 1W-6238-82, informing you of
planned physical changes at our Plant and a minor change in discharge from
Coaversation with Kr, Randy Sovic of your staff and are as follows:
1) Relocate the Ko. 006 outlet sample location,
2) Add Calgon H-9006 microbiocide to our Process Water wells on Slennerhassett Island to control fron bacteria, and
3) Close three
The details of
anaerodic digestionponds.
the planned changes are shown
fn
Attachments
1,
24
3.
Please call ma on 863-4271 11 you have any questions.
-
Very truly yours,
Ai Envirormenta Control Consultant Washington Works
AACtHt:ahcehwments 187
.
.
acrren rumen son serves vine 000509
EID076048
:
Appendix F - page es
:
ATTACHMENT 3
Page 1of 3
CLOSE ANAEROBIC DIGESTION PONDS
Sackground
ousuerd fflourorcTohoprnoetleayimnaemnreaenprtroobdaiunccdtidtoirngeeastftmaieconintlitopifoensds.somelTohnceoantw-eadhsatzoaenrdtiohnuecsluOdhaeiqsoueowRuaistveerrw,asbtaiennkesrftroarme Sauntspeerncdbeidcal$loy11dsigaensdt tahneond-eftoenrfgcentd.etergent, and is held in the ponds to
Povaenrtflloowc.aTthieoTnhitshfroerreeqfupuiorrntedhssershahtvirepeaetenmnoetnotuotflaendtdigeuansldtteiadmrawetaesotpdeeisrpaootfsefad-ls.istoetShtioenyceandtoohtehnoetrcosDtu of
mdaitseprosiaall waste to
osfhitphpeedwa{s3terasitnrwaetaemr,hasa bsetaonragienctraenaksinigs significantly reduce the volume, It is
braepiindglycoannsdtruabcotuetd f5o0r3 otfhethe anticipated that two ponds
wih1e1n tbaenkclocsoendstriumcmteidoiante{l3y,cowmiptlhetet.he third being closed by the end of the year
Description
1)
2) 3)
wTihteh posnldospedareearotfheenartbhaennkscoanbsotutruc2t2iofne,etawpipdreoxiamtattehley basef.eet Adlleep BBdieeknnettoownnaiilttleeswwawasesreaaflxsreoedcuosinnesdtwritutcohtestdeahlefnclle1aa9yk7s5beoifrnort1eh5e76rbewopitltathcoimnrgoefdthctelhaeyw.alls. upriver pond.e, aPnadgeel3evoaftitohnisofattthaechmtehnrtee(iWmSpKo-u1n3d6m7e5n)t usnhiotwss.the location, size The cmbined volume of the ponds 1s estimated to be about 3 sillfon gallons.
Closure Pas~
11) aTnhde scohnitpepnetdsofoff-stihteedifgoerstdiiosnpospaoln.ds will be pusped into rail cars
2) hVainsdiblsehovTeulmesd oifntpoolSyS-tgeatlrlaofniuostreoeelthdyrluemnse a(nidnerltansdofliildlse)d aarteLteotarbte.
3)
The and
bdiostctoolmoroefdth5e011p,ontdos
awild]eptthhenofbe3
troemo4vefde,etiDnecllouwdintgheslduodtgteon
of the ponds.
1573H-6
0095.56
EID076049
apenas age 3
Ancwent 3
Page 2 of 3
CLOSE ANAEROBIC DIGESTION PONDS (Cont'd.)
4) The sludge and earth removed from the ponds will be disposed of 1n our Ory Run landfill (Permit IWL-6282-82).
5) It is then planned to push the earthen walls fmward, 111 with clean soil, level, and plant grass on the leveled ares.
Sludge Test Results
Analysis of a composite sample obtained from twelve locations within the eastern most (up river) pond showed the following results:
COMPOSITE SAMPLE COMPOSITION (ORY WEIGHT BASIS
Fluoropolymers Triton
Ammonium perfluorooctancate ner Inorganic fluoride Chloride
(FC-143)
13,61 9.7%
85 ppm 47 ppm 26 ppm
20 ppm
*fnsoluble, at about background level
The sludge tested non-hazardous dy the RCRA EP toxicity test as shown below:
0router est
mw
Concentration (ppm)
26M Limits Go
ren Arsenic
Sari Cadeium Chromium Lead Selenium
Silver
Go0.006
<4 0.1 <0.8 0.8 0.1
5.0
100.0 1.0 5.0
i:85.0 of 5.0
157347
:
[LITRES
EID076050
J.
r eee
nn1
p_:
Ih
iii
A3
Bi
Hk |
i3 ; 3
LJ 4 age
:ill
Ii
i
|
C
oe
)
ili W1h7a8
+ I I=
i
2--
ii 4 3--
i
+=
1 i S--
S--
ees
meee
rm 3023 CDOMENT 3
wppgoeitioey__of -- SE -- i
33 VU ferurresid
dhe
psrT
et
TYPICAL PROFILE
fr orl HOfwRIV
NORMAL POOL ELEV. 582.2
ees
IE I: pmsi- srise o
hit 3
2 45
e3e
1-
Frgom]. Ys6
LONGITUOE LATITUDE 20.
A
LB
814019.3 BI4s8.c 8/40/7.6% B8140/5.8% 8/40/5.7% 3/40/3.3%
3316 18.4% 391613.5 391618.3% 3316 18.77 35/618.7 391618.8%
7-- 6c.9l 8-- 623.25 9-- I5i.4%
Elev. Res 535.07 af rap oF sCresn
Wak WW= 45252.
ADINKAEEREZLEEIVCATDIIOGNESST&ICOONORPDOINNDASTES
"a
ra
=#09 gagitz EoeOsI
006115
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ce: T3G... GMR... LKAleommsspc/hSi.avoV. -GaDn1g2a0l22-3
3D.. kEjl CFrluemnsborg
5R.DL.AlLiannyeon J. ALLL optoest 0l.H4.. SStcehvnaerieder
July 7, 1987
TO: CJ.. AA.. SDYCKHEMSID FROM: R. J. ZIPFEL
C-8 cowTRoL PROGRAM
vKeerrythvevlalsMywmoistrthevilieinwtttelorenestctehhdiasngieinssrtueheqeuvipirrteedhsenDtrco.eouoBrfrucCpe-r8eKsaeornuctthsicodonentrJtouhlneepprl1o1a,gnrta1m9b.8o7u,ndDrva.erinets. Hfteoesushetasav.teedC-Dr8t.haitKnacvteehhenieaeldsbolofooadc.pclepatcMeeyd tchhtehaerhtsipgohsaeinstdtiotnphreitoshraptietcyoiufriocnemctpohlmeomseyeenetessnvivmriaoldnlemecdnoutnratilinngue the reviev are attached. C-8 controTlheplfaonllvoivtihngthise anecreessstaacteymeancttioofn sttheepsspeicnidfiiccatepdr:ograa tems in our
I. ADHINISTRATIVE CONTROLS A. EQUIPHENT DESIGN
1. IMPLEMENT AN IMPROVED FINE POVDER DRYER GASKET DESIGN (RESP -KLINE)
5. PROTECTIVE BQUIPHENT 1. ATFUDICTURVRAESNHTINPGRTOOTNECTVIOVREKSECQ-U8IPKIENNTBLO(OADNDANODPECR-A8TINIGN APIRROCEDDAUTRAEST)O ADREETETRHMEINE
OPTIMUM AVAILABLE (RESP - LOSCHIAVO)
003855-1 - Rzzkst
EID091375
=S
8g
0005.45
=
.'
CFC.ga'cAe.CO2DNYTRREOSL /PRJO.GRAA.K SCHMID
Sr 7, 1987
C. C-8 HONITORING 1. REDUCE EMPLOYEE BLOOD TESTING TO ONLY THE FOLLOVING JOBS: RAV DISPERSION AUTOCLAVE OPERATOR DISPERSION OPERATOR
FINE POWDER DRYER OPERATOR ENVIRONHENTAL OPERATOR (SUKE) DISPERSION PACKOUT OPERATOR GRANULAR POLYKETTLE OPERATOR FINE OVDER PACKOUT OPERATOR FEP POLTKETTLE OPERATOR FEP VET FINISHING OPERATOR
FEP DISPERSION OPERATOR FIRST LINE SUPERVISION OF ABOVE PERSONNEL
(RESP - LANYON)
NOTE: BHEAFVOEREANVEINTCEHRANNAGLE OBUTRO BCLOOMOMDUNISCAAMTPILOINNG(PRREOSGPRA-M,ZIVPFEELV)ILL VANT TO 2. TPHEERSOFNOALLLOVC-I8NGINJOBASI:R SAMPLING - HONTHLY SAMPLES SHOULD BE REQUIRED OF
RAV DISPERSION AUTOCLAVE OPERATOR
GRANULAR POLIKETTLE OPERATOR o FINE POVDER DRYER OPERATOR
DISPERSION OPERATOR
o FEP POLIKETTLE OPERATOR
FEP VET FINISHING OPERATOR
FE? DISPERSION OPERATOR
(RESP - CPOOLPYOMLEYRHSER-S O-TT20ST)
zS
003855-2 - RJZ:kst
EID091376
0695.15
.
C. A. DIKES C8 CONTROL
P/ RJO.GRAA.M
SCEID
AJUGLEY 37, 1987
3. AERQEUAIPMC-E8NTTN(eA.gI.R, MOFNINIETORPIONVGDER- ADSRYENRESE)DEADNDBYTOARERAESAPRONODUNDTOCRHIITGIHCALLEVELS NOTED VITH PERSONAL SAMPLES (RESP - CPOOLPYOMLEHRESRS- O-TTPOST)
NOTE: EINNOUGEGNHERPAELR,SONVAELARSEAMTPALKEISNG FAR TOO MANY AREA SAMPLES AND NOT
4. DLEOVCEULNSENT(APTEIROSNONA-LEXSPAMLPALNEASTIOONNLSY)OFABROEVASEONSSOXANODF ATHCETIOANELRE(S0P.O56NSEHZBF)OR AIR
REQUIRE (RES -
TPHOPLRYOMVEERHSEN-TOTITN
THE
DIVISION'S
ENVIRONMENTAL
SAMPLING
BOOKS
COPOLYHERS - POST)
D. C-8 CONTROL LEVELS 1. ELESVTEALBSLISH(RMEASXPIM-UMG. SAL.FEKEC-N8NEDIYN B-LOHOADSKEALNLD)C-8 IN DRINKING VATER NOTE: OONFCETAIASSLAEFEVELLEVVIELLLISBEESRTEAQBULIIRSEEDEDT,O TBHEOSREEMOPVEERDSOFNRNOEML TEHXECEEEXDIPNOGSUSROEX AREA
II. PROCESS CHANGES A. CIHMAPMLBEEMRESNTWOURSEKSOF(PRUESRPCHA-SEPDOLLYIMQEURSID-C-C8RUMAS IS BEING DONE AT DORDRECHT AND COPOLYMERS - HERRIDGE)
B. NEV SURFACTANTS 1. BTUBSSIANEISNSFNEEPED-SREJDUUSCTEIFYPRIFOURRITTHYERONUSTEHI(SQUPARLOIGTRYAMANTDOCOTSHTE)POI(NRTESV?HE-RE HERRIDGE) 2. CN-E9W, SCUR-F1A0C,TACN-T1S2. - No ENVIRONMENTAL LINITS ARE PLACED ON THE USE OF
. C-8 RECOVERY
1. FPIRNOECESPSOVDBEYR4D0R87YER(VREENSTP -- SDCEHVNEELIODPERB)ASIC DATA TO IDENTIFY RECOVERY 2. FEP AQUEOUS STREAMS - APPLY ABOVE TECHNOLOGY IF ECONOMICAL (RESP -
SCHNEIDER)
D. LUBECK VATER DISTRICT CONTAMINATION
z
1. ELIMINATE SUPERNATE PONDS - GOAL IS NOVEMBER 1987 (RESP - FLENSBORG)
2. DETERMINE MODE OF CONTAMINATION (RESP - STEVART)
g
At0t0a38c5h5m-e3nt-s RZikst
006.15
EID091377
23
000.17
(
a E. 1. ou PONT of NEMours & Company
ae sr
souruen rosuETs aEmaRTIENT
CC: UR.S.V."EMAenRaetglioovnicThi,tJMS3 aPdhiilcahdeelpshita,sPdA"g, 19107 W6GY3r2e1gDIYEH.ennegorefsro,lnatASveuerpneuRreev.siosuorrces Parkersburg, WV 26101
RETURNCERRTEICFEIIEPDT MRAEIQLUES=TED
duly 30, 1987
WHeY. DiDvaivsiidonW. ofRoWbiantseorn,ResCohuirecfes C1h20a1rleGsrteoenn,briNeesrtSVtirregeitnia 25311
Attention: Industrial Waste Section
:
Dear Hr. Robinson:
Ref: CPoenrsaoiltidKao.teWdV0P0e0r1mi2t79WV/NPOES dPaetreadit7K/o7d/i8f7ication No. 5,
ModificatiTohnisanldetSteerctifsontoD.1comopflyWVwPietrhmiIttemNo,3 o[fWLt-h6e282r-e8f2e,renicneforPmeirnmgityou of a ptlhaennweadstephmysaitcearlialchadnigseposaetdouorf PflnanOtrywhRiucnhLwainldlfilrle.sult in'a minor change in
non-hazardTohuesmastleurdfgaelatnod bdeirtdisfproosmedcloofsiwnigllthbreeeapapnraoexrionbaitceldyige7s1t0i0ontonpsondosf. Tshleudgseludagned dtierstt wrielslultbse abryersohaadwnin(0opTeanv-lteop1tartatialcehresd.. Transportation of the
Please call ma on 863-4271 1f you have any questions.
Wz Very truly yours,
-
A. c. ston Environaental
Control
Consultant
Washington Works
Ahtotnachaent
-
16604-1
:
|
g
acres rinas ron serves uving
EIDO007534
L689
!
~
BLE 1
SLUDGE TEST RESULTS
the easterAnnaloysstfs(oupf arivceorm)pospiotned ssahmopwleed otbhteaifnoeldlowfirnogm trweeslulvtes:locations within , COMPOSITE SAMPLE COMPOSITION (ORY WEIGHT BASIS)
TrFliutoornogolymers ZAimnaensiun perfluarooctanaate (FC-143) ChIlnoorrgiadneic fluoride
153..76%% 8475ppomm 2260 ppppmm ~
*fnsoludle, at about background level
:
.
shown below: The sludge tested non-hazardous by the RCRA EP toxicity test as
P TOXICITY TEST
Hetal
Concentration (ppm)
RCRA Liatts (pon
ABarrsieunmic Cadaium
0a.006 <0.1
1005..00 10
CLheraodatum
<00..55
Nercury
<0.008
55.00 0:2
SSetlievneirum
<01.08
51.00
1604-3
:
0oniig
3: EIDO007535
000529
z
(
sme wa weno sma owHineoeauysrniharigane aBesarmania sBwaoabmiimseson sa
Fax (612)733-1773
"es or -- am
FACSINILE TRANSHISSION INPORMATION suET
sace_Noy 20,197 web4er
avcancton_Binsy Kirradiopn RW. Rickarel Ph.D.
tocatton_Hasell LAR ~~
_
Pax wo. 302-366-5207
Special Instructions or Information:
ORIGINATOR'S NAME Cpls foe
Telephone nusber to verify complete transaission, of to relate problens: GIJ 733-3LTT
.
Qoaiis
ID071428
-
SHEEaRsR,E .
3M Megical Department Tosicowgy
----
i R ener R 6 GastB ,eseo Np 1tP 1.s8 Tfin Atoway 3I T9 uhr E sPeeIn eItepLm onEe TconuRraLsnioinT,rEegust6ing th ERR RG HEI
DTfL PnheiEEeeTtnrcAElyoRsedSemaatetrsitalt S os ainikcelsudeS lDdr.oR SpykheTseL'L gyBOcatRoatbeS erCh2p9,N1M5h87eitme,mogh
aE pErobpeiTr SaebrTaaiL kientioTieseonmuREelrsun eaistTaeSefLr rinnse e1sshae
StTA tatUaInIniyt, sI Rntoeunr RtErnAnrhTReaFAiTrseSi31AatghS eAaoTrf e eshnri, erpr7ss
TEhesmmRtr Sn LHAn IITLR ET SLTLnE BmATUT
Tsar mh "final
youdraf
t
searebing rm TELL report," mailed
too uyFoouoivraitnah,nta
tSMaacyt1ae2d, u19lg8e6s,
cofoRvehRre
enclosure includes pages 15, 16, 22 ane 23.
Ve discussed the statistical analysis of the incidence of lerdis
a T TFOrmTEeShtSaTeAdRRW TeAR aLII dS ST h ehnT ]see at Faskell, 880 control rats in Charles River CD Mat, 24 mont:
ID071429
PRaogbeert2 G. Get, DLV.M. November 30, 1587
uLnguese4e8lvtaos tfihned cnaoneLeiyndihgeceFlCl-16a3densotmuadsy. inThSealeMasrkaetsllofdat2ka mionnths Rsi$v5earcherdepoforrt ysoiunrceiynooursbsrtoiuognh.t iI tboelioeuvreatytoeunthiaovne.the Charles EEnlcrlodo,nedPha.lDe,o 3a RanikeerxtrLaacbtoraftroormieas.tripherepionrftorapsrteipoanredprbeysen8.tedV. S0oiltheScmeenectminengnointedCeritnaitnhleyToCf-1Li3ntehriegshsdaorsereagntirmdasls.the Leyeis AFsevielwucuosfsesdlidvietsh ryooau btyhistelsetpubdoynea,ndveanyfaeAlddtihtaitonaalnysefcutritohneirng of SCalaufaaetsancsehouilndthbiesdomnaetteurn.der your guidance. Ve thank you for cVeontnreucsttioynouvitvhillthissubaaidtdiytoiuornslstactoenmseunlttatfoiron feiens thfeor tsaesrevimcaensnerin
hetore. DIrn. suSmymkeesr.y, pIlfeaysoeu nfeosadl farneye ftuortdhiesrcudsoscutmheinstsrefproormtovuirthfiles, Plesse 16% me knov. Thank you again for your assistance. Sincerely,
oSelniyor Togxiicoorlio aSpieecialist Digleasce of the American Board of Toxicology
nop:n (18105 2.8)
Melosures:
1) MOecmtoobGerreg29,Syk1e5s8,1 D.V.M. to Charles Reinhardt, M.D.
2)
31))
TE3wr1otrpaaYcgeteaserdOorpfealVseosl(uDaifeerto)m1 Letter Gerry Kennedy
oMTaofyxic1i2,ty/1C9a86rcidnroagftenicity to Roger Perxine October
...
16,
First
3967
5) 1E5x8t7ract of Memo 8. V. Kired to E. H. Erickson November 17,
dei 6H.asLkoelKleLnaebtoyr,atoJrr.y
RNeiwtaornk,RoDaEd,129.702.4 Sox 50
X.enoD.s King, DVN, Ph.D.
;
Po. Box 5008
North Branch, RI 08876
EIDO71430
:
QELS
000371
25
AR)
rn--ae--
DEPARr TIsENT e oOi rFwNeAaTaTrEURiAAns eLoemRsEaSOURCES Cont ee a1
no[ unnroLrEsoTa
Noun parsons
December 17, 1987
Suiey Sater:
MEr1. 2TAc.odruCp.oProHanuttsetddoen Nemours & Com.pany
PBLLAANNTT FFIiLeEcory 007 srunvg
PP.a0r.kerBsobxur1g2,17WW 26102
=
~3
RE: VDartyeNorR.unPoTlLWlaLua-td6i2o48n131-8C2o(nHtorodolCoP.e)rm#itY
Hottfication Ror |
Deas tr. Huston:
This serves as Modification No. 1 for che above referenced facility. This
mSCtoohednrpseitefeiomfcb(ae3)tnrioona1n-n3h,aaeizrs1ao9rb5gdi7rocaunTsdteieqgduseeTspsuuttlriigsoeaunga4nppntdeornmdStiisorsesya,ioounWrthheilcceoHthatdVseiIrhssLipLonvogeferoesnoJufuWllotyarpkp3rsr0e,oaxfia1ac9tat8hti7efeelacyynl.dos7u,r1e00of
Should you have any questions regarding the above information, please do mot hesitate to contact John Britvec, Geologist at (304) 366-5880.
Very truly yours,
QD. W.uRobinrdoln,iCchieefnm
DWR/ib/me
ces GCriengdyHNeansgeeer,r, SuTpavs.s.
0003.55
8
EIDOS1114
26 0605.25
:
. nar mv am QP
aa E. I. ou PonT DE NEMOURS & CoMPANY
WILMINGTON, DELAWARE 19898
RCW. HICHAUD, FBR CC: D. G. WIKA, PPD W. H. MARTIN, FIBR K. D. DASTUR, C&P R. Z. FORTNEY, INTL D. P. GLESSON, PPD
April 27, 1988
0: 05.. HL.AYADSAHRIB,Y, "SDHUIMPIOZNUTWOTROKKSY,O JAPAN GRRC.C 0JL... KLZIAEPNNFYNEOELND,,Y,`WWAHASASHSHKIIENNLGGLTTOONNLAWWBOORRKKSS
A. E. MORRIS, CHAMBERS WORKS
20k 7. WOLCOTT, FAYETTEVILLE K. J. HUISMAN, DORDRECHT
J. P. BOLLMEIER, EXPERIMENTAL STA.
FROM: H. A. SHITH Aldi
AMPMOENIURM FLUOROO(CC-8T)FOALLNOW-OUPAMETETIENG
Ref: H. A. Smith to R. D. Lanyon, et al, 2/29/88
A meeting to review our progress and path forward will be held: Date: Wednesday, June 29, 1988 Time: 8:00 a.m. - 4:30 p.m.
Lunch will be provided
Place: Kent Room Hotel du Pont.
We will be discussing: o Strategy for managing C-8 in the workplace. o Strategy for managing C-8 fn the community.
Future program regarding C-8 fn blood - monitoring and goals.
Please cone prepared to discuss and share fnfornation on the following: 3
1. Your personnel air monitoring results grouped by jobs. ~
:
2. Practices implemented to minimize skin contact.
0004.77
serren reinas rom serEn Living
EID079641
.
0. L. DARBY, ET AL
-2-
pri 27, 1088
3. Aassufmolmlaorwys:of your C-8 fn blood data If you have any. Summarize ob % Number of employees at a level of 0.5 ppm or less. ed % Number of employees ata Tevel of 1 ppm or Tess. % Number of employees at a evel of ppm or Tess. % Nunber of employees at a level of 10 ppm or Tess.
% Number of employees at a level of above 10 ppm.
Door ntooot sopvaerrcweortkoyboeurofblroeoadldavtaal.ue, need to over focus on this subject
Idfofntotfhsinogf wqiutehstiiot.nabWlee at this tine.
dvoaluneot
4. DTohees CyEoGur(CsoimtmeunmieteytEtxhpiossugrueidGueildienlei?ne) for C-8 fs 0.3 ug/m3.
5. Aetney. information available on C-8 in groundwater, public waters,
1988 reAfleccotpiyngofth3e'sreslualttesstoMfSDtSheiarndlToonxg-itceirtmy attached.
S(utmwmo-ayreyarS)heertatdafteeeddinFgebrsutaurdyy
is
AtHtAaS/c1hsaent
A, trit ah
2 2
PY
EID079642
27
000429
.
INTEROFFICE MEMORANDUH
FDraotme:: a2PL9NA-TYAHTuOIsWS-19J.88(0T3o:ur4)3mFLAYTIS
oeTeplesNo: 3PP0O4--33F6D3-2775
TO: Roger J. Zipfel
Czere >
CcCc: SJAoLmTEELR.caSuTEMART
ScTrEuAeA)RT
Subject: Test Results - C8 In Groundwater
bLSeeafvmoeprllesMeaswrsyreweientJiaSnniugaebmUttiihhtleeeodnLuesautiaanalrttHarEySesLpaemarpst:leeplsabe.reptchaounosfeed oustrhheemweraensstuolsrtuisrnpgrliisssetrdeadgmrybaenliohwe sbhfeoerreattbheiinwialter
Sample Description s82i12zeDr,ink"1i4n5g00 Fountain Ls/u1b2e/c8ks,Wat1e7r:00- Playtis Home
L8evel none detected 2.2 ppb
RLiittetnloeurHoHcokmien,g 5Ha/t1e2r/88= T5e/s1t1/2W8e,is 1#312070 $Le1t0a8rs8,Uppieirr00Pong L5/o1t0a/r8t9,Low1e1r100Pong
none detected 1.5 poo 1.6 oom 2.2 gon
0081.50 +
2
3: EIDO790%0
|
INTEROFFICE MEMORANDUM
FDraotme::
TDeelpt:No:
To: Roger J. Zipfel
CCCC:: WJAOLHTNERE.M.CRSUMTEWART
Subject: Test Results = C8 In Water
A3N0T-HJOaNnY-19J.89 [0TO1N:Y1]8pmPLAYTIS PPPLDA-YSTPIDS 304-363-2775 ZIPFEL ) SCTREWWMAR)T )
samplTehsefofrolmloowniintgorirnegsulCt8s ihnavleocableenwatreerceisvoeudrcefsr.om TEhSeLyfohradthae tNeorvreimbbleer time 3greetticnognfitdheenitr atnhaatlystihseytonogwivkenowthwehantececsasuasreyd ltehveeilr dofifsfeincsuilttiiveist.y, but they
Sample Description
200CO
1812/122/8D8r,in1k5i:n4g5Fountain
none detected
T1e1s/t4/8W8e,ll 08#:2370
1.3
1L1u/b2e/c8k8,Wat1e7r:00- Playtis Home 1.4
RLiittetnloeurHoHcokmien,g 1W1a/t7e/r88-, 06:00 ncootntpaomsisniabtleed sample, analysis
. 0esiin
EID079089
|
INTEROFFICE MEMORANDUM
TO: ANTHONY J. [TONY] PLAYTIS
DFartoems: DTeepltsNot
W3I1L-LMIaAyM-19E89CRA1W0L:E5Y4am P3CP0RO4A=-N"8LT6EE3NF-EL2O7N4*2TECH
PLAYTIS )
Subject: C-8 Sampling
.
S2uapmgprlniantgeHetPhoehnadLvuebceldcoekscuirdseey.dstetmEhaftffoercittiCv-ie8s 13arake ony more sampling fr
ntioomtmesdeneieacteteshlseya,riymupeatcotwicloolfntnisonmtueeneed
stoampsalvees tthheatsaamrpelibnegingcoshte.ld ofmorthaenaLluybseicsk sshyosutledm.be AanisycaLueesck
cJlyoa?sruDcrueepr.olnyWte,HbeadLsoeistswhaaornutttoldLmtaoaonnldiscftooionrtcionntutheienuiteompastcoatmptolafkeeHtwahateteerSruWpeeslralnmaptlNeoe.sPo2asr7douonnda ll on a monthly basis,
Please call me if you have any questions. Thanks, Bill.
060535
~
=5
EIDO79087
30
0001.25
HE.onkIs. BDAURRPGOENRT DE NEMOURS & CO., INC.
LASH0.INGBTOOXN1W2O1R7KS PLANT PARKERSBURG, WJ 26102 STANDBY PRESS RELEASE
June 12, 1989
Du Pont's purchase of the Lubeck Public Service District (LPSD) facility on Rector Lane is progressing satisfactorily.
The LPSD initiated the transaction in late 1986, offering sale to Du Pont to facilitate relocation of the LPSD's well field to a larger location to meet their forecast increased demands. After careful study, Du Pont agreed to purchase the wells to obtain additional process water and real estate to facilitate current and
future Plant operations.
The Plant has provided the LPSO with information to include in its response to a request from the West Virginia Public Service Commission for groundwater analytical data. Information has been provided from testing that has taken place in compliance with requirements of the permitting process of the Resource Conservation and Recovery Act (RCRA). This includes a test well that is the Plant's well closest to the LPSD wells. Additionally, since the mid-19703, samples have been taken to ensure that Plant operations are hot adversely affecting water quality. We believe that the data
indicate that the water is safe and reliable.
.
--more-
000535. ~
EIDO79154
ou PONT 6/6/89 STANDBY
GE 2
Both the LPSD and Washington Works agree that Du Pont's purchase of the LPSD wells will benefit both LPSD customers and Du Pont. The sale of the property will enable the LPSD to make a transition to its new facility more quickly and to reduce the cost increase to its customers. Benefits to the Plant include additional real estate adjoining the warehouse where products are stored, improving traffic flow and alleviating congestion around the warehouse. The water wells located on the property will also help fill the Plant's increasing needs for process water. Additionally,
the purchase will allow the Plant to delay expansion of its well
system on Blennerhassett Island.
EDITORIAL CONTACT:
HP.LAN0.T RSAUMPSEERYINTENDENT W3A0S4H-I8N6G3T-O2N739WORKS PLANT
eos |
EIDOT91SS
(Background InQfuoersmtaitioonns afonrd APnlsanwtersMedia Contacts)
surfAac:tanItt-'--saadnetaemrmgoeninutm-liskaeltmaotferaiafllsuorinated carboxylic acid. It is a
2.0: Hhat does Washinaton Works use FC-143 for? inclAud:e aItppliiscautseidonsin inthethmeanfuifealcdtsuroef mofediTceifnleo,nk.spacEen,d utsheessoefmiTceonfdluocntkor industry, and non-stick cookware. 3. 0: Is FC-143 harmrul? ratsAihaveThedemiosnssuteraitsedconthcaetntirtatiison-sl-ihgohwtlmyuchto amnoddwehreant.elyAntiomxaicl. stuIndietshesweith aSnaifmeatly DsattuadieSsh,eetth(eMrSeDSw)asnoantesinhduimcaantiosnkinof irlirvietratitoonxsi,cittye.arinTgh,e Maantderial ardevseprisreatoerfyfecdtisocnomefmorptloyweiethhoevaelrt-hexapsossoucrieast.ed wHiowtehveFrC,-14t3heerxepohsausreb.een no 4. 0: Hou lona has Washinton Works been using FC-1432
AL Since August of 1951, nearly 38 years.
S. Qi Where does FC-143 come from? DataA:SheWete p(uMrScDSh)aseaviatilfarbolme 3tMo Cyoorupotrhaattiogni,vesanda gtohoedresuismmaarMyatoefriiatls Safety properties.
6. 0: uhy were vou sampling for FC-1432 by 3AMithHate bietgahnadtbeesetningfoeunmdplotyoeeasccufomrulaFtCe-14i3n hinuma1n979blwohode.n weHewearleso informed uisneidt.iated a program in 1983 to track FC-143 outside the areas where it was
d7r.in0k: ieAt the 1-2 pob level, wil it sccumulate in the blood of those who techAni:calHeJudodgmneontt hatvhaet thite wionuflodrmanottionacctuomucloantfeirmat itt,hesbeutloiwt liesveolusr.
0095.PA3R.8. N
EID079156
8. 0: why does it accumulate in the blood of humans?
res A:not Wereaddoinl'yt processes of the
hpduremecaconimspoebsloedyy,.knroeawItctt,ihse ormeexcpbheralenalikesdmd.ofwrnomWeintdhoeihekmondobswiolstoihgoaiwticpai:lt
2.0: Uhat is the allowable safe Limit in drinking water> TS(hXaiPcsOcASeUwipTatEsabDlWuceearlPecoenuxtlptaoosthueaordscecucbryLailmvcciiuotaln)avteterfhdeotrindagoruisrnatkfheipenlagdlneatvoiefllwyo2rdokfLoeisrteSse,rpbspasbteodfoarnonedqrbuuiinvkBeiornnegensswatAdeeorrs.e if APPropriate reductions were then incorporated as safeotfywaftaecrtorpse.r dey
1t0h.e0se: uhoTo aurheatexpleovseeld htoas Tt itacbeesnhemePaisaunrrsed to accumulate- in the blood of
t3thes5eApiloemvHeeolrsh.laovweerd.eteTchteerde lheavselsbeeunp ntoo a3d3vepprms,e wefiftehcta osnigenimfpilcoapnets pheermcsenntaogfe
11.0: How often is the blood of emplovees monitored for Fe-1432 LFcCIa-n1ct4tAi3iLn.cueesEvC0eoarnnmydsoinspoitrttehoonecrtreduwytrioeeatsrha.fffoiuorrrm WoactschheuipnaagtdtieooqnnuaalcWyorhkoefsaltoeuhmrplsopcaeynredseaosrndewelh,o pwmroeortkescltewisiotnh
12.0: How did FC-143 get into the LPSD water system? TTahhoerseesw8ua:lspttoeWnodefsibsDweuelsrinePeiovpnepctel'doisstetCdocooruaiplnnodort1ah9hte8aer8veEDaunncvdoiPmroreonentpfmlreasoncimtetadetlhwfrPioerotelhidocminyes-,tpsaoilstaelc,ocroilenlceiscsitoinocnhetaposnonenedssw.as
12. 0: What are you doing to reduce FC-143 emissions from vour plant>
but AtLo dpluarnisn.g
cWHoeem'phlayarveewictauhrprreConotgrlrpyaomraitnteo croeemndpvulicireaonnmcaieerntwaieltmhisdsiailrloencstrieoggnouislnagwt.eoriynntaerveeqoupseidrrdaeitmrieionontssa,l the last quarter of 1989 (at a cost of $3,800,000), and we are also
studying means to remove FC-143 from waseeuarer.
.
zgg
000325 \
EIDO79157
1T8e.d7i0ce: tLhfe tahiresatnudffusitsernoetnhTsasrimafnusls,whyarevouspendinganymoney to eefmfiescAstiiso,nsltitbycoirnsetdoiuunrcuteisionntteonotfbewtaoDsytmeiP.noinmti'Ezsveenpoelxtiphcooysuugrhteo thmheiincmihamtiezcreoiuala:dquhceaaosuusseneaCnokdnncoaweinrrn (11 associated with accumulation in the blood. D1u3.0P:ont'sIsputrhcehapsreeseofnceLPoSfD FwCe-l1l4s3anidn ptrhoevercLPySD wsadtiesrcenstysttoem thteheFiroesarsosn for PUrseeseAon:ft.tWheelweaodundleidetdiohnaaanvleamdradedialteioetnshatelatpewu.erlclhAawdsadetietwrihoentsahuieplrpyl,yo,r tanhneodtpwuterhcewhiaFlsCle-1m4aa3lklewoawssgooude to delay the expansion of our well system on Blennerhassect Island.
16. Q: What was detected in the water system? cthhainoAr2:i4d0eAsc--ofumuaplosluncsdocsna,dluecutsoeifdn.gnoUrA.mSda.dlitwEiaPotAnearmlolntyie,tsotrstih-ne-gswuacrtheeqruasiwraefsmoernatnhsaalrydfoznreesdsgrfooarunndmdousrteer Foafrsoma17 rtmehaeftemreoernriceael,sthwaunenrdee2r40detmthaeectteReredis.aolusrcTehtehasCteonwsreeerrsevualttaisnoanldyozaenndod,t RoerncelopyvreerstyernatAccetaqcu(oaRnnOcRteAir}tn.i.es
`e2s.t0e:n? Hou long have vou known FC-143 was present in the Lubeck Water A Since 1983.
18. 0: bhy have you not made this information public knowledae until now?
founAd: wasAt 30thaltow-t-icmel,oswee twoertehenodtetseucrteionof litmhiet.findHiengdsi,d level to be a health problem.
nsoitnceregtaherdletvheel
19.0: Isn't this a female reproductive concern? bFuCt-14Am3:o,reNboue.txtweinItsnhiivtietahleteostrteiisgntigsnabdlyemo3tMnesswttiirtnahgtedprraottcsheadtiunrdtehi.ecatperdoblaemcawuasse nfootr wciotnchern,
20. Q: What is Ou Pont paving for the wells? Ar $1.8 million.
.
z
g
006515.
EID079158
LOCATION OF DU PONT WELL 27
ATTACHMENT 1
LUBECK PUBLIC SERVICE DISTRICT WELL FIELD |
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0003.23
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DEOPSVraATOOEIFFoRWFNAwSATeTTEsURtIRRvEAMiSLROORGUEERiCASNEOSNU.RCTES
Gast`oGonvceamaprenton
Cras2a0si7n:GreaasrarvergSaat3531
June 21, 1989 gRANTFiLECOPE,
4. EoWADRiDrecHtAoMrRICK 1
Mr. A. C. Huston
goror-t.2 uaowepvuwty.Dcireeoctnaare
E..'10.. BDouxPon1t217de Nemours & Co., Inc.
Fike 2303
Parkersburg, WV 26102
'
CERTIFIED RETURN RECEIPT REQUESTED
Dear Mr. Huston:
RE: West Virginia Solid Waste
MIPaeWnrLam-gi6t2e8m2eN-un8mt2beRraesng:dula3t49i4ons
As you should be aware, the West Virginia Department of Natural Resources (DNR) filed Title 47, Series 38, "Solid Waste Management Regulations", which became effective on November 4,
n1o98t8ifi(coantiaonnemtehragtenycoyurbafsaicsi)l.ityTwhiisll lneottwerbewiglolversneerdvebyas these
regulations and to inform vou of what you will be required to do to comply with these regulations.
The regulations specify that all solid wastedisposal
facilities must have a liner under the site and that the
liner system must include a subbase, leachate composite liner (compacted clay topped with a
detection synthetic
zone, liner),
and the
leachate collection with a protective regulations also acknowledge the fact
cover zone. However, that existing landfills
may not have the specified liner system in place.
To allow
paerpmriotvtiesei
for the continued operation
omnayhaspetbieteinonintchleudeddireicntotrhe
of existing
toregaulllaotwiounsse
facilities,
owfhearnebyaltaernate
rcseuysrsotrueemrn.ctelsy.Theemplpoeyteidtiosnysmtuesmtwiilnlclupdreoviadedempornosttercattiioonnofthgatroutnhdewater
The division wishes to begin reviewing these proposals as
psrooopnosaaslsposfsoirblteh.e gWriotuhndwtahtiesr inprmoitnedc,tioynoudeamreonsrterqautiiroends ttoosutbhemit
dSDoielvmiiodsnisotWnrasattoefionMWaatnmeaurgsetmRebenestousrRucebegmsuiltatbteyidoJnwusil.tyh 3Ty1,ohuer19r8ae9spuplultsisicantgoifotnyheoufrEormergency
permit renewal expires within
or Permit Application six (6) months of the
Addendum unless your permit date of this letter in which
0081.44
EID007493
. MPEa.geA.TwoC. Huston
eixntsetnasnicoenthtoisaalgleonwcya wrielalsoneanbtleertatiinmeaperreiqoudesttofcoormpalepteermitthe anlelcesaslalroywandceemsonsetxrhaatuisotne.d foIrf eyoxutrenspieornmitashapsrovaildreedadybyexsptiartuetde,and Tyhoiusaraegenacdyviwsieldl teoxeecxupteedietnifoourscleymesnutbmditiscyroeutriodnesmonisntrtahteisoens. instances. yThoeu apnudrpotshee odfivissoiloincittihnagt ptrheopodseamlosnstnroawtiiosntowilalssbuereabcoctehptable pcroimoprliatnoceit`sscihneidtuilaetifoonr. comTpheletpiroonposoaflthsehoudledmoncsotnrtaatiinona. cSohnotuladctyMoru. rJeoqhunireG. fBurritthveercionfformatpyi;sotnafforatas(s3i04s)tan3c6e6-5p8l8e0a.se veyq Kruly yours,
LEM: bw
Laidley/E11ChiMcecfoy, 4, -
009545
EID007494
33 0005.16
INTEROFFICE MEMORANDUM
DFartoems: DTeeplt:No:
A3N0T-HJOuNnY-19J.89 [T0O3N:Y5]1pmPLAYTIS PLAYTIS P3P0O4~-S8P6D3-2775
TO: WILLIAM E CRAWLEY
CRAWLEME )
CCCC:: WJAOLHTNERE.M.CRUSMTEWART CCCC:: BRiolglerTiJ.ceZipfel
( CSRTWEMWART ) TICE ) ZIPFEL )
Subject: C8 In Water Test Results From ESL
SAMPLE test well 27, 5/4/89 P12 drinking fountain, 5/6/89 Lubeck Water (Playtis), 5/7/89 5L/i4t/t8le9 Hocking Water (Ritenour)
SAMPLE
Letart * = ** + *+ + *
upper lower upper lower upper lower ulpopweerr lupopweerr upper lower
pond, 11/23/88 *, * * , 12/30/88 *, * * , 1/24/89 +, * ** ,,2/20+/89 +* ,, 3/17/89 * , ar25/89 =, *
PPB C8 0.44 none detected 0.73 cnootntapmoisnsaitbelde sample,
analysis
eemMce
4.2 2.3 0.96 1.5 3.2 3.1 11..92
11.a1 0.49 1.5
030i
EID079124
34
0004.15
INTEROFFICE MEMORANDUM
}
FDraotme:: HBaUAaMRuGOAgLR1DKsE,B6U0NG0AR8NEsRt
1!
TdeelpteNo: P(o30k4e)r 8d63s-e4rv7i9c6es
i:
"0: SEE BELOW
i
Subject: LOWER POND LEAKAGE ORY RUN
NTO THEFOBALNLKOWI10N.GLOOUCRATIENSATNRDUCRTEIPOANISR, THBEOSOLEADKR.AINETDHISTHEMETLHOOWDEROFPONRDE,PAITRH.ENUSUIGNG VJEEILNDVTEIONNNTIOTEIA0NDCLTAHHYEE WWWAOASSRKARBOELNCEOM8/MT2E0.'NDDIEGDTHETBYHRPTOAHUTEHGHOW.FITWVAAA.NTDERSOPTIALHCKROCUOTGHNHESERHTVHOEALETIGAORNNODUNSADEDRVJWIAACCSEE.NVTERAYREAS IETPHAIRTEHDE GCULTATPR(OHEOFUWSIELDL RETQoUkIROEF PBEORTMOINTTIITNEG).THEWEPAORNED TCOONFRIEDFEINLTL WiITHLERAAKIN1W5ATER. HTEX WAEMEOKUSNTAGOOF." ALGBAUET WPREES0E0NT,SEEBAALSGEDAEONSOAPBPOESAORAWNICLEL, PUITS AREDSUHCAELDL AOMVOEURNTWHOAFT WTEHEHAD 0OPPIENRCRESAWUSELEFAHTA1EV7ESAVLAOGSLAKUEEMCDEI.D8E050HIENTOTIHNERTEENMPDOOSVNEDTAOTSHEDOISTTEHTFITILSLLESDW.ORSKOLOIDVSERFTRHOEM NTHEEXTUFPEPWERDAPYOSN.D
ROM THISYOAPKONDT.ELLSTHEMEATUHGAUTSTHISSAMPSLAEMPLWEILLREPIONRDTICAFTOER JTUHLEYSWUICLCLESSSHOOFW TNOHESFELOW ODIFICATIONS.
istribution:
00: RFEJLIXYORDKAVIS, R. 000::: RRiOolGgEeyRkTC0.[.GAGCUaLArRnLeSrEN C: PENNY C MAHONEY C: AWrAtLhTuErR MC.. S[TArEtW]ARTHuston, Jr.
YDAOVRIS)E CGGAAARURLLNSREEERRL) ) HAHONERC ) SHUTSETWOANRT) )
Geigy
'
EIDO14083 '
35 0001.50
INTEROFFICE MEMORANDUM
FrDaotme:: TDeelptsNot
A1N2T-HAOpNrY-19J9.0 T0O2N:Y4]5pmPLAYTIS PPLPAOV-TEIRS 304-863-2228
TTOO:: PCEhaNrNlYesC MT.AHOANltEY TO: WALTER M. STEWART
C AMATRO)NEPC ( STaMART
Subjects C8 At Ory Run
Attached are results for various water samples taken at the Dry Run cLhaoannndcdfe-irdlnrlea.dwnabmToahupet. nCu8mIbelaressakcehdriefnJegirmouYttoaakovfartiotohuetsamkasettertrehiaeamslesastmaapkmlepnilnegsoutlboecocfaatuistoehnesITwneoaftsleodnkon my dSou' pseormneateaddbiatnidonsailtest.estiSnign.ce some of these results are nonzers, we may want t
000.5%
EDosors?
INTEROFFICE MEMORANDUM
dFartoems: TDeelptsNo:
9P2e-tAeprr-01.990Spo0h8n:50am SPPPODH-NSPPDD. 863-4732
TO: ANTHONY J. [TONY] PLAYTIS
PLAYTIS )
Subject: Ory Run C8 Analyses
Here are the results:
SOa.mRp.#l1e DDI.RR..##23 DDILRRI.%#4S
c1o.m6C8 00..00 0o.l6a
These values were calculated from the area of the peaks.
00953
EID0S0168
:
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si ec,
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GATTO ce oRrHED Dam NR
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rom mires
039125
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EID08016
| CO
TER LE RETIRE
a EE
EAT ERR
SUPERNATE SLUDGE TO LETART LANDFILL ~ * :- .
(Latter, stevart to Robertson, August 23, 1990)
FouHtaBS:oriRamsXaey Br EE BCC:
J. B. Allen, Legal
C. F. Muska, Wilmington
g
`C. C. Chien, Louviers. ".... 13 f
.
M. S. Eaton
C. R. Campbell F. Davis .
L. W. Goin
L. K. Ireland A. C. Sobrero W. E. Crawley
"
a
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+
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dFt .C.m Manoney 20un Rese tag TELE Jets
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ER SEER ERR hRs a CEl ERe E E es
@UPIRD
E. |. ou PONT DE NEMOURS & COMPANY
roe eera~S_ EE i oMe iers
August 23, 1990
Mr. Max Robertson, Acting Chief Waste Management Section
GRT A a: eRoLate C ter, uA ston htoesReoubricnssan, 7/30/47 Latter, Huston to Robinson, 9/15/87
Letter, Robinson to Huston, 12/17/87
Eh i NPDES Permit Application: WV0076066 base He. Robertson: Permit Number: 3495
Tfhliusorolpeotltyemreriscotontaimnifnoartmedyousluodfgeourfroimntoeunrt tDoryrReulnocaltaendfill to
the Letart landfill.
It is our site policy to segregate fluoropolymer waste from other aplllantofwatshteesflduuoerotpoolfyimreer vpaostteen,tiawle. wiIlnlabneefrfeolrotcattiongconsolidate aiptpsrocxuirmraetnetlylo7c,a0t0i0ontoantsthoef nDorny-hRauznarLdaondufsilslludtogethaendLdeitratrtfrom
Landfill in Mason County. This sludge is the only fluoropolymer waste known to have been disposed of in Dry Run. All other fluoropolymer waste has been disposed of in the Latart landfill.
The sludge vas generated during the closure of three
fluoropolymer anaercbic digestion ponds during 1968. The movement of this soil to the Dry Run landfill vas discussed with and approved by the DNR in the referenced letters (attached). We
boeulrieevxiesttihnagt tLhaetavratstLaenmdfaitlelriaplermtiot.be relocated is covered under
We plan on beginning this movement early in September, 1990. If you have any questions or comments, please, feel free to contact
me on 863-4271.
Very truly yours,
Ww. Yl
FN aE J Environmental Control Consultant
009135
a7|
000457
WIANSTHEIRNOGFTFIOCNEWOMREKMSORANDUM POLYMERS
March 27, 1991
To: CC.. RF.. MCuasmkpabell TL.. WL.. GBoyirnd AR.. JJ.. PYolaakt,iss
WH.. MDl. RStaemwsaeryt ML.. KG.. MIcrCelluansdky L. Williams
From: P. C. Mahoney yh
QUARTERLY C-8 RESULTS AT DRY RUN LANDFILL Awfetortuearcthhnoetdquatirastkeearnn, duup1rd9i9a0nt.gedthDfeuiegtuhtrieordsahmqouiwasircntogemrmt,uhnei1c9Ca9-t08.iornSe,asmupslltaesmspifweoesrrethe bfeaeknenredcueriivnegd.the first quarter, 1991 but the results have mot dcTaohtneatilnpeuoviiennlgtss torfietnCd-w.8ouladIppbweeialrlprteoimsabsuteeurdetehcerteoafsaiisrnssgtu,mequbautrthtisewriwtihrlelsjuulbstets ta awso soon as' they are available.
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C-8 ISSUES AT WASHINGTON WORKS IN A WAY THAT ALL
col RNS ARE ADDRESSED SO THAT C-8 CAN BE EFFECTIVELY MANAGED
AT THE SITE.
AGENDA
ITEM
INTRODUCTION REVIEW OF AREAS AFFECTED o C-8 BALANCE FOR 1990 AIR DISPERSION MODEL RESULTS
CEG STATUS, C-8 IN WATER
C-8 TEST STATUS
RECOMMENDATIONS FOR DETERMINING SIZE OF PLUME FROM SUPERNATE PONDS
PLANS FOR TIEING IN LPSD WATER WELLS TO PLANT PROCESS WATER SYSTEM
OTHER ISSUES RELOCATION OF SUPERNATE SLUDGE FROM DRY RUN LETART PERMIT
727
RESPONSIBILITY
STEWART MC CLUSKY
STEWART MC CLUSKY CHIEN VANDELL IRELAND GARNER
MAHONEY STEWART
0035.54
EID080797
:
BACKGROUND
_c8
WHAT IS C-8?
o
AMMONIUM
FC-143
PERFLUOROOCTANOATE
FC-118 (20% SOLUTION)
CAS NO. - 3825-26-1
WHAT IS IT USED FOR? DISPERSING AGENT - POLYMERIZATION (USED SINCE LATE 1950's OR EARLY 1960's)
WHERE IS IT USED? TEFLON) POLYMERS - ALL POLYMERIZATION BATCHES TEFLON) COPOLYMERS - FEP POLYMERIZATION
HOW IS IT RELEASED TO ENVIRONMENT? AIR - FINE POWDER AND FEP DRYERS WATER - DISPERSION & FEP SUPERNATE STREAMS ~ FLOAT TANKS - FEP COAGULATORS ~ POLYMERIZATION UNIT STREAMS LAND - SUPERNATE PONDS (NOW CLOSED) - SOLIDS (SOME WET) SENT TO LANDFILLS
HOW TOXIC IS IT? ACUTE - MODERATE CHRONIC - TREATED AS VERY TOXIC BECAUSE C-8 BIO-ACCUMULATES IN BLOOD o AL - 1046/M3
CEG = 0.346/M3
[hew
830
(4/15/91)
'
eesti
EID080798
WASHINGTON WORKS SITE
SUPERNATE POND AREA - CONTAMINATED SOIL - GROUNDWATER (-20 FT)
WEST END OF SITE
~- GROUNDWATER (-75 FT)
C-8 DETECTED
LETART LANDFILL
SURFACE WATER ~ LEACHATE POND OVERFLOW
GROUNDWATER - OLD WELL SAMPLE
ORY RUN LANDFILL
.
SUPERNATE SLUDGE SURFACE WATER
- UPPER POND - SEDIMENTATION BASIN - DISCHARGE STREAM AT PROPERTY LINE GROUNDWATER - MONITOR WELLS
PPM 100 100 PPB
2-3
Jiu] 23 2-3
Py 75-100 2-3 2-3 .04-.2 NO
ecntis
EID080799
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C-8 IN DRY RUN
MANAGEMENT PLAN
PROPOSAL NO. 1 -
PROS
LEAVE SUPERNATE SLUDGE IN PLACE, STABILIZE THE C-8 T RETARD MIGRATION BY COVERING WITH 2 FT NATIVE CLAY
~- EASY TO DO - LESS EXPENSIVE = NO TRUCKS ON HIGHWAYS = NOT A COMMUNITY ISSUE AT LETART - REDUCES SURFACE WATER CONTAMINATION LEVEL - PERMIT MODIFICATION NOT AN ISSUE CONS
= MAY NOT PROTECT GROUNDWATER - SURFACE WATER CONTAMINATION MAY BE ABOVE CEG
PROPOSAL NO. 2 PROS
REMOVE SUPERNATE SLUDGE FROM DRY RUN AND RELOCATE THE MATERIAL TO LETART
- REMOVE SOURCE FROM THE LANDFILL - REDUCES SURFACE WATER CONTAMINATION LEVEL - GROUNDWATER CONTAMINATION POTENTIAL IS REDUCED CONS
~ TRUCKS ON HIGHWAY ~ COMMUNITY ISSUE AT LETART ~ NEED PERMIT FROM WV-ONR ~ SURFACE WATER MAY STILL BE ABOVE CEG ~ GROUNDWATER MAY STILL BE CONTAMINATED = COST EXPECTED TO BE 75-100M - OTHER PERMIT ISSUES AT LETART
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39
000155
TEMPORARY OPERATING INSTRUCTIONS
101 No. 91-6
TITLE: Relocation of supernate sludge within Dry Run Landfill
AREA: Power and Services Dry Run Landfill
Extent of work: 09/23/91 to 10/31/91
Objective: sluTdhgeeobtjheacttiwvaes oofrigtihnisalwloyrklanisdfitlolerdelaotcatDerytRhuensLuapnedrfnialtle tion a1n98o8t.herThelocsaltudigoen wwiiltlhinbethmeoveldandffriolml.itsThicsurrneenwtlloocactaitoinon wsilluldger.eduAclel threeapsootnaebnlteialeffoofrtlseacwihlilngbefrommadethetosucpoemrpnlaetteely remove the sludge from the existing location.
SAFETY: Arlelmaisnafeitnyefrfuelcets dnuorwinign eefxfeeccuttioatn otfhetDhriys TR.u0n.IL.andfill will
MSDS MSDS
for for
FC-143 Triton
XF-L1U0O0RADis (aCt-8t)achiesd.attached.
((AAttttaacchhmmeenntt AA--12))
PPE requireSdafdeutryingglashsaensdliwintghofsidtehesshiuepledrsnate material: RLounbgberslegelvoveeds shirts
Nsoupescmnoaktinegmmataetreiraila.ls will be permitted in the vicinity of the
AIvfoiddustbreiasthgienngeradtuesdt dcuornitnagmintahetedexcwiatvhatitohen osrupmeronvaetmeentmatoefritahle. sludge, the sludge should be sprayed with water to reduce the dust problem.
CIofortdheinadtuosrtin(gA. prJ.oblPleamytpiesr)siswtisl,l
the Site Occupational be consulted.
Health
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CONFIDENTIAL
TO: JW.PB.. AANLGLEERNSO-N07-150612026
CTC. RCDC BCAHRIREYN-- N(93g34529-1
.
WM..S0.. CD0E8A8K - 001112003106
M3.S.. ELAETTOTNI-NGWi- Wat0
3T00S0T! LVIANNDDEELLLL -_ 0L131a0e5e6s
0. K. VON SCARILTZ - p11030
FROM: R. J. ZIPFEL - why AV
OHIO RIVER, SITEC-8TESITN WWEALTLESR, SAANMDPLENEWRESLUULBTESCK WATER SYSTEM
pplraenstencseiteoTfhteeCs-t8siwtieenllcSseopntdaenumdcbteetrdh,eann1e9w9e1x.tLeunbseThicikvsePpusrbaolmgiprclaiWmnagtwaepsrrogStroyasmtfeumroftwheetlrhlesanOahflioyorzeRtihvatehre,
nQTeuewavleilLfsuybeincakntohPueutbsOlihidiceoaRDtuievrePronStyasndtaneanilnwyettlihicesa,laqutToiafbgeoarrianbteonrfeyuarttfhhoerrtCh-ei8nsfiIotnrem,Vaatiatonendr
otno tbheeginC-8to data (CH
The results of the sampling program showed the following: 1. Non-detectible levels of C-8 fn the Ohio River upstream of the site. 2. CS-i8teleavnedlsinattheexpdeocuttefdevableuneesathfnthtehesOihtieo(R0i1dverLubdeocwknstVraetaemr oSfysttehmes
walls).
3. Sweevlelns s(7h)oweodfneoing-hdtet(e8c)tirbelseultlseveflrsomotfheC-Bn.ew TLhuebeecikgWhatthersaSmpylsetemgsave a C-8 result near the lower analytical detection limit.
are attachTedh.e cAonmypleqtueestdiatoanspaocnkatgheeseandrespualthtsfoorrvaortdherfroimtemtshisinsetghmiesnt of work wcroimtuenri.cation package should be directed to Penny Mahoney, Dave Ramsey or the
AtRtZa:c5ham1ent
.
EoTsi10
.
00niz
\
PRIVILEGED & CONFIDENTIAL
SAMPLING PROGRAM SUMMARY
OVERVIEW OF SAMPLING RESULTS SUMMARY
PATH FORWARD
950-1
pani
EIDO79111
:8 SAMPLING RESULTS
wTeelslt W#e3l3l1 #27 Well Mi-4 OGhhiioo RRiivveerr -11 Duplicate OOhhiioo RRiivveerr --22 Duplicate OOhhifoo RRiivveerr --33 D(uNpelaricOauttefall) OOhhtioo RRiivveerr --44 Duplicate OOhhiioo RRiivveerr --55 Duplicate OOhhiioo RRiivveerr --66 Duplicate NHeeww LLuubbeecckk WWeellll --FF up] NNeeww LLuubbeecckk WWeellll --B8 Dupl 0011dd LLuubbeecckk WWeellll --11 bupl 0011dd LLuubbeecckk WWeellll --44 Dupl
Tw 3%
ExSptearitmieonntal (PPB C-8)
<7.11 2.7 <<11 3<.19 1196.:58 53.2 42.82 <2.10 <<11 <<11 8a.18 42..92
CHM Hille (p8 C-8)
poten pePslHE
0112 2e.r3e0% 02 fe NNoott DDeetteecctteedd NHoott DDeetteecctteedd 112.000 01.08 111m 00.65 NNoott DDeetteecctteedd Not0.D3etected Dest1r1oyed 01.79 75 46
* ChoowW.TI experienced analytical difficulties. Absolute nusbers may
91501/2/91 .
. 009275
EIDO79112
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* LIMITS
- Tw - AEL = CE6A = CEGW
ug/m3
100 10
0.3 =
0
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CALCULATED DOSE
- REL
- CEG
100 ug/day
6 ug/day
.
EID079258
:
009139
D-E8 TECTED
WASHINGTON WORKS SITE o SUPERNATE POND AREA ~ CONTAMINATED SOIL - GROUNDWATER (-20 FT.) WEST END OF SITE - WELLS 27 & 4 - GROUNDWATER (-75 FT.) KO. 5 OUTFALL - DISCHARGE TO OHIO RIVER
WASHINGTON WORKS EMPLOYEES
e 1991 (VOLUNTARY TESTING)
DRINKING WATER (LPSD) o 1984 - 1989 o 1991
LETARTSURLFAANCDEF= ILWLATER - LEACHATE POND OVERFLOW
GROUNDWATER - WELL SAMPLES
DRY RUN LANDFILL SUPERNATE SLUDGE SURFACE WATER - UPPER POND - SEDIMENTATION BASIN - DISCHARGE STREAM AT PROPERTY LINE GROUNDWATER - MONITOR WELLS
*Revised analytical method
.
0091.34
oH 100 100 PPB 2-4 40 BPH
UP TOS
PPB 0.7 -2.2
3.8%
= PPM 2-3 0.05 - 0.7 PoM 75-100 2-3 2-3 0.04 - .2 PPB 2-5
EID079259
GROUNDWATER ISSUES
-
1) PLANT SITE ROUTINE SAMPLE RESULTS @ VERIFICATION INVESTIGATION
2) LETART LANDFILL eo LINER DEMONSTRATION e SITE OVERVIEW o PROPOSED STRATEGY
3) DRY RUN LANDFILL o DETECTED IN DOWNGRADIENT WELLS
060485."
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INTEROFFICE MENORANDUK
DFartoem:: TDeelpt:No:
J2A2M-EJSan-R19L9A3WSO1N2:23pm LPPADWSONIR 304-863-4618
10: Distribution List
Subject: Great News on Surfactant
tBorxuciec,itythainsd ibsiotaecrcruifmiuclanteivosn. coTmhbienefdavwoirtahblepriroerporwtosrkonshobwoithngatchuitse
shauvrefaactavnitablsehocualnddibdeatseuittoabrleeplfaocreFCE8P mienanmsuchthaotf, "Tfeofrlotnh"e. firEsvetntibmeet,terv,e
the candidate position.
would
be
produced
internally,
improving
our
overall
cost
Waeddhiatvieonableenpowlayimteirnigzaotnionthitsesttionxgi.cityI athsisnekssmtehentfboecfusoreofcowmomrekncsihnoguld now stewsitticnhg.to oCuarn oyroguanpirzoavtiidoen.us Ovbivtihoupsoluyn,d wqeuawnitliltiense?ed pure material for
Tchoentafcotcalhimpotiontdefvoerloopurouirntepratnhalfoerfvfaorrdt.s should be Roger Zipfel. Please
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EID087669
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INTEROPPICE KEMORANDUN
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TDeeplt:No: D54u0p-o3n4t90Chemicais
T7O0:: KH.sus-pNeannceHruanPgrowse
(( PHroOAWNSGEHKSaTATALALaTATicSrLoCnEO)) )
Scei: TA.imcehsar.les`Lasvoebernero
(( LsRoRBSROENRTARC AATT AALL AATT WWEESS |)
Subject: Co-Tas: the rest of the story
Folks:
-- C6-185, aGenrdry hKaevnenedsymehasgoofdinineswhse,d ahinsd bIihcaavcecunsuelmaetisoenentemsatciensg on
It you'll recall, the good news (I've attached the
ETmBpherieatecstwveteiieotCnnuahgs-a7n382mX3wesmaaowsn,adIs3swH5ah'n3isiodtcthiCatBmhseeaspxnrrp,oelldaaeudtsicihsntlas,ytbiivoetiaalnsciiomsniuoinsnddaeeletiyteaabditNylia)visfefirdowiemaihsnehcottehmhpeipaicattreluiCnirs6vgeo-ei;nrTtBisSiittawsasasaiied
iinntothethebloliovdesrt,reabnut(caonudldRenncoet,saeyLilwihetbhieeractcwumaisntSiisnepsiy emcining
finished.TheAbedtettearilendevsrepiosrtthaetn tthhee bsvleoroadllwormkceonnretheismice is
Gfoerrtthycosmnianrge,d vbuitthImweantotseady!you all to be aware of the information
mdEaeyOasl'DsofVsApSriEeksceasodevn"etwCriioyant,lthlryovd,lua*rriwynhiggranotguwphvl)iae:scvheldsaWoevneeowrfeyvraCese7-FdttoaahsveenfeabteneiddooCa38dl"gosriwoehumopupsprterohafiwreamsriece
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average oTfhefirveesualntisna(lisn pfporm eFalcuhordianceainpoitnhee) blaoveodssterefaasr,ioutnhse
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5.30
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33.23
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8.19
0.45
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22.20
$fdZhooe.suCen8sde,vieainnnreTatatthhkieeentnghbbeellsiootnooedddcssottbmrrybeeianamnamatlieatohpnapm,neiacerCt,s5h~eTstsBoieSx.breteosaFurulnoritutnsnhedesrtamsiyoemrveteesh,natmdtohrewenhvesnhneaLleriqoeuliaiilfiec tfliumoerfirnaemele(vGeelrsry'hhsaidgchoremesmtteurncntoendwcaestnottrhtaahtteiotcn-o1nt/te2rsotlecdobualCdsoeohlraievnseembainuheowdthoast same spnhtoirctipasateodnegrdaeya;teritv'asluteosughandtosoteldlidfnrootm tthaekedaatnay bSeemcearuesse wehad dbbgoeaeetytsusweeeCeCnenh-aTt3da0as,yw.2h0ez4nerSotOheatnidmmaetdsearyimaoSlreevednoo)fe.sthleAenaCdvaefwtiihnneadlslbyl,uopodtshitneretlhaiemv'.erdiseednaoetcaonTeerree
yery goon2% (IviPthromGiersreyd'saboavses,ist1a/n1c1e)b,e wanrditwiinlglupRavaecocmopnlieesteorrerpuoirst
report sent to each of you when it is finished.
Jim/Charlie=-
Bruce I've left it to you to forward this note to other ybmoeeutmrtbeeerrnsdt.hoafnyoIuwrhoorsgpaenicziaftiicoanl,lyasis yoiuntkenroeswtmeudchan
=
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=
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2shnadresinicteSwoimIte'h119y0ob0ued on"uebtvesfoorfjeutshItegionefsfoincethethiCss wheoemkoslog3uethoofmgiZeomy)liaTSS,
piLenirvftelhreuowredoilGeogetchr.ttrayn(oKHvisee.cnnteaeccdsoiytndetrdjo(ulZ3s)oMt'nsysalsen"7taC8%Smfj,eu.ntcahtTepihloeCnoterotefoBsfEup.ioptmesarrcsealrnaetsreiennncccoreueorasascgeiannigyn.
ivnersliiovnerAlwtoeoiktghhgetoohgdiagihrnee,rlattehinedvevoaftlouteChase. slcoaoSlkpee,cLiikfbeioctathlhliTly8!,S aantd1t00h%e Cs6ocrease
cs - 13.1ppm
ms
378ppm
ce-r8S -- 705ppm
shows theTheC6-kTeyBSdattoabearecleaatrl5y0%beitntcerreastehaninthlei.vecrheweeigshitc,: which
cs - sam
ms
ppm
ces -- 142ppm
between CE8venandatth2e5%C6i-nTc8rSeasies qiunitleiveerncowueriagghti,ng:the comparison
cs ~ cam
C6135 -- ca 30pm
ce-TBS."Gerry's cover note says: "cs = 30-50X more potent than
Lluorineinthe bloodstreanwork is stillDeinedane oi bie
efficiently.
RAR
.
out
to
Ihe blood
be as good
testing
should
be
finished
soon;
if
it
turns
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C-8 IN WASHINGTON WORKS DRINKING WATER
shown C-8Recleenvtelssamofpli0n.1g, of0.5t,he2.f9our& W3.a3shipnagrttsonpWeorrkbsilldiroinn.kinTghesweatvearluweesllsarehave surprisingly high but do not pose a health threat to our employees. corporateThAeELa.llTohwiasbleleveexlposiusre0.0l1evmelg/mo3f oCr-80.f5o6r popubr. eTmhpilsoyeiessanisaisretborbnyeour bceocnatursoel lseuvcehl.a Aconctornotlrollevleelvelwasfonrotemdpeleoymeeed dnerciensksianrgy.water has mot been set level basEixsp.osAutrethteo ACE-8L ains ebemsptloyuenedercsatnoboed sbyafeetxyamienxipnogsedthetoASaL12onhoaurdaidlosyedoofse h0e.10woumgldofonCl-y8.beIfexpanoseemdpltooyeaedwaeirley tdoosedriofnk0w.a00t6ermgw.i,thora C1-/820tlheveolf otfhe3.A3ELppb c(onnostuem:edC)-8. is essentially fully absorbed by the human body if b.reathed or for airboAtrnethCi-s8teixmpeosaulrle.opeThreatisnlgighatreaasddiotniosniatle earxeposiunrecomipmlpioasnecdebytodrtihenkAiSnLg dwoasteerofwiCt-h8C-a8llolweevedlsbyofthe3-A4ELp.pb should not affect our compliance to the daily GuidelineW)e sfohrouCl-d8noitn gweattercoonffus1.e0d bppyb.thTehicsurgruenitdeCElGeve(lCoimsmufnoirtyexEpxopsousruereto the general public and not for the healthy workforce here on site. enviromenHtoawlevegrr,oupthiasndsittheuatC-i8ontesahmoulwdillnotendbeeavtoarkentolifguhltllyy.undTheerstsaitned these recent sample results and provide you with future programs. from HaskAetltla.ched is the technical basis for the allowable dose exposure levels
06535
EID089421
44 0663.22
-
GSasteonnCnaega,ron
Lig 5
DEPARTDMIEVNITSIGOFNCOOMFMEERNCVE,ILRAOBNOMRE&NETNAVLIRPONRMOETNTEACLTRIEOSNOURCES Cha1r2t0es1ioGnr,oaWnNtr2i6r3S1i1r1ee0t88 July 8, 1993
Oa a can
dni
SMrr.. WE.nMv.irSotnemewnatratl Control Consultant PE..0I.. BDouxPon1t217de Nemours and Company Parkersburg, WV 26102-1217
\ FeW a
pa )
profed XKQD
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w [i Mr. Stewart:
Re: fSooliids Wiaasntcee/pNuPeDeEmSs Wmateerr WV0076244, Dry Run Landfill
\
2|
\PB ,
ISivseaalgeedncnyo'ns-cJoumnpelia28n,ce1w9i93thfcioenldditrieovnisewD.o1f. thaendaGb.o6v.e offactihleity bsaebeiodnvigemenoptpeaertrmiaiottnedapsoinnedx.ccoemspAsllisivoea,ncsetehdweiimteuhnptpeCrhoansdsietdaiicomcneunmtuD.al1ta.itoendduepionntdotheis lnoowter tehxeceslsoivveer psoenddi,meOnuttlaectcumNou.lat0i0o1,n. isFcuratuhseirnmgorae,distcheolodrisacthiaorngeof ftrhoem wreictehiivnitnhgestporneda.m, Tahpepraerfeonrtel,y tdhuee steodiamnenatcactuimounlatpioondnsomfusatlgbaee racselsqeiuasentsetdsinotudtheattaentrdhmietnhieOnugtclaetuthsee00co1faubsaeelgaaolfnaagllrygozaweltdhgfrmoourwsttNhi,tbreitthdeie,sterNamigitenrneacdty.e, To Aumonia Nitrogen, Total Phosphorus, and BOD.
I {4 aTgoenfcaycilsiutgagteeststhethactletahneoutuppoefrtsheedilmoewnetratsieodnimpeonntdatbieoncploenadn,edthoiust CFAloawned rsupbosnedq.uently placed into service during the cleanout of the wae? Tbheisanaagleynzceyd aflosroacruetqeuesttosxicthiatty atshededtiesrcmhianregde bfyropmerOcuetnlettageNo. 001
mmionrntoawlsityand(fDoauprhtnyi-ae.ightDihsosuorlvesdcrOexeyngienng bciocnacsesnatyr)atitoonfsahtahleladbe deternined prior to running the bioassay.
Wsihatlhlinsutbhmiirtty1)dayascutoef tthoexidcaittey oftatshtiinsg rleetstuelrt,s,yo2)urthceompaabonvye oruetfetrheencuepdpelraboanrdatloorwyeranasleydsiemse,ndation3) poandssc.hedule for cleaning
oe pbs"
whal
ofl -
= 069733
EIDO12563
oo MPra.gesttweowart
Scohnotualcdtyomue hatave367a-n2y72q0u.estions concerning the above, please sincerely, OFFICE OF WATER RESOURCES
Dic Bute
JIonhdnustG.riaBlritBvreacn,chGeologist 38/3 ce: SCuipnedryviMsuosrs,er,EnvInisrpo.n,menEtnavlirEonnfmoerncteamlenEtn,forDciesmt.entV,I. Dist. VI.
0001.2
EIDO12564
4s
0001.25
|
PROCEDURE FOR CLEANING OUT LOWER SEDIMENT AT DRY RUN LANDFILL b1.etwIeneneartlhey Aluogweurstspeldaicmeentbapilosndofandhaytheatacthteivenarfrilolwesatreapoitontmiofnimtihezehosleldoiwmen going to the pond and out the outfall if it does rain. f2.roAmfttehre tlhoewerAugpuosntd moovnetrhfllyowsalimnpelesandhavderaibneenthetakleonwerrepmoonvde. the drain plug
3. Allow the lower pond to dry out for approximately two weeks. 4L.anRdefimlolvethtehesesdeidmiemnetntinfrotmhethaectilvoewerlapnodnfdillusianrgea.a backhoe and a bulldozer. 5t.heMepaonsdu.re the dimensions of the lower pond and note them on the a sketch of p6.ondRebpalcackeintheserdvriacien. plug in the overflow line to place the lower sediment
0695.37,
EID017107
a6
0001.27
|
INTEROPPICE MEMORANDUM
TO: Thomas B. Valdron
FDartoem:: Dept: Tel No:
R05I-CAHuAgR-D1A99K3IROSlC:H3NlEpRa, JR KPIORVSECRHR&ASERVICES (304) 863-2992
( VALDROTR)
Subject: Dry Run Pond,
Toa,
MpIel'leavaissneurdebeoyeossunu''rtevethehsienenknouiVstalvvtih'laslt'adsnodgaoEnidy'nsghamorenmm,oasn.hdavvehWahhtenimtoyooeupxepnteactlthk.e tvoaAllBsvooes,oalilf
1tshe lvoaoyk.ingThbeettfearstearndthbiesttesrtufalfl letahveest,imet.he use one?
bIsettheer.eveTnhtautalsliylgtoifnegnceto
Thanks,
The "worst* golfer around...
0601.25
2
EID017129
i
a
0061.85
|-
verses|
Fi-o
;
Mortality Among Employees of a
9
Perfluorooctanoi%c Aci:d Producti: on g
Plant
s
i1
Frank D. Gilliland, MD, PhD
Si ammonium peruoroocnote, ,
Jack S. Mandel, PhD, MPH
erfluorooctanoic acid (PFOA) and its
are' perfluorinated surfactants. Be.
craougseorfstthheeiry nairquewesdurifnce3sce Perfluorooctanoic acid (PFOA) has beenfound at low levels (10 to 100
poacnctuspapteironbaillllyioen)xpionsseedrawoorftkehrse. gAelntehroaulgphopPuFlOatAiohnasanbdeeant rheipgohretredle1v0elbseian
Smet of mance mci ats
ccioznerssu,mleurbripcraondtus,ctwsetitnicnlgudagienngtsp,laastnid-
promoter ofrodent hepatocarcinogenesis and to alter reproductive hormones emulsifiers." Despite their wide-
|
in humans and rodents, there is litle information on human health effects spread use, little is known about po-
|
associated with
between PFOA
PFO
and
Amoerxtpaolsiutryeu.sTihneg
parerseetrnotsspteucdtiyveexcaomhoirntedmtohrtearleiltaytidoensisghni.p
tenPtiFalOaAdvienrdsuecehdeamlathrkefefdecbtse.patomeg-
i The cohortconsof2i78s8mtaleeandd 749femaleworkers employedbetween aly and peroxisome proliferation in
ii
`1m9o4rt7alaintdy
r1a9t8io3
watasa
p.l75an(t9t5h%atcponrfoidduecnecdePiFntOeAr.valT[hCel]a.ll5-6catuos.e9s9s)tfaonrdawrodimzeend
~~
Todent livers. The chemically di-
Verse groupofxenobiotics that induce
|
and .77 (95% CI. .69 to .86) for men. Among men the cardiovascular ~ Peroxisomes is of concern because of
|
gsatsatnrdoairndteiszteidnamlodritsaelaisteys rwaatse .w5a7s(9658% C(I9,5%.29C(I0, ..995)8. tTohe.r8e0)waasndnotshiegniaflil-. 1PSaaisoscourcciiantoigoennewsiist.h"nonPgFeOnAotdiodrboietc-
1| Socrarwlloymeinnr.creTaaesnedyec5aaru5sso%e-fsCpee1mcipf1li0oc7ysm1te0annt1da0ir6nd)iezxnepdorsmeosdrjaotlbistcywoarsantesioomfcoiaranetieltdhyewrcimotemhn.a (BpogreSlloafEdialenr2 iincnroeamsaeS dsniunmbaeryoSefEahreErpt.
i|
pcaanrceedrtdoetatohesmopvleoraylmleanntdfinouPrFaOmAopnrgodtuhcetieoxnp.osTehderweorwkeerrse; otnulsy,sihxeprroessilaltse
`rican ndpromotion) and wi
Po pertio eeior3:0 Pee"
PmuFsOtA,bePRiOntMermpraeyteidnccraeuatsieoupsrloys.aItfepcraonscteartme ocarnacerbmortaelriitnygirseprreoldautcetdiv1e0. afesminatosicntashmaveeshownfsiagninfictantly
`hormones in male workers.
SthueggPeFsOteAd-htraetattheedmraactkesd.rIotdheanstbheepn
maatromkeegralfyorpcraordcuicneogdenbiyc PpFoOteAniisela cl`Tlhetoubmseorrvantiaon3s-oyefairnrctreaPsFeOd ALefydoigd. EynPipnegoRtbsiytOpuadolytuAhiaesnc.sdiatteoahtfaasdrriPesFrciguOoopAnotei-ssosdendna0otcfsawietthidhea
nor are medised by 3 hormonal
|Clme etsehnoSnofoMEnimniamrpeMitieupCioMdetinoStrebraETeoEdTReeSi mpaPdsFsObsArheysdof0ccubpuneioealiybxu
:!! MCa`E iAodidmoreeis,sncNoerowrr eyMsepAsoinmcdoeaTnnucr emnoo:rCoFR lraezgk e Dof.sG0iglp0lCaasnimdi,ssMy D1d,edUSn, ilEvoevrdisiNotEny,soAcflNbaueaqwuMeMriqeudei,doNSMch8o7o1l3o1.f LGcHIeooiaocs8re,mPfeaFocmOci.Ausmgisumrlataelhtlais,otntreheqoarfune1Pro.nFf5sOyuheAePagrFmsmOa.oAy
0CO=G
EID088658
A,
-~
eral populations of industrialized countries'" iz likes 10 he ac result
death certificates for coding by the same GOSOIOPS. In the 2F death cer
men based on US andMinnesota waite male moraiity ries for three
:
doPofsFNeaOsonA. sGhcecarutmhueiaptnooenleofsssmeralndPFnOs0A
oare nee ocoChsnne a tificates from 1970 10 1989 resubmit
ted to the posologist for ICDcoding,
SaipwRtOT cl of fmutoneof latencyiatervals(10, 15,and20years)
and three categories ofduration of
B CPcPrRaooOsnsN-ltcseocate CipohanaaolshPseawtEoucrv OdPikyENeoraOvnsmNaoasnpBgtoo tosiwuocrgkaileoeroensfdoprcooeWaovrderkeTroodsrdse|owlBemoprsoeeedhciatoeogsBomrPoizEraetdOavsa,oexr-
opf roegrpeamodrpeievr,d aeaelkbb(lry(CMRn MoBDoo)snpst1o2eorodndns d.9e2x5% a as 0 carole
pfwioTttmhoidneGcnyeremeuamsietsdneoforedwenheteStshteoSrstemTroonrealalnyd CompsPOoRn
ClSwhooerromtkvieeaecddea]lbepDiemevoiosihCvohne.hUCmwnehieehxpDHeomsoeednnwvorfrp ky Bwearreo tesTtaigmatiEed.s udTts5ihoe3ne8gtdfeptpmrros oodrpoo00rrtciicoDetnnoaetml
Cooierisoorhm3oploanreal 5lywrea.s
hgneemesBDiwO olnbcRoonfoona m. a oe abd women of ue:
ooCfaea oeohpoe1f909,nds eeodhdmaoddesblfsoer fmoem Soa in i calomel
Jets
orate deus ve Sono So ohcpemorment Laddur
The Ipslant coms of sv dike spp a nk iy expected num ofdb eathe sobr tais ned Soi SodTo ates covariates inthe model. Theanalyses
sions, with PFOA production re-
aSvrecbe1e phreoCcheedmiIshDsiviiv.i.A nSdimasp0estmeaynrhoh number of other specialty chemicals
quinquennial age, calendar period, theUnitedStatesand Minnesopotpa-
priatenessof theproportionalhazard
poeoCnsofhBe poavpoicrailsondybsarodf fied models with graphical analysis of
`Thestudy cohortconsiofswtorekedrs whowereempaltto he py lane tfod rat
served person-time.' Because less than 1%ofplant emplowyereeneons-
time relationships and models that tested the significanceof a product
least 6 mouths between Jan 1, 1947, and Dec 31, 1983. Data were ab-
white, white male and white female rates were used for comparison. For
term between exposure and log follow-up time. Proportional hazard
| mmtmnomeme ele AJ
soStrraectevdfortomeerplannat epheredsonpneaflomrnecvorohdswe,
S wnodmpen,eoe nlay UI nciatevn deSttaatedsrBao etenEsdweerre
calculations were conducted using
ty
|J{H3|] ISTpRSoncooioadnwl aSev1c9i5uD6ar7HietayaloAAsdIl9mni8dwnve1iesesrtefarrmoakreteithoowdenimfvpoierittndhhnee
sSaofalreantnenceduy,rdtultrayotiogCn hopf`eermyoplonhyymey,nt, Comoe mom |
DBaeA pSto6tpalT2of3395w377erwoawrorkkeersdr1esn1eic9memp4dpl7ol1ryoe0orddmd. Bogner Sx worker who
| aaofmces cpm ahh eecompu bes ma Lo empl emploment reer
|
+
or hl ep a directory assistance, Metronet a0d
TRW searches, reverse directories,
unexposed workers using stratified
SMRs. SMRs were calculated for
cohort consisted of 2788 (9%) mea
and 749(21%)women(Table1). Mea
|(3| TaBcatiangoSneeeaighrbporosamaDnnedhanerelsartivpeis,neaaeod -- mCy oofos n ni dMt lEna ee,1s 9n471088 ri
}
identifiedas,orpresumed10be, de-
Division
Division
HIEs2 Suea dand caruaseioof ntwocodnectetrhnsinwghitchhe
Female Male Female Male Female Male
i JC ESKacm orlones coyse btceadneussoucdossy;
i ai cue ofdoh
MmWeereeiewieotey
Nmes
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16 Tm
OmeBEmRo OmBs 0m3s
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Movwaos ww ges me Menemacuny wr "wd"di
gms owes mo "ai "wl "Wl
EID088659
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1
.|
ocvbiosdneetrdrvibabtuitoeend,r7w1h,hv1ie1c7hCe.h7weeepremerissoennq-uDyaeloalryisdnoif ~~ CTShhMeeRmiawlcala<scaD.u3is6veis(s9iSe5eM%RwCIo,mfoe.r0n7tthwoeet1m.0o5n)1-. a0 son.Coemicu Urvison. Women (53% Cl 08 10 1.24) 80dthecancer
4.ata5nt9e)cain6ct(ehre4wC%ehreCem1i2c.0a3l7(D19i5v2i%s0iC9oIn,br.o5o5au1yp0 Don-Chrmicl Dwaken coset, 1s the
. }
ctwoou-utlhiorudisodf w1h9i3c0h9w4erepeinrtshoengoeo,. Ceca Division.
(SdMaRa nwoatsh9ow1e)(.95% CI, 4910 1.52) UsingMinnesota rats for compar.
4fChoeommbispcerarovlesdDaitevaiccsdaonn2cger.ocuiTpph,eectrihenrwedawseenprtge
oftiheicohsotarttis(Twaabsleo2b).oTheereforwe1re00$%0 fsoornc,arhdeioSvaMsRculfaorrdmiseenasefosr,aanlld orsasl, cgauaseiofadesastocanadcoaneobgey n1esiandy
: it tdCbeheaetmhoiscna-alCmhoDeniavgiisctihaoelnwcDooimbvoeirnstoa(nInLdcoi3nb9otrhi)en tgchaaesnttcrloyianlteeussttishnaalned1Sip(sMeToaaRsbeslcsewa4wis)a.slfNaroggineaescioorf SveixMspiRoosnwuracesogboLrotri, 0Ftoo5hre%thCupLerCo,hsp3aetm2ei,4cacal4n7Dc0ei)r |
; d2e0adth3s48idneatthhse aCmhoeomgictahlemeDinvi(s1o4n8 wTahseraensysultgswenreisiiimcffwirahelenntafhtroemye1x.. ignrohupe pear than 15-year Meagy
rDiovuipsioanndgr2o0up0).in tDehaethv.on.cCehtefmciaceals bpaosceiddonnuUmbSermsorotfalmiatlyeradteesa.tFhorwetree tioTnaabllbearpdremoedaesl tohrelfloaclapirnopaor..
|i
werFeobotainred twfhoer o9S9M.R5m%fooferdaelaatlhasu,.ses tdheraetehslaftrenocmy ailnltecrvaaulsse,sthreanSgMedRsfrfoomr acmanocnerg, athned 2p7ro9s8tamtea-lceanwcoerrkmeorrstaelimty
:
hI!
ofdeath (SMR = .75; 95% CI, 56 to
p9e9c)tewda(sTasbiglneif3i)c.anTthleyrleowwears tohoansoe.x
75 to 7].For al cancers,the SMRs
rpaonngsegdnifircoamnt1.06 10 1.12 and were
ployed for more than 6 months. The
emsotinmaltyed froerl3atiyveearrisknfocr eall<cagusee
: i oGraloatnenwciytfhordudreaaitohss rofoemmpalllocyumseenst, tioAnmbeotsweemnesa,ntyhecga:usiesof0doeaatshsoacinad: CatI,fs1t07emtpolo0y9m)e.ntYewarsof1.f08i(e5a%
cancer, and cardiovascular diseases duration of plant employment. The ploymeat and duration of employ-
ioit (ChdhaaeatmaiecxtapoeltcisDeidh.voiwsnIi)no.nChMweoomrimucleainltywDaiasvmiolaneng ag7lr2lo1cu0apusa1e.n0sd1)S6fM9oRr9tsh5e%wCehrCe1e,rn8$c69alt(oD9i75v9%i)siCfoLon,r mdceieatntethdswwefirrteohmnmeagolantctiahvuessleyse.mapsTslohocyieartidsekdinswsitoth-eh
: | 5wo%menC,Lth2e3a1l0l-.c8a6us)esaSdMtRewcas e46 (theennotn-sChhoewmni)caTloeDMivisBionsgr.oup sChoemmticgailfnDnivtision was small .and
ii oct
ity ntmhe odef,oallenpgtohsotfeecmapnlcoeyrment inmare the Chemical Divison was posively
! VialStats4nd Causa ofDeathAscertaioammaontg Fama and Mal
tdi wi
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Enhjeen_1C5h47o-m19c0u9Oiun_
oS, Tene we
MreeinnChoamecONFoene__TWoe _
{Clyveroait nwcoee1s30er) iFnoreCwha1e0smiac1a1nl D0ci5m%v
:i;
SAe Tf2eE4 %9A53 W1R1e91 N%889SH46os x9M16W1E2o00 %8E62fT6o39 %9C33HWuAeSo %gNrEs LpSelo6[ycmmleinavteiin0thneCnhem1i0ai0ln apimvipdoend,
|
Tou 265 1080 a a sod 100 veh a 4p 100 ai oo wihworkersnever eploinehde
_
ployment was posiively asadaied
t
`withprostatecancer morality. Length
Obuseersved(Obs)andExpected (Exp) Deaths, StandardizedMortalityRatios (SMR) oDfivtisiimoen ewmapslnooytedsiginnifitchaentClyhermeilactaeld
and 95%ConfidenceIntervals(CI)for 749 FemaleEmployees.
t mortality from Jung cancer, gas
.
--CrHC eecCueeeswu essoe 7w3 c EwBGpnuEiO SooMmmRucGot XmmEawSEnh a ipoa d cann cer, pancreatic cane
;
afCroeoin 23imisFm oSonhm ooommweaen Di"sTchu"ssvsaiosnthefistrezospe)cicvoe-
ScoxUrroneie W3w3 uu EmR taoSmk ooSsmoeam:m pFHolrotyeemdoirnal8oitrPysFsOh uAdyprooe fduwocriokonena rlspmlaenemt.
1
pr w
--_--
DII 3
34
8
2
wn
au
Jueh Shan
; and womenwassignificantlylessthan
ewxoprekcetred.effeBcetc,auinsteernoafl ctohmepahreiaslotnhsy
|
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009.8%
I rrmmo comico 1 sn oe sn be WE RaDTteeaest,hlsAamndcS;ta7n66dairkdLMiioonruaesF,eT u1os (6SME4;Ba4s7eT d1o-9n39r1Mnoens9EovrsT e6WEhmi5pteoyM,euda
summed association between PFOA YSiXoPwOSeUdTsEshyipotbi ess p sbae
.
ntheChemica Ovisn, 1947-1980 Causes AsEmpioyeas
YYoan nEmpotrorie eain
bsseohcocuiladtcihooantocmebaeydbovieenrro.etoaelrpmrmeatayeydb.ehTathvheee
Te of Death
Coane
e --_-- wer
U2 i0n0 oSeme;n
v-- eUaoe eW-- 2Ns s1-- 0 oO72rT-- eIrSa
hDeaumnsItpoffeaaen nuonareevc,oSgenoizrbetdeaedbnovnierob:ne.
OCuPoranewssta Rory
528?4
3567%48 0019048 0u05mi1mB3 3042 102 M148
4{9 Id4oume i1o1am5 o0ossaa1sdrodsrr 12 12 tor Osorss
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PjTreLoruslantga
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2318 02m68%0974 m1T00m%0 0e00630a766-i2101d4s54 11141 1oo10e57Rs70 i221.0N3003 00Sb5o31sh-i41ru8%e4s
13 1207 109 057484 5 478 108 0304s
TcPhFaeOnAgdeasendwrseprdoduectimve 'ahoirmnone
CCodoowsaiar 1T4O5 21182109 00868 00855700880 QS& $77848 00774 0assisigoo Ovoemnencosboar.r TmhoeralleoixwtypSeMcRistataeamrhodeeng
= Corwrovascar
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Sonsmioudip wit he beidy `mostlikelytobe resultofthehealthy
owforkpearcefafepctl. oLartemnecysnarnidsdusraotimon
Sicee
iu Sm on aiid 0 em 10 was pede
3 c CHD. r ere y es
S quis coR nternioonroef methsetocinst.
workers are not sricly comparable
psiloonyeasadTphoenr-eChweemriecagloDsiviipsiifoinceamn.y gerlenvoante-dChSeMmiRcaiaDiCvhiesimoinceamlpDliovyieseosn.
isPpFrOoAblaenmaptriocs.taAtgeec-aadnjcuesrtoecdcuprrroesnaclee c1a9n8c9er(3m4o9ralpeirt.y1a0t0e,s00f0)rom 1983 to
weizreed braastedroaatisoes;shopwuesvmebre,rssahned peass duced uasabe ratios. Evpmseey of
&|
meHnoaswteaivsaeorct,ihaetpCerodshtwaitteeh lcmaDniecvieirsoaficmoeongrmatppallhroliyoty-
were only cT2ah5is%ssloafotwphteroirnptcioodbperarocotfuesduiretaateottcehsnasn(ec9ae9m.rod4rn)eg.
PFOA. exposure were bes on Jos tih henoCihcemsvainct davecraDo mtiievsgr ionrseioy vzneatrr, iaoenymoppflowotoprdekedenr1ss
Z33|| F|
ov`fpiosmreotminaponlvadolaysdhmaeaoznsatsriodicdnianataiehldyeosiwCsihc5.teh%mrTiCe2cen2aLlsyLeeDsa0eiirc:2s .spefmerletevaic.tensgdGtcdhaeeauithshiesgsvhfhfeorrrseiotsmmkhanopflirdosesptadatutiehmscofafocbniorcafdceerosl0rmibeny-.
stPphFreeO`aAbdeiaoloogxnicgepfefewmcpatolsiovensespdcpossseeunnototlfdryPseFaOedyAe.: exposed 10 PFOA ansthe rms
F| `T1heu0seo1fpprro0ossuatt6eecacna0ncceer)rmmooriraalilntiyt.y thie isntcuiddye,nacnedatahdeombosrearlvietdydirfafteer,entchee craste5goruinzeaxtipoonsteadywhmebclhuesyiieymacoxk.
T-a_ e
Propo.rtionalHezard RegreAssCiaounsMeosdcet!DoofaFractorsPradictngMorCtaanitcyaarmaoantgiAsIMaleEmployeesProcaaCancerSaath.
YorweT ollme w Tas n 00m 00r 07 wose T 0meono Gi worss oooowoeoer 0r5 owior
3
OAuFgueyfmmaaaieew7sn Soymen0t1
OU) 0%
os om
001 Gow
108 0
O07 ams
00M om
001 Gow
108 om:
0082 aor
0S om
0oe ow
1088 om
Ma-araan n ot om 02 1 oom oom 02 tmz oor oms om ton 3
RAoerevveatirksE fursceodivr:tE 2c.waretcE papaarcr:eE SEiG:.wandE a areofT speparserA, oe
2&
EID088661
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pboeseed.ecSeudchtombiisacsahsseieffilccaitoensiwmoauleds pReouorrolnoficDiodsw.e[r4:5 P[rWoHx 16. USbaerFG,f Soernveise5.rRoccohedD. Heaw.s
.
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fiponlcworayeeraddtietsnhtedheeualCtlhheimfriaitcnecasr,leaDMsioevdnitsXihosnPmeamOyo S; Gii cs wUithAaomgLmaoonngii.u,mAnpieImrRalluOoNrIroaSicTcaOnyoAmaStu,ed. |15. GIpnudsypiWg,dsFolsieoriAocopmIproounvAdesso,fiiatn
fdoecvsersocreefuleesctcutmhuelabtiiovleogeicxeplfoecirvee. 3,Oof opCAr udenasTodpc eraoa dm, hRoons.boendccWomGanvrtnsy PhSoens
fWloecrtksetrhsebwieoraccxcpoutmeu.dlat1it0oomnmaonafysPoFobOueAsr.
osnSoicasyRtdienOmsaT e atsaa AardttPhheast rfmlaocc,s 4 Puno T,LoeK.PeriM.Gli P.
16. Gc19u7my.Wp, TavsD,bBmreynW.pOercpBryo.. : LenstodcretTinFoBn.
tebheerstpolssa,nbtdasuHrbioeawegenvteshrse,iiroscoeanmtepedlofowbyiemhseenptrmonaa.t oBGifuocadhmemmniocwnaliovm0nedbplmoeyrupmhnorldmocgiapcsalootmeeiiemns: roYodobBroioAchceAemCniSrnymsireCvoabtinvgeceaSrroba oenhuce.
re
ough
he
engt
IE.
SSEisGioon EpaMol Parmt BrATs, 17. GISuytIWoTennasrT pc tL une i
DDomainoviysieon
100mean J O 20d non-Chemictl
Dievmi0siMio.n
CpieSrcslroenseS0rodlftm eoimosniabumBmibeyypmerO,:f
T3 197t5, Comidr nag oCOlWid enshPer
cobortsofmen and womheenco,m: aaron adds nt Bor, 18. Tors Evid tat hr ar to
opanrfisiooounsnndoodffatbghyeedirfatfTekrseTnoahcfeEdiiasnCetarhsOeeTdrairMse.. 6. SmHKeeupaamnteolplloyegyoO.,rRDs1e9or8Ac9m.aa9Ilm:5ow7Lu0i-.5cS81yT.oofcaamamro: 19. af fTooen.aoeIoDf.hAruCaSoom srmIipdu0s e1tiSdanos0nb1u0a-m%fa)o"noserbrcum".sNo
difunceteh,rebsuitntoeomtaceollmipmCaisOnmatPeA,TcSoOnDfouBnOdiWT=nSg have diferent disbutions of these
2KMneuinaansnccaoGsitulo. c.FoonBfdomCeholo.mtCoToomtapotr,.. 153636 35-53.
20. 9GDbieeasntF. BPseOsasnReutDosisoe1d obunmsna FAD ts Misses MG Ui
i ceiumrmerenfcaoceftoeuri.tBomencsahausiep tGhe ddoiesfeioanseed oheJen. 8. CaLooomow)eau,onnMuomfpmLyedoFeubmeedSe, cHLoormaoMb.y 21. sBS tyoroyf:n iTsoeesnsaeud9oEosmoarryby he
: barvueeboefetnecbiaosfedPFtoOwAardexopraovsuarye Omamy 5 R3eCy)O,ErSoUlD,SHEisSeIHTyLpSo. 22 MadamparhoepAsosrismoforasyiv.e Cvomipt
i
the null by uncontrolled confounding
lipidemic hepatic perotisom prokifera-
Biomed Res. 1974;7:325-332.
: |
bwa yaFttiamunedfracocnbtfoirrosm.tse aossodciationeinnebe.
10.StRooroesfasormJpRL&raenaowvmeslsB c N.rClaoO rflatchneslomIpics nacolthca.r-
23.
34.
Mi Cioetxtin .ne'nReOg.re|SstiaoEnnd_armdoiazattsionanodf
risk
te
y
refssmauadllitlnesdgfuirnommhiocbsfhsaecnauscdreeysoaarrnuednrbceaocsuoelgddnohiaznveaed
rCLiro,EnRoCof IToEisIkioUfIpHOSEIpTIIAIlSEaNeEs
25.
wS0ASbSa)sJ iA
Sir SAS
So (8) 1973345 Uses Gide Sis
11 NinR.Ba B,Pret V, ErtoKa. SxGriGamNCSAS it
cTdcoeinonfrcos.uendSitinundghiesfsooamfnrdexoopnsoesausrecPaR1nO0cNoethRien.r. RhDoabwlmeomCao-nrtOunCoohpmtcyBmelconfhaapneitonosf1o9hm0es; 16. nK19au%b,bieAh,PlireetTehseNseiwaY.oik
"
onSeEs 12 A Tool n Poi.Vea m , Non 27. SMoiblaeW.Caa&nSymasu190, evi 1975
gestedincrease inprostatecancer
Roo.RnnovbeeorsfmrotiyodMo.rdPoerlnofxeinsmsoombiemprrooolriufinerrcs-. N1e98no9. BuoefthLeasodtash,M4iaroyflHHaanedm.haU.SSDNeopeavontn,-
AcoHTknheaniltoswawGlorierakdsigvTmaoserImnOotSoosurOpewHdiDosnp1TuSdn-lbhy1yeN1I,e3M4. 13. aTeCciuda,mr2p,A4,mSe5u-tnKrai,ch1Ulc9aor0doApambLe1n0oIndxTye,meNacltcsiEpcoanahcrsd., 28.`BCC1ao9ns9nc8ear.wInasRyiteutHe,i.NsPTHiiPeub.No,No.Cd9v2l-o2o78ro9d,
3 i
Corporation.
References
R8O r,Kuprot okoawd4caS5Ye4.h1Siah2roarntop-nteemercmr,ecnxpopsdueeortfesat8.o. 29.`lRtUieoonnnbaieloetipJinydAePmmioeoklwrogty0.p.NmreowscYtoworikc:Oaxlfo0rd
:
1. Ghursnboeo.mViptoruM.oSulie si1v3e3 bosiCootteyLdtoeIyIiaIalSnos,oDiNAoGeY iTnedrexponMaehMne.n
!
:
1
EIDO88662
]
060504
:
Page 1
AH6&40M4 EMaNcVCIorRkOlNeMAEvNenTuAeL,,SIWNC.
St. Albans, WV 25177
BIOASSAY REPORT
FOR E. I. DUPONT WASHINGTON WORKS P. 0. BOX 1217 PARKERSBURG, WV 26102 AM NO. 93-114
DAPHNIA PULEX
}
DECEMBER 8 - 10, 1993, 48 HOUR STATIC ACUTE DEFINITIVE
AH&M toxicity
Environmental, Inc. of a landfill leachate
conducted a collected by
48 E.
hour static I. DuPont,
aWcautsehibnigotasosnayWotrokdse.terAmignreabthseample
was collccted on December organism, Daphnia pulez.
7, F.
1993. The . DuPont,
sample was Washinglon
tested for Works is
toxicity located
using the freshwater in Parkersburg,
West Virginia 26102. The test was conducted on December - 10, 1993.
DILUTION WATER
Tfrheeshdwialtuetrionthawtatiesrfauvsoerdabtloepteorftohermaqtuhaetidcefoinrigtainviesmtosxiucsietyd tienstthweastesmt.odeTrhaetemloydhearratdeslyyathhaertdic
syathetic fresh water is prepared according AcuteTolcityofEffluentandRecelving
tWoatEePrAtporForteocsohlw"M atere andtMfaorhriMneeo aOsrugrd ainnigstsmhse,
EPA/600/4-90/027." Water quality analysis
`The water is is conducted
allowed to acrate for on the dilution water
24-48 and if
hours prior at any time
to use water
in a test, quality is
not adequate, an additional batch will be prepared or an alternate source wil be chosen.
LEACHATESAMPLE:
TcohlelesctaemdplbeycDoullPeocntetdWwaasshianggtraobn sWaomrpklse pceorlsleocntneedl,onreDfreicgeermabteedr, 7a,nd19p9i3c.kedT-huep sbaympAlHe EwaMs
Environmenul, Inc. on December 8, 1993 at approximately 1100 hours, The effluent was
translucent
was present
a
.
nd had an oran
The receiving
ge color. An odor
temperature of the
was observed anda
sample was 12.4C.
4C and were used in the tast prior to the 36 hour holding time.
small amount of sedimeat
Samples were stored at
00985
WVDEP 02
Page 2
AEPdAefipnriottiovceolto"xiMceitlyhotdesstfwoarsMpeearsfuorrmiendgtfhoreAE.cuI.teDuTPooxnits,itWyaosfhiEnfgutoenntWaonrkdsReaccceoirvdiinngg to Wsaetrieers,sta oconFcreensthrawtaitoenraranndgeMaofri1n0e0%O,rg5a0n.i0s%m,s,25E.P0A%/,60102/.45-%9,0/60.2275".% aUnsdin0g%a(0c.on5trdoill)utwioans
used to test the toxicity of the sample.
TUhpeontesrtecveeispst,elssawmeprlees3a0remllopglgasetdicind,isapsossiagbnleed
test an
vessels. AHM test
The test number
volume was 25 ml. and initial parameters
aterset rveecsoserldeids.raTnhdeomtlesyt dciosntcreinbturteadtiaonnsd aartelteahsetn2m0ixoerdgaannidsmdsecoafntegdiv(e0nthsepetceisetsvaersseelesx.posEeadchto
each effluent concentration, five (5) per replicate.
`DTehaetht/esmtordtaatlaitmyeaissutrheedefifnectthemeteasstsuraerde
biniotlhoegiaccaul,tectheesmt.icaMloratnaldipthyysoifctahle
data, test
chambers
are
monitored Chemical
for and
pehayrsliycamlordaaltiaty(ied.u,rpiHng,
tchoendfuircsttivfietwy,hoduirsss,olavnedd
only every oxygen and
2t4emhpoeurrastutrhee)reaafrteer,
mhaeradsnuersesdaarte amemaisnuirmedumininthaelcotensttroclosncaenndtriantitohnesheivgehresyt2c6onhcoeunrtsr.atiToontaalt atlhkealbiengitiynnainndg tooftatlhe
test.
`The 40%
tseasttutreatmipoenr.atuIrfehorwaenvgeeri,s
25+/-1C. the sample
Dissolved has a high
oxygen oxygen
idsenmoatnadllaonwdedthteo
exceed test
below
concentrations chambers will
oecxchiubritprdiiosrsotloviendtoroxdyugceinngleovreglasnliessmsstthoanth4e0t%estsacwhraamtbieorns,.
acration
of
all
test
A`ThHe&teMst Eonrvgiarnoinsmmesntuasle,d Iinnc.theDatepshtnwiearepu1l-e2x4ahduolutrsDwaeprheniisaolpautleedxownhi12c/h07w/e9r3e acnudlturreecdeiavted
oofnh1e2a/lt0h8./93.AHT&heM DEanpvhinroinamenncotraalt,esInpc.ropdeurcfeodrmasrerebfeelrieenvceed ttooxbiecadnitsteeassteinfgreaendanmdaiinnttahiensbe2st
contol chart for the Daphnia organisms and the techniques
neonates cultured in house applied by the techaicians.
to
assess
the
health
of
our
cultured
RESULTS:
T`Whoerkasdvwearssedeefaftehc/tmsormteaalistuyr.edAitn
4t8heh4o8urhsou1r5%defmionrittailvietytesotccfuorrrEe.d
I, ia
DuPont, Washington the 100%, 5% mortality
occurred in (controls).
the The
50%, and LCSO for
OWa%shmionrtgatlointyWoocrckusrrseadmipnlethwea2s5%>,10102%.5.%,Th6e.2A5c%utaendTo0xi%c
Unit
Was not measurable. Chemical analysis of
See Section efflucat and
V,, of the Test dilution water
Summary for Daily are in appendix A.
Percent A copy
Mortality. of the
All
laboratory bench sheet is in appendix B.
00009a
WVDEP 029
Page 3
AH&M ENVIRONMENTAL, INC.
6404 MacCorkle Avenue, SW
St. Albans, West Virginia 25177
TEST SUMMARY SHEET
FACLITY: WaEsh.inLgtoDnWuorPksont ADDRESS: Parkershurg
West Virginia 26102
TELEPHONE NO:8(1064) 3-4633
TEST DATE: _12/08:10/93
CONTACT: Jim Yoak OUTFALLNO: NPDES NO: Wy.
SAMPLE ID:LandfilLeachate
REPORT DATE: 12/20/93
IL SAMPLE INFORMATION
A. Method of Sample Shipment: AEHn &MvironIm nc.e coun riet r al,
B. Condition Upon Arrival At Labortory:
"
1. Temperawre 124C
2. pH
8S2 tdUni5 ts
3. Chlorine --O_ mgn
54.. CDoOnductivity u _510m00h imogs l
6. sAmppaelalraamnoceunTtroafnsselduicemnetn.toragecolored liquid, odorpresent,anda
C. Collection Dates: __12/07/93
D. Collection Location: Prortodischarge
O. DILUENTINFORMATION
A. Method of Dilueat Shipment: Notapplicablepreparedinhouse B. TPrreoattomcoelnt6o0f0/Di4l-u9e0n/t:02M7oderatelyhardsyntheticfreshwaterprepared toEPA
000505
WVDEP 02
Page o
AH&M ENVIRONMENTAL, INC. St6.4A0l4baMnasc,CoWrekslteViArvgeinnuiea, 2S5W177
TEST SUMMARY SHEET
C. Conition of dilution water
L 2.
Temperature 25.4C
pH
8.U07 nSudits
43.. CCohnodruicrteivity _3_00_uOmhmogs/l
5. Do
Bomgn
6. oApo pearance Translucent,colorlessliquid, with nosediment.and/or
D. Collection/Preparation Dates: 12/0193 E. -Co--llection/Preparation Location: AEHn &MvironImnee , ntal
lI. TESTSTART
A. Test Organism: Daphniapulex
B. Age: <2ehrs Isolated 12/07/93
C. Test Vessel Size: _3m0 D. TestVolume: _25m E. No.of Replicat_es4:_ F. No.ofOrganismsper Replicates: 20 G. TestDawcyTimes: BEengdiinnnginDgaDtea:te: 1122//0180//9937TTiimmee:: 11221100 H. 100% Effluent at Hours
1. Chlorine Initial __Omgl Adjusted NAogtpliczhle
23,. pSHIantlalin8 ity Init1 ial _9 _uQniptd os pt AAddjjuusstteedd NNoottAApppplliiccaabbllee
003729
WVDEP 029
Page 5
AH&M ENVIRONMENTAL, INC. 6404 MacCorkle Avenue, SW St. Albaas, West Virginia 25177 TEST SUMMARY SHEET
45.. HAlakdaoliensisty 2_02068mgmlgl 6. Conductivity 600umhos 7. DAeOrIantiitoinalPe_rioBd (iif necmessgary)lNotAApdpjluisctaebdleNotApplicable I DILUENT at 0 Hours
1. pHInitial _8.05stdunits
Adjusted NotApplicable
2. Salinity Initial _Qppt Adjusted NotApglicable
3. DAeOramtiitoinalPeri_o8d.0(imfg/nlecessary) NotAApdpjluisctaebdlNeotAppliczhle
4S..
AHlakradlniensitsy
__62mgl
9m4g/l <
6. Conductivity 310 ymhos
IV. TESTRESULTS
A. Test Accepubility
1. 2.
Control Survival _100% Average Weight per Control Organism _-
B. Satstcal Analysis
I. Method of Statistical Analysis_NotApplicable_
2. 48 Hour LCSO 2>100%
3. 95%Lowerand Upper Confidence Intervals NotApplicable
Cc. T1U, TU = 100/LCSO = 100/> 100% = AA (Below detectable)
006445
WVDEP 029
AH&M ENVIRONMENTAL, INC.
St.64A0l4baMnasc,CoWrekslteViArvgeinnuiea,
SW
28177
TEST SUMMARY SHEET
v. TABLE1DAILY PERCENT MORTALITYTESTCONCENTRATION
ee -- S-- -- S--_-- VI. COMMENTS
030 AL
WVDEP 02
GI212
(.
:
HASKELL LABORATORY
FDORUPOUSENONTLY LInITED DISTRIBUTION nloitterbaeteunrTeeh,viaslbuoratethveidpeuwbfloriresfhslecedicetnsatnidtfhieucnpaumvbealriiiltsa.hbelde.CotnotSxaticuctdiitsyHsaskhealv)e Laboratory if you have questions.
Common Name: Ammonium Perfluorooctancate (APFO)
Chemical Name: Octanoic acid, pentadecafluoro-, ammonium salt synonyms: Fc-e8-143
CAS Registry No.: 3825-26-1
Chemical structure:
CF=CF~yCF,~CFC ,~CF F;~; CF; ~C-0= NE+
.
Physical Properties (5):
.
DKeoslcerciupltaironW:eight:
L43i1ght-colored powder, slight odor
BMoeilltiinngg PPooiinntt::
s--ublines @ 130C
VBauplokr DePnrseistsyu:re: Flash Point/Flammability:
07'.x6-01.0-75 g/amnLBg @ 20C ---
ESoxlpulboisliivtey:Limits:
S-oluble in water, ethanol and
Conversion Factors:
a1cmegt/onLe= 57 ppm
1ppm = 17.6 mg/m
T2h3 ispagleisterofatutreext saenadrch62 cornetfaeirennsces. Annew %daitna thaeddledeftat matrhgiisn upidnadtiec.ates
TRhiicsharsdearC.chGwraahsamp.repaSreeedthbey last
g
puapgdeationfgthhiisstodroyc.ument for its
3
EID087793
L
009115
.
Exposure Standards:
DuPont AEL = 0.01 mg/m} (8-hour TWA), skin
+ DuPont Community Exposure Guideline (air) (CEG,) = 0.3 ug/m
+ DuPont Community Exposure Guideline (water) (CEG,) = 1 ug/L
+ ACGIH TLV = 0.1 mg/m, skin
.
DOT Classification:
None
EPA RCRA Status:
None
FDA Status:
.
None
:
TSCA Inventory:
Yes
TOXICITY
summary:
470
C-8 has mg/kg.
Amnodearqauteeousacuptaesteoraolf
Ct-o8xipcirtoyducweidthmialndLDtSoO moidnerraattes
of
irritation on the skin of were seen at doses as low
rabbits. Clinical signs of toxicity as 1500 mg/kg. Instillation of the
solid material into opacity, iritis and
tchoenjurnacbtbiivtiteiyse. proTdheuceodculmaordereaftfeectcsorngeraaldually
eryeecsederde.covePrreodmptmorweashqiunigckloyf.
the By
eye the
reduced acute
itnhhealaetfifoenctsrouatned,
these C-8
is highly toxic with a four-hour ALC a two-week subacute inhalation study
in the rat of 0.8 mg/L. performed at 11 and 83
In
mg/m), liver enzymes were
doebgseenrevreadtiaotn,botehnlcarognecdentlriavteirosnsa.nd
Aincsrcecaosneds stinudyliwvaesr
sreuennatin 1,the7.6ratasnd ex83p.o9semdga/tm.1 mgN/om'c.ompoEuxnpdo-sruerlea-treedlateefdfecmtosrtawelriety
was seen at macroscopic
the and
mhiigchroslcevoeplicofliveexrpospuarteh.ologAyddiwtaisonoablsleyr,ved
in
the
aanpipmeaalrsedextpoosbeed raetver7s.i6blaen.d
83S.u9bacmgu/tme}.studTiheesse bylivtehre
effects oral and
skin
absorption the liver.
roInutetswoofchraodnmiicnisftereadtiinogn sctuodnifeisrm intheratesf,fecCt-s8
of C-8 on produced
an increase and testis.
iCn-8thewasinncoitdentceeraotfogetnuimcorsin intestthse
liver, pancreas, by inhalation and
gavage and was not mutagenic in the Ames test.
-2-
=Z
EID087794
E
009424
A. Acute
1. oral
ALD (rat) = 480 mg/kg (3.18).
ALD (rat) = 670 mg/kg (3.1,3.5).
.
LDSO (rats) = 390 mg/kg (11.10).
o LDSO (male rats) = 470 mg/kg (3.15).
o LDSO (female rats) = 482 mg/kg (3.15).
LDSO (rats) = 540 mg/kg (5,12).
DSO (mice) = 457 mg/kg (3.16).
LDSO (male guinea pigs) = 178 mg/kg (3.14).
LDSO (female guinea pigs) = 217 mg/kg (3.14).
o oC-r8alwadsosessligtohtltyhe tofxoilclowwhienng agrdomuipnsistoefrerdatsi:n swienagnl--e lfienmgasles(,21LDdSaOys=ol5d8)0:mg/mkagl;es,youLnDgSOa=dul5t73s m(ga/pkpgroxa-nd nigm/aktgelyandeigfhetmalteos,tenLDSwOeek=s 4o5l3d)m:g/kgm;aleosl,derLDSrOats=: 470 mnagl/eksg,; LnDeSwObo=rn33(6< mtgwo/kgdayasndolfde)m:alesm,aleLsD,SOLD=SO343= 243 nrge/gkargdsandtofethmealesse,x oLfDSOthe= 2r5a6tsmgs/hkogw.ed nTooxisicgintiyfiicnant odlidfefrerernactes. hadHowleovweerr, LDnSeOwbvoarlnue(s<twtohadnaywseanolldi)ngsandot young adult rats (3.32).
o Cy-o8ungisadmuoldteramtaleelyantdoxifcemwahleenraatdsminthiastt'erweedreournatlrleyatteod oIrts sLuDrSg0iciasllbye-tmwoedeinfie4d00 (aonvdar4e9c1tommgi/zkegd oorf bcoadstyrated). wreaitgihots. werNeo csheaenngeisn finemallieverrawtesigghitventosibnogdlyewediogshets osfingulpetoora2l00domsge/kgof (eoivtahreercto10m0izeodr o2r00nomrgm/aklg).proAduced aCnastirnactrieoansereindulcievdertheweimgahgtnitoufdemaloef trahtes.liver weight hienacvrieearse lbiuvtersrattshancadsitdrattehed acnodntrgoilvse.n 2C00linmigc/aklg had asnidgnspersienenealinarC-e8a atnrdeatsepdorardaitcs wienicglhutdedlossstai(n3e.d21)f.ace
EID087795
=
-3-
g
3
009745
=
ATwPoFOmzileedbweiatghliens 4g8ivehnouras.singPlleasmdaoseenzofyme4s50wemrge/kg mgiavreknedl20y0emlge/vkagtedhad24-e4l8evhaotuerdsGaPfTtearndiGnOgTestiinon2.4 hoDuorgss pwlhaiscmhaneonrzmyamleizeldevealfsterisoniendwieceakt.iveThofisceilnlcurleaarse in damage (3.3).
pThreetroeraaltedLDSwOithofphC-e8nobwaasrbidteatlermsiondeidumionr rpatrsoadifen dhyidfrfoecrhelnocreisdei.n thTeherLeDSOwervealuneo osfignC-i8fic(a4n78t mg/kg) sfoodliluomwinogr pprreo-atdriefaetnmehnytdrwoichtlhoreiidteher(3p.1h9e)n.obarbital
AsPiFnOglewasdosaedsminriasntgeirnegdfrtoomra1t.s5-b2y250stmogm/akcgh. tuCbleiniincal sairgonusnd ofthetonxoiscei,typewreirneeailnadcitisvciotlyo,rataiorned anddiscwheairgghet leonslsa.rgeAdnilmiavlesrs re(c3e.1i)v.ing doses > 200 mg/kg showed
e mRagt/skgrheacdeiveinnlgargiendtralgivaesrtsric(3.d5o)s.es aGsastlroowinatses6t0i-n9a0l i(r3r.i5,t3a.t6i)o.n was also obsecved in rats ingesting APFO
ApPrFoOd,ucegdivenno cinlinsiicnagllesi12gnsmgo/fkgtdooxsiecsityto (t3h.2r)e.e rats,
eo EPxrceh-adnogseingResorinpaotst-1d00o0sinmgg/wkgithchDaonwgeexsth1e-X2t-oCxlicTon eDofvfeexcst,s oefithCe-r8 bienforraets.or AalflterratCs-8dohsaeddrweidtuhcedthe maolrotneali(t3i.e2s3).compared to the rats dosed with C-8
*
Gsrionugplse odfoseyouofngeatdhualntolraatts60w0e0remga/dkaginiorsteare1d5%a
asosliuntgiloen dionsetheoifrCd-8rinatkindgosewatleervelfsorof1420d0a,ys48a0n,d/oorr
o6f70etmgh/akngo.l foInllothweedra24tshoaudrmsinilsatteerredbyaC-s8i,nglaelldotshee
draaytss aafdtmeirnisdtoseirnegd. 670Inmgt/hekgroaftsC-a8dmidnieidstewirtehdinethanol
afdormin14istdearyesdbe4f80oreandC-8670dosmign/gk,g aofllC-t8hedireadtswithin 6
dsahyoswedaftaershdaorspinign.creaLsieverinweaillghtt/hbeodryatsweitghhatt ratios
rraetcseivtehdat C-r8ecwehievned coonmlpyareedthatnoolc.ontrTohlesre awnedretonothe
scoingtnriofliscanatndditfhfeerreantcsesthbaettwreeecneivtehed ounntlryeaettehadnol or
bC-e8tweaennd tthhee ertahtasnotlhatprer-etcreievaetdedonrlaytsC-a8dmi(n3i.s34t)e.red
=
.
EID087796
2
3
0695.25
:
i
tSeoexicRietlyateadndRkeifneerteinccse o13f pfeorrfliunofrooromcattainooniconactihde.
2. skin
LDSO (rabbits) = 4278 mg/kg (3.10,6).
mRga/bkbgi.ts wSekrien diorsreidtataiton750o0c,cur5r00e0d, at30a00llanldeve1l5s0.0 bclrienaitchailngsiagtnsallinlcelvuedlesd, wweeitgnhetsslosusndearnndealtahbortehed mboodsyt, lecvyealnsosi(s3,.10d)i.acrhea, and lethargy appearing at
o LDSO (male rats) = 6959 mg/kg (3.10,6).
Mianlietiarlatsweidgohsted loasts.3000R,ats500d0oseadndat75050000mg/okrg 75s0h0owed mmga/jkogritweyrehadlewtehtargaincd/oocn sthteaindeady poferitnreeaaltmeanrteasa.nd the nCgh/ikogmod(a3c.r10y,o6c)r.hea was seen in rats dosed a-t 7500
sFekmianleirrriattsatidoonsedandatin5i00t0ialorwe7i5g0h0tmgl/osksg. shAotwed750m0ild anrge/akgwearestaailnsoednoftaecde a(n3d.12a,6w)e.t and stained perineal
.
+ Aimrmrointiautmionpewrhfelnuoraoppolciteadnoattoethdeidsnkoitn opfrodruacbebits (5).
o AtPrFunOk (a50n0d mlga)terwaals aarpepalsiedofassixanmaalqeueoruasbbiptass.te Atfotetrhe m2o4dehroaurtse sskeimni-oicccrliutdateidonc.ontaOcbts,ervAaPtFiOoncaautsed48mihloudrsto indicated slight to moderate irritation (3.9,6).
ePvearlmueaatteido.n ofThrfeieveoftyptehse ogflovgelsove(sNeboyprCe-n8e,was mneeaossuyrnatbhleeticbrleaatketxhroaungdhnattiumrealandlatpeexr)meahtaidona rate ca-f8tersoleuitgihtonho(u3r.s22)o.f continuous expos1ure to a 30%
See Related Reference 14 for additional information.
3. Eyes
AwPiFtOh acaussmeadllgeanreearaloifzesdevemroederoaptaecitcyo,rneianlteorpmaictitteynt m3o8d.3eramtge ofiristoilsid antdestmodmeartaetreialcownajsuncptliavcietdisintwohenthe orciuglhtarceofnfjeucntcstivgarladusaacllyof raecerdaebdb,it'hsoweevyeer., Tthhee small
-5-
gz
EID087797
g
068:
vaarsea miofldcwoirtnhealvasocpualcairtiyzapteirosni:stedAnanedye ztGos2e1-d28widtahys RtaohredeeartaoetfsetslmtoiagthestrliiagtlhotmaoncddoencpjarutonemcpttcilovryintweiasalshweiodtphachanidotyaLeanlsdtmailcl wGfioErtfehcimtni.ld14Tchodeanyjsueynec(t3i.w0va)as.lnorremdanlessw,ithwihnichsewvaesn dmoatymssiexcept
A2PFOrab(b1i0t0smg()mewaanssmcoordeera=te1l4.y0;irrhiitgahteisntgptoossitbhleeeyes
Fs"ecEtofereectesv=ida1e1pn0p.te0a)ri.endunwIwhraeisndihaeeldyeseaynewdse,rceonbwjuatusnhcoetndilvyaalccotneejrfufneccttisval
exposure (5).
RDaetrsiodexpeoxsheidbitteodAPcFoOrnedaulrinogpacaitfyoura-nhdouwriceirnahtailoantion wdhayisch (w3e.r6e). still microscopically : evident after 42
4. Inhalation
-
+ Four-hour ALC (rats) = 0.8 mg/L (3.6,7).
GgCro/onLuc.pesntArotaftiaroantcssonwocfeerneAtPrFaetOxipoornsaendogfinfgo3r.2frfoomumgr/L0.h3oo8urrsmhgi/gtLhoert,o 5a.i7l
eeTxnoplsoasrudgareteeadnrtweitturhreinanicnhge48d thoaoumnroasrxmiaamlfutsew:istehevixenpnost4u2ored1.a4ysd.aLyisveAraPfEtOer
"ashighly toxic yhen inhaled but no changes in cell
morphology were observed (3.6,7).
*
d-hour LCSO (rats) = 980 mg/m' (11.12).
NnSooimgindsneaaltdhusrcionnrgceesnuetlxtrpeaodtsiuocfnerovmoefraeABoFnrOeedh(on1ua8r.s6alemxgpd/oiLss)uc.rhearCtgloeinaical
yaYenealdlomlwaactresirtmiaaaitlniionangf.ouofndStihmteihelaacnevoe-ssgi,egnnisetxacalepspsefiuarvr,eeddsrapyloisvtra-atlieosn,,
exposure in a ld-day observation period, Bilateral
mSoutttolpisniges of(5t)he lungs was observed in eight of ten
5. Intraperitoneal Injection
e LDSO (mice) = 192 mg/kg (11.3).
. o Stehee RteolxaitceidtyRoefferpeenrcfelsuor15oocatndano1i6cfoarcidi.nformation on
e-
EIDO8T798
5gg
009525
B. Extended Studies
1. oral
-
BwiiotchheAmPiFcOa-lindaundcedmorhpehpoaltoogmiecgaallycwhearnegesstaudsiseodciaitnedrats.
oGfrouApPsFOofformal1e, 3r,atsorwe7redayasd.miniSsomteererdats50 rmegc/ekigv/edday
dCoiste-.labeThleedrsatosdiwuemreacektialtleed34aftheorurstheaftlearsttdheaselasotr 3
hSooudrisumafatceertatteh,e aanddminthiestrlaitvierosn owfererardeimoolvaebdelefdor
eixnacmrienaasteidoni.n alLlivAePrFOw-etirghetastedwerreatss.ignTihfeicarnetllaytive
amount of DNA/g total amount of
ohfepaltiivcerDdNeAcrweaassendo;t
hsoiwgenviefri,cantthely
aNf-fdeecmteetdh.ylasCeytoacchtriovmietyPw-e4r5e0 asnidgnbifeinczapnhteltyamiinncereased
bayndAPcFaOrniatdimninei-sptarlamtiitoony.l-trCaanrsnfietriansee-acaecttyilvtirtainessfewrearsee
daelnseothsyilgansiefiacacnttilvyityinwcarseasdeedc.reasEetdhoxayftreersoroumefino-rO-
tdhirpeheosdpohsoegsl.ucuGrlountyalt-htiroannes-fSe-rtarseanswfeererasneotand uridine
SIingcnoirfpiorcaatnitolny aofffercatdeidolbaybeAlePdFOsaoddmiiunmisatcreattaitoen.into
hanedpatsitcerollispidcsonetxacienpitngfo2r7 dciaarcbyolnglaytcoemrsolwsa,s squalene,
Psrioglniiffeircaatnitolny oifncrtheeaseedndobpylAaPsFmOicadrmeitniicsulturma,tion.
mtirteoactheodndrraitas,, anThdepehreopxaitsoommeegsalwyasinodubcseedrvebdy AiPnFO is
dPueeroxtiosohmyeperptrroolpihfyerartaitohnerdotehsannohtypenrepcleasssiaar.ily result
iinncrheyapsoelipiindelmiipao,genasesiesvidiennctehde btyreattheedobrsaetsrve(d9).
Atdomisniixstrraatstiocnausoefdtemnodesruactceesseinvleargdeomseenstofof6.t7hemgl/ikvger aSnidmulstlaignhetouselnylartgheemreentwasofakisdlniegyhst daendpretsessiteosn. of pSalnicgrhetaltyicenwheanicgehdt panndeumtohenitliusngs(3o.2f).rats showed
o dIinspaertswion-gweeakgenfteewdaisngasdtmuidnyi,ste25r%edTeifnlotnhe wdiiteht AofPFOa gtrhoeuptroefatesdixanriatmsa.ls Ahfatderslaighttwloy-weheekavireercovleirvyerspertihoadn the controls or animals receiving Teflon without the APFO (3.2).
EID087799
"
-1-
SE
[DEER]
0
Ca-c8encpmraozduciendTaants infecdrez3s00edppimnciofdenCc-2e ofofrLeIydyeizgrsc.ellA
hsionrcmeonaCl-8 (wnaosn-ngeegnoattoixviec)inmeschhoactn-itsemrmwsasteesxtasminfeodr
genotoxicity.
Ggraovuapgse days.
oatf daodsuelst mofale1, Also included,
ra10t,s w2e5,reoradm50inmigs/tkegr/eddayC-8forby14 in'addition to an ad libitum
c5i0nontmbrogod/lykgw/gedriaoguyph,tC-w8aansdgroarueppl.aaitriAv-efeddaocsecc-eodsnestrpooerlnydegsnertxoupdoregctaroneatshee:
w(eAiSOg)htsweiofghttsheva5s0 msgee/nk,g/wdiatyhgrtoheupresliagtniivfeicAanStly less
etshtarnadtihoolseloefveltshewepraeir-efleedvatceodntrionlst.he S10e,rum25, and 50
mngg//kkag//ddaayy ggrroouupps.wereEst2r.a7d-ifoolldlgerveelasterinthtahne t50hose of
etshetrapdaiiorl-feldeveclosntrooclcsu.rredTheatinthcereassaemeindosseerulmevels as
tshiegniifniccraenatsedoiwnnwhaerpdatitcrenbdetwai-tohxiddoasteionwasactsieveintyi.n A
2sderulinbitteusmtocsotnetrroonles.leveHloswevwehre,n wchoemnpartehed w5i0thmg/thkeg/day
gsirgonuipfiwcaasntcomdpiafrfeedrenwcietsh wtehreeirsepeani.r-feCdhalcloenntgreols, ne
eLxopceactiimoenntosf,`a whliecshioncaniniadnenetnifdyocrtihneepraxeisse,nceweraend
udnodwenrwtaarkdentretnodcilnarisfeyrumthetessitgonsitfeircoannecefoolflowtihnigs the
aofdmirnaitsstrwaastioandmiofniCs-t8e.redIn50 thmigs/kge/xdpearyimoefntC,-8 a fogrrou14p
deaiytsh.er Oanehumhaonurcbheofrioorneictergmoinnaadtoitorno,pinrat(shCGr)e,ceived
gcohnalaldeontgreo.pin-FroellloewaisnignghhCoGrmcohnaelle(nGgneR,H),seorrumnaloxone
stiegsntiofsitcearnotnleyldeevcelrseasiendthbey 5500%mgf/rkogm/dtahyosegrooufptwheere
2Rodtsliibgintiufsiccaonntt,rolwse.re Sseiemnilairn dseecrruemasteess,tosatletrhoonuegh
nfgo/lklgo/wdianyg CG-n8REgraonudp.naloxone administration to the 50
TtheessteostsetruodnieesfsoulglgoewsitngtCh-a8t atdhemindiesctreraasteioninwasserduume to
Aandlreossitoneneadtiotnhee lleevveellsofinthteheteCs-t8ist.reated rats were
dseucgrgeeassteidng60t%hefdreocmretahsoese ininsethreumadte`sltiobsitteurmonceontrols,
fthoellocwoinnvgershiCoGn cohfall1e7n-gaelphmaa-yhybderodxuyeprtoogeastdeercorneeaseto in
aenldervoastteedneedsitornaed.iolThleeveclosnclinusitohen wCa-8s tthraetatetdhe rats
may be responsible for the decreased relative
8
EE
EID087800
<
000226
Jaecvceeisssorsyiensexincrtaniasn, weciignhdty aasndwesielrumsstethsetositnecrroenaesed cihnrcoindiecn,ce2o-fyeaLreydfiegedicnegllstauddeynomians roabtsseravdemdiniisnteared c-8 (2).
.
Amg/gkrgou/pdayofofmalCe-8 raftosr w1a4sdaaydsm.inisItneraeddditbyiongavtaogean25ad
o1ibtihteun25comngtr/oklg gCr-o8upg,rouap.secAonddeccroentarsoel iwnasbodpyaira-nfded
laicvceersswoeriyghotrsganwasunisteenweiignhttsheaCn-d8angroiunpcrwehaesne in
gcroomupparewdas wictohmpatrheedafdo libtihe tpumairc-ofnterdolc.ontWrholen grthoeupC-8
osnelryumthteestloisvetrerowneeighctonwcaesntriantciroenaserde.maiAnletdhouungchhantgheed,
htihgehesreruinn tehsetraCd-8iolgrocuopncethnatnratiinonthweaspasiirg-nfiefdicantly
control group (1).
o Aobnseirnvcerdeasiendmilcieverfedwei30ghtp/pbmodoyf Cw-e8ighitn trhaetiixo wdaiset for o1f ndaoynsa.decWahfelnuorC-o8decwaasnoiccomabciinde,d waitshimialnarequeaflfecatmowuanst produced (3.31).
@ G3r0o0uposr 3of000tenppmmicoef wCe-8refofred14a ddaiyest. coAnLtLaintihengmi3c0,e 3f0e0d 3pp0m0.0 ppBmodyofweCi-8ghtdieldo.ss wDaesathisndiaclsaotedoccautrr3e00d aatnd s30h0a0rpppimn.creaLsieverovewreigchotn/trbooldsy wineigthhet mriacteiosfedshotwheed a 30 ppm C-8 diet (3.26,8).
G1r00o,ups300o,f 132000m,ice300w0ereorfe1d0,0a00dieptpmcoofntCa-i8ninfgor101,4 30, dpapyms.grouDpesa.thsBoodcycurwreeidghtinlotshse w10a0s0,ind30i0c0ateadndat10,t0he00 benoddyofweiegachht wreaetkiosatsh30o0wedppma asnhdarpmorien.creaLsieveratwe1i0ghptp/m ainndclwuedreed wdeoasken-edsesp,endternetm.ors,Clipniilcoaelrecstiigonns, ofpaltlooxri,city stained perineal area and unkempt appearance (3.17).
o Cw-e8ekswastoadrmatisnisatnedremdicethraete thtriemeesdaosweeelkeveflosr, th0.r1e,e o1.c0curorred10imng/tkwgo. feWmeaaleknemsisce fdoolsleodwedatby10demagt/khg. bSoptohradsiecxesweiogfhtmicleo.ss Awassisgeneinficinantthelivfeermawleeigrhatts and aidnmcirneaisseterweads n1otaendd 1i0n bmgo/tkhg.maleSiagnndififceamnaltelymice aindcmrienaissetdereldive1r0 wmegi/gkhgts(3w.e3r3e). also noted in male rats
=
:
EIDoggg,
g
009525
t
e GG.r0o%u,ps8.o4f, mi$.c3e. we1r.8e, fe2,d a10dioert 30conotpmainoifng80.0f1o,r 20 dsalyisg.htlyLivheerasviewrereatsi3 gpnpimficaandntlayppeheaarveidernoramtal30atppa, g10roupppms. fedNo1chpapnmgeosr ilnesslivoefrC-w8eig(h3t.2w9e.8r)e. seen in the
ARtats10w,e0r0e0 afnedd 300-,3000,0000ppmppmallAPFaOnimdaalislydifoerd w2i8thdaiyns.the bfiordsytweweiegkh.t anIdn agneneirnaclr,easaendimallisvershwoewiegdhtdec(raetas>e3d0 pFoeml,atemdalehsistaonpdat>h3o00logpipmc, chfaemnagleess)a.ppeaTrreedatmiennta-ll test dgorsouepds.at >In1a000sipmpimlardietdeswtituhsiinngtmheicefiarlslt atnwoimawleseks. Amtuscduolsaers woefak>ne3s0s00weprpem eavirdoeungth hianirmicceo.at Sanldight aCyvaenroasgies,livdeercrweeaisgehdtbwoedryeweailsgohtnogtaeidn a(n5)d. increased
G1r00o,ups300oforten100r0atsppwmeroef Cf-e8d dfioerts90cdoanytsa.iniNnog c10h,ang30e,s cinonsgiedneerreadl btoehabveiodri,recatplpyearraenlcaetedor tosurCv-i8vawle.re Aseen csloingshutmptdeicorneawsaes sineenbodfyorwmeailgeht rgaatsin inandthefoo3d00 and u10r0i0nalpypsmisgrovuaplsu.es Hfeormattohleogfiecm,alebiorcahtesmischaolwedandno vcahlaunegses obctoanisniedderefdor tothebe marleelsatesdhotwoedC-a8.sliAghtfew dleovweiratieornythfrroocmyttehe cocuonntt,rolandvaleuleesvat(ei.de.blosoldiguhrtelay Cniotmrpooguennd-raenldataeldkalgirnoessphoobsspehravtaatsieonsvalsuuecsh).as tehnelarsguermfeancte oafndtvhearyliinvgerdweegrreeesobsoefrvdeidscoalmoorngatimoanleon orbastserviantitohnes10a0m0ongppmfegmraoluep.ratsThefrreomwetrhee n1o000sucphpm gfreoveulps.or sintamtailsetsicoarllyfemsailgensififcraonmtlovwaerriatdiioentsaryin csoemxp-ogurnodup rmeelaantedo,rgaonccuwerirgehdtsi,n wlhiivcehr woefreratcsonsiindetrheed u3n0a0c-coamndpan1i0e00d bpypmagnryoumposr.pholAolglicothaelrtervaatriioantsi.ons were Mciocnrfoisnceodpitcoaltlhye, lcivoemrp.oundT-hreellaetseidonslescioonnssiswteerdeof cfyotcaolplatsomimculteinfloacragle,menvteryofslhiegphattoctyotessliglhotc,ated in cIeonbutlreisl,obualcacro-mmpiadnzioendalin resogmieonsinsoftantchees afbfyecitnecdrealsievedr almiopuonftuscGfin yeinllocwyitsohp-lbarsomwnof phigempeanttoscytreesseamnbdling oicnccaisdienocneallayndinrelsaitniuvseoidsaelverliitnyingofcetlhles.abovTehe lesions
-10-
EIDOST802
g5
00053%
g
.
wmeernesprteedeomiienanttlohy asevmo.n Tphaelesctnaenrd mcohraengepsroncoeucnocredded
niinnatutmhoresatlllyiivneosrctcanuacrnerdsinogtahmedorinsgetaitssheessuecsaonndwterrotelheylanedswieortenesstproefrsaetnst
(5,111).
.
Gorrou1p0s0 opfpmraotfsC-w8ereforfed13diweeetkss.contBaoidnyinwgeig1,ht10a,nd30,
Cweurmeulastiigvneifbiocdayntwleyiglhotwergaitnhanforthotshee o1f00thpepmcornattsrol
GSriogunpi.ficHaenptaltyicinpcarlemaisteodylinCorAatsoxiaddamsienisatcetrievdity30waasnd
1t0r0anpspimenotfly C-h8i,ghearnd lervaetlss.admiEnnizsymteereldeve1l0 sppafatehrad 8
waedemkisnisoftrarteicoonvewreyrefonloltowisniggnitfheica13ntlwyeekdsiffoferednitetafrryom
tihnocsreeasofedthaebsoclountterolasn.d rAedlmaitniivestrlaitvieornweofighCt-s8 canadused
haedpmaitnoicsetlelrueldar10,hyp30e,rtroroph1y00 inppmtheofliC-v8ersaftoefr ra4,ts7,
ahnedpat13ocewleleukslarofhytpreerattmreonpth.y diThdenoptrogarpepesasriaptoofbe
aoonfbfseeicrntvteerddacbeayrlelutlhsaeurggleemsnetgtitahvbeolofiofsmtareaacntdommepmnoatuy.ndb-erTehaelsastcoehcadinagteeefsdfect
wTietchovepreyr,oxitshoemsee pchraonlgiefserawteiroen.notAtobstehreveedn,d of
icenvdeircsaitbilneg. thaTthertehewaisncnroeasceonsiinstleinvterpawteitgehrtnsfwoarsthe
h2o8rmoandemindiestterramtiinoant.ionsNonwehicohf ctoheuldhobremonaettrliebvueltsed to
wtehreere saipgpneiafriecdanttloybedifsfomeecenitndifcraotmiocnontofroleslevaalttehdough
edestterramdiinoaltifoonr. theThe100NOApEpLm gwarsoup1 aptpmth(e11w.e1e3)k. 5
Gorrou1p0s0 mogf/kfgourofmoCn-8keypservedraey afdormin90istdaeyrse.d 3,The10, 30 mmtoghen/kkegsy/tsduadyyt).reaaAltlteddtwiheietdh3d0utrhmeign/ghkiggw/hedeearkysddootssweoa,geth(rl10eo0vueglh, fitvhereeof malolnkesyhsowdeidedsidgnusrinogf wteoexkiscitsyeveinn tthheroguaghstr1o2.inte'sThteiynal btlraacckt s(taonoolrse)x,ia,paleemesfiasc,e asnodmetgiummse,s bsrwoowlnleninfcaocelora,nd epyreoss,trastliiognh.t toThesevmeornekeydsecrofeastehed a30ctiavndity100and mfgr/okng/tdhaeyfdiorssatgeweelkeveolfsthsehowsetdudyb.odyBewceaiugshet olfosstehse cdcaoornsldayugcetdeeldae.tvehls,Tohfethemtohenckleimynosinckaealyts lthaaetbort3h0aetomrg1y/00kgt/medgsat/sykg/wddeoarseyagenot Tevel showed, in the first month of the study,
-11-
EID087803
g:
000%55
wBseetlielihitials idrLecncrierczeacareseepd.fnicapilrikonaltihtnrieomembpihtnoRs.PpthimaTe.tTa.sa0endtaacilntuievasci,ttiyvaasitned
2mtohelnokwesyearlufbmruoam(isntthavitsailsudteoi.scaaglelAyt lestvhieeglniefniidncaotnfhti)st.hepersOtinulodydy,osnheotwheed
oTnelveyl resmhaowiendingappmaorneknety afnreommiat,helo30w mblgo/okdg/dgaluycodsoes,age
Vaallkuaelsi.ne Tphheorsephawtaassem,o mtootratlaliptryoteaitnthaend10albmugm/ikng/day
mGdaooysnsakgeeyin lewexveheeilkb.it1e2 dOnaepndalmeoonckcfeaaycseihoanadnadllbylgaucmaksn.orsetoxAoitla tohainnsd sedovnoeesraagle
level there was a very slight increase in the
ASf.iiPrg.snTti.fTim.coanntvtha)l.uoefs Tthhieneresthteuwedryfeem(annlooet csmhotannakgteeiyssstiicdnaulrtliheyngotthheer
indices and no changes in the body weight. In
pTseihvnoegsllpseh,atmaotsnhekeeryeisnwetfrhreeomstertrehuenmd.s3 tanoIdvnar1t0dhedmegcc/orknegtra/osdleadyandadolskaatglheiene3
Rtcgoh/xaikncggie/tsdya.yindoStshoaefgtebosdtloyeovlew,leigdthhiteasrrerhaewnaadsonronoesimmgoenrsstiasloifwteyr,e no
moebnsteirovneeddocsciagsnsionoaflltyo.xicTihtey mionrttahelit3y0 aanndd t1h0e0 above
Tmhge/rkeg/dwaasy in single
madoosntakrgeeeynsd laettvoewlatsrhedwet1r0heemgcs/aommkepgo/udsniadgy-nrsdeolsoaaftgeetdo.xliecveilt.y
bTSheietgnwse3enomfg/tkhtego/xidacadiymtiynd,oissatgeTerheedrleedveoilssesasneaemnesdvidttoehentbedergefrrleeaeetiooofnfshtihpe
wtteoirxseiscuiectsoyn.soitdhNeeorredtgrhoacsnosmptohoreunmdaid-crrreenolasalctsoe,pdicwbeornleeesmisaoernersnowwi,hnicshpleen
and lyaph nodes for male and female monkeys at the
at3n0hedan1a0dd0re1nm00agl/smkgg//fkdrgao/yndamdaoylseadgoesaandgleevfelelemsvaellehsa.mveonkMceioycmsrpoosauctnopdtihceal3l0y,
mCaerlcatoewdfmraormkemdaledifafnudsefemlailpeidmdoenpkelyestioant; thtehe 30bonaend
TS10yl0aipghhmtg/nkotgode/sdmaoydferrdoaomtseamgaelheyplaoencvdeellslfuelhmaaardlietcymo;omnpkoteuheynsd-srpaetlleaettnheedan3d0
maondder1a00temagt/rkogp/hdyayofdoslaygmepholiedvelfsollhiacdlecso.mpound related
mSetaantiwsetiigchatlslyofsiganiffeiwcaonrtganvsarioactciuornrsed inbetsweexengrotuhpe
waCeocrncetormooplfanuiaenndkdnobewxynpemrboiirmopelhnootglaiolcgailcgarlosuipgasnl.itfeircTaahtneicsoeensvaan(rd5i,aw1te1ir.oe2)n.snot
ia
EIDO87804
gz
005%
B
dGireotuspscoofnta1i20ninrgalecizaancdr 1210G ofxema3l0e0 LrPaRts Gfwar-e fefdof UP
utnotrtewoateydearfse,ed.whilTeheamacjoonrtroiln-lgirfoeupfirnedcienigvsed only
daossseo-cdieapteenddewnitthdeC-c8reaasdeminiinstmreaatniobnodycownesiigshtted gaoifn aand
maalterse;atamenstl-irghetlatterdeatimnecnrtea-sreelaitnedfooidncrceoansseumpitniotnhe in
Tihnecriedenwcaes noof aitnacxrieaasewasinombosretraveldityinobtsheecvfeedmaliens.
peoiptuhleartitorne.atment group when compared to the control
Cr-a8tsrecloantseidstehdemaotfoldoegcirceascehdangreesd bsleoeond icneltlhecoturnetast,ed thienmeosglotbhirno,ughaonudthetmheatotcwroi-tyeavraluteesstspeeernioadt. vaWchiiolues vtheerydeecarrelayseisn tihneersytutdhyr,ocyttheiscocuonntdsitiwoenrediodbsneortved ptrwoog-ryeesasr sitnutdoy.a generalized anemia by the end of the
wHeirsetopfaotuhnodloignictahlelyl,iveCr-.8 aTshseosceiatcehdangteosxicwercehanges sCihzaeraocftertihezedlivbeyr icneclrlesasweidthlivvaercuwoeliagthitosn, ofinctrheeased dceygteopnlearsamt,ionanwditshomeocceavsiidoennacle sofignhsepaoftocneelcrlousliasr. As wcihtahngetshewerreed nblootoedd ecealcllyfiinnditnhges,stutdhyeseandlivsehrowed vreermyainldietrtleofevtihdeentcweo-yoefarprosgturdeys.sion over the
Trheelatiinvceildyencleowofandtumtohrestyfpoeusndofinnetohipslassatsudyfouwansd were
not different from in geriatric rats.
tHheepattuomocrellpurloafriletsumocrosmmwoenrley
vfeoruynd
hsolwiegvhetrl,y niontcretaosetdhe ienxttehnethitghha-tdowsoeuldmalbee erxatpse;cted
hcoenpsaitdoecreilnlgulatrhe smtoirmpuhloaltoigoincaflirsetvidseenecne atof thcehronic
one-yeac necropsy (11.11).
wAeLrLeofcartcheinolmiavserantdumotrhse ifnocuinddenicnethien atbhoeveconsttruodly, 30 pfpemm,aleasn:d 030/050,ppm0/5g0r,oup1s/50()madleisd: no3t/50a,ppe1a/r50,to5/b5e07dose trheelatleidv.er T(hmealeisn:cid1e/5n0c,e 0of/50n,odu2l/a50r;hyfpeemralpelsa:sia0/5i0n, s0/t5a0t,ist3i/5c0a)llywassiaglnsioficsainitglhytly(3i.3n5c)r.eased, though mot
-13-
EID087805
zg 2
000525
APLrLacuocfedtheinotthheirs tre1muayrkawbelree stsusmcocrliiintecdidewnicteh values
Shdocrine or endocrine-sensitive organs (3.35):
T(h2e03)i,nci1d9e/n50ce (o3f8%)m,amm2a1r/y50gl(a4n2d3))fibsruogagdeesntoemdasa (10/50
Hcaosmkpeoluln'ds-cehliasttoerdiceaflfeccto.ntroHloweivnecri,denwcheen focromptahirsed strain of rat (373), there does not appear to be
to any
compound-celated effect.
E
Ts(hu0eg/5g0eisntc(ii0vd3e)e,ncoef3/5oa0f cto(e6m%sp)to,iucnud1l/-a5rr0elaL(te1ey4d%d)i)gefwfcaeeclslt.alasdoeWnhoemnas csotmrpaairnedoftoraHtas(k6e.l1%l,`s rcaongnetro1l-12i3n)c,idetnhcee infocridetnhcies in tihnecre3a0s0e.ppm group shows a statistically significant
.
+ ci-n8vevsatsigaitnicnlgudeedxtrianheapamteicc.hantiusmtoircibnidduacstsiaoyn by
cInomptohuinsdsstwudhyi,ch30i0ndupcpem poferCo-x8isowmaes pfredolitfoerraattisonf.or
t2(w/so8i0nygleiean,rsa.dmulltIiinbpcilrteeu)amsehcdeopnatitrniocclisdeanadcneednsom3ao/sf79c(o1imn0b/i7p6naeidvre--rfseuds
c2/o7n8troilns)c,onLtreoyldiggrocueplsl),adaenndomacsomb8i/7n6edveprasnucsrea0t/i79c and
accoinntarrol ceglrloupasd)enowmeraes n(o7t/e7d6.verTshuestu0m/o8r0 ainndcid1/e7n9cesin
wfaeodrrjeusHtoamusetknsetildlesLtatahbteoirsathtiiocsrstyo,railcsaaonld sicunopnpatodrrdotiletdiiontnhc,eidecangocene-clursainogne
tlihvaetr,thepantcurmeoars,inacniddentceesstiswer(e3.e3l6,e1v1a.t1e4d).for the
2. skin o Tfhorreesixgrohuopusrs/odfay1,5 mfailvee draaytss/wweereek efxorpostewod dweeerkmsalltyo 220000mg/mkgg/,kg20r0atsmg/lkogstorwei2g0h0t0 mdugr/iknggAPtFhOe.. ex`pAotsu2r0e0 of pSearliiovdatiaonnd wsahsowendotesdligahtt20r0e0ddmegn/ikngg. ofDtohsee-rsekilna.ted ifunnccrteiaosne.s weLrievernotdeadmagien weanszymfeosundmoniintoarllinggroluipvser wfaoslloawninigncrtheeasetenitnhlidovseer. weiDguhrti.ng tCroeaagtumleanttivethere niencrtowsoisratosf dtohesedepiadter2m0i0s0 amtg/ktgheafdtoesre stietnedawyass.noted Btleonotdh odaryganofofleuxoprosiudree.leveTlhsesewerdeecreelaesveadtedduocningthea 14-42 day recovery period (3.11,6).
-14EID087g05
009:36
3. Inhalation
Gpraorutpisculcfar ivatmroorssphewreerse Bours a day, five days
osfxpo1s1edo,f h83edmgs/omly,offoC-8, six a week for two weeks. The
bexopdoysewdeigrhatt.s shLoiwveedr aindjoursye-roreladtyesdfunscutpiporneswsaison of
eSnuzgygmeesstedforbyupdostoe-r28eldaatyesd ealfetveratitohneslaosftpleaxspmoasure.
Lthieverenddegofenetrhaetieoxnposwuarsedpeetreicotde.d hiTshtesoelogliicvearllyeffatects
wfeerceovencoyt. obsEeyreveedxamafitneartio1n4,s 3r2evoerale4d2 dnaoyscoomfpound
related effects (3.7).
+ Gdaryosupsa wofeekratfsorwetrweo ewxeepkossedtosi1x.0,hou7r.6s aorda8y3,.9fmivge/m
QoefixSpcochs-a8u.rrgee.osbhsoewHreovdweavtoeinrol,nys safloftiegrhctlitnnhiarcseaaell toasnidgfnosuorcudlduaarryisngon
atTneaostttshehartadw8a3ls.o9stsmagac/ccmio}fniscoiendederiranabtleexdtiaremedomuidnsu.trinogfBotewhexipagohfstu.rtehesaBenoddy
Gwfeigihhte ocfonttrheols1.0whimlg/em'thegrbouopdsy wweerieghtssimioflartheto7.t6hose
gbo/dym wegirgohutp wrearteiossigdneimfoincsatnrtaltyedhigahedro.se-rOerlgaatnedto
wsTeiiivggenhrit/fbiocidamynmtewdeiiiangtchretelaysreaafttiieonrs lwueenxgrp,eosuslriievgenreinfdiaencdda.nttlesyTtheehsigher
pienritohde. 83.C9linmgi/cma}l glraobuoprattohrryougmheasaur2e8m-ednatysrecovery
ephmoosnpshtartaatseedinanalilncerxeapsoesurien gsreoruupmsalakfatleirneten
Etxhproosuugrhes1,4 wdhaiycshofperrseicsotveerdy.in Ptahetho83l.o9gicmga/lml group
eTevsailounastioinn trheevea7.l6edanhdeav8y3.9livmegr/sm angdroumpisc.roscTohpeisce
.
Gpceheraminoogndes.strawetBreleododaredvfoelsruseoir-birldeeelatafenodalllyopswriiesnsgencclaeea2ro8lf-ydCa-y8 reincovaelrly
gBrloouopdsdeicnrcelausdeidngwittheh ctoinmet,rolbsu.t waTshedeatmeocutnatbloef Ca-f8terin
g8r4oudpays(3.r1e3c,o7v)e.ry in both controls and the 83.9 mg/m}
.
cRheapnegaetsedanedxpoesluerveatoefd orratgsanotofluCo-8ridperodluecveedlsli(v1e1r.12).
c. carcinogenic Potential
pInrodcuhrcoendica,n 2i-nyceraerasefdeediinncgidesntcuedieosf tiunmorrasts,inC-t8he
Liver, pancreas, and testis (3.35,3.36,11.11,11.14).
-15-
E
EIDO87807
z
009.37
.
*
@ See Falsted Fsfarsnces 17-23 for irfcrrmation on the
hepazocazcinogenicity of perfluorocctancic acid.
D. Mutagenic Potential
o AtPyFpOhiwmausriutmestsetdraiinnsmiTcAro9b8,ialTAas10s0a,ysTAusi1ng5SaT3lAm1o5n5e3l,7la AlL tSEeTAstTsSH0weraendneSgaactcihvaeromWyictehs ancderweivtihsoiuate astcrtaiivnatiboodn.
(5,12).
.
cC-e8llshadanda nloowevoirddeernceofofcyttortaonxsifcoirtmyatiionnCw3aHs107-1/2
observed (11.8).
-
mSueetagReenlaitceidtyReofferpeenrcfeluo2r4oofcotranionifcoramcaitdi.on on the
E. Developmental/Reproductive Toxicity
eo The oral administration of APFO at 25, 50, 75, 100 noorrogta1n5r0oegsemunlget/skigis/ndaa(yndyaytsodeasrtiahxtss.tdhurAroiungtghoxit15cheoeffpfeegrceitsotda.otofiforne)dudciedd obfodygeswetiagthitongaiinntoheccu1r50redmgb/ektgw/edeany ddaoysse sgirxoupa.nd nThiene etfwofecntonopnregbnoadnytwe1i50ghtmgo/nkgd/adyaynirnaetsofhadthea msotruedysetvhearne Cthoensipdreerganbalnet ahimgohuntdosoef dwaemisg.htThaenyd lonoestwaas observed to have urinary incontinence on days 11, 12, and 13. `nsTighg/enksgp/rdaeangydnandgtoasiendeadmgsrowueopfisghttdheidat25n,octom50ph,aavrea7b5,laebannoldremvae1ll0s0 cltoinitchael control group. Four fetuses were examined from each soffeorctfioeouyreneddchaamhnsagdeisne.yethAeclhla25ngoefasndthce1o5n0sriemsagtd/aibknlgge/dofafyetodunoesseesorgrmoorueps torfhurnontiuhnegghfootlnhleeo-whliaenlngfs: otro ladtrhigrseeoer-glqeanunsairzteclederfslte,nosfdaftrhikeberwssat.yreakThe Ltehnosseaobbnsoerrmvaelditiiensthoeccutrworedpreivniotuhse staemreatolloocgaytion as asbtnuodiremsaliotniecshemiincatlhliys srteuldaytedappceoamrpoeudndmso.re pThreonounced stthuadnieisn, thteheprteevriaotuosgensitcudieefsf.ectIwnasthea pdreevveilooupsmental eye abnormality which appeared to be an arrest in
development of the primary lens fibers forming the
aembberryroantailonslenosf tnhueclesuesc,ondfaorlylowleednsbyfibseerconofdartyhe fetal
nucleus. The same general morphological changes
occurred in this study (11.6).
16-
069225
EID087808
TGShr0ro2eu7eps1ro0a6ftshprianegentahneOtfhiCrgaEhts downoseerceeyGeraodumfp-i1nfGiisetoaef.regderii-0&s.0t5ic,ianus1.e5d,
oTroweamebarnyotbooxdiycweeifgfhetcstsinwertehisfogurnodup(.11.7N)o. teratogenic
.
+ JgPaervceauggrneraendtonardnaadtyssduwer6ri-en15gadotmfheingiedssottsaeitrniegodnp.e1r0i0oMdma,tge/rktngha/eldasyduerabvtyihvsing
dtahmes cgoanitrnoeld lterations
wadaebmroseu.t soounEgxeht-tet,rhniaraldn,d levtsihsesceebryoaedlsy, woefaingdshetvsekretalhlaental
TsfheteteursoeenoslsycooffpiinecadacilhnlgylinantodtteerdhistinthaotlbootgchioculagdlroluyppossfsoriwebrlaeylteberexaatmCii-o8nnesd.
VcTeeerslsiauftseidcatwthaeisonianncsiidtieensnccreoenasientdhethienfciricsdotenntcrleoulmboafgrrofuevpte.ursteesbTrhaiwesith
dTSitif1gfneiprfreiencscaeenntceinownalisyncipidfreonabcnaeabllyywzasead srbetysaptoianssoteincea-tltolayigleenderatlesitz.ed
0oS8tsrtetpshasereoeuvfnofksepvdiraibnbigylitfthryeo,m tgaordxiodcwitthisotnaratalete,dofamasntdhegdiedvavepensl.oCp-m8eTnhwetere
xAfodatmmiindnieasmttoienorsentdr.aoftedCtrheitoteprubeipasaodffvoerrdseeexvlteyelronpaamflefnetcatletidenrcalbtuyidoetndhes
C-8 and
Sphthalmoscopic examination of the eyes (3.25,10).
o SGotrfoug5p0esstmagotf/ikogpnr.oefgnaCAnt-t850irnambdgbi/itskstgiwltelhreeeddwaaamdstmeirnliosostnterdmeaodyrse1w.65e-,1i8gh5t
wCehraen otbheseruvnetdrea(t1e1d.9)c.ontrols. No teratogenic effects
GG2r1aoyunpogsnymdofayosfprCe6-g-61n.5antofMartgaetesrsntaawlterieodneaetxthposos0.eo1dc4c,ufrorr1e.2ds,ixat9h.9otuhteost21a
nags/oansg g/m
tcghroeonucpse.unrtvrNiavtoiinotgnerdaanatdmosgeonvaiencrdt armetosonpxgoincsitethyoswweaassofobesvteiherdveen9dt.9
waa%staenomybpsoerofravryetdheroeendlxuypcotsiieondnthgiernou2tp1hse.mbgo/dEmymbrwgyeroiofugpeh.ttalofOtthotexhreicipttuhypasn
SEeceonm ithneth2e1 mofgf/smprignrogup(,3.m2o4,1a0d)v.erse effects were
F. Metabolisa
Animal studies
dSSeitxsupdoyasniditnisopcneactsio,efsmridacidefi,foelrhaeabnmecsletesedrsiC,-n8athnwedereerxacobrbbeisttesir.ovnedTahniedn a
174
=
EIDog7g09
Z
easy
ftheemalzeimirnaitseacnrdedthedosmealebyha1m2s0tehrouresxcarfetteerd odovseirng9.9% of Ceoxncvreertseedly3,9 ainhde G6a0.%coffa.the27%admihienisfteemreleed tdoesmestebry 120 htohuersC-8posats-droaspiindgl.y anBdothcomspexleestelofy arsabbtihtes feexmcarleeterdat aonndlyma2l1%e ohfamsttheec.admiThneistmearleedanddosefeminale120micheouresxcreted (3.28).
.
HCa2l8ebayndintfermaavleenoursatsinwjeercetioand.miniFsetmealreesd hraaddioelxacbreelteedd
ehosusresntwihaillley t1h0e0%maolfestheexcardemtiendistoenrleyd2d0%oseofwitthhein 24
anodtmidneitsetcetraebdledosaef.terRa17diodaaycstivien tthiessufeemarleessi,duewshilweere
atthe36lidveary,s, 1m.a1%le inraptslashmaad, 2.a8n%d olfowetrhebuctarbsotni-ll14 in
detectable amounts in other organs (11.5).
TfheemalueptarkaetsanfdollcolweianrgancaesoifnglCe-8orfarlomdotshee vbalosodraopfid waintdhwitthhe vpeiarktuarleacthoteadloncel-etawroanhcoeurbsy p24osth-outrrse.atmeAnt dcGohosasineng-ger.sespionTnhsebelosowldaosweCrd-8emcollneesavrtearlnsacteefdolrwlatioetwhinignno mmauallpetpiaprrleaentts orwaals GGeenmeornasltrastteadtemfeonltlsowianpgplya sfionlglloewinogralindhoaslea.tionThe same eexspuolstuered. inApesaiknglbeloosdix-lheovuerlsiwnihatlhaitnioonneexhpouorsuraefter cfersosmattihoenbloofode,xpotshueren,umbteher omfateerxipaolsurreaspiddildy ncolteared acfofmepcotundblomoudchlemvoerles,Sloawnldy.malePrergantsantcleaanrdednont-he pfroelglnoawnitng reaitsthesrhowoerdal siormilianrhaCl-a8tibonlooedxpolseuvreelss. Specific data follows (3.20):
Fp ournaclto iaodnmis nofisttt riamteio- n, d femao le rs ats,i C-8nlevg els . as a
Ct-h8e dloesveels(25ofmg1/4kgp)p.m weTrheeseseelneve1l5smirnousetestofaolpleoawkingof a26ppprpomxibmyateeliyght30hopuprasatandonetoto0.7twoandhou0r.s0,45drpoppmpeadt t24o and 168 hours, respectively.
Ctohneclbuldoeo:d oCf-8femisaleabsroartsbedgiavnend arapsiindgllye cloeraalreddosfer.om
-18-
EID087810
:
005:30
Emre Cra) adminict-ation, female rats, C-8 levels as a
C-8 levels at 1/2 hour following treatment ranged
from 3 to 162 ppm, doses administered 2.5 to 150
wmgi/tkhg.blooTdhe vaslaumees dorsaengirnegspofnrsoem w0a.s12 se(e2n.5 atmg/2k4g)houtros
18 (150 mg/kg) ppm. The response was linear.
Caomnoculnutdeo:f C-C8-8adinmibnliosotdereids doirralelcyt.ly related to the
OraS-lsinaadlmeinoriasltratdoisoen,oF m2a8le Baajnkdg.female oo rats followin
Cp-p8m l(eevieglhst hionurfse)m,ale0.7raptspmwe(r2e4 h1o6urpsp)a a(n1d/20.h0o4u5r),ppm26 w(e1r6e8 h23o,urs6)3., 50Theandco2r3repsppao.nding values for male rats
Cfooncalugdree:aterC-8extiesntrettahainnedfemianletheratbsloofdololfawimnagle orraalts treatment.
Oral adfunctmioninofistnruamtbieorn,of femdoaslees: rats, C-8 levels as a
dBolsoeosd lofeveCl-s8 wienrefenmoatlecornatssidegriavbelnyondeiffveerresnuts. 11 oral aCnodnce1n7trpapmt,ionosneatand1/411hoduosress,posrte-stpercetaitvmeelnyt. were 14
Aatt e1i/2ghthouhrourCs-, c26onacnedntr13atippomn;s waetre2416houarnsd, 250.7ppaa;nd a0n.8d p1p1m;dosaensd, atre1s6p8ecthiovuersl,y. 0.045 and 0.10 ppm, one
Conclude: C-8 does not appear to accumulate in the bttroleoaoitdnmfeolnfute.nfceemTahlteehe nruCa-tm8sberbflooolofldowtilrneegvaetlmreewnptiestahteddodeossoeranlortemasieneimng constant.
p Inhao latfuncits iononof t extpiomr seuree s, x femaple o rats,sCu -8 lr evee ls ar s a
aC-8sinlgelveelssixof-ho9u6r ppimnhwaelraetiosneenexp15osumrienutteos 10fomlgl/omw'i.ng This level stayed around 100-110 ppm through one fhouurrt,herfeldlecrtoeasaepdprotoxim52ateplpym 7a0t p24pmhaoturseigahntd dhrouorpsp,ed mptoagt/t0me..r3n9 Tpwhapesm l1sa6eg8en phhoiaunsresratslsaeteenerx.ipnoseTodhrailsto esaxempieotshuegrreense0r.a1ilsornot1
-19-
5
g
EID087811
2
000.34
Sseoennalahttieondueexpotsourbeloo(dratshaemrplitnhganfoallsoiwnignlge oaraslix-dhoosuer at's given, finite time).
CCiohnnahcCalhluiadoteci:donofeC-x8pfoesmiusarleea.bsroartsbedgivanedn arapsiidnlgyle clseiaxr-ehdourfrom
InhalationPaetionf expdsosseurres, female rats, C-8 levelsTais a
i-(aB6hoatlleanvteeilosncoeantxcpeon1s/t2urraethiouorrnasngfeoodfllo0fw.r1ionmgto2a t10osina1gg0l/0emip:psai,xT-hheour
SS2oi8an%)e1,4f,%eo0ie7g5h6te,shpo"o5u2nrsspepm()v0a.s8-5,cseoen4n,cen7a1ttraptptwmoi)onhsoaunrdcsor24r(3e,shopuo17rn,sdin69g
0341, 1%ana 10 ag/a.7 The response is linear at
1/2 hour (correlation coefficient of 0.999).
SCPooonncGlhlutedaeot:fanccCae-8 rianinthealbelidso.odsoAmitsewdhtiahtreecshtlilogywheersrteltahltaevneedlsteoeusnetdha,et
h{nethSeevecrlealrevaenlcse. sysTtheias. suggests massive overloads
Inhaaloation exposures, maTlatetoanndof TfeUmalBearazts followin
c6(3-384 opBlaoe.uvte(slt)sw:o ihnotuhfreesm)ac,loerr71ersatppsopnmdwei(rneegigvh1at09luheopusprmsf)o(,f1/2manadlheou5r2r)a,ptspm
wete 137, is7, 162 and 147 ppm.
CCoonncelugdree:aterC-8extisantrettahainnedfemianletheratbsloofdollofowimnagle rats
inhalation exposure.
fa oermaalleardamitnsi,sCtr8atTioenvveettloss FprFoeeliglnToaonwnitinngagnada snstoinnag-llpereeogornnaalnt
fCf-oo8slelnolwteiivneaglislya instihenbgoltsehame2p5re16gmnga/ankntgd
oanrdalndoons-eprewgerneant rats 10 ppm at 1/2 hour, 33
2Pnoauce3,9 Appomn-patregtnwoanthouarnsd, pr26egnaanndt31ratpsp,m artespeeicgthitvely.
fCootnclauldtee:redC-i8n cplreeagrnaannctevsf.ollnoowni-npgregonraalntdorsaitsn.g is
20- EID087812
;
005.3%
InTekvselisstiuzsnosoTeumcctaolohroefatizoeiotte,r.rrssfnomaenst: rats, C-8
Borlootdenldeovseelss oifn pC-r8egnwearnet reastssentgiivaelnlyeitthehersamoene,1/2six a1n7d2 h24ourhoutrhse fleovlelloswiwnegrethe18,las1t2 oarnadl 12trepapmt,menotn.e, Astix atnhde tleenveltsreastemeenntast, twroesapnedctievieglhyt. hoWuhresnfoclolmopwairnignga saerlioewserionfgtoefn Cc-o8nsbelcouotdivecodnocseenst,rattihoenrse aipnpetahres rtaotsbe g11ivecnomptaenreddosteos 31(15atcoemipghatredhoutros)2.5 ppTmhisatmatywo hours, dionsdiincagtebutanwoeunlhdancreedquicrleearcaonncfeirmofatiCo-n8 wpirtiohrmutlotiple atcencepctoannsceecutasivefacsti.x hBoluorosd/dalyeveilnshalfaotliloonwinegxpoosnuereosr were not different.
Cbolnocoldudoef: preC-g8nandtoesrantsotfaoplpleoawringtoraecpceuamtueldatoeralinorthe
inhalation exposures.
-
RtoaditohelabfeelteudsesC-8ofwapsregtnraanntsferrartse.d fAromsimnagtleern1a0lmyb/lkogod dMoasteernwaals baldomoidnisatnderepdlacoernatlally olnevdealsy o19f oCf-8geisntcarteiaosne.d bdeetcwreeeansedtwobetawndeenfoufrourhouarnsd aefitgehrt dhoosuirnsgafttheern dosing (3.27).
aIbnlea ptorevrieoduuscesttuhdey,acuDtoewexlsethIaoln EexfcfheacntgseofResCi-8n.wasIn thhoiusrs satufdtye,r dcoatssinganwditmhiceC-8w.ereNogivseingnsDowoefxenhraensciend24 eailrimivansatisoenenof(3C.-380).via the feces, urine or exhaled
+ SmeeetaRbeollaitsemdofRefpeerrefnlcueosroo2c6-t3a9noifcoraciindf.ormAaltsioonseoen the
Rfoerlattehed Rdeefteerremnicneastio6n1 oafndC-682 afnord apenrafllyutoircoaolctmaentchiocds
acid in biological samples.
Human Studies
*
o Phuemrafnlsu.oroAoctsatnucdiycofaciodcchuapsataionloanlglyhaelxfp-olsiefdewoirnkecs
aftluoaripnleantlewvheilcshipnrotdhuecebsloCo-d8 rsahnogwiendg ofrrgoamni1cto 71
pprmo.n tOhnee fwlourokreorchweimtihcala plreovedluctoifon70 aprpeam waansd hriesmoved
bmolnotohds.analAyfzteedr f1o8rmoonrtghasn,ichifsluoorrignaenicovefrluosreivneerallevel
had decreased only to 39 ppm (45% reduction) (12).
-21-
0695.25
EIDog7g13
;
G. Biochemicalstudies . o cInatsexfvoilvloowisntgudi1e4s,dayLseydofigdocseilnlgs. werTehe isolated from
hTteaetGssotsohtsaitdemruolsnacetaecdipsrtLoiedcyuadclitgliyonceglrtlehsaatnefrrinomicnotcnhreteraosCle-ss3.-tirneIanted cvToientsthtroaCss-tt8e,ropnrceoudlutacunedrdedata Led5yo00dsieg-uidecepplerlnosddeunctterdeadtaeendcicnincerIeavainsstereo in
estradiol (1).
.
eo pSeeeroxRiesloamteed pRreofleirfeenrcaetsion40-a6n0d ofxoridaitnifvoermation on
phosphorylation of perfluorooctanoic acid.
4. Clinical Reports of Hunan Exposure . + "tHeehmaepleltohyfelssucororefoecnhiaenmg3iceapxllasam.nitnatNtiohoanthsepawlrteohrdeucpeordofbfleCe-rm8esdasrtoewleatlthleedas
awTmaoosnegxo.pbostsehurorsveeedteoxbaemtfiwlneueeodnr.ocdheAevdmidiaicttaiiloosnnsawleflrryeo,mennnoocorumrnaetlleartbeiedotnwseheinp TfFlraueboqorurieanntetolryy(tetheensctoLuinvrteeersrueledtnszytmeaesntdSGbrGleTosouwdlatsleevxtechleesedmioofnsgtortghaenic ntoora7a.l6 gra/nmge)(12)C.-6 exposure levels ranged from 0.03 . o Apotsetundtyiawlalsy meaxdpeosoefd WtaoshC-i8n.gtonReWsourlktss eofmplbolyoeoeds Coihcnecdmuiicpsaatttreiydonnatolelsytc-iornnegcllau(tsSeiGdOvTe,heeavLDliHtd,henAcpPer,oobflanedmanbaimloinrgubwionr)kers
exposed to C-8 (3.38).
I. epideniology
Acaprleotyreoesspeacttivae3HcohpolratntmwohretraelitC-y8,staudlyongwaswitmhadeothoefr
1$f2lo1ru8orsoeicxmopnmlpooonyutenhedsss,woerriemsormreaenvui(fe3aw6ec8dt8.urweodrO.knelrysR)etchoworesdrese whoionncwlourdkeedd
doievnaetrthahsle,lmo1tr7h7etaldniuetmaybtehrfocleolfrotwid-feuiapct.ahstesOwafswetrhseeig1on8bi0tfaiicknanenodtw.lny less
than expected. The observed-to-expected ratio for
cancer deaths was 1.0 (11.4,12).
.
pIrneeclafaltuirooerntsorhooicsppteacnbtoeiitvcweeeancciodhmoorr(ttPaFmOlAio)trytaplarinotddyucetsmtipuoldnoyy,mpelnattnhetatwerae
favestigated. The cohort consisted of 2788 male and
-22-
E
ElDog7g;4
g
069.34
.
70Th4.e975 afleflmoroalceamuesnweosraknedsrtsa0n.7de7amrpdlfioorzyeeddwombmeeontr.wteaslniAtmyo1n9g4r7amteeann,d(St1R9h)8e3.vas
cSfaAirtgdenisiotfivinacasalcnutlldayirseiaSnsMceRrseawsaSesMdR0w.ca6a8susae0n-.5ds7p.etcheifTihacelrle-SgHwaRasstfroorn-o
w2"niedtehe0:2..408m3eninionfthtewhoemneoCnhn.e-mCihceTamhleicaSDlMiRvsiDsiifvooirnsipogrnroosugtpraotu(epexpc(oansnoectde)r
Xgfrrpooounspepdrthoestrtoeatcehweemrcieacnac4lesro).b.serTvhIeenrdethaenwdasCh2enmoeixcpsaeilcgtneiDdfiivcdiaesnaittohns
atishnesoeciSitHhaRetrifoorngropburepot.swteaetnIen antcyhaencceaCruhseemwiacsoafl1d.eD61aitvhiisniaontndhe glragotrueepna,ctyer
. tcthhaainnecerp1l5a-vnyeter,asrus6lda6etaeetnxhpcseyctwgeerdro.uep.reFcuorFortrdheedrallfroermseenparroceshmtpalitoseyed at
nbeeetdweeden toPFOeAvalaunadteproasntdatceoncfainrcmerthe(4)a.ssociation
J. Aquatic/Environmental Studies
-
B
o 96-hour LCSO (bluegill sunfish) = 569 mg/L (11.12).
.
96-hour LCSO (bluegill sunfish) = 634 mg/L (3.37).
.
o 96-hour LCSO (fathead minnows) = 766 mg/L (11.12).
48-hour LCSO (bluegill sunfish) = 1500 mg/L (3.4).
48-hour LCSO (snails) = 820 mg/L (3.4).
.
48-hour ECSO (Daphnia magna) = 632 mg/L (11.12).
o 5l0e%velgro(wstehvenreddauycst)ion= 7(2d0iatmogm/sL) (=3.42)4.00 mg/L; safe
=ld-73daymg/ELCS(11(.g1r2e)e.n alga, Selenastrum capricocnutum)
o cop = Nil; 20-day BOD = Nil (11.12).
o TihnedicSaotielsAbvseorrypthiiognh mCooebfifliictiyenitn a(Koscajndyis l1o7a;m tshoiisl (11.12).
-23009.35
EID08785
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2. C1o1o3k(,3) J3.09C.20e7t a(l19.5,27Toxio col.tApi pl. TPhhaamrmaacceoll..,
3. Dupont Co., Haskell Laboratory Data:
210. MmRR--660044--77,, HHLL--5565--6611
43.0 AMcRa-d.33-N1a,t. HLsc-i1.23-P6h5iladelphia Data (1968) (C-1762)
65.. MMRR--11017908--11,; HHLL--116208--6698
78.. WMRR--23755637--11;, HRLL--623553--7799-
109.. MMRR--33556677--11,, HHLL--665396--7799
:
1121]. MNRR--53354627--11,, BHLL--568892--8800
-
11340. MnRR--53364922--11;, HHLL--229015--8811
1156]. MMRR--55334422--11,, BHLL--239259--8811
1178). MMRR--55431482--11,, AHLL--556650--8811
-
1203. MMRR--54314420--11,, HMRL--4516477--811, and MR-4152-1, HL-593-81
2212.0 MMRR--54314928--11,, HHLL--661020--8811
2234)] MMRR--54314239--11,, HHLL--882881--8811
22560. MMRR--54411380--11,, HHLL--112--8822
2278.. MMRR--44217553--11,, HHLL--6612--8822
239000 NMRR--54431780--11;; HHLL--342035--8822
33120. NMRR--55344534--11;, HHLL--573878--8822
334300 MMRR--55435443--11;, RHLL--17398--8843
35. L(eAtEtLerF,ileG). P. Sykes to C. F. Reinhardt, dated 10-29-87
3367.. MMRR--59638063--11
38. DRievpiosritondatoefdCo1r-p15o-r8a1t,e WM.ediE.calFay(eCr-w4e1a2t4h)er, Epidemiology
4. G3i5l(l3i)l:a9n5d0,%95F4. D(.199a3n)d. J. S. Mandel, J. Occup. Med.,
-24-
3
EID087816
Z
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9. P(a1s5t8o7o)r., T. P. et al., Exp. Mol. Pathol., 47(1):98-109 10. sStaOplIesR, RT.j hEa.eteitalal.,om mFuyndame . Appln . Toxe icol.,
11. 3m co. Data.
1. IRDC Report No. 137-089 (1978) (3-3546)
2. IRDC Report No. 137-090 (1978) (J-3545)
3. Personal communication, J. Long to P. J. Gort (1/8/79)
4.
AS(sccsh-uo4mc1a2in4a,)tesL. See letter
Re.p w.
oratnd (J1.980S). H. Pearlion
H(atSnoudbeTml.i,tOt'eEBdpriydtaoenm)iEoPlA(oCgo-yn41234-)22-82,
S. R{ickietredLaibnorRaetfoerrieensc,e b1r1a.g11)Metabolism Report 1-20 (1980)
6. Report M-601 (1981)
73.. 5.
RGEBoenacpvttoihnrr,etorn,mNSoet.noEtn.ae0Gl6.8R1ePTseaRtetOah1rao1cll0.ho,gyL(Ra19iLb8kao1ebr)roartaoL(traJoib-re5oys9r,1a8t()oD1re9p8it1e.)s
L(aJb-.412M4e)d. Data (1982)
10. H(acz-l4e12t4o)n Laboratories America, Inc., Report Dated
11. 2R(i-3k6-e-7r8674L)a(bSourbamtiotrtieeds,toIEnPcA.,, TRSeCpAoBr8teCA0P2,81CFRi0c0h1e253(61998847))
1132]. MH(Sa3Dz-Sl9e87t(8o1)n993W)isc(oCnistiend, inIncD.u,PonRtepoMrStDSHNWoI.-6322596-11720101)(1993)
14. EPA Submission (8e Notification Letter dated 10-11-93
(AEL File)
12. U(b1e5l8,0).F. A. et al., Am. Ind. Hyg. Assoc. J., 41(8):584-589
"aso 000.37
2
g
EID087817
RELATED REFERENCES
oral
13. Kojo, A. et al., Arch. Toxicol., Suppl. 9:465-468 (1986).
w"iTsotxaircitryat.a"nd kinetics of perfluorooctanoic acid in the
skin
.
14. Dpuront Co., Haskell Laboratory Data, MR-4234-1, HL-736-81.
"FC-143 occluded skin test on rabbits."
Injection Studies
15. o7l0s(o3)n,136C2.-3T7.2an(d19M8.3).E. Andersen, Toxicol. Appl. Pharmacol.,
p"eThrefluaocrutoedectaonxoiiccityaciodf ipnermfallueororoactstanaonidceafcfiedctsandaa tissue fatty acids."
16. S(m1i9t6h0,). F. A. et al., Toxicol. Appl. Pharmacol., 2:54-58
t"oSxcirceietnyi.n"g of fluorine-containing compounds for acute
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17. SAEbCdeellTaItif,11A8.50)G. (eBtrosalT.s, TArAchR.TInt. Physiol. Biochim.,
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18. A(b1d9e9l0l).atif, A. G. et al., Carcinogenesis, 11(11):1899-1902
c"aPcecrionxoigseonmeesipsrolbiyfe2r,a4t-idoinchlanodropmhoednuolxaytaicoentiocf arcaitd,liver 2an,d4',5n-atfreniocphilno.rophenoxyacetic acid, perfluorooctanoic acid,
19. A1b1d1e(l3l)a:t5i3f0,53A7. G(.199e1t).al., Toxicol. Appl. Pharmacol.,
p"eThceflumoordouloacttiaonnoicofacriadt, liaveprerocxairscoimneogepnreosliisferbaytor."
-26-
EIDOST818
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p"eOrnoxtihseommeechparnoilsimferoaftotrhse."hepatocarcinogenicity of 21. R(ecvaic1i,0E.6, :U.S1. 6Pat9ent0N3o. 54,n6274,8751 (1986)
"Treatment of symptoms of neoplastic diseases."
22. Takagi, A. et al., Cancer Lett., 57(1):55-60 (1991). p"eSrhfolruto-rtoeorcmtaenxopiocsuraecidto antdhe peprefrlouxoirsoodmeecapnrooilcifearcaitd,orsc,auses DSNiAgniofficraantts."increase of 8-hydroxydeoxyguanosine in liver
23. Twaakaygi,esA.ieest asl.,yJ. Environ. Pathol. Toxicol. Oncol., h"eHpeaptaotcoamrecgianloygeinsesainseairnldyucebdiombayrkpeerroxfiosrome proliferators."
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"A QSAR model of teratogenesis." Hetabolisa 26. G(o1e9c9k2e),. C. N. et al., Chem. Res. Toxicol., 5(4):512-519
"pAercfolmupoarroactairvbeoxytloixcicoalcoigdiscailn irantvsesbtyigaftliuoonrinoef-19 NMR Spectroscopy.
21
:
EIDOS7819
:
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RELATED REFERENCES (CONT'D)
Metabolisa (Cont'd)
27. 1Ha7n1h:i5j0a-z5v5i,(1R9H8. 2)e.t al., Proc. Soc. Exp. Biol. Med.,
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26. H(a1n38h7i)j.arvi, H. et al., Pharmacol. Toxicol., 61(1):66-68
s"uEblcihmrionnaitcionadmaindnisttorxaitciiotny ionf pteherfWliusotraoroctraanto."ic acid during
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30. P(e1r9m92a)d.i, H. et al., Biochem. Pharmacol., 44(6):1183-1191
m"eEtfafbeocltiszionfgpeenrzfylmueosr,o efnaztytmyesaciwdhsichondexteonxoibfiyotriecactive forms of oxygen and 1ipid peroxidation in mouse liver."
31. 4R0o(z3n,er,ParM.t A1.):6a7n5d D(.198R.1).Taves, Fed. Proc.,
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32. 1Si8n0g2e)r:,111L.14a0nd (R1.382O)p.haug, Crit. Rev. Clin. Lab. Sci.,
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33. V(aTnodxeBn18/H8e9u/v3el6,405J2.).P. et al., Lipids, 24(6):526-531 (1989)
p"eIcsfolluaotriooonctaanndcipcuraicfiidcsatifornomofratpertfilsusuoerso.d"ecanoic and
34. V6a(2n)d:e8n3-H9e2uve(l1,991J). P(.Toetxsarl.s,/9J2. /B0i4o5ch8e%m8.).Toxicol.,
p"eTcifslsuueorodoicsttarnibouitcioanc,idmeitnabmoalliesma,ndanfdemaelleimirnaatts.i"on of
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g
EID087820
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g
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.
RELATED REFERENCES (CONT'D)
Metabolisa (Cont'd)
35. vanden Heuvel, J. 2. et al., J. Biochem. Toxicol.,
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RInehniablitoerxycreetfifoenctofofpetrefsltuoosrtoeroocntea.n"cic acid in male rats:
36. vTe5n(k4a)t:e6s1w2a2r6l7u7, (P1.992e)t a(l.B, IJ.OASssTocS. /Of9f.3A,na0l.40Che9m.1)Int.., "cboimrpeocutndsdetbeyrmailnuamtiinounm mofonoifnlduiovriidduealmoorlgeacnuilcarflaubosroirnpetion Spectrometry."
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:
41. Handler, J. A. et al., Toxicol. Lett., 60(1):61-68 (1992).
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RELATED REFERENCES (CONT'D)
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42. H9(aSsuepgpalw.a, 1)R.:50et (a1l9.9,0) F(rBeIe0RSaIdSic/a3l1/Bi0o7l8.2M0e0d..,
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1"-Iancdyulcgtliyocnerboyphpoesrpfhloucohrooloicnteanoaiccyltarcaidnsfoeframsiecroisnomraalt kidney:
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-
45. K(a1w9a9s2h)i.ma, Y. and H. Kozuka, Toxicology, 71(1-2):151-160
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47. Keller, B. J. et al., Toxicology, 7L(1/2):49-61 (1992).
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"aPlrboutmeiinn--pfelrufolruooraocoicdtanionitceraaccitdi.o"n-bovine serum
49. L2e0v(i3t)t:,303D.-31a6nd (A1.987L)i.ss, J. Toxicol. Environ. Health,
b"i"Pnedrifnlguotroinpaltaedsmafamtetmybraacniedss."alter merocyanine 540 dye
-30EID087822
00415
: RELATED REFERENCES (CONT'D)
:
Biochemical Studies (Cont'd)
S0. Levitt, D. and A. Liss, Toxicol. Appl. Pharmacol.,
86(1):1-11 (1986).
u"TroixniecitByceolfl pelrifnelsu.o"rinated fatty acids for human and Si. S(oah1l0e8n1i5u/s9,2/3A0.0-8K7.) et al., Biochem. J., 285(3):779-783 (1992)
pS"eeTxrheolxeielsfaoftmeeecdtsprdoioflffiefpreeerrnafctleiuoonrionoacnmtdiacnero.ei"lcateadcidpaornamehteeprasticshow no
52. Sohlenius, A.-K. et al., J. Biochem. Toxicol., 7(4):205-212 (1992) (BIOSIS/93/13220).
fiver. wperfluorooctancic acid has persistent effects on
peroxisome proliferation and related parameters in mouse
53. S(1o9h9l3e)n.ius, A.-K. et al., mee Pharmacol. Toxicol., 72(2):90-93 pB"erproeowrxneilsutooomraobloectafaafntfeteyctseuadclifdobnyibcepteara-ocoixdxisiodimasetiaopnprootlaeinndfteroatihtneodrruscearcitniovfmiotuisees Tiver.
Si. T(h1o9t5t0a).ssery, J., Fed. Am. Soc. Exp. Biol., 4(3):ASTL A"Dostuhdoyrmoonnestheplaeyffeactrsoleofinpeprefrlouxoirsooomcatlanoeinczymaecidindiunction adrenalectomized rats."
55. T(hzootxtaatsss9e2r1y3,75J1.1)et al., Hepatology, 15(2):316-322 (1992)
e"nRzeygmuelaatcitoinviotfiepserafnlduorhoeopcattaoncoeilclulaacridg-r-oiwntdhucebdy paedrroexniaslomal
hormones."
56. Uy-vu, N. et al., J. Pharmacobio.-Dyn., 13(9):581-590 (1990) (BIOSIS/91/03735). "Ettects of chronic administration of perfluorooctanoic aS2cmhioodnsgghoonscthefoaalrtitosyyeloaccaiocdeynlzmtyermtaenasbfoAelridasesmsea,tiunraanrsdaet,acliylvl-earcc:yolmRgpelolysacitetiriooon-nshoifp Ricrosomal phosphatidylcholine.
-31-
I
z
EIDO87823
3
000.15
- RELATED REFERENCES (CONT'D) Biochemical Studies (Contd)
57. Ufys-sY0u), NG. aetoasl.,woBioochiemo--. mPhaarimaycols., 39(9):1492-1495 b"icoocmhpeamriactailve restsupdoinessesonofselxiv-elrisnketdo dpiefrffelcueonrcoeoctiannoic acid between rats and mice."
S56. v8a2n(d3e)n:31H7e-uv3e2l8, (J1.992P).. et al., Chem. Biol. Interact., i"nCovthaelenptlasbmian,dinlgiveorf, peacnfdlutoersitnesateodf fraatttsy.acids to proteins
59. wTh6i:t9e1h1o-u9s1e5, (M1.967W).. and I. F. Skidmore, Biochem. Pharmacol., c"oumnpcoouunpdlsi,ng"nooftaobxliydapteirvfeluoprhoopsipnhaocroyll.a"tion by some zfluoco-
60. w8W5i3gl)e:r,4562.24W6.3 a(n1d986Y).. B. Shah, Toxicol. Appl. Pharmacol., 2"-paemrifnloupoarroidneecanionictheaciLdS17i8nYactcielvlatmioenmbroafnea acnhdannreelcovfeorry of the channel.
Analytical Kethods
61. Belisle, J. W., 3M Co. Data (1978). "analysis of serum for FC-143."
62. B(e1l5i8s0)le,(aJE.Eea/n8d0/0D.862F1.).Hagen, Anal. Biochem., 101(2):369-376 i"nA bmleotohdodanfdorotthheerdbeitoelromgiincaatlionsaomfplepse.r"fluorooctanoic acid
Ns.ovwe.mbesrnyd2e4,r 1975
uKpidmabteerdlybAy: Iverson:ad April 18, 1981
JRuilcyhac2d3, C.198G4rah-amI:NmPd1:9.4 Jung 1,71994 - DATA4L.14
R SCCc. orci
-32-
EIDO8T824
069.14
000715
50
wo --
UPOp N wre SORE
v-
PARKERSPBOU.RGB,oxWV12276102-1217
J
Office of Env. Enforcement
D2i3v1.1 OohfioEnvA.venPureotection Parkersburg, wv 25101
JOofhfniceG. ofBriWtavteecr Resources 1I3n0d4ustGroioasle WRausnteRoaSdection
Fairmont, WV 26554 July 8, 1994
CERTIFIED MAIL RETURN RECEIPT REQUESTED
Mr. Mark A. Scott, Chief OD1fi2fv0ii1cseiGornoefenoWbfartiEeenvrrirRSoetnsrmoeeuenrttcaels Protection
Charleston, West Virginia 25311
Attention: Industrial Waste Section
REF: WV/NPDES Permit Application WV0076244
Dear Mr. Scott:
pSeirbmmiittteadppElnficoclraotsrieeodnnewiasflotrhoetfhoetrhiDegriyrneafRluenraennLcdaenddffoiuplrelr.cmoiptiTehisisssouafedpopulorincWaJVtainoSunoalriyids 1Wb2a,esitn1eg9/9N0.PDES - froa the THihsetoartitcaaclhedPrpeesrearivtataipopnliOcfaftiicoenodfoetshenaWtestinVcliurdgeiniaan Dapipvriosviaoln olfetCtuelrture
and History. The results of an archaeological survey of the area were submitted to the Historical Preservation Office on June 10, 1934. The report indicates
tThaantdfitlhle.re Waerewinlol arseeansd yoofuathheistaoprpircoavlal silgentitfericafnrcoem itnhethHeistvoirciicnailty Porfesetrhevation
Office when it is received.
Also, we have been working to obtain the storm event NPDES samples
craeqmulicrteidonfoorfthtehepesrammiptlianpgplaitcatthieonl,anbdfuit11w.eathTheer croensduilttsionwisllhavbee fdeolraayredded to
you when they are available.
signed afAfidcahveictk ffoorr tthhee S$t1a,t0e0m0e.n0t0 rfeonrewBailllainpgplifcoartitohne cfoesetsisoafttpaucbhleids.hinAg legal advertisement is also enclosed.
If you have any questions or need additional information, please call
me on 863-4271.
Very truly yours,
.
=
AItvtlawch(m6e8n58t-s1)
WS.t.M.EnSvitreownamretntal Control Consultant
Washington Works
BETTE 009:.15 _ THINGSFOR SETTERLIVING. Lo
EID0S3308
51 00017
INTEROFFICE MEMORANOUN
FDraotne:: 1R3I-TSHeEp-A1L994 09:51am EOF Dept: RITCHERLBISCOCYMICOC1I0ML Tol No:
To: PLAYTISAA!
Subject: Oucataan
ViSasil To inforaation: WPS: PLAYTIS
TDoa:te:ZIP0F9E/L13/9-4-W09S:30:49 PLATTS es
MVIALLHEENRTFRP.-_-uHLScILVoAtX
SFruobnj:ectB:obDuRcitacthaesyn, FLPR SHEA, CRP711/130, 999-2870
TAIhfawttaesrscaheuurriNoacudosnfaetfrotreennscdoeerdec4aliclnofnoyfreeasrtseetnridcoaeny,oanndI thhceeaalrlodefdft-hhJaautnddye`KdPeFlOcrAoaamtseahnstbeoncskhe4befhaacdsatu-sstaerdaeck
Jausdy& PFOA
ipnodtiecnattieasl Tchaartcinoongeenof.the production at the 3M plant
ctoo-apurtohsotrasteofctahneceJrOM(tahretidcealtehacsesrotciifaitciantge
csotnudfye)renpcreeseonnteOdccutphaattiopnaapleranadt UthreogeNnaittiaolnaClanCcaenrcse.r IJnusdtyitautet'esndleadt.e Was presented without any disclaisers or qualifiers or lisitations
ATphreilpa`p9s4 and Judy
wNfiaotdrh tfNoeGaIrbiatonefd hbekenrionwgTnobnrtgaounebdeTeodvteahrveyoidiinnctdeuhrsaetlsrltyeendgriesninpgonoistcec.uopnaAttaihroenoanflllcaeainrcw,eerses,paiwdtehienmnioiltogis
KaPaacrrkrsnhoonulteoidngaenaddtteitnhneddaincpcaaetpeedwrastionAlhfairnsonOhtuicsoaftfaetaehnle,inawguhdotiheaintscewPiFatOshAaWanVsUe.xconelHle4enfctaalsltpae-pdterraO.c.k A
t(o309beiantgtacihdeedntioflidedemaaisl)4,pWohtoenctailalledcarOrc.inoZgoebne.l atOF.IMKawrhrohinaldeirctaetdedJhuedy
Hweouldodn'ctallknOouwcaWtaatan.case fron Oucataan or anyone
eolfset.hat
call,
but
have
not
heard
anything
mare
cIa'svee oafsketdheJufdoylltaowpconwtiathctOuOcr.ataZeonb.el or Jeff Mandel With 3M and ses what
TI HApTassarethi"soutaltohnegreto Regards,
akreoeupndusC3a.ll
avare
of
the
perceptions
and
linkages
B2a*b To:
RFiotrcwhaeryding note froa AITGHERL--13COCVMI
WALRATJ
--ISCOCVMY
09/13/04
08:84
+=
Frou:EpJiuddeymWiaollroagtyh/Haskel1/CALD, 38-66504
8S0udb,jectF:orDuycoautraainnformation. learn. Judy
I'll follow-up With 3M and et you know what I
T#o+:* WFAoLrRwAaTrJdin-g1SnCoOtGeVMfIroa KARRHEW --ISCOCVAY 05/27/94 14:44 *o+
Froa: Bruce W. Karrh = 4.9813 * N-10480-8
009.18
EID073255
CSsAuloAbanrjnfTaalcrUD:aGunrccaaecdoacuaTtcnuaantroaoeaafntiyUconuisveGeiardvseiotnythe3ofA"wTaasptiocaatrlr.ilcekdi:sseacnSodondaaiyfn. wenHaesarkeatshaptlataNntTihnegheNsCaDny TCEHooanrrVkoaLGauaodenndyotwrhDUitEsUhseCGdootlhsdapLtacuhinc5adh5,e'msihcwe"aohluwalosdtualnddVgeitr1Lgeii%kinenitahS<:ea0nuepbhelKarnoritimn,ivnfoslcovhhmeeiwdsiSneiHieannscgeLstreTse.isstdhm,eeetssreeycocnhbaeflirn sassLotn rto thoiacAallaln'GsarrAyceKreensatcery?buTtrannassas not in: WiLL yeu Flesse ce: REIMACE noxvAX ce:SePKREEETWTERODGLYes[-.sIsSccOoOxoVMnIs Oavid L. Pest PORAROITLTECAHREESDAO.LA-.C1-3S1C03O00C0U0MWY RDeovbeertNolL.aesRite
Hosowe. wes
0004.19
EID073256
52 000530
70: See Below Subject: C-8 MSDS
INTEROFFICE MEMORANDUM
DFartoem:: DTeeplt:Ho:
M0i9c-hNaoevl-19E9.4 Ge1l1l:28am GEENLGLRM-ESEARTO AL AT ENGG (704) 362-5943 Fax 8-362-5934
(suspect - small *c* carcimogen 7)
MaTrhsehaaltlt,ached MSDS for C-8 indicates that the compound causes ntoutmorlsistinedmaamsmaalsknaownnd iasnda fseudsepraelcltycacrocnitnrooglelne.d Tchairscincoogmepno,undbutis DauspkoendtHHaasskkeellll lalbababcoountsidtehresexitpoasurseuspleicmtits(stmahlely hcavcearceisntoagbelni)s.hedI fcoarrciC-n8ogeanndwhtehneythienydicsaettedthethaAtELtahnedy CcoEnGs(icdoemrmeudnitity eaxppootseunrteial gCuairdceilniongee)n.iciItyamofnottheinC-a3,pobsuittioHnaskteollcomLmabentisonandtheI suggest we discuss this compound with Haskell.
TchoencCeEnGtraoftio1nsug/sleeninindroiunrkincguswtaotmeerrsmWayTPbeeflfolwueerntt,habnuttheI don't kfnionwishenotuhgehy waobuoultd hwoawshthofefy parnodcedsisschtahergefibteortahendehnvoiwromnumcehnto.f Ithaem s. ahmoewemvaetre,riacloncferronmedanythpaltanwte ctohuatldmapkoetsentoiralplryocedsissecshartghee tfhiinsish.
WLiololkintghisatctohmepounnotdesfionnd itthse wKa-y776i2ntofintiheshwaIstgeewtattehre? impression cthuasttomweerswilwlillnotmotdetseecetitC-8ininthetihre waaisrteowratwearterandsysttheamts,ourbut will wiicllbebethetrheereatatsomseomecocnocenncternattriaotni?onIanadm cIonamcernontedsutrheatwhtahte Co-u8r oprbelsiegnactei.onIissugtgoesitnfotrhamtthwee sdiistceusasndthtehepoctuesnttoimaelr oefxpotshuatre of the oluirghtWHTof yisttsempotaenadtitahaltcoafrcionuorgecnuisctiotmye.rs to this compound im
hIavaem caonfcienrinsehdthtahtatcwoentamianyshaavesuasppecrtoduccatrcisntoegweanrdsthhiapt iisssmuaedeifawned
uprnoicnefsosremdedoncusatoDmuePro.nt Ifsittehatandcustthoenmergoedsoesoutnottohaanpdoletentthiealplryoduct
with adequate precautions there could be a backlash to DuPont as
e
the supplier.
8
iPslseuaes.e let me know if I can be of any assistance with the C-8
2g
009.51
B10089977
|
N? "0025
QA LAB WORK REQUEST WURR HEWUEST
meauesTeo BY.LrNuomlneCt oars
UNIT, PROJECT OR DEPT THIS WORK SUPPORTS: __Q)
_4-lgGS
REPORT RESULTS TO: (Name and phone number)___
J1vY\
SDAAMTEPLAENDDETSICMREIPRTEISOUNL:TS(Srameplae Pvoient,eCoont_ailnerj, Ceondtenntes,sDadte,aTnimye)
_-- _-- SAFETY: (Circle One) Nomal Hydrocarbon; Acidic; Caustic; Other ___SH1n|( => ANALYSIS REQUIRED:
To 4 Sur
WHY IS WORK REQUIRED:
.
Leighboor Compla n=
-_--
ANALYTICAL RESULTS: (Attach additional pages if necessary)
Svve e FaFctent 12,5 Plan_
Co
1010 my fl/
Jatt ht Lohpr #1
nn
Iss
1426.7
L1V540
X4
#5ny)
ADNAATLEYCSTO:MPKETED:y
_
FORM FOLIO NUMPER: _9002 1065
com
SAMPLE DISPOSAL
RETURN SAMPLE TO REQUESTER [] RETURN SAMPLE TO RETAIN [] DISPOSE OF SAMPLE []
009.55
CA 002
Water Sample from Dry Rua, wv SSaammppllee wraesceniovtedprbeyseJrivmedHolorberctoolferdo.m EJ Tennant on April 18, 1995. pCHonosfidsearmpplHe owfassa7m.p8l.e aOcheisoptRaibviesr. pH on April 12, 1995 was 8.0 thus
gCoheesmicaabloveOxy2g5enmgD/eLmasnod 1w0a1s0 1i0s10emxgt/rLe.melSyhehlilg'hs, treated waterseldom
Stuhrerfeactaarnetdelteveerlgewnatss 1p2r.e5spepnmt.. This should be close to zero. Shows
Tfoltoaoldedsuhsapsensdoeldidssoloifdslewsass th4a6n.8 10mmg/gL/.L. The Ohio river when not
Gisivecnontthaemisnmaetleld awnidththseewdaegteeragnedntsisprheasremnftu.l. My guess is the sample
CA 003
L(ewo3sT5i7oe< CChemicatho ofSolfuaHioed
hiTHe
/,
Sampl[ei wo wir Jsuited--1-- 6/-- 95
Ralwedr tds id few co +Blefor"_
000054
ices
5/e2/95
nreRorrIcE wasoRAou
os:00m ssoscen
cate: 26ape-1sss from camo a
ArrasLTzoarions
oop: EsuRoncen
Tove: ser-2e8
T0To!o: WCGiAewLooTnoEcnRe'wb.xo.visoETraiLueAnDT TO! Ricard X KIRSCANER, an
{{ swRotiromtomaua)t1s { ernscunn's
cer own 0 aacxson
ancrsono
Subject: ATTACHED REGARDING CITIZEN coveents
rtERorrIGE waHoRANO
037m
once: 25-ape-19ss
from: dope:
SRoEfciuLsntcAsobetroocmuuasvcen
TToo GAenDaavid aroya.n mn.
Tele: Ioecses zoe: { rfoasseea)
Subgace: Re: DRY Ru LawDrILL
cdaemcrey,toRod Newell! a 61 mechanic in the Zycele A/C ares
fo2F8im=nedyienisgtaetaroudmtaaytimoonrniabnogutasakniyngtmreoubilfe I vecoauilgdhthelbpe
hia in having
at
the
ZoT3aiLse1s49a61b1o1u1t.
Rod 60 50
owns about 90 head of
200 acres up by the cattle. There vere
Landeiis basically
JDBSiaeasrlldoaehdcbsaaotmrtSo'lusuetntWcsipolrmlooefmnsptttfsaoerudtntoMccahooimsigt,nrogaazsneedekitnhfetuhretfahceftrietlihdnasftonrmemxeattimoveanss;kf,ocshioiimsced
CbCoEymtTaka,zsa4t3iuonchheadstd10meinntchieosn
fron the sun ott bs Tap Boies cihnatsteaigcnhaitne pToooelsT.areDmuroiangnethse
.:
So calves that wace scLll born and YEE8 th 1535 tuo he had ever had.
his He
neighbor had vas not crying
ane. to
ElRiAaTk to the Landfill but aid want to register it'swrpirnegsents.
c$
g
000::5
3
EID007456
out, 1sHis neighbor, Sarl Tennant, Rod is quick to point
RCohdbaitcheonhatshesereenacatnidonacroyllesicdtee.d
Earl has dead fish
made comments and frogs out
to of
2tE6hfae, irnuda has thea frozen, has complained to the ONR and the
a"nhdadhas had a sample tested himself and the results showed
aSzSoAuCndin the water". Earl owns about 700 acres out and
The landfill and also raises cacele.
explainAefdtetrheRosdittuaaltkieodn.to Rmoen IwacsongtoaicntgedtoRolnooMkelionotne aLntdand gBeatck to a. We. have missed each other several times in to dTaaystand half. This morning I called George and relayed the
tiensftoirnmgatoinon to hin. He assured me that surface water oaqubnaotruhtter2al8nyd.diffefGseeurolertngste frpsotamactaentdhsecetorJsmmeoanrietthoerrreeipnogrsthewodeullldtsonotathreebesrteaptoerteeadch Zaz as the health and safety of his cattle.
relayedAfGteeorrgney'sdicsocmuesnstiosn other.
twoithhimGeaonrdgeofIfetraeldketdo
tgoatRhoedr
aanndy
isantfiosrfmiaetdion for him i he still had concerns. Rod vas
uannddertshtaannkdfiunlg foofr the
tthhee
iexntfeonrtmatofionmonaintdornionwghawse
paecbfeotrtae.r
He
Daelnltioned that he was turkey hunting this morning and foun
tchheenvay down to the creek was very heavy in the run off. I
Kpnaosws'ed that information onto George and asked Rod to let me
if he did not ses an Laprovenent in a couple of days.
anythinTghaetl'sse has
aTbosuhtoualldl oIr
kcnaonw.do.LetOnmee oktnhoewr
icfomtehnetr,e
iRsed
Sproached thts Ln a very cals and professional manner and
working with us. It gives us a great opportunity to improve
PR status with the abutting land ovners to the lendfill.
Thanks,arts
1.
08:43am wovrozca
. INTEROFFICE MEMORANDUM
Date: 04-Mavy--1995 from: GEORGE
0095:
2 c 3
z
EID007457
Cee ReVveissed
DIVISION SOTFAETENVOIFROWNEMSETNTVIARLGIPNRIOATECTION `ENVIRONMENTAL ENFORCEMENT LANDFILLINSPECTION REPORT
>.sve
rE
ExAppiprlaitciPoanrmDiattOer_d\er=Na o. MIunincipadlAuZs36t36r20a7l
Naofm Facie ity EZ DuPoct. Cay Rue, Lad Q\
Weather Cuno"
`Cument Monthly Tonnage
Osteoflastinspecion 3eects
StatusofOperation: Active(X)Inactive ( ), NotStarted ( ), Closed ( )
Per--mitAc_reage----
Estimated disture bed acre eageattimeof inspection
Rating: SM--SaMtairsgfiancatolry, U -Unsatisfactory, N/A -NotApplicable, N/O - NotObserved, N/D -Not Determined
.
LiUinneerrSSyysstteemmMCaonisnttreuncatnicone LeLaeacchhaatteDCoeltleeccttiioonn SSyysstteemm LeachateStorage System
LLEACHATE MANAGEMENT
[[s7a]] MMoonniittoorriinnggWReelplosrts
f[iEas]] TSreewaetrmeHnotoPkleapn
[[4xx]] SLperaacyhbaatcekTRreocaitcmuelnattiSoynstem[i[eS]a OOtthherr
[a] PumpoutandTanspot [ga] Other
1sthere 3leachatedischargeinoreceivingsueam: Yes (X) No () Receiving Steam Dao Sam
Outer Sanus:
owavemer or|[TT T T 1
mig Lo|
[TTTT7
CoAmmmrecnosmTmhae = SebaanesSous fUonmmn nodoiyeed oud wen oegsecoefsdei.mAouhesauy_ Lo
EI YO VP ere
ee
RZIA Mec I%S . SoT Soa EA =Au RENT ARE Shwe Me uolva. TSQiund
IDnatielrymCeodviaetreCover [[GCiia]] oCowraccasons
[[5Z5a|] HCWo.EnxcthasimonSiaPinlsaDaniinstsppoeescadtlions
FEirnoasliCono,vSeerdimentCantal, [Tis] COodnotrroCloonftrWoilndBlownMaterial[[_CSS]| ATsrbeeDsitsopsoDsiaslposal
ReOvwevgeertsaitoinonDitches
FOiursetCCoonnttrrooll:
[[CT5=]] SOurdmgDeisDpiospsoaslal
=
Access Roads
AOcpcereastsiCoonnstPrloaln Placementand Compaction
VectorControl
GReacsorMdasnagement Equement
[CS| ShreFludffDdise posral
[5TA]] InoftehcetriousWasteDisposal C=] ote
CoAmmmeenetsn: Dimsaaes:aas TSioheetsny deoeses`asaeoeCaybo"SsTeed MbaoesevmiueenSaSsdteoennvdosD
SN Ae od = Senimon aide onde. [gochede "am oAye `oud ow
WsAoRgeNhINGT YNoouTaArNe hE erebywat rXEmedoheaa tshees folwi rSEeATmedaialEmeraasusres mustbetakeno~noSrTeSforste eas
ox
dat
oe
Number ofNONsissuedon le ale: Iam Co SaoNone |).
CompanyRepresantativeandTite: 1 _ "ud 2 =.
iteEee
Sa
One Io Prone MISRS
White Copy -District Yellow Copy - aspecor PakCogy -Chartesion Goldearod -Facily 1 000559
000239
|
\ fet wire
: rr ed
PR TEvoV:
frnr
INTEROFPICE MEMORAKDON
fens ppnr nko Hopp
loan on of ee
- Aperd
' Date: 02-May-1995 03:00pm
7
Prom: SWTAELVTAERRTM.STEWART
- TE7 L
DTeaplt:bo: (P3P0D4-)SH8E6A3L-E4A271
TO: Distribution List
Subject: MEETING - LANDFILL ISSUES
THERE WILL BE A MEETING ON THURSDAY, 5/4 FROM 10:00 A.M. TO 12:00 NOON INMY OFFICE TO DISCUSS ISSUES CONCERNING THE DRY RUN AND LOCAL LANDFILLS. THE TOPICS WILL INCUDE:
DRY FM
1) STATUS OF BLACKWATER IN THE POND AND STREAM
2) FOAM INRUNBOTHON ANDOFF OUR PROPERTY
3) C8 sume
LOCAL
:
-
1) NEW PERMIT REQUIREMENTS
2) COMPLIANCE ORDER
3) STRATEGY - ACCEPT OR APPEAL
LET MEKNOW IF OTHER ITEMS SHOULDBEADDED TO THEAGENDA. `THANKS.
EY
000:81
:
=
s8
EmO0s0sos g
|
:
Loaizall Ko|m 4 ub afeo ed
Daw
swws
ST
@< &s)
oAmmavo
-- ENVIoROmNeMrElNaTAgL/e
GASTON CAPERTON
GOVERNOR
DIVISION OF ENVIRONMENTAL PROTECTION 1304 Goose Run Road
Fairmont, WV 26554-1390
September 25, 1995 Mr. W. M. Stewart SWEPae.I0sn..hiionrBDgoatxEboonnnv1ti21rW7dooenrkmseNnetmaolursConatnrdolComCpoannsyultant Parkersburg, WV 26102-1217
LAIDLEY ELI McCOY.PR.D,
ORECTOR
Re: Solid Waste/NPDES Water Pollution Control Permit Application No. WV0076244, Dry Run Landfill
deelcldnci This agency's May 16, 1994 field investigation revealed numerous ls" uskraitnhgs poration of che Dry Run danafiti Although your company was advised of these deficiencies at that
time, March 23, 1995 and May 3, 1995 field investigations conducted 21 an inspector from the Environmental Enforcement
group revealed measures had not been taken to correct ihe deficiencies.
below, are of
These deficiencies, which are discussed in detail concern not "a, because of Son-ceaplisies with the
operational Management
requirements of Title Regulations (SWMR), but
47, Series 38, aiso because
Solid Waste the structural
integrity of included but
the landfill could be effected. were not necessarily limited to
Said deficiencies the following:
sparse vegetative cover, poorly defined benches which were not
providing `adequate routing'of Itormuater and leachate thus causing numerous erosional gulleys on the landfill surface, lack
of interceptor channels to properly route stormwater and leachate fo _the surface impoundment, lack of a leachate collection system,
wlaasctkeoflifsturftahciecknweastseers.diveSrasiidond chanineenlcsi,es anadreexpcriemsasriivley soduleidto
the design of
design. Psuerrpvoiscee,s otfhisa
actgohenenscyu,llatniTdnfeigqlul efsitwrsmhihcahvthmiatynsygtoeubxrueppcegormtrpiaasdneyeidcnonltanrda`ofcritlTltHhies
four letter dated June 9, 1995
above referenced Environmental
indicates that in response to the
Enforcement inspections, diversion
c2arhreaeaanneatlonsdaihfdaurvteihnebrdemreoanriend,iunggdrtwaoaintperrpeivpeFenrstomhratuvhnee-onabreeetano. tihnesAtlaacclhltoeiudvgheitnlhaentsdheefilflill
efforts are commendable, meet the Teguiremants of
be advised that diversion channels must Section 4.5.2.b. of the SWMR as further
rienfsetraelnlcaetdioninoSfedcrtaiionn Cp.i2p.ebs.1d.oesbelnoowt. prAelcsloudebethaedvpilsaecdemtehnatt tofhea
leachate collection system (see Section C.2.e. below) .
Telephone:Of(f3i0c4e) o3f6W7a-t2e7r24ReFsaox:ur(c3e04s) 367-2727
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bMeaeyn 3,fou1n9d95toFibeeld incomplete. is needed to continue the
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Am.i9nim-izPartoivoindepdreotgarialmedwhiicnhforshmaaltlionincrleugdaerdipnugtretshceibwlaestematerials. Also provide details of the waste minimization programs which
,.
osfhalwlastienclrueddeuctaiodne,scrreiupstei,onreocfyctlhiengt,ecahnndoloegnieregsyanrdecmoevtehroydowlhoigcihes
are applicable to the wastes being disposed.
wBi.l1;lb.Con-sTihset aofppalpipcraotxiiomnatreelsyves2l3s% tslhuadtget,he28s%ludfgielterilatledr uater. As the rilter press has subsequeitly been placed
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poeprecreanttiaogne,s.provide actual sludge, filter aid, and water
Bl.e2t.ter- dAsateidndSiecpatteedmbeirn increased dramatically
r14e,vis1e99d4,Att%abcihom-esnotli7dssuobfmitthteedswliutdgheyhoauvre pufsuant'to the recently started operation
tolfraetaattemrfeintltotetrphleapnrutersisftretorom)4d.te8ow%a2t0e(4rr-e3sf0le%urdegansecedrferfoiemnrtAe.hnCec.ewdaHsuIstnteowAnatstt'aecrh3a/1s/n8t87. Q.
Tthhee aimnocurnetaseofinslbuidogseluddigseposceodncesnitnrcaetitohne afsilwteelrlpraesssinbcerceaamsees in
boapcetreartiiaonaalndhaivreonaspuplafriednetlyrecfaeurseendcedtheinpryeosuernAcperiolf a13n,aer1o9b95icand
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mixture shall also be determined.
Cp.rlo.vci.de=bAosrintghislogasgenancdy whealslncoonrsetcrourcdtioofnWeilnlfoMrWm-a1t2i8o,n pfloreasseaid __. well.
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how they were derived.
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precipitation through the waste material.
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It must be determined if slope drains should be utilized to
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alternative diversion channels.
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cdSehutarenfrnamecilensiinmrgpeofueinfrdeztnehcneetd,reiqnsuaiylroduerdmiesnJctuhsnaerofg3esSTeecmttutisdotrnsbsere4.i5rn.oc2ul.tucde.edAd.tow(hCcet)nh; e
d4ii:mv5pe.o2ru.snid.omAne.n(tcgh)atno(nBep),lrsovaisndhdeou4l.idm5p.ir2no.sv.teAed.a(dsge)bdei(mC)ernoaturateetdiobnaerinocgounntdmreottl.h.e
Nsoutrefactehat If it is
ddee0ttaeuirplngeirdnaeddedrattvhheiantgssutrhfcealcereaerqluiyimrpeoimunendndiatcesanttianrgefocnchooatnngfbeoesrinngUwhiimetcthh, Ws3a1ip1rdov`ibdeenade
dEroeecqvuuiimszeeendmtedanettsisio.gnn (oCcfoanlctcuhurelraetsniutorlnfysa,,CevVeitrmhbpaogtuehn)edmteronetviismneeddeitcsdateetnhetihmartesq(upirrtheoevmiednets
of the SWMR.
cIhtanigsedtheconacguernrceyn'ts Therefore, provide
wuriintsdheerrpsotdneatdnadiirlnesgc.otnhsattructtheionrisinerAusgtursutctu1r9e93.vas
psCl.te2r.aubsc.et5u,rceon-fiiAsrtmatacs1uh5c"mhe.ndtiamNIoef.tenor1t3,stieinendldiicpcaiatpteees. tihtsaItftyttphheeisdainisdschcdaoirragrmeeectte,r. Cr.e2q.uci.r1e.d n-otItonislythtoe pwrroivtiedre'sacocpeisnsiontothtahte waorhakuilngrofaadceibsut also Tgthoeearlpaerfoovofridee17ipn=rdoitc1e0a0ct7teiho(anourlfaorromaoadrr(eesa)sexppirannedvpeildoanussvlciyaleewu)t.oinlizaStemadatipfoonhravaniinugsm'pbaoesrasl. rr(oeoafnederaponnecresda1i00dby'pfsleatentativmoiinneiwmnuummam)pb.erssh.PalrloAvliasdloesohparbuoelviidrneodaiadcaLptryeopdfiicflaoelr(se)ach haul ccrohraaodns(nsse-)ls,sectsiihfoounalpdpolfibcetahbeilnehc.aluuldedroaidn(sc)r.oss-Isnetcetricoenpstoorfantdhedhiavuelrsion
NSoetcetiotnhat4.5a.c3c.ebs.s orfoadtshemuSsWMtR.be dAsesirgenqeudireidn abyccoSredctainocneswi4t.h5.1.b.D.
Coin
EIDO12678
sy
MPra.geSteeiwghatrt
Ju Ii 4. + rt1
dCpaurenlaadviken4rda.tig5,s.e3c.hwdbahi.ritFgcc.hehessoohffaalnltd hce1-ubySle eWvaWRerU,rm,NtEp2Tor4epdo-evhnoiiudnregscraaailrncecu-alclaaltpieonvsesd.oofcuFpmoaersnstisinungcgh tthheat
ffeoertm tpheer diameter
esfxeopclrolenosdwsienbdgaseiidn nUinpfchoesnor--cyarb_e 2m5---aytrti,hneip2dol4ea-snnhiog:uvnirewSv,teolropmcr.iotvehyiEmdEe>in
isn utiasnle LoL
eDininttvrueymr,ienoeiunlsveevraCttoiaoetnleedvoafctoiproorniungtoaftoefpdo'imennetttraylo,fpidspiiest.cehacHroOgRoeEr,)dinaCanoltdneencgssrteihtos:ef
piSpiec, pe, poinc of
coordinates of point of discharge.
cf.bi2se.eldrd.v1ei.dn,vdesuEtr.i3i.gnAag.titoh-nesT,Mhaeytahpa16pt,'lsioc1la9i9t4di,onwMasactroecrhreisc23t,bleyi1n9rg9e5f,perleaancncededsN,aiyn asa3,igwha1es995
p4fl;oa6oc:t2e:dl2i.fiCtn.s.laoyfeTrhtsihsenopStrWoMecRxecwdehueircdehinignretnqwouotireifsenettchoaimtnpldsieoaplntichde. wwTaihstetheaSbseohmvatelilolfbiecld
biIoanxnvedesesitliafgnedadtimowenthsailchrperavoredeaulcedtdisf.tihcauAtllttvhaostuotgehCmoamtpetahercitaaplpsslucihcvaetar3iaonbleairingngsdiccaartdebsoard
tm(ihpmaritenfiaezravatabisloytneelemifinfnioinrmatitszea)atrimeoantiepnrriooagrlrdsaemrwhtiioschsiunabrseetffaednctitif.aflicgur1yle,tatrseeedrucvceoamsptaect
2tu8hteilsilazaiendddfmiaalstle.rSieacltPsiroonvpiods4ee.6.ta2h.etah.rsCei.azte otrfoequttihhreaesbStutrlhulacdttouzraeanrlw8h1i5incthCeagtrisiecrypiloflar
compactor or other equipment of equivalent weight be utilised.
Sfug2'%gae2sit
C.2.d.1.
Ttr.heTivhceekaleasdrpeRleidigichsatptoisofenodotianslciofrftriseelcwdtelryeInsvbteeasittneigsgauttthiiaoltniszleradya.efresrsnucpedto in
wwmaahtsietcrehiasllhisafltlretfbheeircekinnmcepesldsemmeiunntsetCd.2n.otdot.1ce.oxmcpaerleeyd thickness.
wtiwtoh fteehti.s difficult
Describe mSoelsisdures treoquciormepmaecntt. teac thtihee
die.nv2s.eudlf:of4pi.mceien-nttAofdfeotrthaetihliePsdhapsnuearsrproaosftei.dveesiTighsneantneeaedrdredabteinavcseheAsmtutaspcrthemvreienoftuesrl1y2so isthe referenced in Section C.2.a.5. #70 cSliaonazndnadiddiicfftaiiitltoeisnE'swi.hsderoneodtw'agsgeatnneheer,ailshleystoauctpkipplliiilzceeaddtidodunurriirnneggferiiennnccclleeasmmeennttthawwteeaattthhheeerr,
+ 9$16-:2(:b41r.9a79v.4inf-giRHeeGlg3dasr)dri,envgiaelwt,htoheuitghslisusdungcoehtwfmaiaslrlkneaodrceasinbaiocnstdriicvcseatdeoudnrisoannlgdAttdthraeacwhMimanyegn.t
1[AY
efIfinflelacdtdaeirdet,aionwtahsetouqtupiarlnoitvziietddyi,ngofparosvltiuiddmgeeeafduritashmpeoorsidezudraitnaignodnwhbiytchehwthyitpchehe
ssulcuhd'gveas and
quantity of materials mixed with the sludge prior to disposal.
.
009146
EIDO12679
uFri.gesntienveare
FSpCo.aay2ck.tedorn.iu'8aia.lclhs=tohifetPersyostovi.uit"dre"esoSutosraneifdnfDigrmaeiwntnitdnnaiegtcviaaoHtyenesdsc1sot.nhdtaerts"1oiolag3n0camhceFaeaiessesuriraaoetns`sureetrvroiesewb:ecoWumenm:deer-7),+
AsiflSni'vettehshsetetriiaggSpauaptmtliaiiolcontanstciovoofonnu'olprdrionavnd)eiidceacStuomeanmsdaduractitthceaeitdnbguy"bbooitulnhheicSwhiaFliildtnhaoesnyniclteeywsi.tbosre
bisana'elrauebtmoiret,edAd:c ames omitted:
OSCofno3nd8a2u4cfete,mempdpoorrrueaapdrroeinirllaylySnagccChllboooss"reefddruotuaaurrreSeeas.e"caopvrSeiBrhooarrdmryaoftoweFraseieriaeeildsirnsSagLia:itndeLicresos=vissd*ohNeeeo1raeien'lcbtieshiaxolanric
SPBrrieotveiltdceeimipnotthrearqyufainnCatolivteirceosvreeroqfuirrbeeofmererrneotnwscemdarteefirneiraSelnesccetdmiounsitnC.bt3he.iasarvsse.ieicbetobitigCnnatitceo
cCTfo.ral2vn.la0egs.cteti]igoTanthsieuosrnMyfsaasycceeen1v6wt,uhanildc1aeh9d9r4al,ryieinanMgalprirctkehheesley23nf,dciulels19o9fta5vo,ehatu:hmaeendroTTuMahsaceykrseao3g,sofrpaet1,99gin5on,eacsfhhieeetled
BadCaoiutllreleireinicvgatalittsoehnehtNehsfaiyoyssrtsep3mr6,oabnmlu1esa9mt9d,4dibtsNfrii.openllaaodlcSeod1ivn1vfuieEpcsothonifgvtawahtaseisottenexaitrmshsaacattilenrgaihawyallesstschcseinsaTtrpsilvaecresd.
SodLfaaeiatdSceehrcasattyieisnotinefga14ot.us5hh.eaf4ir.lso2rm.obeptehoerdfedtssheiitesgein,ieSnWdM`wRchi,rinchta`hcTtwcoioldrTledetaabencecrhemaliGsvntigitLlohitfzhfeetldhecatmilonrosenmqcuslioasetmeesn,cs
[jp StLLthaaaenstdcfihIioaaltnnledo?f1Pf1el1rtofnuome'rosmdhUaSasnliclAiern'mgbyaCp"drrCeeootsgretrpreasmdnionfbeeyndZttnihgteliFrenodWenaartt"sehHeiyvsdaehrpaxolsillsotgPiLxienpcgeurBtisvimielstiiehusesesscdsii.oe a
jv| uTiphtoenrdetephsreiegsnernetpqsruoipTteehrmeetniutelsst-ioomffateStheecftoijooetnapcr4hian.tt5e.o4fc.o7lt,hleeScdhtiailsolpnosbsayblstIeanmsc:erspbeasreadved
dcsielhRtaeteeyortsmtGiahpneS,ehdaHtEcoLupoPtsaioplmiuiolcdz,eiilncgancaduntcahplveyuesfgfiseistn.aadlteirviLceveoeandccfohivagfeturreroantiHintoohwnpelapsRcrhaeoav:slirlnagsaIniapssuehotan.leb}hdafbcoeaot
PgEtrhunoibagcnrkianttmeeh.seesd,,f'eAaamcoalhbxeasistmseuetmrhcaottdlahiiiaslcfcyktinnoeolnsue'ssashcyhhasaateytceetnhiedobinesu'cthisalisirgzghdeetdeEmdu'XisftEijf)buceshteisFst"aoiTlenicdlrsbetyedthe
pScRoeyolrtsltteooecrnmtalyitboeundttopasdyllsseptoteeesnrtb;mheien"neslooittczahaitenteghdtaothwfisicetkpchniEeipisneossntohlef$o0ct3al.hte4eea:dcrhl'waeAita:etchh(cia3)otnlelFtechaceqotuliilloteenecastchiaottnheat
tS$lyhrosasattsdeeimnmt.ghseptGplPilretnoaghvcoihuda1tet3e"CcSrcFauolslcshluuielcncatgtti:iicoolnnos"nAeslyisaSnocedtpriareconavgitsieidhneo'gfeoctashluaScttuufpliplacoetiraitaconhntaasntcteaiipccnaiodcpliialctteaeyctdtiinogn
unodecrolnytiinnugevatsotefumnactteiroinalefofceccutri:vely should settiement of the
RoLvoexeurtlisineebguctotfhuerlaeelnatchifarnteeesgarraeivatalyy. efxrt"oeNmnltethaeotfnalttaehnedfCisolellrlieeacsrteiaoofn isPyhsactsreeintiIcmabulseencthoes
a
000.71
EIDo0I2680
MPra.geStteenwart
AFtaseonfdedCrhiaeessnpscootesocdap,ilatoifeondptSeherwecaottriidkooiinnsnspgoCs.efa3xal.tc3ee:nas5rd.eraef,ifrnoeamrtlhelentchbeeredevbraaimesnperlrSeaoeddfcetaitPhhoeansedCi.s21p.eao.smsai.inaalrea
S2spcnhradailloelrthpelttlolarc=tehrde1e0l0ap7itlmeamdc(eeodmwrieoanarttkemilonyGrgfeprftiaehcoxaeprsal.ntsdoaecdthThanetaersacefrooilreelseocntoifoanPphiiasmabmpneeedcvIisiIaecwhseoirmniyecchnhetsor
ddtiihvveeerrlsseiiaoocnnhaccthheaanncnnoeellllsse;,ctaainnoddn
csuylsvteermt,s.itsIrsncotaueltreic)negptiotnrodiccihanattneenrepSiieopp:itnngd DtiiTgnof culverts shall be numbered with' each
hcp(hracaovrnvioninsedgsle-,saeicdnrtieitvfoaeenbrrssle)ienocnefsohcrathmloalntanhbeeedle,dtseausaibinlmgdeindtctvuedledrvlaewofricotnir.gt.yeaFcohDrettaaypicelhedocfudlrivanewteiarnr.glssptor
Stslyoopcpeoen,dofbimanasvteeedrrtiueadplonelferavoma2t5-iwyohrni,chof2i{ti-nhcriosmsictnoogmrpmofsleevoadwn,,itn,ainctdsuibtsilicenndvgioFtscehmte.eettdbpiret,4r the
2si0nindadbvieatchtaueittoiinnilgniotztfeehrdecoeupfittongortereitrndhfgeiatcfcellhoeewbas.ec.thawteAeAellsnsocooplrltihoeenvcdlitiedicaeoacnthedateetthaeciolltelydpeecdtriosfowinmnegSbsyesctienmi
tdSIheosetiaelcrehomcavtiteenireolydncionlsiglyfesgcttaeiomotneaxndtsiysltteheeniusanndndee.reitdyheeidng1)Tessubcbengtirwraeedesenoy,soe1teiahnnen.g'deli3e)iaInecthshmaeoycassttempsand
hSproeooavrdiedsletoisirseatiiniosntahvnletaeasdtfsefidol,mrtaeptreamcrchaioitaofesliyrsnigabtlesh.eaiedcvyaIpfletuy(aipstte)i(nis)3gf.opabdereIttfeiurcitmtliielniiezsdmeodtdvehesamaotneednmtinaendd
gsaiechnocattoteerrdxciteJniipsglttleoeyrx.ftsainldsnTeeedLdRiaeuvdsen,trotsbsipeonneeceddideeittdtye,crhtaehpisre.oovotiydpoIeefe'(Jsgst)euofgifesircedieietlnaetrmrIiaanteindosnaadtlehsdat cor
tpachrcaootvriddgieenogtrleayxt.tiiolnealeisfnoort-cnheoeodseidn,g psraoivdidteypes(usf)tf:oicibeIenftutiitrlatiiizsoedndesicaeoncdmined
aiIn:ns2v.Sehecs.cattuiisg-oiantnAigso3.nct2soh.nediiMonftadiriToccinhatstl2ee3nd,o't4t6h1,aa99tl5Sl,eotrwhieaaebnslddeisNcaihnyars3g,teat1ef99rw5oamtfeOiruestlldertefNeop.enc0e0d1
cCnoorntecaetpnmrteornvatitdiiiosnngsfsuourbftsfheierrcvieerdnetfaltelceOtauectdhlaebttye
tthreeI,atemlteehnveta.tseudrfanBcOeDeu.tfiiCmoopDio.eunncadnmdentToCis No. 00% during the ifsc four
SmSaeycosccntettepihntos,anbols4fe.a.5i1.d919.5cA.soonfctehCTenoitntrcslaueetrniftoa4r7nca,setiwSoiienmlrsplioeousfn1dit5mk8hee,inlstyGrmdiooamuegpsnnadciwttnauotsdtereerccaomnritesaiinronce.na. 1naE)
Protection
. 0607575 '=
EIDO12681 '
Mr. Stewart
Page eleven
Ley 2, .
sRheaglullatbieonesvaleufafteecdtivfeorJutnheei1r,po1t9e9ntisatlatetso c"aeuxsiestigrnogunidmupaotuenrdments
Stcspohohoaetaneltdnlatemisibainelagtntiafokornreem.qnuusgitrtrooWeubhmeneeedrlntweriamegittonerearoetfneics,toi=tnaettldoamwtfiihonterahtdc8iae3oo.gnn0rlt.,eiasnmeTirhnpeoarfratsyecisfecoaoinmrctheeee,nSxiIieNswt.Rhthi.sec,hthSceauIhtrcsftemaigecosen
tIbyEepedi(etst)eirsmtiodneebtdeerumiitfnielgdiezoettdehxatatndqilueoptrweoixvltliidlebeervuaittliillizbeadutiinlitsheed,lipnreorvisdyesteenm:ti
type(s). If it is determined that geoteoxntaillee foisr cnohtoosniecnegsssaariyd,
ftehrteotveairbdoeviesndurifcefafitceeirdeenntctehdartaBtOSiDuo,lnfalCOeCDo,natcraconoldrdiThnaOgsGlyc.boenecneYnuotturrialtiMizaoeynds1.2t,o
1995 reduce
Therefore, As use of
supcrhoviidseJeareMlayteraia"lstoDpatgaapS"afmeetaysusrhee,etprfoovridtehedeptroadiulcetd.
information regarding indicated in your May
all 12,
steps beinginvestigated =~ 1995 letter - to el. minate
as was the black
wTeattuerrndoifschBOaDr,geCOfDr,omantdheTOfCilltoaraeccaeptthaebrleeb'ycorenscuelnttirnagtiionnsthe
t:h3e-2s.o3i;l borArvoaiwlaarbelae ssotiuldiecsoverrefesrhaelnlcedbeidnetSeecrtmiionnedCb.y3c.o4no.ductingW
mCo.3d.ecl.lin-gIptroigsratmhispreavgienocuys'lsy rbeefleireefntcheadt iuntiSleicztiaotniCon.7o.fe.thweouHlEdLP
hbayvethibseeSnecmtoiroen.appTrhoeprreifaotree,foritpriosvirdeiqnugesttehde tihnaftormsaaitdionprreogqeuainrebda
uthteilipazreadgrtaapkhingbelionwt.o cSohnosuildderyaotuirocngtmhpeandyefbiecliieenvceiesthartefethreendcaetda in
garegenelenircaabytleewdilalsbydaacttchaeeptgmeenttehheroadtuteridelfbiezyraetntihcoeendHoEiLfnPAstmatoiaddcemhlemlteihnnotgdp1rp9orgoirvsaimdas,e.dthtihsat
you Note
Sepang, that
if
provide detailed rationale in support the method referenced in Attachment
of 19
said method. is utilized,
tthaekendefiinctioenaccicoeusntr.eferenced in the paragraph below must be
gil be iy 2. As the May 16,1954, March 23, 1995, and Hay Attachment 19 indicates that "slope at the surface of each cell
w3,ate1r9,95thfeiewlrditienrvedsoteisgatniootnsconrceuvreawlietdhntuhmiesrouasssuamrpetaisono.f ponded'
Attachment 19 also states that "the area is covered with an impermeable
remaining 16.9 acres clay (1x10-7 cm/sec)
of fill which is
ppsaapelipradlcmieecdacabotiviielnorintayco6in"ontfdaciioc1nmaxs1tp0ea-sdc6et.eetpdhatArlolaottythheeeord.u"gchgorvaAHesotrswt,eamvcaeththreme,re.inatAltt15aicnhsimtneednaitdcate6exshoifbtihttahste a
revealed a sparse vegetative cover.
May 16 field review
It shoul also be noted that
surface run-on must also be considered in your evaluation.
nEe.2c.ees.sar-yTh"etoampapilnitcaaitnioncomsptaatcetsionthaantda f6o"r dcuosvteranisd d3ePbprLiisedcoanstrol mwdahutereinrnigdaelStaenaraimtd,isnJiecnrogimcpcdaocsvt.eironi.sIntdoicbaeteapfpalciteodr.s wAhliscoh daersecrciobnesihdeorwedcover
000475
EID012682
HPra.geStteuweairvte
E.4.a. -
E.5.8.1.
Describe use of
- Provide name,
each type of
address, and
equipment utilized.
qualifications of the
landfill contractor.
OE.7i.
dust
c-ovSeerctiiosnsappEl.7i.ebd. asandnecEe.7s.sca.ry itnodimcaaitentatihnatcoampsaicxt-iionnchathhifcokr
that waansdtedsebrairse
thickness
ccoonvterroeld
aisn
wsoionndyaspeproisosdisblwehiwliethE.7a.hm.iniimnadnicates ox
over refeorfenc6e"dofincEo.m7p.abc.tedandcovE.e7r.cm.ateirsiatlh.e saImnediccaartte siofyasdo!il =
referenced in E.7.h.
contifct Teh sections C12.0.. and 6.Soaa nce nedapplication: E.10.a.2. - Section have been disposed concentrations less
C.3. than
of Attachment 20 indicates S0PPM are to be disposed.
pcs having If PCBs
in the pus. `please trovife the types na quantities of wastes containing
addition to the dates they were
PCBs which disposed.
were disposed in If PCBs were not
Adtitsapcohsmeedntin 29theinpdaiscta,tepsletahsaet
confirm
maximum
such.
1ift
thiScekcnteisosnesC.4O.fotfen
feet
Therefore, please reconciie: having a ieee, not exceeding 3:1 will be maintained. This is in
ScoevcetrionmatCe.1r4i.al swtialtles bethaatppla iemdinitomutmhetheinctkinreses soolfid6" waosftecomapraeacted
faoQpnepccleeiscesaaatcrihyontwoowrhkmiiancignhtadsaityna.tceosmptahicastticaoonn6f"alnidscotisflowricdtouhvsetrSecaitnsdioaGnpepblEr.i7ie.sd
of the
caosntrol
in windy periods. Therefore, please reconcile.
Section F.3. of is to be placed
Attachment 20 indicates over completed sections
two feet of soil cover of the fill. Verify
that "completed" grade which will
rseeccetiivoens noreafdedrittioonlailftwsaswtheichmathearviealrse.ached
final
Quarterly by Permit
Monitoring Well Reports No. WV0076244 reference
(QMWRS) submitted as Teguired that statistical comparisons
the data provided background well 14
for are
downgradient wells not meaningful as
6A, 12A, and 14 monitors
13A
with
of
aquifer. Therefore, groundwater JTeriey
your company contends that in the aquifer monitored
a different background
2nd 13A should be by wells 6A, 12A,
measured for the fidresftinfedouarsqutahretearvseraignethoef dsaactahparbatsme.ecis specifically the period
the first quarter 1991.
covering the second quarter 1990 through Be advised that the SWMR Iequire `that
Hbtohawacstkvgeraror,uendthhyeJrrSooWugMneRdoulaoatigelirocwallbyaaclkuigptrgyorbuaenddidegenrttoeuronfmdiwnthaeedterd.isqpusoaaslmaipltlyinargteoaw.beells
based on sampling of wells that are not hydrogeslogically
ubapcgkrgardoiuenndt gorfoutnhdewadtiesrposqaulalairteyathwahtereisotasherrewperlelssentwailtliveproovride
00057
E1D012683
e ------ e --------------
. MPra.gesttheiwratreten
muoprgeradrieepnrtesevenltlast.ive lnootcatbeedutiimlmiezdeidatetloy
"tthhearneftorhea,t apsrowveildlesd dedtoewrnmgirnaediebnatckgofroutnhde
beAy, hy1d2Ar,ogeaonldol1i3caalslcyh dgirsopuonsdawlataerreaq,ualtihcehy.
mu
st
dHgTi4hhs7eip4rso0asf,aao5glr%esn,tcaryheeoaywt.'ihlealrrSehwcoenoluonllts(disdl)yeoorcuamrtuteshdtecomubiptemaimnlaeytidizilaealittezieceoltdny: otdofowFnvGogeerrLllaltidshziieseWnAcN"pWieorAosiecA'altnshda,e/eor
gdMerHmo=ou4nnAsdtw(raiatnteerldideautthaoatf inscaointdshetrweaulqclut(iisfn)egrwnimelwolniwetalodlreseq)du,atbyeiltyMWmOpu6srAto,vibMdeUe-12A, HW-13A.
and
dBSSofaecscuvetmadieroniunotpuao5snt.i5.oad1ne.rcaijvoouinfsestwitohfeofyfintSghMeARptphSleailRcvlaaotwlpisvroenorvfiNoodor.erdtWmhVote0dh0iaw7fta6ii2cvs4aue4trr,ieoiowncratieimvsnoetdrpisrfoivocifadteido.n pSSrehocovtuiildodensyosuu4rf.4f,iCcoim4e.p6na.tn2y.jbdu.seAts,iifrieacnatdtoi4o.pn1u.2r.s2ueawpapievaerrstoofbetahpepsreopsreicattieo.ns, Q3AAus.pa7pl.lvi7ais.tc7ya0tifCinoodnntithcreNaoot.leSdMWPRVli.Oan0n7t6ch2io4sn4siamsgutesennctyt'iswnicltFuhedberthueaarQyrueaq4,luiirt1ey9m94eAnstslseetrtaoenfrc,eS/ection eCBxoypmrplelesitsatenedcreadaDdtieevsidisirNoeonv,teomAbieirrnci3P0no,eirlau1tt9ei9o0nsotloCiodnRt.iLrf.oiledWCemsoemermt,ihsascCirhoyinel,fa,tyyou aqdsifuiraasulnppyto.sisetesid.eTsah|etroIefftfhodmerieetsD,hpraoycsiraRnyludlniaactslieaavntedeslfiliriluflpa.imeataslhhIlafchaarsbsvy,alinaoplttraeobvblsieeiderenulpeddaiaacstshpehaosbshieaaidnsi,dcybeen please indicate accordingly. ts2oe2a,l1bse391iarmopiulnnesdmpeewncettleilodsntboyiMW-tn6hsitasanldlaHgWes-nuGrcAfy.acreeTvhseeearalelefsdortaerh,oeunpldraocvtkhiedosefemsewuaerlsfluasrc.ee oAIbtnttdaaiiccnhaetmdeentwfhoiNroc.hsem1l4io-caranetnfiuoeanrlenicsleesuatchiSalttirezeeadmanaSflaoymrspiclsio.nlglecPtoiiontnsof1 tahned s2.ample R2Abehosedvoeeutarabcoirevleseeqduearndnseatqreurdefasottuiiernvdfeo(,4ri)mnawftchoioeroprmniea.etsiaopnopPfrloteposarasimeCaehtiseetu,fob,mmisytGharlftalihtecteeancortcoiifogominWpnaaatnlateyrmtcyhoepy of cF19oa9ni6tr,imnoun8at0. tofhfaitcetheinraenvieewxpeofditAipopulsicamtainonnerNob.utWpV0r0i7o6r244o mJaaynusry 11,
000575 '
:
:
EIDO1268
?
'
ER
uPea.gestfeowuarrtteen
SShoonueladceynoeu hataveTaaddn)y Tesi questions concerning the above, please Sincerely, OFFICE OF WATER RESOURCES
JGB/3b cc: Cindy Musser,
Insp.,
Qe 4Bioee
John G. Britvec, Geologist Industrial Branch
SW Dist.
BR
000.7wr5
EIDOL. 2685
||
INTEROPFICE MEMORANDUM
Date: From: DTeeplt:No:
C0R5A-IDGec-K19D9I5LLO1N1:29am DFlIuLoLrOoNpCrKoducts 304-863-4972
To: Distribution List
Subject: Meeting Notes - C-8 at Dry Run
ATemfeloent+inwgaswtaes htehladt oins Nproovpeomsbeedr t3o0 bteo dliasncdufsislletdheataccDerpytaRbuln.e C-T8hosleeveilns for a(tPtoewnedran&ceSewrveirceesW)a,ltJoShtnewaDrotughatnyd D(aCnenWterablerLa(bE)n,viraonndmeRnotgaelr),ZipWfoeold,y EIdreJlaamneds, and Craig Dillon (feflon#).
bZyiptDeolughptryesefnotredC-d8atlaeveolns.variDoeutsailTsefloofn*thweasstaemplseasmpleexstrtahcattedwearree erxetcroarcdteeddin rboeofkereNon.ceEeSx6t5r3a8ctpiaogne d1a23ta(fDuorungihstyhedLogb?y).QualDiantyWeAbnearlytailcsaolprLoavbidonedbiaos-cake. Summary of the data is as follows:
SAMPLE
DESCRIPTION
C-P8OLYLMEEVREL EXWTARTAECRTEDEXTC-R8ACTLIEOVNEL BRM|_p _ RMas
150-1 Fine Powder Trench Scrap - undried
59
0.48
150-2 Granular Vacuum System Scrap - dry
2
0.08
150-3 PFA from Process K test dryer - dry 1
0.04
150-4 FEP-4100 from Line 3 - dry
7
0.04
150-5 1 ppm blank ,
-
1.04
NA Bio-cake sample (Quality Analytical) 0.5-1.0
0.004
Dtohuagthttyheexatnralaycstiesd tmheethsoadmpulseedtbhaytQQuuaalliittyyAnAanlayltytiiccaalldiafnfaleyrzeedd.froWmebtehre nmeottheodd uWseebderbyinDdoiucgahtteyd tonhattheappproolyxmiemrateslamypl7esp.oundBsaspeedroynetahreofbloC--8cakies canuarlryesnitsl,y landfilled at Dry Run due to bio-cake.
UbesinlgantdhfeillteesdtartesDurlytsRuna.s aIgnuiadded,ititohne, graonuypmealgrteeeddstchraatp GPFrAanuolrarFEPscrcaapn cbaen twlhoaeunlddfeixlibtleedsscirdaaetpoDmfryattehRureni.aelxtgrFeuonrdeerrPFaAta,enddthabitesyotnwhdoeule(dxgiebtneesriasdlcleryapofcmubatethsee)r.ihaulmFigodernheeFEraPat,'tterdtehaiastter garnodupbeytohnadt t(hgeeneproatlelnytiasllablsa,ndsfhirleld,amocuubnetss).of tIthewsaessctrheapcomnasteenrsiuaslsofwoutlhde not significantly impact C-8 levels at Dry Run.
TFhoirsFwianse Pboausdeedr/oDnistpheerstieosnt, rneosupltrsoceasnsd salcsroaponwiplrlocbeessalcloonwfeidguartatDiroyn.Run.There
is concern that the process configuration would not allow for distinct
009475
EIDO16730
sPeopuadreart/iDoinspeofrsiC-o8n amnudstnboen-Cd-i8sposscerda,p. theInf athliasrgmeatearmioaulntsohfoulfdinbieshetdestFeidnefor CJ-r8oupandthahtandTlefeldono*n acnontiinnduievitdoualdribavseist.he Istalewasofalasllo tshcerapcontsoenrseudsuceofthtehe need for landfilling.
00057 oh '-
Si
&iDO16731
<
.
:
12/23/95 notes from Dawn Jackson a AJBiem CFfreotumthmea,tiievnehEddelekiihflnarssdompDaoNEiiRasreslOofncfTioienncngtena,actnthteecdaadlbelDroee,urdtmTiehwnoamtttaehosred,ayfarlteaohabew.oiunStgtaTtafeernocaamnltlDubttohoanlttd'she E R Eer e eia ehaefeviLhacietet),hh'atdashnhedGoounJDreeed,pftfc.bouMntctofaccwrtAiagtdrhhyiiocsututollltdosucarahtelii.smfDaNtcCoRtriuocomfanfl.iltcoelm,edC,rwTuehmKninnccoahawnlitlnegd hoe 2 haa come background info on Mr. Teanant. TTSeeineenmaaelnditcoeutntotlidtyh.Cbruem"Wfhitevhnea,CtrunbuemmtepurieoneunnsedtdhheeiemrmodhnaotdhwsnbeooenfnnApupmrobiielsrosna,enddtOhicentottbhoeetra,l wFiotuhndOcotneobemreabzeiDnrgy Rtuhne. lasCtrumtimteoldthaTtennTaenntnantthastaiidf htehawtouheldhad
contact the DNR office when he finds a fresh carcass, the DNR
whaiiltledtdoaonielaadteindsgrsmubeeirnanotfahleyssBuiceshl.laenvai(llCylrseuemsariewnahdeincinatte1h9de8r8et.o)wmaes tahvatirutshekDiNlRling
PThDeneendrnieaMcnaotvcmaeasdaslsaconahenpdarpcoJreviceiamsidecneCcrduelmes.vOeefvlermHaeeolfrcsuva.rei0ryd0y57itnshpapptetmch,eihfisiDacrnydvkaitRtneuhdranst satontrfaheelaydmspe,iitsaiwtlahssat t"onot
ITeineeadayruee aanldeeThsaarieddatvheatwiDtuphon5tgwaalslontsreoaftinhgydrtohgeenlapnedrfoixlildep.onds
Wthhnie.nlfCersnuommmaenoantsekesdcalodTuelndtnhaagtnitvehetohwiomsuhlasdroenm'ethihseslhapowtveitrthehanhEaielspyosrcitastttloien.afonyowCniretuhm the
eopledatheidn tthhaact tthhee DDNNRR wtoouullddn'dCo aaddcriessssuethseampclaettloen aissfuree,shbudteer
cazcase.
miienmafbCeoruutmospc(rhweeiythnurwmehbionetmrrooodufurcrtWuiHmoEonCr)shascsohauwtnodretkdheedveDroNynR
astymplaetashtetiocneapnrdojteocltd struggles with. He
oSauildactahalti"cuosntaifctihneghuesarsvasfraomcMoru.rteTseynnacanltl,agaainnd.he said that he
BHSeeomeaaltsshkoiendgamsektehdaitfmeMwre.sdpToeecnianfnaincatanlamllyaysyiisfhavwoeef
ssreeen tarnedatmiinsginttheerpproentdesd,witahnd the materials that Mr.
Tennant mentioned. I told him that I'd get back to him.
I talked with Ron Meloon and Woody Ireland, and Woody pointed out
mDtSoohrntaettahtalamwyriasnretecnoioocfnt,hAeampneryDriEcPltu.rr1ey1a,WtomtoaeodnnydtchpaatHnlhgsaeotaremrteahaecymaoPhlnHalgveedoftohoemctechepuharyrrpodaenrmddoe,tgaeesrnDsurtpoeurrhteeoipxnoiveradtlseeydas
CGSeeoveenedcrlyYutoTdnueaenasytdchsahacyith/neTgdihutullrewisakdsedauyrab.ieanitngigRfootndahoennaeonsrdumeaWmvloeegorradysycThuaatetrr/eeTmahcatuhymree.cnhktaivnmegaylweihdtavhTeeBnonbsaeneotn toto
BIankeconscelnuses.iona,ndDaswhne wliosvheessheNEr. jTobe,nnashnet haopveeszytMheartrythCesherisntomtaess.
go
g
ous
EID010289 g
60 060:37
INTEAGFFICE MEMORANDUM OFartoen:: R27o-gMearr-o.159Z8ipt0e2l:50pm EOT Oept: zFilouroreoproducts Ted Mo: 304-sed.2567
70: 7 addressees Gor GERALD L KewiEDY
KENNEDY AT AY AT HOAX)
Subject: Phone conversation with Gerry Kenney
AXtetmanecdhye.d aSriencethe1 4naotneostofgooadphHointeh scoonaveorfsatcihoenssIwarredcse,ntlysehyadhawviethnoGterGroyt the Story completely correct. By this note, I an asking Gerry to correct any arror in note taking on ay part.
PGa0r4Ganrrey the botton Line ia that item 1 is not good news and items 283 are Roger.
C055
EID073253
G8 Toxsesty ro: Bone conversation with Gerry Kennedy on 3/20/96 uG1)-n8de3rMcsotnacanendndtiHrnoagst.cihosTnths'eyar(er1a0n0r0uannaniicn`rgUongts/ecashlte)sdutltheoadtfOuWClA.l8ySegyaxnvpteahnedesqiucsiuvrotceGskatln.oreTTshoeuxyiitcsiftoyuonndgeatnohigh Toxicity. They are currently collaborating on why this happens.
WtihhnaedtriecaCt-Ti8hoinscoutWlhiadltlbCeg-o8clinacsosutlihdefiefbdeutaua8frfee4citslianrnggoetOWc"AlC,FearTc,haercbiuwntoorgstethni.scasies sthceanafirrisotis 2t)he3MsiagnndiiHcoaancchestofhavteheprCUoPproasnetd traotthpeanAcPrHeEatitco LSoeonkcaratcotnhceerhnusm.an relevance of G3L)aonva3l1Ms0.%has`bReehsciuorlnetfdsiraoafnedte.hpiiTsdheeneifofsloaromtegisawtroertkoetrhartPeOlPotoUhkLeATaaItfOfNeIcMwtas(s19r94e11p)%o0rKtoeexrdskRebirynehtdohresWieutnohetldaMtienn. Tatatkeecntsina1r9e93n4o1t9e8d3.and again no relationanipe of C-8 exposure To Normonal showed tAhatFeloonolky 1aofthethepr8ostcarsaetse scaasnce8rsG-3notwoerdkeirn. the 1991 Uofiinn study
3 plans to publish this work.
> EID073254 00s
NE
INTEROFFICE MEMORANDUM
Date: From: DTeeplt:No:
W1A0L-STeEpR-1M.996ST0E4W:A5R9Tpm SPTPEDW-ASRHTEAGEA (304) 863-4271
TO: See Below
Subject: DRY RUN LANDFILL COMPLAINT
U.S. EPA,I RHEAGVIEONHADIITIWOOFFCIOCNIVAELRSSATRIEOGNASRDISNIGNCEA YCEOSMTPELRADIANYT R(E9C/9E)IVWEIDTH
CFORRORMEMCRT.IVEEAARCLTTIEONNANGTR.OUPBOATNHDMASRAYRAHBECCKA,SPARRE,PREFSROEMNTITNHGE STUHPEERRFCURNAD
RAELMLOEVGAELD TEHNAFTORC1E5M0ENCTATTALNED ODIIELDSAESCTAIONRESIUNLDTICOAFTEWDATTEHRE FCLOOMWPLAAICNRTOSS HIS
APRVOEPTERETRYINAFRRIOAMNOU(RNOLNAANMDEF)ILLT.HATHETEOEFTFHEREEDXAAMSINPERDOOFFROMA STHTEATEDMEEANDTCAFTRTOLME
SHOWED
SIGNS THEY
OBFOTHFLUROERQIUDEESTEEDXPONSAUMREES. OF
THE
STATE
PEOPLE
WE
WERE
WPOERRKMIITNGWWRIITTHERAANDNDICGIANVDEY MTUHSESMERT,HETHNEAMEESNFOOFRCJEOMHENNTBRIINTSVPEECC,TORO.UR
MS. CASPTAHREIENPDAICAITSEDTAKSIHNEGWOTUHLEDCBOEMPLFAOILNLTOWVIENRGYUPSERWIIOTUHSLBYOTAHNODFITTHEWNA.S
TSWTOATWEEDEKBSY MFSR.OMCNAOSWP.ARSHTEHATINSDHIECATEEXDPECSTHEEDWTOOULDVISLIETT MTEHEKNSOITWEWHAEBNO,UTAND
TSOHMAET OTFHETHSETATBEACKWGORUOLUDNDBEAABSOKUETDTHTEO SPAIRTTUIACTIIPOANTEA.NDIINFDIILCLEADTEDHETRHAITN WOEN
WOULD COOIPLELRATKEEEWPITYHOUTHIENMFOIRNMEDINWVHEESNTIGIATHIENAGR TMOHREEMAATBTOEURT.THIS.
Distribution: TO: H. DAVID RAMSEY, JR. CCCC:: MRAOYNNAALRDDWSMEEALTOOONN, JR
CC: LYNWOOD K. IRELAND
CCCC:: DGAEWRNALDD JAACPKLSOOENGER cCcC:: HChaRrAYlesHODT.GESAlt CCCC:: GRAORBYERTW. L.KLERSIETLCHEY CCCC:: DGAEONRIGEEL WAOWYETBOWEIRCH
( RAMSEY ) (( MEEALTOONOSNSRW) )
( IRELAND )
(( JPALCOKESGOEDRD ) ) (( AHLOTDGE) SHR ) (( RKLIETSCEHLEGRWL )) ( WEBERDA ) ( WOYTOWIG )
O0LEs
EID010291
|
INTEROPPICE MEMORANDUM
:
DFartoem:: T1h6o-mSaesp-1R.996Wal0d2r:o2n3pm
Dept: WAPPLDD-RPOOTWRER/SERVICE
Tel No: 304-863-2489
TTOO:: RLYONNWAOLODDWK.MEILROENLAND
(( MIERLEOLOANNDRN) )
cScE: DRrARALA wKIeReSnCHNER, JR
{( vKaIsRaSrCoHnRA) )
Subject: Dry Run Landfill 09/16/96
oIbssearwvantoiIoenxtspo.ousreed1d) DarreyTahseR.unneLw2)alnydTfsiholewlnrgitrpoa-dsrasayppsaeneddeddmaiidtsechgertsohewwienfrgoelwleodlwoliinngganda agcoodthejotbimoef),holtdheindgisbcahcakrgmeostfroofm tthheemtwhaesrumno-sotflfy (cilteawra.s r3a)iniTnhge dluoevertopaondsmvaalsl asmtoiulnltveorfySgolriedesn wiinththesomreunosflfi.ght4)disTchoelroerawtaison asonmdepefrosaimsitnigngcodmoiwngnsdtorweanmipnatsottthheeloouvtefralplo.nd fI roinmstthreuctuepdperthepond Tohpeerawatsotretwoapsutcoampqlueacretlyofcovaenrteid-,foeaxmceipntthwehatuphpaedr bpeonedn.dep5)osited during the morning hours.
Any questions, give me a call.
'
Tom
0094.85
EIDo16848
63
000549
|
INTEROFFICE MEMORANDUM
DFartoem:: Dept: Tel No:
0Th7o-mOacst-1R.996Wal0d1r:o5n5pm WALDROTR PPD-POWER/SERVICE 304-863-2489
TO: RONALD W MELOON TO: LYNWOOD K. IRELAND
( MELOONRW ) ( IRELAND)
CC: RICHARD A KIRSCHNER, JR CC: DANIEL A. WEBER
( KIRSCHRA ) ( WEBERDA )
Subject: Ory Run Landfill
couple ofI tthoiunrgesd tthheatOrIymaRduen cloarnrdeficltliontshistooa.fternoon and found a
the
1) The exit pipe.
outfall It also
had some appeared
tcoonspiedresriasbtleinftohaem
in and stream
around down to
tahbeoutpontdhevi5a00thefooatirlelvienle. andI
added about
about a quart a pint to the
of anti-foam outfall exit
to
itself. The foam began to immediately disipate.
face of t2)he aIctailvseo ffioluln.d sAompeparsemnatlllyatrheeastroafshexphoadsedlaitnrasuhncoovnertehde amlaltewreieaklenbde.foreI hienstlrefutctefdorthteheldaanydfainldl hoepertaotlodrmetohecowvoeurldtheget it done.
grass
grMoowsitngofonthtehesreacnedntltyhosseeedpeldaceasreatshathavheavea
good been
crop of exposed
by
the the
proencdesnt harvaeinslowtsillof be4
wrheeseeleedredtrtahcikssweienk.themThaesmeitadoWwosuldbelow
aprpepseeanrt.thatAnysomqeuoensetioinss,Stiglilvermuennaingcaltlh.at area When we are not
Ton
000.2%
EID039281
|
INTEROFFICE MEMORANDUM
DFartoem:: Dept: Tel No:
W1A5L-TOcEtR-1M.996STE0W3A:R4T9pm STEWART (P3P0D4-)SH8E6A3R-E4A271
T0: Distribution List
Subject: EPA AUDIT ENVIRONME1NTRAELCEMIAVNEADGEAMEPNHTONTEHICSALLAFTFERRONMOOMNR. (K1E0V/1I5N)SCIONTFTO,RMPIRNCG ME THAT HOEURANDRDYARNUONTHELRANDEFPAILLPERFSORONTHWEOULNDEXBTESCEOVNEDRUACLTIDANYGS.ANHEINSIPNEDCITCIAOTNEDOFTHAT TIHTEWOIUNLSDP_ESCTTAIROTN WTAHSISTAHFETERRENSOUOLNT.OF MR. TENNANT'S COMPLAINT AND THAT SAMPLINGTAHTE TIHNESPLEACNTDIFOINLLW,ILALNDINSVAOMLVPELINVGIEWDIRNIGNKTIHNEG WSIATTEE,R WEEXLTLESNSIIVNE THE VICINITY. 1 INDICATED THAT WE WANTED TO SPLIT SAMPLES OF ANY TAKEN ATMRO.URSCLOATNTDFIDLILD.NOT WANT TO COME TO THE PLANT BUT WAS 4 - GTOHIENGINDSIPREECCTTIOLNY.TOIFTTHHEERLEANDAFRIELLA.NY IQUWEISLTLIOKNESE,P PYOLUEASIENFCOARLMLE.D ABOUT
665435
EID024318
BN
GASTON CAPERTON GoveRnor
DIVISION OF ENVIRONMENTAL PROTECTION 1N0itMrco,JuWnVki2n5R1o4a3d October 15, 1996
LADLEorERLecMeTcoany, Pho.
Mr. W. M. Stewart Senior Eavironmental Control Consultant `EWLasDhiunPgotnotndWeoNrekmsours and Company P.0. Box 1217 Parkersburg, West Virginia 26102
Re:
Dry Run Landfill (WV/NPDES Permit (WV/NPDES Permit No. WV0001275)
No.
WV0076244)
and
Washington
Works
facility
Dear Mr. Stewart:
DHuoPwoenvte'rs,E.oLapveeDrruatPtiohoenntspaodsfet tNsheeevmeDroarulyrsmRouannnthdLsa,CnodifmnipslpalencatynodrhsatswheiatlWhwaDasyhEsiPnbgehteaonvneaWoovbarslkeursevdefadcciislteiitrzyie.onusoDfusrhWioenrsgttcnoVumiimrneggrisnoiuiasn. inspections, DEP employees noticed, among other violations, the following:
1. bOlnackseavaerdaoldoocrcoausisonlse,acDhuatPeotnotbhearselaelalsoewdedf,raonmditcsoDntriynuReusntLoaanldlSoiwl,lianltaorDgerfylRouwno,f in violationof its NPDES Permit and the West Virginia CodeofState Regulations,
2. OintssWeavsehrianlgotcocnasWioornsk,sDfuaPciolnittydiinstcohtahregeOdhiToefRliovne,rD,elinrovino,lNatyiloononfaintdswNaPxDbEeaSdsPferrmoimt and the West Virginia Codeof State Regulations;
3. Orunn-soefvfefrraolmocfclaoswiionngsa,cDruoPsosntthheaDsrfayiRleudn,aLnanddafpiplalraenndtlhyacsofnatiilneudetsotcooflalielc,ttoanpdrterveeaatt olfeSacthaattee Rgeegnuelraattieodnbs;y the Dry RunLandi, inviolationof theWestVirgiCnoidea:
4 DOEnPsetvheartatlheoqcucaalsiitoynso,f DthuePloenatchhaatsegfielneedr,ataenddbayptphareeDnrtlyyRcuonntLiannudeisltlohfaasie,xtcoeneotdiefdy WtheesdtesViirggnicnaipaacCiotdyoeftofheSttarteeaRtemgeunltastyisotnesm;, in violatoifotnsNPDES Permit and the
005.24
EID012733
Mr. WM, Stewart
October 15, 1996
Page2
Ss. On several occasions, DuPonthas failed, and apparently continues to fail, to properly
compact the wastes disposed at the
Virginia Code of State Regulations;
Dry
Run
Landfill,
in
violation
of the
West
6.
On numerous occasions, Du
Dry Run Landfill in greater
Pont has deposited,
concentrations than
and continues to deposit, waste
the concentrations approved by
in the
DEP,
in violationofits NPDES Permit and the West Virginia CodeofState Regulations;
7 On several occasions, DuPont has failed to properly operate and maintain the Dry Rua Landfill, in violationofits NPDES Permit.
8. DuPont has failed, and continues to fai, to retrofit the Dry Run Landfill surface impoundmentwith alinersystemandleakdetectionsystem,inviolation of the West Virginia Code ofState Regulations;
9. On numerous occasions, DuPont has allowed the effluent from the Dry Run Landfill 10exceedthewater quality standardisn, violatofitohneWestVirg Coi deonfSitaate Regulations;
10. Onnumerous occasions,DuPonthasallowedthe effluentfromtheDryRunLandfill 10 exceedthe discharge limitations established in its NPDES Permit, in violation of its NPDES Permit; and
11. On several occasions,DuPonthasfailed,and continues to fail, tocomplywitheach and every conditionofits NPDES Permit, in violation ofits NPDES Permit.
Due to the foregoing violationsatthe Washington Works facility and Dry Run Landfill, DEP intends
to file
relief
a
to
caivdidlraecstsiocnurargeanitnsatnDdupProonstpeicntitvhee
Circuit Court of Wood C
violations and will ask
oun
for
ty.
the
The agency will seek injunctive
assessment of civil penalties for
current and past violations. Acopy of adraft complaint is attached.
1 have instructed DEP'sOffice ofLegal Services to initiate formal proceedings against DuPont in
circuit courtby nolaterthan January 15, 1997.
potential resolution ofthe enforcement action
Should
before a
DuPontwishto eater into
complaint is filed, please
negotiations
contact DEP
to explore.
attomeys
Matthew Crum or Scott Goldman at (304) 558-9160.
Vey $f yous,
Bojac
Laidley Eli McCoy, Ph.D. Director
009425
E1DO12734
IN THE CIRCUIT COURT OF WOOD COUNTY, STATE OF WEST VIRGINIA
WLeAsItDVLiErgYinEiLaIDiMvcisCiOonY,ofDirector,
Environmental Protection,
Plaindff,
DRAFT
v.
Civil Action
E. I. DuPONT DE NEMOURS & COMPANY, INC.
Defendant.
COMPLAINT
INTRODUCTION
PlaintiffLaidley Eli McCoy, Director, West Virginia DivisionofEnvironmental Protection
("DEP"), by counsel, alleges the following:
1 `Thisis a civil action brought undertheWaterPollutionControlAct, WestVirginia
Code 22-11-1 to -28 (1995) ("WPCA") aod the Solid Waste Management Act, West Virginia Code 22-15-1 to -20 (1995) (*SWMA"), against Defendant E.I. DuPont De Nemours and Company, Incorporated, based on violations of the WPCA, SWMA, and the regulations
promulgated thereunder forinjunctiverelief, theassessmentof civil penalties,andattorneys fees.
009.2%
EIDO012735
PARTIES
2. Plaintiff, Laidley Eli McCoy, for and onbehalfof the State of West Virginia, is the duly appointed Director of DEP, and is thereby authorized by the WPCA, and the regulations promulgated thereunder, 10 enforce the water pollution control laws and regulations of this Ste. Specifically, W. Va. Code 22-11-22 states:
`Any person who violates any provision of any permit issued under orsubjectto the dporlolvairssipoensrodfa(ytohfesWucPhCviAo]latisiosnu,bjaencdt taonyapceirvislonpewnhalotyvinooltatteos eaxncyeperdovtiesnitohnooufstahnids. artoirocflaney rule. .. is subject to acivilpenalty not toexceedtenthousand. dollars per day of such violation. Any such civil penalty may be imposed and collected only bya civil action instituted by the director [of DEP] in the circuit courtofthecountyinwhichtheviolationoccurredorisoccurringorofthe county in which the watersthereofare polluted as the result of such violation.
Upon application by the director, the circuit courts of this state or the judges
otfthhe epirnovrvaicsaietoinosoonfmtfahyisbyairtnijculnec,ttihoencruolmepsoefltchoemp[leiaavnicreownimtehataanldequnajloiitny]viboolaartidoonsr
dtihreepcrtoovri,siefofnlsuoenfttlhiimsiatrattiicolnes,,otrhae ntyeromrsdeanrodfctohndeitdioinsorfeaoncfybtpoeaorrmdri,tagnrdanttheedvuenndueer
of any such action shall be the county in which the violation or noncompliance
exists as the
or is taking place or in any county in which resultofsuch violation or noncompliance.
the
watersthereofare
polluted
3. Additionally, Director McCoy is authorized by the SWMA and the regulations
promulgated thereunder, to enforce the solid waste management laws and regulationsofthis State. Specifically, W. Va. Code 22-15-15(d) and () state:
ru(@l)eoArnoyrdpeerrsiosnsuwehdopuvriosluaatnetstaony[tphreovSiWsiMoAn Yofi[stshuebSjeWcMtAtLo,ac(iavlinlypepnearlmtiytnoortatnoy exceed twenty-fivethousanddollars for each dayofsuch violation, which penalty osr ihnbtehareceicrlocvueilrtecdouirntoacfivKialnaactwihoaneCiotuhnetriy.nthecourtwherein theviolationoccurs
(6)Thediremacysteeokarn injunction,ormay instiatcuivtielactionagainst any
person in violation of issued pursuant to this
any provisionsofthis article.
article
or
any
permit,
rule
or
order
2 000527
EID012736
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v
4. Defendant E. I. DuPont De Nemours & Company ("Defendant"), is a corporation duly authorized to conduct business in the State of West Virginia. Defendant owns and operates. a facility ("Washington Works") in Wood County, West Virginia, which produces plastic and acrylic resins. Defendant also owns and operates a noo-hazardous waste landfill ("Dry Run Landfill") in Wood County, West Virginia, that serves the Washington Works facility. At all pertinent times hereto, Defendant was and is doing businessinWashington, Wood County, West Virginia.
5. Under the WPCA aod SWMA, the definitionofthe term "person" includes "any industrial user, public or private corporation, institution, association, firm or company organized. or existing under the lawsofthis or any other stateor country." W. Va. Code 22-11-3(15) and 15-2(22). Defeadant is a "person" as defined under the WPCA and SWMA.
JURISDICTION AND VENUE 6. This Honorable Court has jurisdiction over this action pursuant to W. Va. Code 22-1122 and 22-15-15(9). 7. Venue is proper in this court pursuant to W. Va. Code 22-11-22 and 22-15 15(d) because Defendant's Washington Works facility and Dry Run Landfill are located in Wood `Countyandbecausetheviolationsreferencedhereinoccurredorareoccurringin Wood County.
STATEMENT OF FACTS 8. Defendantwasoriginallyauthorizedto operatethe DryRunLandfillin 1982 through issuance of permit No. IWL-6282-82 by the DepartofmNaetunratl Resources ("DNR"),
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EID012737
predecessor to DEP. Such permit authorized Defendant to discharge a specific amount and type
of pollutants into Dry Run,a tributaryofthe North ForkofLee Creek, which is a tributary of the
Ohio River. Pursuantot W. Va. Code 22-11-3(23), Dry Run, the North Fork of Lee Creek,
and the Ohio River are all "waters"ofthe State.
9. On Jamuary 12, 1990, DNR reissued IWL-6282-82 to Defendant as Solid
`Waste/National Pollutant Discharge Elimination System ("SW/NPDES") Permit No. WV0076244.
As written, the SW/NPDES Permit was scheduled to expire on January 11, 1995. A copy of
SW/NPDES Permit No. WV0076244 is attached hereto as Exhibit 1.
10. Solid Waste/National Pollutant Discharge Elimination System Permit No.
`WV0076244 incorporated by reference, a5 a term and condition thereof, information subtitted
by Defendant with SW/NPDES Application No. WVO0076244, as well as information contained.
in correspondence from Defendant dated August 10, 1987; September 15, 1987; March 1, 1988;
April 14, 1988; March 16, 1989; and May 9, 1989. See Exhibit 1, page 1.
11. Under the federal Clean Water Act, 33 U.S.C. 1251, esteq. and the WPCA, the.
State of West Virginia, through DEP, is authorized to regulate discharges into the watersofthe
State of West Virginia through implementaotfitohen National Pollutant Discharge Elimination
System ("NPDES") Program. Specifically, the NPDES Program is "the [olational program for
:
issuing, denying, modifying, revoking and reissuing, suspending, revoking, monitoring and
enforcing permits, and imposing and enforcing pretreatment requirements under Sections 307,
318, 402, and 405 of [the federal Clean Water Act], including any approved (s]tate program."
Ses National Pollutant Discharge Elimination System (NPDES) Program, ("NPDES Program"),
`West Virginia Codeof State Regulations ("CSR"), Title 47, Series 10 2.27 (1993).
4
EID012738
069.23
12. On February 16, 1990, Defendant appealed the terms and conditions of SW/NPDES Permit No. WV0076244 to the Water Resources Board, predecessor to the Environmental Quality Board. The appeal wasresolvedby the Board's eatryofanagreed order dated March 12, 1991, 2nd resulted in a corresponding modificationofSW/NPDES Permit No. WV0076244. The agreed order is anached hereto Exhibit 2.
13. Byletterdated January 11, 1995, DEPextended the expidatreoafStW/iNPoDEnS Permit No. WV0076244 from Jaauary 11, 1995, to Jamuary 11, 1996.
14. By letter dated January 3, 1996, DEP conditionally extended the expiration date ofSW/NPDES Permit No. WV0U7624t4o September 11, 1996. Such extension was conditioned `upon Defendant providing DEP with additional information regarding its Dry Run Landfill.
15. By lener dated August 22, 1996, DEP extended the expiration date of SW/NPDES Permit No. WV0076244 to December 11, 1996.
16. In additiontotheDryRunLandfill, Defendantalsoownsandoperatesthe `Washington Works facility whichproduces plastic and acrylic resins. On September 30, 1994, DEP reissued NPDES Permit No. WV0001279 to Defendant for its Washington Works facility, such permit authorizing Defendant to discharge a specific amount and typeofpollutants directly into the Ohio River. NPDES Permit No. WV0001279 is attached hereto as Exhibit 3.
Violations of ConditionCsONUotNATllIowable in State Waters 17. Plaintiff hereby realleges and incorporates the allegations set forth in paragraphs 1-16 abovaes if fully restatedherein.
s
:
00aIan
EIDOI2739
A.
N
.
18. Pursuant to the Requirements Governing Water Quality Standards (*Water Quality
Standards"), 46 CSR 1 HACER 3 (1996), entitled "Conditions Not Allowable in State Waters,"
SNtoateseswhaalglec,auisndeustthreiraelinwaosrtem,atoerrioatlhleyrcownatsrtiebsutperetsoe.n.t i.ndaisntyinocftltyheviwsiabtleersfolfoatthineg
osrlusdegtetlebaabnlekssoolindst,hseubspoernodmed.
so..lidos,]dsocrusm,infotahme,viocrioniiltyy
slicks
of the
.
w.at. e[rds]e.po.si.ts[oorr]
[d]istinctly visible color.
19. OnMarch 23, 1995, Cynthia J. Musser, Inspector, EnvironmentalEaforcement,
DEP, inspected the Dry Run landfill. During the inspection, a flow of very black and odorous
leachatewasemanatingfrom thesubject landfilland enteringDryRun,thusdiscoloringDryRun
and imparting an odor thereto.
20. On May 3, 1995, Inspector Musser conducted an inspection of Defendant's Dry
RunLaosn `Theleachate fromthe landfill remainedodorousandblack,andthedischargefrom
thesubject andi intoDryRunwasodorous, turbid,andgreenwithalgae, thusdiscoloringDry
Run and imparting an odor thereto.
21. OnAugust 13, 1996, Inspector MussercondictedaninspectionofDefendsat's Dry
Run Landfill. The leachatefromthe landfill remained odorous and black, and the discharge from
the subject landfill into Dry Run was odorous, turbid, and green with algae, thus discoloring Dry
Run and impartingan odor thereto.
22. On August 20, 1996, Inspector Supervisor Charles A. Moses, Inspector James C.
Laise, Jr., and Inspector Musser conducted a river patrol of the Ohio River in the vicinity of Defendant's Washington Works facility. During the river parol, the inspectors sampled deposits
onthebottomoftheOhio Riverandalong theriver'sbanksimmediatelybelowOutfall 002of the
6 009505
EID012740
Washington Works facility. The sample contained beads made of Nylon, Delron and Teflon - all materials manufactured at the Washington Works faciliy.
23. During the August 20, 1996, Ohio River patrol, the inspectors likewise sampled deposits along the banks of the Ohio River immediately below Oufall 003 of the Washington `Works facility. The sample contained beads made of Nylon, Delron and Teflon- all materials `magufactured at the Washington Works facility.
24. During the August 20, 1996, Ohio River patrol, the inspectors sampled deposits onthebottofothme OhioRiverbelowOutfall005ofthe Washington Works facility. The bottom deposit sample yielded beads which contained Teflon and Delron - both materials manufacrured at the Washington Works facility.
25. During the August 20, 1996, Ohio River patrol, the inspectors observed floating solids onthe OhioRiverandalongthebanksof the OhioRiver whichwere determinedtobe 2 mixture of Teflon and wax and which bad been discharged from Outfll 005ofthe Washington Works facility. The floating solids were located along the West Virginia river bank of the Ohio River for approximatelyone-halfmile below Outfall 005.
26. On March 23, 1995, May 3, 1995, and August 13, 1996, Defendant was in violation of Water Quality Standards 46 CSR 1 3, (1996) "Conditions Not Allowable in State Waters," bydischarging aturbid flowfromDryRunLandfillintoDryRun,such flow constituting the discharge of distinctly visible colors, turbid conditions, and odors in waters of the State.
27. On August 20, 1996, Defendant was in violation of Water Quality Standards, 46 CSR 1 3, (1996) "Conditions Not Allowable inStateWaters," by discharging beadsofmaterial
7
069585
EIDO12731
:
manufactured at Defendant's facility, from three separate discharge points, into the OhioRiver,
waters of the Sate. Such deposition of material constituted the illegal discharge of seleable
solids into waters ofthe State as well as the impermissible deposition of materials on the`bottom
ofthe subject stream.
28. On August 20, 1996, Defendant was in violation of Water Quality Standards, 46
CSR 1 3, (1996) "Conditions Not Allowable in State Waters," by discharging a floating or
suspended mixtureof Teflon and wax, materials manufactured at Defendant's `Washington Works
facility, into the Ohio River. Such discharge constituted the illegal placement of distinctly visible
floating or suspended solids into watersofthe sate.
Fallure to Prevent Run-oCffOaUnNdTCoIlOlect and Treat Leachate 29. Plaintiff hereby realleges and incorporates the allegations set forth in paragraphs 1-28 aboveas ffullyrestatedherein.
30. Solid Waste Management Regulations ("SWMR") 47 CSR 38 4.8.1.band d
(1996), entitled Leachate Management," state:
o4f.t8h.e1f.abcAilaityylwihqeuriedwachtiicvhecwoamsteesdiinscpoonstaalocptewriatthiwonasstaereoorcaccucrurmiunlgamtuessitnbeahpaonrdtlieodn aDElPe]acihnatweraintidnpgr.operly treated . . .unlessotherwiseapprovedbythedirector[of
operations. 4.8.1.d Inthe caseofan industrial landfill, the leachate collection and treatment
facilitymustbeinplaceand operablepriortothecommencementoflandfill
005507
EIDO12742
31. Solid Waste Management Regulation, 47 CSR 38 4.5.2.b.A. (1996), ented "Run-on Control System, sates:
(an)d Pmaeirnmusiitn:s ofall SWLFs [solid waste landfill] must design, coastruct, operate,
(di)sposAalraurae-aoinnccloundtirnogltshyeasctteimvecappoarbtlieonooffptrheevSenWtLinFg dfulroiwngopnetoakadniyscphaarrtgeoffrtohme atleast a 25-year, 24-hour stom.
32. DuringaMay 16,504, field reviewofthe Dry Run Landfill conducted by John 3 G. Britvec, Geologist, OffofiWacteer Resources, DEP, and laspector Musser, Mr. Britvec and A InspectorMusserobservedthatDefendantbadnotnsalled asystem which wouldcollectaodtreat
leachate, 2s required by SWMR, 47 CSR 38 4.8.1(.d55).
33. Duringbe May16,1994, field review, Mi. Bitesaod ospecor Muss observed aeDetediot1d oc sled iverson dices thefly, a seidbySWMR, 47 CSR 38 54.5.25.A. (1996).
34. During the May 16, 199, id review 1d on ite occasions, DEP personnel advised Defendant's managerial personnel thta leachate collection system and diversion ditches must be installed at the subject landfill
35. DutrheiMarnch2g3, 1995, insopftheeDrcyRtuniLaondsnill Defenddiadnnott Jp have acollectionsystemortreatmentfucilty tocollec ortreat leachategeneratedbythe DryRun " Landfill, as requirbeyd SWMR, 47 CSR 38 4.8.1.d (1996).
36. During the March23, 1995, inspection, Defendant did pot have diversion ditches in place tore-directsurfaceflowofrun-on awayfrom theworkingsurfaceofthe landsil, as required by SWMR, 47 CSR 38 4.5.2.b.A (1996).
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EIDO12743
'
37. Upon information and belief, in April 1995, Defendant constructed two diversion
ditches above the Dry Run Landfill to prevent run-on from flowing across the landfill
38. During the August 13, 1996, inspection of the Dry Run Landfill the diversion
a ditch on the upper sideofthe landfill was not properly maintained by Defendant, as required by
SWMR, 47 CSR 38 4.5.2.b.A. (1996).
7
39. During the August 13, 1996, inspectionofthe Dry Run Landfill the facility did
5 aot have eschae collection system installed, as required by SWMR 47 CSR 38 4.8.1.4.
(1996).
40. From May 16, 1994, until August 13, 1996, and upon informationandbelief, to 4} the present date, Defendant has been in violation ofSWMR 47 CSR 38 4.8.1.4. (1996), for I failuretoinstal aleachatecollectionsystem.
5 , 41. From May 16, 1994untilApril 1995,Defendantwasinviolation ofSWMR47 JS CSR 38 4.5.2.b.A. (1996),forfailure to design, construct and operate a run-on control system. 42. On August 13, 1996, and, upon information and belief, to the present date, \ Defendant was and is in violationofSWMR 47 CSR 38 4.5.2.b.A. (1996), for failure to maintain a rua-on control system.
COUNT II Failure to Notify of Violations
43. Plaintiffhereby realleges and incorporates the allegations set forth in paragraphs 1-42 aboveasiffullyrestatedherein.
44. Solid Waste Management Regulation 47 CSR 38 4.8.1] (1996), specifying notification requirements, states:
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EID012744
S
s`tTehpespteormbiettteaekemnusitf.i.m.me[doi]apteeraltyinoontoiffythteheldeiarcehcattoert(roefatDmEePnt] faancidlidteysucrnidbeer rtehmisedriualle
tchaenno[tfepdreeravle]ntCtlheeafnaciWliattyefrroAmct.. a.n[dv)itohleatirnugletsheatnedrmsreogfulitastipoenrsmitp,ro(mSuWlgMaRt]e,d
thereunder, thereunder;
or or
W. . ..
Va. Code 22-11 and [cJausing surface water
the rules pollution
and regulations or groundwater
promulgated degradation,
contamination, or pollution.
Further, Solid Waste Management Regulation 47 CSR 38 4.8.L.] (1996), states:
st`eThpespteorbmiettteaekmuesnt imif.m..e(dtilahetfealcyilniottyiifsytgheendeirraetcitnogra[qoufaDliEtPyo]ranqdudesacrniobtfelreieamcethdaityael. thatexceedsthe designcapacityofthetreatmentsystem.
45. Defendantbas failed to notify DEPthatthe operatofitohne DryRunLandfill
exceeded the design capacityofthe landfills treatment system and that, as a result, such facility was in violation of the terms and conditions of the SW/NPDES permit, the WPCA, and
regulations promulgated thereunder.
46. Uponinformaantdbieloienf, Defendantcontinuestofail to notify DEP whenthe qualityofthe leachate generated by the Dry Run Landfill exceeds the capacityofthe treatment system, thus causing violations of established discharge limits into Dry Run.
47. On numerousoccasionsDefendanthasbeenand,uponinformaandtbielioefn, still
is in violoafStWiMRo4n7 CSR 38 4.8.1 (1996), for failure to notify DEP when operations
of its facility exceeded the design capacity of is treatment system.
COUNT IV Failure to Adequately Compact 48. Plaintiffhereby realleges and incorporates the allegations set forth in paragraphs 1-47 above as if fully restated herein.
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EIDO12745 .
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P) gre
49. Solid Waste Management Regulation 47 CSR 38 4.6.2.0.C, "Layering 1nd
Compaction," (1996) provides:
Solid waste must be placed in layers not exceeding two (2) feet in depth and ccoommppaaccttiendgwiabtihliatym. inimum of three (3) passes with . . . equipment of [effective]
50. During the May 3, 1995, inspection, Defendant was compacting the wastes in the
Dry Run Landfill in layers exceedingtwofeetindepth. 51. During the August 13, 1996, inspection, Defendant was continuing to compact the
`wastes in the Dry Run Landfill in layers exceeding two feet in depth.
52. On May 3, 1995, and August 13, 1996, and upon information and belief, to the
present day, Defendant violated and continues to violate SWMR, 47 CSR 38 4.6.2.2.C. (1996),
"Layering and Compaction," by failing to properly compact the wastes disposed ia the Dry Run
Landfill.
Changing Composition of WCaOsUteNTWiVthout Proper Authorization 53. Plaintiffereby realleges and incorporates the allegations set forth in paragraphs 1-52 aboveasiffullyrestatedberein.
54. Section G.1oftheSW/NPDES Permit No. WV0076244states:
'OWnVlOy07t6he24w4aasntedimnatthereilaelsersdpaectiefditehde i1nst(dSaWyo/NfPMDaErSc]h P1e9r8m8imtayApbpelidciastipoonsNeiod.n the landfill
55. Section C.4 of SW/NPDES Permit No. WVOU76244 stats:
This Permit may be modified, revoked and reissued, suspended, or revoked for
cause. The filing of a request by the permittee for a permit modification,
5
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069.67
EID012746
=
revocation, anticipated
and reissuance noncompliance,
doorersenvooctasttiaoynaonryanpeormittciondfiotiifoncp.laannetdcihaongens
or
(Emphasis added.)
$6. By leter dated September 14, 1994, Defendant informed DEP that it had changed. the composition of wastes being disposed at its Dry Run Landfill.
57. During mid-1994, Defendant did dramatically alter the composition of wastes being
disposed at the Dry Run Landfill. wot Fo
58. From mid-1994 through, upon information and belief, the present date, Defendant hasdisposedandcontinuestodisposeofwasteattheDry RunLandfill,thecompositionofwhich differs substantially from that which was specified in Defendant's SW/NPDES Permit application 20d subsequently authorized in the SW/NPDES Permit No. WV0076244 without having obtained prior approval through apermit modification, in violationofSW/NPDES Permit No. WV0076244 G.1.
COUNT VI Failure to Properly Operate and Maintain Facility
59. Plaintiffhereby realleges and incorporates the allegations set forth in paragraphs
1-58 above asiffully restatedberein.
.
60. SectionD.1ofSW/NPDES Permit No. WV0076244, entitled "Proper Operation
and Maintenance," states:
Tsyhsetepmesromiftttereshealalaattnadmlcloenttinrmoeltsp.r.o.pwehrilcyhoaperreaintsetaanlldedmoairnutsaiendbalylthfaecpielirtmeisttaened to achieve compliance with the conditionsofthis permit.
;
13
i egos EIDO12747 :
,
|
i
ob
47
wt
\
6l. On May 1, 1995, upon information and belief, 3 drain valve for he
sedimentleachate pond located at the Dry Run Landfill was opened to lower the levelofthepond.
The drain valve remained open until May 3, 1995. From May 1 until May 3, 198,34 a result
of Defendant opening the drain valve, an indeterminate amount of untreated leachate
p 5
discharged directly into Dry Run.
62. During the May 3, 1995, inspection, the discharge/sediment pond was
approximately three (3) feet ower than the ponds normal elevation. This condition resulted from
Defendant' failure to correctly operate such pond.
63. From May 1 to May 3, 1995, Defendant was in violation of SW/NPDES Permit No. WV0076244, D.1, by failing to properly maintain and operate the drain valve on its sedimeateactate pood.
Failure to Use a LeachatCeOLiUnNerTaVnIdI Leak Detection System 64. Plaintiff bereby realleges and incorporates the allegations set forth in paragraphs 1-63 aboveasiffullyrestatedherein.
65. Solid Waste Management Regulati4o7n CSR 38 4.8.3.c.B. (1996), sexing forth requirements forsurficeimpoundment, statesthatsurface impoundments, such as.the sediment/leachate pond at the Dry Run Landfill:
2mde0utdsecttabieolcnesaokyndssetttreeucmct.tieoSdnuwrsifytashcteealimimanpesorpusrynesdstmceermniobtesfdciaumrnrien[nitSlmWyuiMmnRo]ufmsteuwtshota(et2i)dtlohiennreobrteshaacnlvdoesleaildneeoarrks. draettreoofiftttheidstorucloen.form to this section within six (6) months following the effective.
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EIDO12748
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66. The Defendant has failed to construct a lining for its sedimeat/leachate pond at the Dry Rua Landfill
67. The surface impoundment used by Defeodant to treat leachate has not been closed or rewoficed to properly treat and collect the leachate and does not use a leak detection system.
68. Defendant bas violated SWMR, 47 CSR 38 4.8.3.c.B. (1996), by operating the Dry Rua Landfill without retrofitting the surface impoundment with a liner system and leak. detection system.
69. Uponinformationand belief, Defendant continues to violate SWMR, 47.CSR 38
4.83.c.B. (1996), by operating the Dry Run Landfill without retrofitting the surface
impoundment with a liner system and leak detection system.
Violations
of
COUNT VII Numeric Water Quality
Standards
70. Plaintiff hereby realleges and incorporates the allegations set forth in paragraphs 1-69 above asiffully restated herein.
71. Section C.12 of SW/NPDES Permit No. WV0076244, "Water Quality", staes: `qTuhaeleiftfylsuteanntdcaorvdesreaddbopytetdhibsyptehremi(tEnmvaiyronnomtenctaaulseQuaalviitoyl]atBioonarodf.applicable water
72. Section G.8ofSW/NPDES Permit No. WV0076244 requires Defendant to sample: Dry Run approximately one thousand feet (1000 .) downstream of Outlet 001 for several water quality standard parameters and submit such results on the "Monthly Stream Sampling Report Form."
15 03ALY
EIDO12749
73. The water quality sndard for the conceatraion of tol iron in Dry Rua established in the Water Quality Sndards, 46 CSR 1, App. E.. 8.15 (1995), is 1.5 milligrams of iron per 1.0 liter ofwater (1.5 mg/l).
74. The water quality standard for the concentration of manganese in Dry Rua established in the WaterQuality Standards, 46 CSR 1, App. E., 8.17 (1995), is 1.0 mg/l.
75. Results submitted by Defendaonnt its Monthly Stream Sampling Report Forms for May, 1995, July 1995, September 1995, Jamuary 1996, and March 1996 showed the stream contained 4.8 mg/l, 1.7 mg/l, 1.9 mg/l, 6.0 mg/l, and 3.7 mg/loftotal iron, respectively - all exceeding the 1.5 mg/l total iron water quality standard.
76. Results submited by Defendaoant its Monthly Stream Sampling Report Forms for February 1995, April 1995,andJuly 1995, showed thestreamcontained 2.5 mg/l, 1.1 mg/l, and 1.9 m/l of manganese, respectively - all exceeding the 1.0 mg/l manganese water quality standard.
77. Onat least eight separate occasions, Defendant has violated SW/NPDES Permit No. WV0076244, Section C.12, "Water Quality," by exceeding numericwater quality standards.
78. Upon information and belief, Defendant continues to occasionally violate SW/NPDES Permit No. WV0076244, Section C. 12, "Water Quality," by continuing to exceed the numeric water quality standards.
COUNT IX Violations of Discharge Limitations
16
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000s 55
EID012750
79. Plaintiff hereby realleges and incorporates the allegations set forth in paragraphs 1-78 above asiffully restated berein.
80. Section E.2.a ofSW/NPDESPermitNo. WV0076244, entitled "Reporting, states:
PMeornmiittotreiengshRalelposrutbm(iDtMeRa)chimndoinctathinagcicnotredrinmgstooftchoenceennctlroasteidonf,oramnadt/,ora qDuiasntcihtairegs,e
the values determined
otof bteheinctohnestpiltaunetntesfflluiesntie(ds)i.n
Part
A.1
[of
the
Permit]
analytically
81. Section A.l of SW/NPDES Permit No. WV0076244, entitled "Discharge Limitations and Monitoring Requiremeats," establishes amaximumdaily discharge limit for total
suspended solids ("TSS") as 60 mg/l forOutlet001.
8. Section A.l of SW/NPDES Permit No. WV0076244, eatitied "Discharge Limitations and Monitoring Requiremeats," establishes a maximumdaily discharge limit for total
iron 257.0mg/landan average monthlydischargelimitfortotaliromas 3.5mg/l.
83. Defendant's required Discharge Monitoring Reports ("DMRS") that were seat to DEP for January 1995, May 1995, and July 1995 show the effluent of the Dry Run Landfill contained TSS concentrationsof64 mg/l, 190 mg/l, and 75 mel, respectively - all exceeding the maximum daily discharge limit for TSS concentrations set forth in SW/NPDES Permit No. `WV0076244 A.1. Copiesofthe DMRs for 1995 and 1996 are attached hereto as Exhibit 5.
8. The DMRs submited by DefenfdoraMnaty 1995 and May 1996 showed the efflueatoftheDry RunLandfillcontainedtotalironconcenotf8r.7amtg/ilaondn3.s6 mg/l,
respectively -bothexceeding theaveragemonthly discharge limitfortoaliron concentrations set forth in SW/NPDES Permit No. WV0076244 A.1. Seg Exhibit S.
1 000025
EIDO12751
85. Upon atleast five separate occasions, Defendant has violated SW/NPDES Permit No. WV0076244, A.1, "Discharge Limitations and Monitoring Requirements," by exceeding the oaly two discharge limitations that were specifically established in SW/NPDES Permit No. WV0076244.
86. Upon information and belief, Defendant continues to violate SW/NPDES Permit No. WV0076244, A.1, "Discharge Limitations and Monitoring Requirements, by exceeding the only two discharge limitations that were specifically established in SW/NPDES Permit No. WV0076244.
COUNT X
Duty to Comply
87. Plaintiffherebyreallegesandincorporatesthe allegationssetforthinparagraphs 1-86aboveasiffully restated herein.
88. SectionC.1.a of SW/NPDES Permit No. WV0076244,entitled "Duty to Comply" states:
T`nhoencopmeplrimaintcee comnustsittutceosmaplviyolawtiitohnofaltl heco[nfdeidteiroanlsCloefanthWiasteprerAmcitt]. andP(eSrtmaitte WPCA] and is grounds for enforcement action."
89. Issuance of SW/NPDES Permit No. WV0076244 was based, in part, upon information submitted by Defendant with SW/NPDES Application No. WV0076244, as well as informationcontainedincorrespondence from Defendant dated August 10, 1987, September 15, 1987, March 1, 1988, April 14, 1988, March 16, 1989, and May 9, 1989. A copyofSW/NPDES Application No. WV0076244, dated August 10, 1987, is attached hereto as Exhibit 6.
18
5
000555 EIDO12752 z
:
90. Inthe information submitted by Defendant on August 10, 1987, Defendant stated
that the surfaceofthe Dry Run Landfill would be crowned to provide 3 1% to 2% slope to
eliminate ponding on the surfaceofthe landfill and to direct surface waterto diversion ditches on
cither side of the landfill. Ses Exhibit 6, page 7.
91. Inthe information submitted by Defendant on August 10, 1987, Defendant stated that compaction would be provided by a dozer operator who would spread the waste material in Layers up to two feet thick. See Exhibit 6, page 7.
92. DutrheMiarnch2g1, 1995,inspection,Defendantwasnotproviding a 1%to 2% crown to prevent ponding on the surface of the landfill as stated in Defendant's SW/NPDES Application No. WV007624.
93. DutrheiMarnch2g1, 1995, inspection, Defendantwasnotadequatelycompacting the wastes at Dry Run Landfill, as staied in Defendant's SW/NPDES Application No. WV0076244.
94. During the May 3, 1995, inspection, Defendant was not providing a 1% to 2% crown to prevent ponding on the surface of the landfill, as stated in Defeadaat's SW/NPDES Application No. WV0076244.
95. DuringtheMay3, 1995, inspection, Defendant was not adequately compacting the wastes at DryRunLandfil, as stated in Defendant's SW/NPDES Application No. WV0076244.
96. DutrheAiugunst1g3, 1996, inspection, Defweasnpodtpraovindintga 1%to 2% crown topreventpondingonthesurfaceofthelandfill,asstatedinDefendant's SW/NPDES Application No. WV0076244.
19
.
000355
EIDOI2753
v
97. During the August 13, 199, inspection, Defendantwas not adequately compacting
the wastes at Dry Ru Landfill, as stated in Defendant's SW/NPDES Application No.
WV0076204.
98. Upon at least six separate occasions, Defendant bas violated SW/NPDES Permit No. WV0076244 C.1, by failing to comply with every condition of the subject permit.
99. Upon information and belief, Defendant contimues to violate SW/NPDES Permit
No. WV0076244 C.1, by failing to comply with every conditionofthe subject permit.
PRAYER FOR RELIEF
WHEREFORE,pursuantto West Virginia Code 22-16, 22-114, 2-11-12, 22-11-15, 2211-22, 2215-5, 22-15-10, 20d 22-15-15, SW/NPDES Permit No. WY0076244 C.1 and
C.14, and otherwise, Plain, Laidley Eli McCoy, Director, West Virginia Division of
EnvironmentalProtection,praysforanOrder ofJudgment againsttheDefendant, E. I. DuPont de Nemours & Company, that:
1. Prelimicarily and permancaly enjoins Defendanta its Dry Run Landfill from
violating the Water Pollution Control Act, W. Va. Code 22-111 to 28, the regulations
promulgated thereunder,theSolid Waste Management Act, W. Va. Code 22-15-1 to -20, the
:
rulesandregulationspromulgatedthereunder,SW/NPDESPermit No. WVO0076244,andanyand
al othereavisonmenltawasl,rules,orregulationswhichDefendantmightbecurreatly violating;
2. PreliminaryandpermaneatyenjoinstheDefendantfromplacingwastematerials attheDryRunLandfill untilsuch timeastheDefendantbasinstalled aproperly constructed
20
.
EIDOL27S4
069345
:
landfill and leachate treatment facility, including a a lined impoundment, to prevent the current
and future degradationofthe waters and soilsofthe State of West Virginia;
3. Orders Defendant to constructa systemofditches aod other permanent, mechanical
devices to prevent water from running onto the Dry Run Landfill and mixing with the waste
deposited therein;
4. Levies acivil penalty nott excesd $10,000(tea thousand dollars) per day against
Defendant, as specifically authorized by the West Virginia Water Pollution Control Act, at W. Va. Code 22-1122, for each of the Defendant's violations of SW/NPDES Permit No.
WV0076244, the West Virginia Water Pollution Control Act, and the accompanying rules and
regulations;
5. Levies:civilpenalty nottoexceed$25,000(twetahoutsayndd-ollfarsi)pevrdeay againstDefendant,asspecifically authorizedbytheWestVirginiaSolid WasteManagementAct, at W. Va. Code 22-15-15(d), for eachofthe Defendant's violations of SW/NPDES Permit No.
WV0076244, the West Virginia Solid Waste Management Act, and the accompanying rules and
regulations;
6. Leviesacivil penaltynotto exceed $10,000 (teathousanddollars)perday against Defendant, asspecificallyauthorized by SW/NPDES Permit No. WV0076244 C.14(2), for each ofthe Defendant's violationsofSW/NPDES Permit No. WV0076244, the federal Water Pollution
Control Act, the West Virginia Water Pollution Control Act, and the accompanying rules and
regulations;
21
&
g
EID012755
=
0G0R1sE
1 --
.
+
7.
Awards to Plaintiiftsf costs and disbursements, including reasonable attorneys fees,
incurred in this action, as specifically provided by the West Virginia Solid WasteManagement
Act, at W. Va. Code 22-15-15(g); and
8. Awards such further relief that this Honorable Court deems appropriate.
BY COUNSEL:
Respectfully submitted, LAIDLEY ELI McCOY, Director, West Virginia Division of Environmental Protection
MATTHEW B. CRUM, DEPUTY CHIEF SCOTT D. GOLDMAN, ASSISTANT CHIEF OFFICE OF LEGAL SERVICES WEST VIRGINIA DIVISION OF ENVIRONMENTAL PROTECTION 1356 Hansford Street
Charleston, West Virginia 25301 Telephone: 304-558-9160
2
000317
EID012756
Co
ORY RUN LANDFILL LEACHATE COLLECTION AND TRANSPORT To WASHINGTON HORKS (Letter, W. M. Stewart to Barbara S. Taylor, dated11/8/96)
BCC: IP.n MTucrGne:e, Legal, 08065-1
TUHR. .D.LiRtamtsleey
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WW.l A.
HM eloSotnewa/rtL. Kirschner
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T In TTarn:ant
JRL. JL.. MRietncthienyk
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hew: 15633-3
0005319
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OomSueeee etosps
November 8, 1996
CERTIFIED WAIL
RETURN RECEIPT REQUESTED
Charleston, W 25311-1088 Ms. Barbara S. Taylor, Chief
Office of Water Resources WV Division of Environmental Protection 1201 Greenbrier Street
Dear Hs. Taylor: RE: Letter, L. E. McCoy to W. M. Stewart, dated October 15, 1996
. syste described in this letter will be used until design modifications generated ThatisDrlyetRtuenr Lisandtfoililnfoanrdm ytoruanospforoturitplatnosWatsohicnogltloenctWolrekaschaftoer treatment in our bio-oxidation wastewater treatment Tacility. The interim csopmepclieftieedd ainnd oaurreDriyn RoupneraLtainodnf.ill permit renewal application have been
Currently, approximately 15 - 20 thousand gallons per day of
landfill leachate is collected in a leachate collection system servicing the
sbeoptatroamteporptiipeondiosfchtahregeasctitovea fislulrfaacreea.inpoThuinsdmesnytste(mupdprearinpsandt)hrofuogrh three
striexa-timnecnht.pipeWetphratopwoislel tgorarvoiuttye dthreainthrienetoeaxnisatbionvge-dgirsocuhnadrge50,l0i0n0esgailnltaona
modular collection tank to be located above the upper pond (refer to
bAtotTatc-htmoegnetthe1rfdoersilgoncatfiaocni)l.itatTeasnkasdsiemmebnsliyonast tahree 3s8i'te.x 38' x 4'9* and the
zzg
be clearedPrainodr ptroepearreecdt.ingThtehetatnaknk,wiltlhebearesaetaobnovae oonfe-tfhoeotupcpoemrpapcotneddwiclllay g
ptsaounbes-ltbsaabsiceolmiapzprepirsotexhdeimaaoftreeal1y6psr4a2i`uogrextog42a'lpvlaaincniezmseeidznet.stoefeIltfhwenielcclelsasbyaerbyas,suep.pgroarvtTeehlde btwyialnlk wbaellused "
galvanized 2* x 2* x 1/8" and 2" x 2* x 3/16" steel angle and galvanized
tension cables. A 10 mil geotextile material will be placed over the tension cables prior to installing the 20 mil HOPE tank liner. A photograph
of a typical modular tank is included as Attachment 2. Stormwater will be
routed around the tank into the upper pond.
EID010843
06030
.
@ iran
'
Ms. Barbara S. Taylor, Chief
-2-
November 8, 1996
to Washington orks for treatment primarily during daylight hours. transfer Athe3-HlPeacshuabtmeerssihbrloueghwelalpprpoumxpimwaitlellybe500moufneteetdofintswiod-eintchheuntadnekrgtroound
plastic pipe Just east of
to a 5,000 the closed
gallon tanker asbestos fill
truck area.
located at the The well pump
top of the hill, will deliver
between 50-60 gpm of flow and will take approximately 90 minutes to fill a
tank truck. We estimate three to five tankers per day will betransported
The 50,000 gallon collection tank is sized to provide two feet of
fitreweiblolardnotapdovewriflilllbedupruimnpgedthteo niitgshtm.inimTuhem ccaoplalceicttyioneacthankdawyiltlo beensure that inspected for leaks on a daily basis.
leachate
An NPDES permit modification request to process the through our site wastewater treatment facility will
collected be submitted
under separate cover letter.
proposed Wientreerqiuneslteawcrhiattteenpuampppirnogvaslysttoenprsoocetehdatwiwtehmaiynsbteaglilnatiloenachoafteour
collection and transport to Washington Works.
'
If you have any questions or need additional information, please
call me on 863-4271.
Very truly yours,
.
Attachments hew: 15633-2
W. H. Stewart
Sr. Environmental Control Consultant Washington Works
cc: OMsf.ficCeinodfy MEunvs.serEnforcement
JOofhfnicGe.ofBrWiattveecr Resources
$2
Div. of Env. Protection
Industrial Waste Section
2311 Ohio Avenue
1304 Goose Run Road
Parkersburg, WV 26101
Fairmont, WV 26554
WMaitchearelReAs,ouZrecfeos/Waste Management
i
Environmental Enforcement 1356 Hansford Street
Charleston, WV 25301-1401
0007
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`Governor
DIVISION OF ENVIRONMENTAL PROTECTION
No1v0emMbcJeurnk2i7n, Ro1a9d96 Nitro, WV 25143-2506
wore tu uecr, mo, OIRECTOR
DMWuraf.so.HhniH..tngDtaDovanivdidWoRrRakmmssesy,ey, SSuuppeerriinntteennddee:nt
orcore Srivpoorsun2ey1303
Post Office Box 1217
Parkersburg, West Virginia 26102
Dear Mr. Ramsey:
I vas very pleased that ve could reach a settlement in
Program concept ith Governor Undervood's staff. wisi sisi ine principal on
opportunity,
the Dry Run Landfill issue. assuming I will, to discuss
As the
soon as I have small business
an loan
abrordayngoef athmeeeptrionpgo:sal. Once that occurs, I will call you and
pErnovgirraoAmns.meinttIafsltwaenPrdaosjreencotws),ucwctiehlselsf$u5ble0,0ai0nv0aielSsaEtbPalbel(iSstuohpipnclgaepmtiehtneatlailprzoegrtahme,
loan
that
will this
constitute an end to DuPont's commitment. loan program should not be adopted, I will
In the event that contact you to
decide how to redirect the Supplemental Environmental Project
funding in the manner we have discussed. work with you directly to develop the new
In this case, I will SEP, including other
funding opportunities from appreciate your assistance
DuPont as per our discussions. I in this matter. Should you have
do
questions, please feel free to call me at 304-759-0515.
Singhrely, g7
idley Z McCoy, "Ph.D. Directo;
LEM: jrb
ce: Matthew crus, Deputy Chief, oLs
a
CARS
EID012824
December 13,199
rPj AeGg Ere vormae ra Marmagiemeent nc [fPrararcriar.fi2eA 19103
Pc
OMsn.-SScaernaehCCoaosrpdairnator US. Environmental Protection Agency
8R4e1giCohnes3tnut Philadelphia.
PBuAild1i9n1g07
Subject:
Field Trip Report Preliminary Assessment
TDD Number 03-9609.0013 Dry Run/N. Fork Lee Creek Bovine Site
`Washington, Wood County, West Virginia
Dear Ms. Caspar:
PRC Environmental Management, Inc. (PRC), is submitting the enclosed trip report for the Dry Run/N. Fork Lee Creek Bovine site under the Site Assessment Technical Assistance (SATA) contract labor hour pool. Contract Number 68-55-3002. If you have any questions about this report or need additional
information, please contact me at (215) 656-8703.
Sincere!
~o SA
PKreovjienctSMeoannager
Enclosure
Gc: CBialtleHBargoecl.k,PPRRCC SATA Dedicated Team (cover leer only)
005.07
@--=" USFW C15
PRELFIIEMLIDNATRRIYPARSESPEOSRSTMENT WADSRHYINRGUNT/ONN.,FWOOROKDLECEOUCNRTEYE,KWBEOSVTINVEIRSGIITNEIA
Prepared for: U.S. ENVIRONMENTRAegLioPnR3OTECTION AGENCY
P8hi4l1adCehlepshaiaa,utPBAuil1d9i1n0g7
DEaPtAe PRreegpiaorned `TCDonDtraNcutmNbuemrber Prepared by TOenl-eSpcheonneeCNoourmdbienartor
D3ecember 13. 1996 6083-.5956-0390-000213 PRC Environmental Management, Inc 1(K5ev)in65S6c-o8m7)03 (Sa1r5a)h 5C6a6s-p3a2r83
00:25
USFW C15
TABLE OF CONTENTS
Section
Page
10 INTRODUCTION
.
3
1
20 BACKGROUND
.
.
.
1
30 SITE ACTIVITIES
.
.
1
40 DATAEVALUATION .
et sen eeraery eaves
n
50 CONCLUSIONS AND RECOMMENDATIONS
srtaerneaeeaens 12
Appendix A SITE PHOTOGRAPHS B SAMPLE CHAIN-OF-CUSTODY RECORDS LANCASTER LABORATORY SAMPLE ANALYSIS REPORT
Bigure
I 2
FIGURES
SieLocatonMap .......... SampleLocationMap ........
rodraesesseryios soervas
Page
3 wae 6
Table
| 2 3 4
TABLES
Page
SamandpAnallysiis Sunmmgary
vans
correiaae
7
Field Measurements...
oes
ross
n
Summary of Laboratory Analytical Results (Aqueous Samples) -...
3
Summary of Laboratory Analytical Results (Sediment Samples) ............ 13
USFW 015!
;
000.29
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10 INTRODUCTION
PRC Environmental Management, Inc. (PRC), was sked by the U.S. Environmental Protection Agency (EPA) to conduct 2 preliminary assessment at the Dry Run/N. Fork Lee Creek Bovine sit. in Washington, Wood County. West Virginia. The work was conducted under Contract Number 68-553002, Technical Direction Document Number 03-9609-0013. The purpose of the preliminary assessment was 10 investigate a citizen's complaint that hazardous materials are presen in the surface water and sediments of Dry Run, a ibutry of the North Fork of Lee Creek, a wibuary to the Ohio River.
20 BACKGROUND
Mr. Wilber Tennant, the cirizen who placed the complaint, claims that contaminants are discharging into Dry Run from 2 landfill owned by the E. I. DuPont Company (DuPom). Dry Run flows across Mr. Tenant's land befor it discharges to the North Fork of Lee Creek. Mr. Tennant raises cae for beefonhis landandhiscadritnkfreom Dry Run. Mr.Tennantallegesthatthenumerousdeaths, blindness, and other illnesses suffered by his herd are directly acributable to the comaminans in Dry Run. He also aaributes someofthe health-related problems experienced by membersofhis family to
these contaminants
3.0 SITE ACTIVITIES
The following summary describes field activities conducted to investigate Mr. Tennant' allegations.
Qstober15,1996
`At about 1000 hours. PRC represeniatives Mr. Kevin Scon and Ms. Alicia Shultz arrived at the West Virginia Deparment of Natural Resources (WVDNR) in Parkersburg, West Virginia, where they met with Ms. Cynthia Musser. an enforcement officer for the West Virginia Deparument of Environmental Protection (WVDEP). The PRC personnel reviewed the sute's files perining to the Dry Run landfill while awaiting the arrival of EPA Region 3 representaive, Ms. Sarah Caspar. The Dry Run Landsil, as determined by the file review, is an active industrial solid waste landfill owned and operated by DuPont and the potential source of contamination entering Dry Run. The landfil is used by DuPont to
1
060-35
USFW 015
vontare
dispose of waste that DuPont identifies as nonhazardous waste generated a its Washington Works facility located in Washington Boriom, West Virginia. The landfill i located in Washington, West Virginia, about 10 miles south of the Washington Works facility. The approximate location of the Dry Run landfill is shown in the site location map provided 2s Figure 1. The landfill permit application filed with the WVDEP lis wastes deposited at the landfill as fly ash and bottom ash from the facility's nonhazardous waste incinerator, "biosolids" (fer cake) from the facilits industrial wastewater treatment operation, polyamides. acrylics. polyacetyl polyvinyl buryral, polyethylene terephthalate cardboard, and construction debris. `While at the WVDNR office, Mr. Scot placed a phone call to Mr. Tennant and arranged a meeting berween EPA, PRC, and Mr. Tennant at the Tennant residence. Mr. Scot also contacted Mr. Walt Stewart, environmental manager for the DuPont Washington Works facility, to gain access to the Dry Run landfill. During the conversation berween Mr. Scott and Mr. Stewart, Mr. Stewart indicated that DuPont would like to obtain split samples of all samples collected during the site assessment. He also requested a meeting at his office before EPA and PRC conducied the sie assessment. EPA representative Ms. Caspar arrived at the WVDNR Parkersburg office at about 1500 bours. After further review of the sute files, EPA and PRC persounel departed the WVDNR office and traveled to the Tennant residence in Washington, West Virginia. During the meeting between EPA, PRC, and Ms. Tennant, Mr. Tennant indicatedthatmore than200caulefromhis herd havediedinthepast 2 years from uninown health problems. He also said that be observed other dead wildlife n or near Dry Run, including, minnows, frogs, crows, raccoons, and deer. Mr. Tennant auributes the deathsofhis cale and the wildlife 10 exposure to the contaminants in Dry Run through ingestion and direct contact. While at the Tennant residence, Mr. Tennant showed the EPA and PRC personnel a cow skull that he had saved. Mostofthe teeth in the skull showed black suining and were easily removed fromthe jaw bone. According to Mr. Tennant, the discolorationofthe cow's teeth was indicative of fluoride contamination. He also indicated that mostofthe cate in his herd were or are affected similarly. EPA and PRC personnel traveled with Mr. Tennant and his daughter Amy to Dry Run, near its confluence with the North Fork of Lee Creek. Dead minnows were observed in Dry Run a short distance upstream from the confluence of the two water bodies. An oil-like sheen was also observed on the water when stream sediments were disturbed. A whitish-colored foam also was observed on the
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surface of the water at several locations along Dry Run. PRC took photographs of locations along the run that showed visible signs of conuamination. The photographs taken by PRC during the site assessment are included in Auachment A. Mr. Tennant used a video camera to collect additional photographic documentation of stream contamination. PRC observed that the condition of the stream continued to degrade as they moved upstream, closer to the landfill.
October 16,1996
`At about 0900 hours, EPA and PRC personnel met with Mr. Stewart at the DuPont Washington Works facility. Also present at the meeting were Mr. Daniel Weber, senior environmental engineer at the facility. Mr.Richard Kirschner, chemist and wastewater reaumeat plant engineer, and Tom Waldrea, supervisor of operations at the Dry Run landfill. During the meeting, EPA and PRC informed the DuPont personnel of the site assessment sampling objectives and schedule. Mr. Steward suggested that EPA and PRC personnel be shown the landfill and leachate ponds in the morning and rewurn after lunch to collect samples. Before traveling o the landfill, EPA and PRC personnel reviewed DuPon's files and analytical daa pertaining to the landfill and Dry Run.
At about 1100 hours, EPA. PRC. and DuPont personnel depared the Washington Works facility for the landfill. The Dry Run landfil is located off interstate Route 68, about 10 miles south of the DuPont facility. While at the landfilla tractor trailer load of fly ash was dumped onto the upper lit of the landfill. A heavy equipment operator, operating a bulldozer, spread the fly ash across the lit. The bulldozer operator appeared to be the only worker preseat atthe landfill during our visit.
Failure to meet lift height and compaction specifications were noted as permit violations in several of the inspection reports prepared by Ms. Musser forthesae. Based on PRC observations during the site visit, the current lift height appeared (0 be above the 2+foot permit limit. Additionally, the waste `material did not appear adequately compacted.
A sample of the wastewater treatment plant sludge was not obuained as planned because this material had been covered with fly ash and compacted before EPA and PRC personnel's arrival.
Downgradien from the landfill were two leachate collection ponds. A steady stream of leachate was discharging into the upper pond from a single oufall at the footofthe landfill. According to DuPont. the flow rate of the leachate was approximately 20,000 gallons per day, and the outfall accounts for
USFW 016:
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nearly all of the flow in Dry Run. An aeration system was in operation in the upper leachate collection pond. The system was powered by a diesel-powered air compressor, located west of the lower leachate collection pond. DuPont indicated that the aeration system is presently alternated between the upper and lower collection ponds. Mr. Weber indicated that DuPont was installing a permanent electrical system for continuous operation of the acration system. Photographs of the leachate collection ponds. and leachate discharge oudall are included in Appendix A
`At about 1265 hours, all personnel broke for lunch. DuPont agreed to meet EPA and PRC personnel back at the landfill at about 1400 hours.
After returning to the landfill, PRC personnel prepared to collect a sampleofthe leachate from the outfall atthe foot of the landfill Atabout 1500 hours, leachate sample L-1 wascollectedatthis location. A sample location map is provided as Figure 2. A suffcieat volumeofthe leachate was collected for multiple analytical parameters, including the target compound list (TCL) of volatile organic compounds (VOC) and semivolatile organic compounds (SVOC); and the target analyte lst (TAL) of metals and cyanide: and fluoride, formaldehyde, and sulfate. The sample was collected in containers specific to eachofthe analytical parameters or laboratory conducting the analysis.
tniialy, the PRC sampling team had difficulty obuining a viable sample for the VOC analysis due to a reaction between the leachate and the hydrochloric acid preservative in the sample vials. The reaction produced gas bubbles, which prevented the samplers from obtaining a sample with no headspace (as required by sampling and analytical protocols). The preservative was removed from the sample vials, and a viable sample was obained. Three separate laboratories were conmacted to analyze the samples for the various analytical parameters. Two EPA contract laboratory program (CLP) laboratories. American Analytical and Technical Services, Inc., and TMA/Skinner and Sherman Labs. Inc... were contracted to analyze for the TCL organic compounds and TAL inorganic compounds. respectively. Lancaster Laboratories, a PRC-subcontracted laboratory, was contracted to analyze samples for fluoride. formaldehyde. and sulfate. A summary of the sample collection information is presented in Table |
In addition to the laboratory<ontracted analytical parameters, the leachate samples were screeoed in the field by PRC for pH. temperature. and dissolved oxygen concentration. Due to an instrument
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malfunciion, however. pH measurements were not obained. Dissalved oxygen and temperature measuremens for the samples were recorded in the logbook and are summarized in Table 2.
At about 1540 hours, sediment sample SD-1 was collected from the upper leachate cllecion bank. A sufficient volume of sample was collected for the same set of analytical parameters as described above
AC 1600 hours, PRC personnel collected leachate sample L-2 from the discharge pipe of the lower leachate collection pond. The outfall isa routine sample collection station for DuPont ad is identified 25 No. 001 by a sign siaked in the ground near th outfall. From this location, the leachate flows a shor: distance through an underground culvert and empies io Dry Run, Sediment sample LD-2 was collected in the same vicinity as L2.
Background surface water and sediment samples were collected from a small unnamed wibutary of Dry Run, which converged with Dry Run several hundredfeetdownstream from Outfall No. 001. Aqueous sample BKGAQ and sediment sample BKGSEDI were collected at about 1730,
Berween 1800 and 1830 hours, PRC personne collected aqueous sample DRIKAQI and sediment sample DRIKSED! from alocaton along Dry Run about 1,000 feet downstreamofOuttall No. 001. "This location is a routine sampling station for DuPont. A thick film was observed on the surface of the creek at this location. A violet reaction occurred again in the sample bole when PRC personnel anempied o collect a water sample for VOC analysis. PRC emptied the preservative from the sample via and recollected the sample. Aqueous and sediment split samples were again provided to DuPor.
TABLE 2 DRY RUN/NF.IFELODRKMELAESEUCRREEMEEKNTBOSVINE SITE
[em repTia
Utica
Lene :PeECeolm;EonRY
[T r oxera Tr wre f J Ta owwn]]|
10 080729
USFW 0168
mart7
DuPont personnel were provided with split samples for eachofthe locations sampled by PRC. At
`about 1830 hours, all personnel
sample paperwork. All samples
departed the
were logged
site.
onto
PRC personnel returned to the
laboratory-appropriatechain-of
hotel
custody
complete
(COC)
the
records, identified with sampl-specific sample tags. and placed into coolers in preparation for
shipment to the appropriate laboratory. Copies of th EPA organic and the inorganic raffc report and
COC records are provided in Appendix B.
.
At about 0900 hours, EPAsPnidEpacsonnelreamedGED Waging Wors facil to
mer Stewie. Evt p Me:Seedh fing svecontuced he
previous day. Ms.Shu signed he goroploge1d06record the li warps, Sfficially relinquishing the samples to DuPGi.AFSbopt 3000 bouEPrAsaaTdPRC.persone departed the
Washington Works facility and traveled io the WVDNRoffice in Parkersburg, West Virginia, to gather
additional information about the site. Ms. Musser was unavailable, and the EPA and PRC personnel
departed shortly after their arrival. PRC personnel completed sample shipment preparations and traveled to the local Federal Express office to ship the samples. At about 1230 hours, PRC personnel departed Parkersburg, West Virginia to rem to Philadelphia, Pennsylvania.
4.0 DATA EVALUATION
`Table 3
the ste
summarizes
assessment.
fluoride, formaldehyde, and sulfate analytical data from samples
The results of anlyses of the samples were compared with EPA
collected during
numeric removal
action levels (RAL) for contaminated drinking-water sites, EPA Region 3 risk-based concentrations
(RBC) for up water (developed by Roy Smith, EPA toxicologist), and background sample
concentrations. No concentrations of fluoride, formaldehyde, or sulfate exceeded eitherofthe EPA
action limits or guidelines. Fluoride was observed at concentrations above background in both of the
leachate samples and in the downsteam sample. Fluoride was detected at concentrationsof220 and
160 micrograms per liter (ug/L) in leachate samples L-1 and L-2, respectively, and at a concentration
of 130 ug/L in sample DRIAQI. Fluoride was not detected in the background sample (BKGAQI).
The highest concentrationofsulfate (34.500 ug/L) was detected in the background sample.
USFW 0169
un
0CO-i0
ooTrn gAPT
TanLe 3 SUMMARY OF LDARBYORROATNO.RYFOARNKALLYETEICCRAELERKESBUOLVTISNE(ASQTTUEEOUS SAMPLES)
[ms| ER ET
ara feet | Sd Egat ens = i
(De
Gat
etn JOE1A ENTE Saba |cn
oe
eeros. IE Fe SAE
[Foote |NA | 220 Jul]20[ 1604<i0[ 0[ 100]
[Formaaiyee|so0| 730 [wi]&B7] <sT<sf--<s| 5|
sur. e+ Jo ooe st] | == awatt |lun apt + Nos econ NA No Applicable WL Micograms per ler
<doE oLoolii ero[Soasoi
Table 4 presents a summary of fluoride, formaldehyde, and sulfate analytical data from samples of the
`sediment collected during the site assessment. The results of analysesofthe samples were compared `with EPA Region 3 RBCs for fish and to background sample concentrations. Fluoride was detected at
concentrations of 396 and 411 milligrams per kilogram (mg/kg) in sediment samples LD-1 and LD-2,
respectively; 335 mg/kg in the downstream sediment sample (DRIKSED1); and 198 mg/kg in the
background sample (BKGSEDI). The fluoride concentrations in these samples are significantly above
the EPA guidance level of 81 mg/kg.
Tables
Fluoride concentrations that exceeded EPA limits are shaded in
AppendixC provides te Lancaster Laboratories Sample Analysis Report or th aqueous and sediment samples.
The analytical results for the samples submited to the CLP laboratories are no included i this
`evaluation. Upon receipt and evaluation of the remaining sample analytical data, PRC will prepare and submit to EPA an addendum to this trip report.
USFW 0170
12
0005.15
AI3O TrgN RPT
TABLE SUMMARY OF LABORATORY ANALYTICAL RESULTS (SEDIMENT SAMPLES)
DRY RUN/N. FORK LEE CREEK BOVINE SITE
EEE eam
[Dips cyShi} Tuvinh|tIMIS PARSER poe Aids evo]
CE
alae rr ON |
[Fone |
[Formatechyee|
sin
oN
[opie emseninent iene |
Jagng|es| os[o4 [ <o7[or |
boswe wa [stywl 61|260] ma| ms| os |
Nos:
, ESSE. |
`PSDeodirmeenltcismamnmpalteoomantnytitcaal* FictesedarEePpreesreiresdasredrm!yawediegtnresults.
oRNA NNooomaarmnoptedoe
eke Milgrampor opm
-
% by wt Percem by weight
-
=
.
. 5.0 RECOMMENDATIONS -
-
Based on the limited sample analytical data available to PRC at the present time, PRC recommends that an in-depth
evaluation of the CLP analytical data be conducted before conducting further sampling at the site. Ifthe evaluation of
the CLP daa shows that additional sampling is warranted, PRC will make this recommendation to the EPA.
USFW 0171
13
e000
I9eOTrNeR3PT
Co
GASTON CAPERTON GOVERNOR
LSp a
DIVISION OF ENVIRONMENTAL PROTECTION
1356 Hansford Street Charleston, WV 25301-1401
LAIDLEY ELI McCOY. PhD. DIRECTOR
ORDER ISSUED UNDER THE WATER POLLUTION CONTROL ACT
WEST VIRGIN!NIA CODEE,, CHAPT]ER 22, ARTARITICC] LE 11
THE SOLID WASTE MANAGEMENT ACT
WEST VIRGINIA CODE, CHAPTER 22, ARTICLE 15
ORDER NO. 3850
RERCECEEIIVVEEDD
ANZ 1997
spies
DATE: December 31, 1996
TO: Mr. H. David Ramsey, Jr.
E. I. Du Pont de Nemours and Company Washington Works
Post Office Box 1217
Parkersburg, West Virginia 26102-1217
Avention: Mr. Ramsey, Jr.
`This order is issued by the Director ofthe West Virginia Division of Environmental Protection (or "WVDEP"), through his authorized representatives, under the authorityofthe West Virginia Code, as amended (hereinafter, the CodeTM), Chapter 22, Article 11 and Chapter 22, Article 15 to E. I. Dupont de Nemours and Company (hereinafter Dupont").
FINDINGS OF FACT
`WashinAgtsona
resulta
Works
result
facility
of inspections
by authorized
conducted at Dupont's
representativesofthe
Dry Run Landfill and the
Director and in support of
this Order, the Director of the West Virginia Division of Environmental Protectionhereby
finds the following:
Telephone:O(f3f0i4c)eoSf58L.e9g1a6l0SFearxv:i(c3e0s4) 5884255 G0 1E
Page 2 H. David Ramsey, Ir. E. I. Dupont de Nemours and Company December 31, 1996
and
A. Chapter
Dupont is 22, Article
a person as defined in 15, Section 2. Dupont
Chapter 22, Article 11, Section is 2 corporation duly authorized
3 of the Code to conduct
business Works")
in in
the State of West Virginia; and Wood County, West Virginia.
owns and operates Dupont also owns
a facility (~Washington and operates a non-hazardous
waste landfill ("Dry Run Landfill"), `Washington Works facility.
also
in
Wood
County,
West
Virginia,
which
serves
the
VirginiaB.NationDaulpPoonltluitsanatutDhiosrcihzaedrgteo Eolpiemriantaetithoen DSrysytReumn(L*aSndWf/ilWlVuNnPdDeErSS"ol)idPeWramsitte/NWo.est WV 0076244. The permit authorizes Dupont to discharge a specified amount and type of pollutant into Dry Run, a tributary of the North Fork of Lee Creek. which is a ibutary of WthoerOkhsiofacRiilviteyr,.whDiucphonatllaolwsso thhoeldfsacailiWtyVtNoPdDisEchSarPgeermaistpeNcoi.fiWedV0am0o1u2n7t9anfdorttyhpeeWoafsphoiinlguttaonnt into the Ohio River.
C. Authorized representatives of the Director conducted an inspection of the Dry Run Landfill on March 23, 1995, May 3, 1995 and August 13, 1996 and noted a discolored leachate flowing from the landfill into Dry Run.
D. Authorized representativesofthe Director conducted an inspection of the Ohio River in the vicinity of the Washington Works facility on August 20, 1996. The inspectors noted solids of wax and polymeric materials of the type manufactured at the Washington `Works facility in the Ohio River and its banks.
E. Authorized representativesofthe Director inspected the Dry Run Landfill on May 16, 1994, March 23, 1995 and August 13, 1996 and noted the absence of a leachate collection system. Inspectors also noted an absence of diversion ditches during the May 16 and March 23 inspections.
F. Subsequent to the inspection, Dupont constructed two diversion ditches above
the landfill to prevent run-on from flowing across the landfill. Dupont incorporated designs
for a leachate Tandfil.
collection
system
into
the
permit
application
for
renewal
of
the
permit
for
the
G. Authorized representatives of the Director inspected the compaction procedures used at the landfill on May 3 and August 13, 1996 and noted that the wastes were being compacted in layers exceeding two feet in depth.
wastes
H. being
Dupont disposed
notified the WVDEP in September 1994 of a at the landfill. Such wastes were disposed of
change in the at the landfill
ratio of through
September 1996.
Office of Legal Services
Telephone: (304) 558-9160 Fax: (304) 5584255
aools
03:15
" PH.agDea3vid Ramsey. Jr DE.ecI.emDbuepron3t1,de19N9e%mours and Company
landfill
I does
noRtepurseeseanlteaatkivdeesteocftitohne
sDyisrteectmoorrhaavleinenro.tedDutphaotnttheinscuorrfpaocreatiemdpdoeusnidgmnsenftorat
the
leak detection landfill.
and
liner
systems
into
the
permit
application
for
renewal
of
the
permit
for
the
near
J. the
Authorized representatives of the landfill on May 3, 1995 and noted that
Director the water
inspected level was
the leachate pond located approximately three (3)
feet below normal elevation. of the pond.
Dupont had opened a drain value in preparation for treatment
K. discharge
limitsWawteerreqeuxalcieteydesdtanfdoarrdTsotwaelrSeuesxpceeneddeeddSaotliDdsr,y
mRaunngaLnaensdefi,llanadndirpoenrmasicreported
on Dupont's Monthly Discharge Monitoring Reports.
1995, MLa.y 3, A1u9t9h5oarnizdeAdurgeupsrtes1e3n,tat1i9v9e6s aonfdthneotDeidretchtaotr2i1ns-p2e%ctcedrotwhen lwaandsfinloltopnroMvairdcehd t2o1, prevent ponding on the surface of the landfill
REQUIREMENTS OF ORDER
Now, in accordance with Chapter 22, Article 15, Section 15 and Chapter 22, Article D1i1,reScetcotrioasn f1oSlloofwtshe Code, it is hereby agreed between the parties and ordered by the
In seclemen of all issues in the Findings of Fact, Dupont agrees to the following:
of
filter
1c. ake
Immediately upon the effective date of from the Washington Works wastewater
this Order, Dupont shall treatment system at the
cease disposal Dry Run
Luanndlfislulc.h
Dtuimpeonats
will the
refrain from future disposal instalation and operation of
of all
such filter cake at the Dry Run improvements to the landfill s
Landfill required
under the SW/WVNPDES completed.
Permit
o
be
issued
by
the
WVDEP
for
the
subject
landfill
are
leachate2.generaItmemdeadtiattheelDyruypRounnthLeanedfffielcltiavneddattreanosfpotrhtisitOrfdorert,reDautpmoenntt tsohatlhle cWoalslehcitntghteon mWoodrikfiscawtaisotneswaotfetrhetrWeaasthmeinntgtfaocnilWitoyrukpsonWVapNprPoDvaElSofpeWrVmiDtEoPoaflltohwesuncehcetsrseaaruymepnetr.miDtupont wreialccmoennttinfuaceiltiotycoulnlieclttshuecihnslteaalclhaattieonaannddtorpaenrsapotritonitotfoatllheimWparsohvienmgetnotnsWtortkhse wlaantdefrill as
TelephoneO:ff(i30c4e)o5f58L.a3g1a6l0SFearxv:i(c3e0s4) 5584255 oaagy
Page d H. David Ramsey, Jr ED.ec1.emDbuepron3t1,de19N9e6mours and Company
required under the SW/WVNPDES landfill are completed.
Permits
to
be
issued
by
the
WVDEP
for
the
subject
3. maintenance
Immediately upon the on the diversion ditches
effective date of this currently in place at
tOhredeDrr,yDRuuponnLtansdhfaillllpaesrfnoercmesssuacrhy
for the
controlled landfill.
flowof
surface
water
through
such
ditches
and
away
from
the
active
face
of
ctehretiWfaitede4.rmaQiulaloiWrtiysthhMailanlnthahaginredtmyed(en3lt0i)vFeduranytdosatohfcehtoehfcefkiecfoeffeoctftwiEovn-evhdiuarntodenrmeoedfntthails oErndfeorr,cDeumpeontntfowrildlespeonsdi viina
payable
to
"West
Virginia
Division
of
Environmental
thousand Protection."
dollars
(5200,000) :
0
the
5. benefit
Dupont will perform a of the environment but
wshuipcphlesmheanltlanlotenbveirdoinrmecetnetdaltopwraorjdecstf(acSilEitPat)ingto
accrue
caDoguneptnorcniytb'urtseiscopnoomnopsfliifbialfentycfeotrhwoiduteshvaesnltdoaptdiuotnlolgrayrasnodf(/$or5re0g,iu0ml0ap0tl)oermtyeonrateniqnueigsrcaermloeownatnasc.pcroDougunrptaotmnotbewilhlelmdafkoer athe
neontvibreoennmednetvaellocpoemdp,litahencfeiftbyy
small business. thousand dollars
If by May ($50,000)
1, 1997 such a held in escrow
designed to facilitate loan program has will be returned to
2aDcumpnuoottniatllelassyndhacaacnnepaftliatfbetrlyre-attShioEvuePsaSbnEydPdJousllhlyaalrl1s,b(e1$95d90e7,v,0e0lD0o)u.ppeodnItbnetwtihwleleeesvneenntdthetvhipaaatrctteihretesi,fpiawerhdtiicesh fsahiallltobneegvoatliuaetde
MdealniavegremtoenthteFouffnidceaocfhEencvkifroornmfeinfttaytlhEounsfaonrdcedmolelnatrsfo(r5d0e.p0o0s0i)t ipnaytahbelWeattoer"mWaQieulsaltoirVtiywriglilnhiaand
Division of Environmental Protection."
GENERAL PROVISIONS dleegfaelnsaeust1,.hofraicttys,WoatVshDewreEltPlhaarnsetsthehorsvreeiseghnatlulmtreoirgaahittsseedaanisdn atdhebefaseFinissnedfsionrwghssiupcopfhoFrtathcietny.gmsauychhalvegealpuarustuhaonrtittyooarny `CUhnadpetrert2h.2is2,OrAdretDriuc,pleoDnu1tp5,ohneStreecabtgiyroewneas1i5vteoasunndidtseCrhrtiagaphktteertaol2la2ap,cpteAiaroltnistchlrieseq1ou1ri,dreeSrdecubtnyidoetnrh2et1theeorfpmrtsohveainCsdoidoen,s of mrcoeangddaeirtdiiinonngtshtiohsifOstrOhdirsedreOrra.dnedrHroaewnseedvrevceorsn,saeDlnutpriotgonhttasnddaonewdsildnleonftoeatndscmeosinttaevasantiyltahfbealcejtuurailsdoirctliegoanolfdtehteermDiinraetcitoonrs
regarding liability and
Telephone:O(f3f0i4c)e5o5f8L-e9g1a6l0SFearxv:i(c3e0s4) 5584255
0Q0nY
Page 5
H. David Ramsey, Jr.
E. 1. Dupont de Nemours December 31, 1996
and
Company
responsibility administrative
ionracniyvilp,rotcoeeendfionrgcse
rtehgiasrOdridnegr.these
facilities
other
than
proceedings,
either
3. notification
froTmhitsheOrAdgeerncbyectohmatesDuepffoencttihvaesosnattihsefadcattoeriilnydciocamtpeldetaendd
shall terminate upon all tasks set forth in
the
requirements of the Order.
122i lag
Effective Date
L2p an0) [nn N`aWetsteVirginia Divitsilonio}f Environmental Protection
A. 4 2
S-oi
:
EN.amIleDupont de Nemours and Company
i Te
Plant Superintendent Tide
Telephone:O(f3f0i4c)e5o5f8L.e9g1a6l0SFearxv:ic(3e0s4) 584255
0gs'S5
BF PO=f3250 E.I DU PONoTwDtE N-vEiMroOoUnRsSamAenND COMPANY
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INTEROFF ICE MEMORANDIN
DFartoea:: TDeelpt:No:
0RO3N-AJLaDn-1W99M7EL0O4N:20pm KEPELOPOasNRY 304-863-4753
10: Distribution List
Subject: Leachate to the Biobond
> LeaEacrhlaytethfirsomafDtreyrnRouonnbawceksutocctehsesfnuelwlydebwraotuegrhitngourfacfiilristty.full load intendALLtopucmopnst,inueequihpamnednltingandlealcohgaitseticosvewrortkheedweweelkle.nd.AY this point we
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Om
[SEERER
EID029946
@UPORD DuPont Haskell Laboratory
January 9, 1997
HAZARD CHARACTERIZATION FOR HUMAN HEALTH C8 EXPOSURE CAS REGISTRY NO. 3825-26-1
Prepared by: L. B. Biegel, Ph.D.
Senior Research Toxicologist
! 009%5%
8
Lee0808
HAZARD CHARACCATSERREIGZIASTTIROYNNFOO.R38H25U-M26A-1N HEALTH C8 EXPOSURE
Table of Contents
J I. MAMMALIAN TOXICOLOGY crvE 3 LL. ACULE TOXICITY SIUBIES corres: 3
11D. ACUtE Dermal TOXIC worms
LLd. Acute Lhaltion TOXIGHY srs
121.16Su.bcAhCroUnEicIJTOEXCIOCNHYTOSXAICSHSY v.cvvrerrurrearrrevrrrreenmrrrsrnmsnresmmrsrrnsmmesmnmmemnmeonmoemmseosn 1
1.2.8. SUbCHIONC OFal TOXICHY rors oes, T
1.2.5. SubchrOniC INRAIEtON TOXIC ..ryrrrrrrrmrsemmemsn 10
1.2.c. Subchronic 1.3. DeVEIOPMENtal
Dermal TORIC
TOXICHY usr rnin
10 LL
FL
IL.16M.ECThArBonOiLcITOSXMIGi.tYccnodovONcCrOsBnErRsICsIsYsv smssssme omsmnmr memsesr msmmsne sonnen
13 19
HLEEMECHANISMS OF ACTION... rcsrmssmenemmmenemmmsmsmn--mn--n 20
TILL. 1.2.
Investigation ofC85' Investigationof C8s'
Effect Effect
Oonn TtehsetLiIcVuElTa.r.Le.y.di.gcC.erllr.r.o..m.r.r..r.r.mooswmrmmonnnr
20 21
IV.113,CLIInvNeIstCiAgaLtiRoEnoPfOCR8TSS' EOfFfecHtUoMnAthNe PEAXNPCOISEURRSE..w.c.....r..rrmmsrrsmmrno 2222.
a
A
VL`VIDL.ISCDUiSSSICOUNSOOFFSTIEANTOGDEDPtOOITNGATNSS .v .....ccers remrremrrs rmrrmsnemennsmnnn 2233
V1.2. VL3.
TDiusmcoursssiAosnosofcDiiaftfeedrWeintchesC8iniSnpheceieR s-Speca ific St ensitive ities .. ........ ........ ....
24 24
VL... SignificanceofC8-Induced Rodent Tumor to Human Risk................. 24
3&3
2 Lo 009niy
EID08080Y
.
HAZARD CHARACCATSERREIGZIASTTIROYNNFO.OR38H25U-M26A-1N HEALTH C8 EXPOSURE
INTRODUCTION "This document is a Hazard Characterizationof C8 for human health. C8 is also
known as ammonium perfluorooctanoate (AFPO; CAS # 3825-261) and is the primary ingredient in FC-143 FLUORAD Brand Fluorochemical Surfactant. Within this document the chemical will be referred to as C8. However, it is acknowledged that many ofthe studies discussed actually tested the product FC143, which is a mixtureofseveral straight-chain perfluorocarboxylic acids containing approximately 93.0-97.0% C8. I. MAMMALIAN TOXICOLOGY LL. Acute Toxicity Studies
La. Acute Oral Toxicity Numerous acute oral toxicity studies, in several species (rats, mice, guinea pigs, dogs), have been conducted with C8 (see Table I-1). The results of the various studies havebeen consistent in their results. Administration ofa single dose of 12 mg/kg to 3 rats produced no clinical signsoftoxicity. Studies demonstrate that newborn and older adult ats appeatrobemore seasitive than weanlings and young adults. Additionally, while mice and rats appear to be equally sensitive to the acute toxicity of C8, guinea pigs are more sensitive than mice of rats. In the rat, acute oral exposure generally results in enlarged livers, elevationsofliver enzyme levels, gastrointestinal irritation, and weight loss. C8 is considered to have moderate acute oral toxicity. Inaddition tothenumerous studies listed below, several other studies were `conducted which investigated the effectsof C8 alone or on animals pre-exposed to other chemicals or drugs. Pre-treatment ofrats with phenoberbital sodium or proadifen hydrochloride does not result in an alterationofthe LDsoof C8 (478 mg/kg). Pre or postdcoosmipnagrewidtthoDraotws edoxsed1-wXit2h-CC18laolnonEex.chAansgtuedRyewsaisn acton1d0u0c0tmedg/tkogderteedrumciendeitfheprmeo-rtality treatment with ethanol (a single doseof60% ora 15% aqueous solution (v/v) in drinking water for 14 days) modifies the effectsof C8 on liver weight. This study determined that pre-treatment with ethanol did not alter C8's effect on liver to body weight ratios.
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BTL IEE
:z
Cog
HPRARe E aHr gfLy te
grrr aay
Hosen |
| oan
EIDOS0811
HAZARD CHARACCATSERREIGZIASTTIROYNNFO.OR38H25U-M26A-1N HEALTH C8 EXPOSURE
LLb. Acute Dermal Toxicity
`Acute dermal toxicity and irritation studies in rats and rabbits have been conducted with C8. C8 is considered to be mild - moderately irritating to theskinand `moderately toxic by the dermal routeofexposure. Rat skin showed less iritation than raadbdbiittioanndtoidnegremnaelrailrrtihteateifonfescetvsewraelreclminoircealpsriognnsooufncteodxiicnitmyalweesrethoabnseirnvfeedmailnebso.thInrats awnedt raanbdbliotrssitnariensepdopnesreitneoalC8areeax,pocsyuarneo.sisTh(ersabebiotbsseorulvya)t,iodnisarirnhcelaud(readbbbiotdsyonwleyi)g,hltetlohsasr,gy
(rabbits only), labored breathing (rabbits only), and chromodacryorrhea (rats at
7500 mg/kg)
Table12 SUMMARY OF ACUTE DERMAL TOXICITY/IRRITATION STUDIES WITH C8
TSETope TTI. R Si1AbDE i,arpien
Spm Waeddee
Dee (@pke)
Er 5 W000
RAS BeA e ES00, 0wd 7500
"SiAbie RS ReeS000Rad7800 Dw
ERT a Qa 75Wile00) S500000,,070500,0
Rews
Reems
MaDe emEeh
RLS
FemalIeLDD s= >m750p0mgg/kg HUA WKeanR edy,D 1985)
Mild skin irmiaion
LMiDldSsin immiatgion THLE
LSegg er
43/44 w3021000000 a 100
H(KeunLedy,A1985) 09R7e5po0rAtBN0o4.8S
aod abraded sis
*
1580)
a YG SNR VdVRaHLA
Slightmoderate itionst48 bours
Llc. AcuteOcularToxicity
bemoderEayteeliyrrirtiattaiotninsgttudoitehseienyrea.bbIintssthiallvaeiboneoefn scoolnidduCc8teidntwoitrhabCb8i.tcCy8esipsrcoodnusciededred to
=
`rmeocdeedreadtoevceortmiemael.opPacriotmyp,triwsa, sanhdoicfonntjhugenectyievirteids.ucTehdetsheeeofcfuelcatrseaffnedcptsrogvriaddueadllaymore
2 g
rapid recovery. In addition to the eye irritation studies that have been conducted, rats
$
09.5%
EID080s12
HAZARDCHARACCATSERRIEGZIASTTIROYNNFO.OR3H82U52M6A-1NHEALTH C8 EXPOSURE wexhpiocshewdetroeCm8icdruorsicnogpai4c-ahlloyuerviidnehnatla4t2iodnapyesripoodste-xchixbpiotseude.comeal opacity and ulceration,
Tae 13
SUMMARY OF EYE IRRITATION STUDIES WITH C$
Sem ERw DGgw)
Rem
RE ts T Umamedor
Reese ------asm
(1 uwaavsahsehde)d,
MoMdoedraetresietvsere cornea opacity
AdMoaderue conjunctivitis
MCiolrdevlasocpualcariitzyation
Washed eSyleightmodest coral apaciy
AT aSalyisghtmoderate conjuncivits
Aled Mid conjunctival rdacss
Hai SSwaeshded
Usaibed oMyeoder iation rCoinsjunciviis
Washed eye
BiNco.TlkIa395Raper (Griffit1h98a0o)d Loss,
ATd"a4n6 eyes were fieof maton
L1.d. Acute Inhalation Toxicity
exposurAectuotCe8inbhyalianthiaolnattoixoinciistycosrnusdiideesreind atotsbehahvieghbleyetnoxciocn,dwuicttheda 4w-ihtohuCr3a.ppArcouxtiemate hlietghhaelr,colnlceanttsradtiieodnw(iAtLhiCn)4i8nhaotusrosoff0.e8xpmogs/uLr.e.AtAtcocnocnecnetnrtartaitoinosonsfb2e.t2wmegen/L0.C388aanndd in0.c8r3eamsge/dlLiCv8e,r-rtatos-beoxdpyewreiiegnhcetdraatnioiwnihtiiaclwherietguhrnleodstsoftohlelhoiwignhgeeaxpdoofsutrheeannodrmeanlrange: 42 days post-exposure. Additionally, allratsexposed to 0.81mg/L C8andhigher showed comeal opecity and corrosion.
$z
i
g
Leonpa.uls
EIDO80S13
HAZARD CHARACCATSERREIGZIASTTIROYNNFO.OR38H25U-M26A-1N HEALTH C8 EXPOSURE
Table 14
SUMMARY OF ACUTE INHALATION STUDIES WITH C8
Seem TRC
Wedd eas
Co(mmglmL)un 038,"0h8o1,w0o8p3,o2w2s,4e3,57
Res
Reem
ShLwCAo=L0C9=80mpRgmLgl (KeaseAdLyT,eOtSal, 1986)
RT
Gy Gp GSmL EyeNaneddraesipicuiory imitation
(Gr 198a0d)Cog,
LLe. Acute Injection Toxicity `Acute toxicity ofC8 when administered by intraperitoneal injection was assessed in mice (3M, 1979). The LDso by intraperitoneal injectioninmice is 192 mg/kg.
1.2. Subchronic Toxicity Studies 1.2.2.SubchronicOral Toxicity Numerous subchronic oral toxicity studies in several species (rats, mice, and
monkeys), have been conducted with C8 (see Table I-5). The resultsofthe various studies have been quite consistent in their results. Administration of C8 in the dietorby daily gastric intubation produced death at concentrations of 1000ppm and higher for rats and mice and at 30 mg/kg/day for monkeys. The primary target organ for toxic responses in all species studied is the liver. C8 produces increased liver weights, increased liver enzyme activity, hepatocellular hypertrophy, and hepatic peroxisome proliferation.
In addition to the numerous studies listed below, other studies were conducted `which investigatedthemechaonfiacstiomnof C8.Thesestudies are summarized in Section IIL. Mechanisms ofAction.
! . Pry
S2s
EIDOSO:814
Ef if 3 2 5 3
B2 ALyR| FE i BRI2 E_R
PPaothi oRgDfoodpr hodlin
J ELoGiE BER 22 ify
2fo Eil feBiraaligd Hayl gdiyg Hinil
fi EE|l B[3p2 aaflg i oi 2G:i2l: lnmif :
33 s| EiERG: Hisin ii :
i 11 Tz
ii; p SLwE,rf ,zPolgai ,
;Fo
: PE:
FL
fr orci
I REECET Epaa
sprig: 0 mE of
.
een in
EIDO080815
is
i
is
i
iHeIR1E0s HHGL Hosi Caadil Edd ol
i ip BRE
oI
(`| EELEfehis
a
i EsiHlRl
sEiEjl
h HEe LE
2 ful
lB) bd HL:
B0og)og phndnaE! HhRy H Ig E
die ro Boilie 1 i: gg] =z 2
5
s
5 1 gf
:
oo
;
'
EN
5 jit g 2
32
3
ie =
.
:
5i
i
i3
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i ity
000m: 1
EID0S0816
HAZARD CHARA`CCTASERRIEZGAITSiTCRiYsNFO.OR38H25U-M26A-1N HEALTH C3 EXPOSURE 1.2. Subchronic Inhalation Toxicity Similar to the oral toxicity studies, inhalation exposure to C8 produces reduced body weight, increased liver weights, increases in plasma enzymes indicativeofliver injury, and pathological lesions in the liver. Measurementofthe blood fluoride levels (indicativeofthe presenceofC8) determined that the blood half-life of C8 in the rat is 57 days following inhalation exposure.
Table 16
SUMMARY OF SUBCHRONIC INHALATION TOXICITY STUDIES WITH C8 IN THE RAT
"SGT (sexSidaose) Ceemwmies
(R@yks)es
Rees
wr ith a 42-day fof 6 houriday oDfoboedyweigy Ghtemaintaineedydvuerheie 42n-dgay T
recovery
irnedciocvaetriyveopefrilovdeatin8j3u;riynpcrreaesesdcuppla(ats0ma28cudzayyesmes
offohlloweingpthe aasitncterxepaososeudrleci;vgerrywaeniugtlhatsde,eagoesoaccru;aloanr.
eTfhfeelctisvewreerfefeocbtssewrevreed.not observedair 14,32,or
42 daysofrecovery.
De
ead i Wd
HAO
wdiatyrheacnov8e4r-y
for boursiday pweliacgshatzs,ynomoecuslairnedfifceacttisvoeobsferlivveed;jinucrrye;ased (Ken158He6a)ldleyta,l,
2n0cdrceeaastedrlloivbeurlwaeihgehpattsoctel>lu8lamryE/y'pe,rpreonplboybualnadr
dTahyerleivceorveefrfyecptesrwioedr.ereversible followi82n8gDodescereraesleadiewdiptrhetsienmcdeourfinCg8tah trheecbolvoeorydp,ewrhiiocdbhut wNasOsAilEl=Ldet|emct/awbl"ea,faelrib8o4dugahy1s3opf premcovery.
oerxgpaonsoufrieuo0ri|demyv/aas'detected immediatly following
12.c. Subehronic Dermal Toxicity
Table 1-`7T)h.e sSiumbiclharrontiocthdeeromraallttooxxiicciittyysotfCudi8es,hadserbmeaelnesxtupdoiseudreintothCe8raptraondducreasbbrietd(usceeed
binojduyrywaenigdhlte,siinoncsreiansetdhelliivveerr.weiMgehatssu,rienmcerenatsoefsbilnopoldasfmlauoernidzeylmeevselisnidincdaitciavteiovfeloifvtehre
deprremsaelnceexopfosCu8r)e.deAtcerommipnaerditshoanttohfetbhleoodderhmaallf-elxipfeosoufrCe8stiunditchse troatthie5f-e7eddianygssftouldlioewsing
z
leadstotheconcltuhatsthieroatensof absorption of C8bythesetworoutes are not
g
significantly different.
g
Ss
0
Coons
EID080817
HAZARD CHARACTERIZATION FOR HUMAN HEALTH C8 EXPOSURE
TET wTitohd1234 day recovery
Hg Rade wIi0edxpos1u4re dayrocovery
Tae 16
SUMMARY OF SUBCHRONIC INHALATION TOXICITY STUDIES WITH C8 IN THE RAT
(WisSexedomne) TS Male Ra
Co(wmakem)a b20o,u2r0s0d,ey2,0500 for dayseck
(Rmeyel) Sboidy weiiagihtonaa>230200;0;inrcerveeasedprlaesdmia on cliavrerymweesigihndsicaattiv2eo0;fbievpeartioncjeulryl;arincressed ebffyectps abeserarvnteddrnecorospishy 120; 80 ocular Tfohlelolwiivnegfaf4c2t-sdawyerreecgoevneerryalpleyriroedvearsib2l0e0. Dwhoiscehredlatoed pcrersewniectehostfimtCed8ueriidtnegtbhleoroedc,overy Tpeorvioedyb.ut was sll detectable he 42 days of
Reema (KeAaaeLdyS, O1985)
H(seAx not specified) 10 Rabbits
001000, 2000 Ealoao oF a3000 OF a 1000,0 64 510d0ayfuoirm6ehcokursday, S Reversu iblleeverc lesdwucetrr ieon5.a4e,b6o.d,y4w.eipgphtm; Bolrood
m1a4l,e1s3a4a2d810d.a1y,so1f2.t1h,e18sdtu3dy.,5 freosrpfecetmiavleelys.t7,
k0r97L9Ri0elApbBoorOtm4iSoSn,e," March 15, 1981
13. Developmental Toxicity
Developmental toxicity studies have been conducted in rats and rabbits (See Table 1-7). The original developmental toxicity study in ras indicated that C8 might be a `tweerraetocgoenndiunctreasd.toHcolwaerivfeyrt,hebercesauulst.e tThheereasdudlittsiwonearlesqtuuedsiteisodniadbnloe,tcaodndfiitriomnalthsetuordiigeisnal result. Overall, C8 is not considered to be uniquely hazardous to the conceptus.
alteratio`nTsh.e tIwnothae orriogifenqauleassttuisdoyn, twheerleeaasppaalrteernattiloennss caobnnsoirsmtaeldiotfietsheanfdolslkoewleitnagl: large
ens cleft,darkstreakrunning %to %of thewaythroughtheleas;ordisorganilzeensd
fibers. Inthesubsequentstudies,the lensalterationswere determinedto beanartifact
created in the lens during frechand sectioning. Processing Bouin's-fixed fetal heads that
wesesreeattiralilmymeeldimoinnaetiethdetrhsiisdaertofftechte. oErxba,miinnasttieoadnoofftthheroeuygehsotfheocfefnstperrionfgtuhseinegyef,ocal
illumination, indirect ophthalmoscopy, and slitlamp microscopy were also used and did
soittesdoentetchteafniyrsCt8l-uremlbaatrevdeertyeebraalteeirnatiroantss.anTdh1e3srkielbestianl ralatbebriattsi.oBnsotinhcolfutdheedsoesaslitfiecraattiioonns
2z
are considered to represeat stress-related changes indirectly related to C8-administration. g
3s
U eoonen
`EIDOS0S18
HAZARDCHARA`CCTASERREIGZIASTTIROYNNFO.OR3H82U5M-2A6-N1HEALTH C8 EXPOSURE
Table 17
SUMMARY OF DEVELOPMENTALREPRODUCTIVE TOXICITY STUDIES WITH C8"
Spm
Comeswmes
Ree
75(#Ri.adosse5) 0.7510.0, 150mgks Reduced marl bgo/dkygweightgaa 5d
(#ouspecified) bygavage
calibnincalosrigmsoaafl:2wi5xiatcaiidye1a5s0150; eye
Reem 3M ReporMOT assy)
ERE TO0mg bygavage TT Mweeigahtlgaidne;ano ddeeveclroipemednmtaatletroixailciBtoy dory TTT(SHtaLpleTs, tal,
sbuormalites observed.
1984)
12a 100mpkgbygavige weMaitgehrtnagladiena;t2h0s,ldereaiocnsrimneaptoeasrtnpsaalrbetuomdd,y ovciuablialrietfyf,egctrsowotbhsrearev,eodr.development. No
RG (aotspecified)
Gi08, 30 bygavage
TSO my
MeimlbdreaoyoaaobSgot;rmCaolHgSrxodssiafiencdin,gs,
`o0bsmearlvfeodrimnatilolngsr'o.upFse.taDlleetnsefrimnidtoinbwneeegdr3se.
prroecespsinrg artotriafcdatc,t.muaNlocee/ftefmailfoevnreaotveiaoc,riets,
wieigmhtsp. lsats,ncotrpoaraltutei,oofetnal
06SSITMRROLaIpOe,r1981
REG 20, mg byiahalation
tVoxiicsiety 1d19e.a9d;No2teorvearttmoefagfeecltnswierce ocbsemrvebdiaraatyoxyoifcittohyewea-xspoofbsseedergvreoaduaps2l;1; processingarifacts wereobservedon leas.
(HSupUls,Ical. 1984)
by gavage
C8 was not embryotoxico teratogenic' MToaiyci2t4y,1Sh9e9e6t,
Preguantrasweredosedbygavageoadays6-15ofpregaaacy. Prerabgbitsoweraedonsedtby b.. gSavaageocndroanyDis6a-yf1281oioffpcgreegseataiaodcny.. cd.A Puspisgnsifiacanct rohingidhaeyrfi3nc5iipdoescntcpeeoarfutdmhe.skeletalfinding "onesteroabrasmissing",occurredinthehigh
Fduorstehegrromuopr.e,Tthhiesiwncaisdenmcienoofrtshkieleftianldinegdriradtnoontdnifdfwe afsrnoomttchoeocsoindterroeldgramoaulpfoorrtmhati3olnoiwnert-ilsevseuldy. reammentgroups. Theincidencesofskeletalfindingsassociatedwithdelayedossificationand ib e. sTbheerraetwiaosnswaesuraeisntoctadlilfyfseirgeanitfaicmaonnigntchreearsaiimatehnetingcrioduepnscaenodfcon3trroilbssi.nthehighdose groupaxd13 Ftihbasnsipnutrhreecdointrtohlesm,ithdedyoasreegnrootucpo.nWshidielreedthewfbientdeirnagtsoageensiicgcnhifaincgaentsloyrgmraelaftoerrimnattihoenstr,eraattehdearntihmeaylasre `considered 0representstest-elazedchanges 0compoundadministration.
z> g
g
2 _ oopig; EDOM
-
HAZARD CHARA`CCATSERREIGZIASTTIROYNNFO.OR38H25U-M26A-1N HEALTH C8 EXPOSURE. 14. Reproductive Toxicity
No information is available on the reproductive toxicityofC8 1S. Mutagenicity
Ithas been demonstrated that C8 is oot mutagenic in a variety ofmutagenicity tests (See Table 1-9).
Table 19
SUMMARY OF MUTAGENICITY STUDIES WITH C8 IN THE RAT
SGT
SmGDees
Res
Reem
ceTrAeLvSi3s7i,aeTDA4LySe3a8s,t,1w0idtThAaIo0dDw)iataodu.t `meabolc scsvaton.
RmG icronuOcleEus TT 600,800w,aaed 10d0o0smegd/WkglanBd0b0,o4o00,
mahorurrosawfweradsoesvianlgu.aiedat 24,48and72
CK
RE
sberation cwhroiamaodstwoimtahlhosubtermmeattaiobnosliicncCtHivOagcoenll.s
"rWansifosrmationGasEsey Asasdacydwtafxoicciltly ia CstIoHma1a0TiIo/n2pcooilcoanayl cells.
Eu
LBIFeProoje1c,t12907838, (Gr1is98af0d)fLoisss,
GRRE TT
1i7n3g88W04i5d5,e, May 16,1996
NG
i
A1p7r3il88205,413979,6
LNEo evi3d3eagcaeolfceolwrSarnissfioerdmiactiiyon T a Minnesoi ta Envoe ifron. Pa`iAnprLialbs,, T12998412,
16. Chronic Toxicity and Oncogenicity `The chronic toxicity and oncogenicity ofC8 has been investigated in two 2-year
feedingstudies inrats (see Table 1-10).
E
g
5 0085s
EID0S0820
HAZARD CHARAACSTERREIZGAITSITONNFo.OR36H2U3.M2A6:N HEALTH C EXPOSURE
Tae 110 SUMMARY OF CHRONIC TOXICITY AND ONCOGENICITY STUDIES WITH C8 IN RATS
TTR
(mean ally intake, mg/day)
OW15,W20p4 m15 mgku/day)
Deconnssumepiolniyncreased siaR . DevescnE paredheodasee d 0T 281Ce ROO! ny RvaBluCes.couTnatcsr,ehaesemdogllivoebriwne,iaghdtsh,emvaetroccreilt. (April 1981-May 1983) hNyopterctornospihdye,reddegiebaeercaaicoinzoagnedanieccrosis.
SMe Op S00a
acosnsumdptionB.odIynwcereiagshed estradnidofloloevdels. Ipannccrreeaasteidciancciindaernceeolfalidvoerr,eLseydig cll and
( DuPontC MaRl -1596k 5846)
In the original study, in-lfe findings consistedof a dose dependent decrease in `mean body weight gain and increase in food consumptioninmales, and aslight treammenterelatedincreasein the incidence ofataxiain females. No increase in mortality was observed. C3-related hematologic alteration included decreased red blood cell counts, hemoglobin and hematocrit values observed at various times throughout the 2yeartest period. However, the decreasesinerythrocyte counts were observed earlyi the studyand did not progress into generalized anemia. Histopathologically, C8-associated alterations were observed in the liver. These changes were characterized by increased leinvyetrhwreoicgyhttesc,ouhnytpse,rttrhoephheyp,athiecpaatlotceerlaltuilonasr wdeegreeneorbasteirovne,daenadrlnyecirnostihse.stAusdywaintdh tshheowed litle progression over the remainderofthe 2-year study. The incidenceoftumors was relatively low, and the typesofneoplasms found were not differeat from the tumor profiles commonly observed in geriatric rats. Hepatocellular tumors were slightly increasiend the 300 ppm males, howevenort,o the exteat that would be expected considering the morphological evidenceof hepatocellular stimulation observed at the 1year necropsy. The incidenceoftesticular Leydig cell adenomas (0/50, 3/50, and 7/50 at 0,30, and 300 ppm, respectively) was suggestive of a compound-relaced effect. However, because the incidence was within the historical control range, it was not considered to be a compound-related effect. Basedonthe tumor incidence,typesof tumors,timeoftumorappearance, and the survival rate atthe 2yeartimepoint, the o0v2e8r1aCllROc01o2)n.cHlowwueavssetrih,aiotnCtn8hiwsaosringointaclasrtcuidnyo,gesnoimceoinftthheeraptat(hRoilkoegriLcaalbofriantdoirnyg,s were equivocal (liver and Leydig cell tumors), even when evaluated by an outside laboratory, and therefore a second 2-year study was conducted to clarify some ofthese findings.
`The second study included many mechanistic endpoints to help determine the
`mechanismoftumor formation (DuPont MR-S686, Cook, etal, 1994). In addition to the
pardolliifbeirtautmiocnon(tBr-oolx,i8dasteicoonnadctciovnittry)olawnadsceplaliprr-ofleidfteoratthieonC(8BgrrdoUu,p.6-dPaeyrooxsimsootmiec pumps)
E z
H
EID080821
ee0ass
HAZARD CHARAR CTERIZATIOe N FORmHeUMwA)Ns HEALTH C8 o EXPOSURE
`lwuetrieenmiezainsgurheodrmionntehe(LliHv)e,r afonldlitcelsetss.timSuelartuimnghhoorrmmoonneele(vFeSlsH)(taenstdosptreorloancet,ine)stwreadrieola,iso I`mnecarseuarseedd.reIlnatteirviemlisvaecrriwfeiicgeshtwsewreerpeerofbosremrevdedatin3t-hmeoCn8t-htrientaetrevdalrsatsa.s wHeelplaatsicatox| imdoantthi.on caecltlivpirtoyliwfaesraatlisoon winacsrenaostedsiignnitfhiecaCn8t-ltyrienactreedarsaetds iant talhletCi8m-etrpeoianttesd. gIrnoucpo.ntrCa8std,ihdenpoattic significandy alter the rateofLeydig cell B-oxidation or Leydig cell proliferation. tMhoereraotveoerf, htehpeatraitceBo-foxBi-doaxtiidoant,ioinrrienspLeecytidvieog fcetllrseawtamsenatp.prSoexriummatteelsyto2s0t-etriomnee,s FlSesHs,than prolactin, and LHlevelswere unchangedinthe C8-treated rats when compared to the ctornetartoeldsr.atTshaetr1e,w3,er6e,,9,ho1w2e,v1e5r,, 1s8iagnnidfi2c1antmoinntchresa.seHsiisntospeartuhomleosgtircaadlioelvallevuealtsioinn rtehveeCa3le-d `trceoamtpeodurnadt-sr.elBaatseeddioncnrtehaesedsatian,ltihveer,LeLyedyidgigceclelllt,uamnodrspaanpcpreeaarttioc abceindaurecteolthteumors in C8cacoimnbairnacetlilotnuofmeorlsevaarteerdeleastterdadtiooalnleivneclrseaasnedirnesdeurcuemd cprhoollaecctyisntolekvienlisn. (TChCeKp)anlcerveelast.ic
IL. METABOLISM
of C8Niunmvearrioouuss sspteucdiieess.haAvdedibteieonnaclolyn,dusctutdeidesinhvaevsteibgaeteinngcotnheduecxtcerdetwiiotnhaenxdpdoissepdosition b`weoernkenrosteadt,awmhaenruefaasctruerpirnodgupcltainvtewshaitcuhs pinrofdeumcaelsesC8d.idSneoxthaanvdesapneceifefsedcitoffnereexnccreesthioanveor dCi8s,powshiitlieonmainleratrsa.tsRaabnbdiftesm(abloethhasmesxteesr)s, efxecmraelteerCat8s,maonrdemsallowelhya.msMtiecres (rbaoptihdlsyeexxecsr)ete. ebxlcoroedteleCve8lseviennanmoerxepossleodwlwyo.rkCe8raslhsoowheads athlatontgheli-fliefeiinnhmuemannsis.greMaetaesrutrheamnen1t.5ofyeaCr8s.
ILL. Animal Studies
and ra`bTbhietse.xcSrteutdiioensahnadvdeisalpsoosiitnivoenostfigCa8tedhatshebeinefnluienvnecseotifgraoteudtienrofaetxsp,omsiucree,.hTamhsetseers. studies are summarized below.
injectiIoLnL.a.FeMmaalleesaenxdcrfeetmeadleesrsaetnstiwaelrley a1d0m0i%noisfttehreedardamdiinoilsatbeerleedddCo8sebbyyin2t4rahvoeunrosu,s w`ewrhielneomtadleetsehcatadbelxecarfetteerd1o7ndlayy2si0n%othfethfeemaadlmeisn,iwshtielreeadtdo3s6ed.ayRsamdiaolaecstihvaedti2s.su8e%orfestihduees LYaCbiornatthoerylidverru,g1M.e1t%abinoltihsemplRaespmoartan1d-2l0ow(e1r98bu0t).detectable levels in other organs (Riker
observIeLdLbi.n aSsetxuddyioffferraetnsc,esmiicnet,hheaemxsctreertsi,onanadndradbibsiptoss.itMiaolnoefarnaddifoelmaableeleadniCm8alwseorfeeach
pr 5
sp2e4c,i48e,s w7e2,r9e6d,osaenddb1y20gahovuargsepwoistt-hdo1s0imngg./kAgniC8m,alasndwuererthaienadnsfaeccreiefsicweed,reacnodlblleocoteddaantd
g
1s eesidy
EID030822
HAZARD CHARACTERIZATION FOR HUMAN HEALTH CY EXPOSURE
tissues were analyzed. The urine and fecesofrabbits was also collected at 144 and 168 hours post-dosing, and rabbits were sacrificed at 168 hours.
The female rat and male hamster had excreted over 99%ofthe administered dose at the timeofsacrifice. The male rat and the femalehamsterhad excreted 39 and 60% of the administered dose, respectively, at the imeofsacrifice. Both sexes of rabbits excreted the C8 as rapidly and completely as the female rat and male hamster. The male and female mice retained substantial amountsofthe total administered radioactivity in their tissuesatthe timeofsacrifice, only excreting 21%ofthe administered dose at 120 hours post-dosing (HL 62-82)
IL1.. Cholestyramine, a non-absorbable anion-exchange resin, was demonstrated to protect rats from the acute lethal effoefcCt8 when administered within 2 hours of C8 dosing (HL 828-81).
A second study was conducted to investigate the effect ofcholestyramine on the `emlailmeirnaattsioanndofm'iCc-eCw8er(e10gimvge/nkcghoblyesgtayvraagmei)nfer(o1m00ra0tsmga/ndkgmibcyeg(avHaLge4)052-482h)o.urAsduafltter
dosing with 'C-C8. The cholestyramine did not enhance the elimination of C8 via the feces, urine,or exhaled air. Similarly, Dowex lon Exchange Resin was also able to
rehdouurcseatfhteer adcoustienglewthiatlheCff8ecntoofsiCg8n.soWfheenhnarnactesdanedlimmiincaetiwoenroefgCi8v,enviDaotwheexfecerse,siunri2n4e or exhaled air, were observed (HL 405-82).
To further investigate the useofcholestyramitneo enhance C8 elimination, athird sivt.u)daynwdatshecnonwdeurcetefdedindireattss.coInntatihinsinsgtu4dy%, crahtoslweesrtyerdaomsineedfwoirth14'd"aCy-sC.8 T(1h3e.3 mg/kg, by cholestyramine increased the eliminationof C8 via the feces by 9.8 fold and decreased the concentrationof C8 foundinthe liver, plasma, and red blood cells (Johnson,etal., 1984).
ILL4. A seriesofexperiments was conducted toevaluatethe uptake and clearance 0f C8fromthe blood ofmale and female (pregnant and non-pregnant) rats following oral exposure, and inhalation exposure.
`The uptake and clearanceof C8 from the bloodoffemale rats followinga single
oraldosewasrapid,withpeakreached 1-2hourspost-traendavitrtmuaeltnottal
clearabnyc2e4 hours.Adose-responsewasdemonstratedwithnoapparentchanges in
blood C8 levels following multiple oral dosing. The slower clearance rate in male rats
`was demonstrated followinga single oral dose. Thesamegeneral statements apply
bflololoodwlienvgelisnhwailtahtiinon|ehxopuosruarfet.erAcesssiantgiloen6o-fbeoxuproisnuhrael;attihoen meaxtpeorsiuarlerraepsiudlltyecdliena:repdeafkrom
theblood;the number ofexposuresdidnotaffectbloodlevels;andmaleratscleared the
z
compound much more slowly. Pregnant and non-pregnant rats showed similar C8 blood 2
g
1
esas EPO80823
242080 PH CASTRB REGILSA OTRNY NO,338H25U.M26A-1NHEALTH C8 EXPOSURE
leexvpeelrsifmoelnltoswairneg seuitmhmearroirazledorbienlhoawl.ation exposure (HL 593-91). Specificsofthe
ILLe.1. Oral administration-Blood levelsof C8 as a functionof time post-dosing.
(female rats)
C8 levels of 14ppmwere seen 15 minutes following administration of C8. These
levels peaked at 30 ppm at 1-2 hours, dropped to 26 ppm by 8 hours, and to 0.7 and 0.045
ppm at 24 and 168 hours, respectively. C8 is absorbed and rapidly cleared from the
`blood of female rats given a single oral dose.
IL.1.e.2. Oral administration-Blood levels of C8 asa functionof dose (female rats)
C8 levels 30 minutes following administration of2.5 -- 150 mg/kg ranged from 3
-162 ppm. The same dose response was observed at 24 hours with blood levels ranging
eflraotme0d.t1o2t-he18ampopumn.tTohfeCr8easdpmoinnsiestwearsedl.inear. The levelof C8 in the blood is directly
I(fLe1r.nea3l.e rOatrsa)l administration-Blood levelsof C8 as a function of number of doses
Blood levels infemalerats given I versus 11dosesofC8 were not considerably
different. Concentrations at 15 minutes following administration were 14 and 17 ppm for
1 and 11 doses, respectively. At 30 minutes C8 concentrations were 16 and 25 ppm; at 8 `hours 26 and 13 ppm;at 24hours, 0.7 and 0.8 ppm;andat 168 hours, 0.045 and 0.10
ppm for 1 and 11 doses, respectively. C8 does not appear to accumulate in the blood of
female rats following repeated oral administration. The numberoftreatments does not appear to influence the C8 blood level.
IL1.ef.e4m.alOerraaltsa)dministration-Blood levels of C8 folloawsiinnglge 25 mg/kg dose (male and
-- imefollowCiongusrin)gleoraldose. % "M5 BalloeoRdaLs ev oFfee Cm8al (lxpepRsma)ss
284
5
0267
--_
18
0
005
C8isretainedinthe bloodofmalerats to agreaterextentthanfemalerats.
IL1.rea.t5s.) Inhalation exposure-Blood levels of C8 as a functionoftime post-exposure (female
C8levels of 96ppmwereobserved15minutes following asingle 6-hour
exposureto 10 mg C8/m'. The levelwasmaintainedthrough 1hour,fellto `approximately70 ppm at 8hours, 52ppmat24hours,anddroppedto 0.39 ppmat 168
:
z
> g
7
Toes
EIDOS0S24
HAZARD CHARA`CCATSERREIGZIASTTIROYNNFOO.R,36S25U-M26A-1N HEALTH C8 EXPOSURE hours post-cxposure. This same general pattem was observedinrats exposed to either 0t.o1bolroo|dmsga/mmp'l.inTghfeolllaogwpihngasae6s-eheonurfoilnlhoawliantgioonraelxpeoxspuorseur(erawthaesr ntohtanobasseirnvgelde hdeorsee datuea given time). C8 is absorbed and rapidly cleared from the blood of female rats following a single inhalation exposure.
IL1.e.6. Inhalation exposure -Blood levelsof C8 as a functionofdose (female rats)
TT BTl achloe vegsagdlRelCiGpm
hlioGnoeurpyo)ntede ___(AFFoT lovhgepoTangrae"nCin ig
-- E 2 g 2 me m 7 OR&E
23
0o3ise
0o)se
72
`The response is linear at 30 minutes. C8 blood levels are directly related to the amountof C8 inhaled. At the high concentration used, the clearance rate is somewhat slower than observed at the lower levels. This suggests massive overloads in the clearance system.
ILLe.7. Inhalation exposure -Blood levelsof C8 followinag single 6 hour
exposure to 10 mg/m' (male and female rats)
Tek Bella oC
--m %2 w 157
28
11892
72
C8isretainedinthebloodofmaleratsto agreaterextentthanfemalerats following inhalation exposure.
ILLe8. Oral administration-Blood levelsof C8 following a single 25 mg/kg dose (pregnant and non-pregnant female rats)
"Time llovingsage onldose
-- Go% w
28
Blood Rol CiGom
eoou1m6Ra NoepemBer
32
3a
female rCa8tcs.learancefollowingoraldosing issimilarinpregnantandnon-pregnant
g
g
1 000070
EID00825
HAZARD CE4FCAACSTERREIGZIASTTIROYNNFO.OR38H25U-M26A-1N HEALTH CB EXPOSURE 1.1.9. Oral and Inhalation exposure -Blood levelsof C8 as a functionofnumber of exposure concentration (pregnant female rats)
Time Following sagle aldose Giis) 28 2
Blood Levels ofCF Gp)
p5ie exp7osures V0 Ghp1o7iiies
33
o3d
11s
2
od
1
fToimelowirang gwhales
----EE
ony ed
72%
a
Bod LE oli GRE)
s77ip
0 Si5poiies
%
od
`When comparing the C8 levels seen at2 and 8 hours, following 10 consecutive oral doses, there appears to be aloweroiftnhge C8 blood levels. Blood levels following 1 or 10 consecutive inhalation exposures (6 hours/day) were not different. C8 does not appear to accumulate in the bloodofpregnant rats following repeated oral or inhalation exposures.
1I1., The ability of '*C-C8 to transfer through the placenta was investigated in rats
(HL 61-82). Asingledose of 10 mg/kg '"C-C8wasadministered to pregnant ratsonthe
19 dayofpregnancy. Matemal blood and placental levels of '*C-C8 increased between
2 and 4 hours post-dosing,and decreased between 4 and hours post-dosing.
"Taeollfov1i0gmagen dor
LeeBercs
ou7rs)
(ug equivialnentymLblood)_ (ug equival7enty/mL tissue)
hn8
212
33
IL2. HumanExposure
Determinations oforganic fluorine blood levels in workers exposed to C8 in an
industrial environmentwereperformed. Approximately 90%ofthe organic fluorine wes
`composedofthe C8 anion. The highest levelswere foiunwonrkedrs withthe longest
`work historyin luorochemical production.Themajority ofthe values remained at
`approximatelythesame levelthroughoutthe 2 %yearmonitoringperiod. Monitoriongf
z
C8 blood levelsof a worker who was removed from the fluorochemical production site
g
due to high C8 blood levels (70 ppm) suggests that fluorochemicals are very slowly
:
000.34 EIDOS0S26
HAZARD CHARCAACSTERRZIGZIAATTRIYONHFO.OR38H2U52M6A-1N HEALTH C8 EXPOSURE
eliminated. From this limited data it is hypothesized that the %-lifeof C8 is 1.5 years in men (Ubel, et al, 1980).
TT Gmw
Nambwmed Bleed Ogu FluoraeLevel
eIndmustrial controls L(a5b2o0rayetaorrsy epxeprossounrnee)l
Plant workers
Fo pH4 5
000S10.08 0042.00 1071.00
IL MECHANISMS OF ACTION C8 is not metabolizedinrats. C8 produces hepatomegaly, irduces hepatic
peroxisomes in mice and rats, andhasbeen shownto produce hepatic, Leydig cell, and pancreatic acinar tumors in a 2-year feedingstudyin rats. Themale rat is more susceptible to the toxic effectsof C8 than the female rat, presumably due to the longer %life in males. Short-term studieshavebeen conducted investigating the mechanisms of action responsible for the various effects
HILL. Investigationof CBs' Effect on the Liver.
IIL1a. Because C8 had been shown to inducae striking hepatomegaly in rats, a study was conducted to investigate the hepatic biochemical and morphological changes associated with C8-induced hepatomegalyinrats (Pastoor,et l., 1987). In this study `maleratsweredoseddailyfor1,3,or 7dayswith SO mg C8/kgbodyweightby intragastric intubation. The total cytochrome P450 content and activity ofbenzphetamine oNf-sdmeomeotthhyleansdeopwlaassmiinccrreeatsiecduliunmt.heIlnicveornstorafstC,8t-hteresaotleudblrea,tsc,yitnodpilcaastmiingc tehnezyprmoelsi,feration glutathione S-transferase and UDP-glucuronyltransferase, were unaffected. Carnitine acetyltransferase activity was disproportionately increased relative to carnitine palmitoyl transferase activity, confirming the predominant proliferationofperoxisomes versus mitochondria. Electron microscopy confirmed the proliferative responseofthe endoplasmic reticulum, peroxisomes, and microsomes in the livers ofthe C8-treated ats. `This study also demonstrated that C8 does not possess hypolipidemic activity.
TILLb. C8increasedserum estradiol concentrationsin2-week gavage studies,
`andfeedingstudiesat various timepointsup to 2years. Thiswasaccompanibeyd
increases in liver weights, and hepatic p-oxidation activity (Cook, etal, 1992; Cook, et
al, 1994). Since peroxisome proliferators induce both B-oxidation activity and
cytochrome P450 enzymes, aninvestigatwieosn conducted to determiifnCe8 increases
serum estradiol levels by stimulatingaromataseactivity(Liv,et al., 1996s). Fourteen
daysoftreatmentwithupto40mgC8/kg/dayproduceddose-dependentincreases inliver
w`waesigehtsst,absleirshuemdebsetrtawdeieoln, easntdrahdeipolataincdahreopmaattiacsaeraocmtaivtiatsye. aActisviigtnyi.fiJcnanvtitlrioneeaxrpceorrirmeelnattison
33
usingculturedhepatocytessuggestthatthe incinrsereumaestsradeiolis atleast partly
00013n EIDOS0S2T
HAZARD CHARAC8TEBRIEZNAETITORNNCYF.OR18H3U8 M26A-1N HEALTH C8 EXPOSURE dauroemtaotaasdeirceycttoecfhfercotmoenPt4h5e0liivnetrhteoeinndcorpealsaesmsiycntrheetsiicsoulfuems.tradiol through induction of HL2. Investigationof C85 Effect on Testicular Leydig Cells
Because C8 produced an increased incidenceoftesticular Leydig cell tumors in a 2-year feeding study in rats, and because C8 was negative in short-term tests for genotoxicity, anon-genotoxic(hormonal mediated) mechanism for tumor formation was investigated. The studies summarized below support a hormonally-mediated mechanism of Leydig cell tumorigenesis: C8 produces an increase in hepatic aromatase activity, `which elevates serum estradiol concentrations, which in turn modulates growth factors in the testis, which results in tumor formation.
IM12.e. Fourteen daysoftreatment with up to 50 mg C8/kg/day produced dosedependent increases in hepatic B-oxidation activity, and serum concentrations of estradiol, and decreases in serum testosterone concentrations, body weights, and relative `accessory sex organ weights in male rats (Cook,et al, 1992). Challenge experiments, using human chorionic gonadotropin (hCG), gondaotropin-releasing hormone (GarH), or naloxone challenges, suggest that the decrease in testosterone may be due to a lesion at the level ofthe testes, due to & decrease in the conversion of 17a-hydroxyprogesterone to androstenedione.
IIL2b. Using in vitro, in vivo and ex vivo studies, C8 was examinedfor ts ability to directly affect Leydig cells in vifro using isolated Leydig cells from untreated rats, and x vivo using Leydig cells isolated from C8-treated rats. Additionally, the ability ofC8 to affect testicular interstitial fluid hormone levels and induce aromatase activity was investigated (Biegel, etal, 1995). The in vitro studies demonstrated that C8 directly inhibits testosterone production, while the ex vivo studies demonstrated that this inhibition is reversible. In the in vivo study, serum and testicular interstitial fluid estradiol were increased and testicular interstitial fluid transforming growth factor a were increased. Additionally, hepatic aromatase activity was increased while aromatase: activity levels were not affected in the testis, muscle, or fat. These data suggest that the increases in estradiol levels are primarily due to increases in aromatase activity.
IlL2.c. Previous studies with C8 showeda direct effect on Leydig cells to alter steriodogenesis. It was therefore proposed that peroxisome proliferators, in general, may directlyaffectLeydigcellfunctiontoproduceLeydigcelltumors. Astudyinvestigating `whether several peroxisome proliferators (including C8), directly affect Leydig cell functioninvitrowasconducted.Thisstudyshowedthatperoxisomeproliferators,as a classofcompounds, directly modify the steroidogenic function ofLeydig cells in vitro. TahlissoianldsuocseuLgegyesdtisgtchealtlctoummpoorusnidnsvwihvioc(hLdi, ietarl,aef1f9ce9c6tbt)L.elydyig cell function in vitro may
Z2Z
g
21 Leeann EOS828 c
AZARIL CHARCAATSESREIGZIASTTIROYNNFO.OR38525-A26-N1 HEALTH C3 TXPOSURE IIL3. Investigationof C8s" Effect on the Pancreas
Several peroxisome proliferators have been shown to produce pancreatic acinar cell hyperplasia/adenocarcinomas in 2-year feeding studies, including C8. Therefore, in vitro and in vivo investigationsof C8's (in vitro only) and Wyeth-14, 643's (a model peroxisome proliferator) mechanismoftumorigenesis in the pancreas were conducted. `These mechanisms include cholecystokinin receptor agonism (CC)trKyps,in inhibition, alterations in gut fat content, cholestasis and altered bile flow/composition. Allofthese `mechanisms enhance pancreatic growth eibtybihndeingrto the CCKx receptororby ifaniclreedastionignphilbaistmtaryCpsCinK, laecveolsm.moCnB mdeidchnaotnibsimndfdoirriencctlryeatsointghepClaCsmKa CreCceKptloervealns.d iItn vivo s`ptaundcireesatwiicthtuWmyoertshb-1y4c,ho6l4e3stassuigsg,eswthitchahtmthaeysebpeerreosxpiosnsoimbeleprfoolriftehreatdoercsrperasoeduicnebile acid `output which contributes to the increase in plasma CCK levels. Therefore, for Wyeth-14, 643 (and perhaps C8), the pancreatic tumors may be secondary to hepatic cholestasis (Obourn, et al., 1997) IV. CLINICAL REPORTS OF HUMAN EXPOSURE IV.1a. Health screening examinations were offered to employees ofa 3M plant that produced C8, as well as other fluorochemicals. No health problems related to exposure: `were encountered among those examined. Additionally, no relationship was observed between deviations from normal laboratory test results and blood levelsof organic fluorine (the liver enzyme SGGT was the most frequently encountered test result `aelx,ce1e9d8i0n)g. the normal range. C8 exposure levels ranged from 0.03 to 7.6 mg/m' (Ubel, et IV.Lb. A study was madeofWashington Works employees potentially exposed to C3. Resultsof blood chemistry testing (SGOT, LDH, AP, and bilirubin) indicated no conclusive evidenceofan occupationally related health problem among workers exposed 10 C8 (Fayerweather, 1981). IV.Lc. Although C8isthe major organofluorine compound found in humans, file information is available concerning human responses to C8 exposure. Therefore, study `was conducted among 115 workers exposedto C8 occupationally (serum fluorine levels variedbetween 0 and 26 ppm, with amean of3.3). In an examinatofitohne crosssectional associations betweeC8n and hepatic enzymes, lipoproteins,andcholesterol, there was no significant clinical hepatic toxicityofthe C8 levels observed in this study (Gillilandand Mandel, 1996). Serum C8 levelswerepositively associated with estradiol ahonrdmnoengea.tivTehley ansesgoactiiavteeadswsiotcihaftrieoentbeesttwoseteenrotneestaonsdtenrootneasasnodciCa8tewdawsitshtrlountgeeirniizninoglder men. Thyroid stimulating hormone and C8 were positively associated. Prolactin and C8 `gwleurteapmoyslitoixvaelloyacaestsiocciaactiedd einndmgolduetraamtyeldpryinrkuevrisc. trTahnesaemfifneactsoefdaedcirpeoassietdy aosnCs8eriuncmreased. `Theinducotfgiaommna glutamy! transferabsye alwcasdoecrh easeodaslC8 increased. TheeffofealccohtolonHDLwasreducedas C8increased. Apositive associstion
2 Lo econ
ED080829
--_-- Co HATAm RE CHa ARCAASs STIRNEIGm AISTTIROYNY N|G.SE3N 8H2U5-M2A6o 1N HEs ALTRa CE EXe POSU) RE bTheetsweeerneshueltmsogsluogbgeisnt,tmheatanC8cealflfuelcatrsvmoalluemer,eparnoddulcetuikvoecyhtoermcoounnetssawnidththCa8t twhaesliovbesreirsvneodt. aC8siagnpipfeiacrasnttosimtoeodfitfoyxihceiptaytiicnahnudmiamnsmuant ethreeCsp8onlseveeslstooxbesneorbvieodtiincsth(iGsilsltiuldayn.d aHnodwever, Mandel, 1993).
V. EPIDEMIOLOGY `whereVC.L8aa.ndAortehterrosfpleucotriovecocmophoorutndmsoratraelimtaynusftaucdtyuwraesd.maRdeceoorfdesmopnlo4y2e1e8saemtpalo3yMeepslant `iwnecrleudreedviienwtehde. moOrntlaylitthyosfeolwlohwo-uwpo.rkOefdthfeor 1680moknntohwsnordemaothrse, (1376788dewaotrhkceerrst)ifwiceartees woebrseerovbetda-itnoe-de.xpOevcetreadlrlattihoefnorucanmcoebrfddeeeaattrhhsswwaass1s.i0gn(iUfbiecla,nteltyall.e,ss19t8h0a)n.expected. The
and empVl.oLybm.entInaatareptlraonstpewchteirveecCo8hoarntdmoortthaelriftylusotruodyc,omaproeulnatdisonasrheimpabneutfwaecetnurmeodrtwaelritey ifnevmeaslteigwaotrekde(rGsilelmiplalnodyaenddbMeatnwdeeeln, 11994973)a.ndTh1e98c3o.hoTrhtecoanlsli-sctaeudsoesfs2t7an8d8armdailzeedanmdor7ta4l9ity riantcere(aSsMedR)cawusaes-s0p.e7c5iffoircmSaMleRsfaonrdme0.n7o7frowrofemmeanl.esT.heThSerMeRwsafsornoprsoisgtnaitfeiccaanntcleyr were 2w.e03rie4n tohbeseerxvpeodsaenddgr2oeuxppeacntde0d.d5e8iatnhtshfernoomtp-reoxsptoasteedcagnrcoeurp.. AImntohnegemxepons,ed10gyreoaurpstohfere eprmopsltaotyemceanntceirn mCo8rtparloidtuycwtihoennwcaosmapsasroecdiattoednowietmhpalosiygmneinfitcainntp3r-ofdoulcdtiionnc.reaGsieveinn the smasasloclinatuimobnebreotfwpereonstpartoedcucatnicoenrwdeoartkhsanadndptrohsetnaatteucraalncehr miusstofbtethveiodeiwsreedasyaes,htyhpeothesis Cg8en,etrhaetirnegsualntsdofntothiosvesrtuidntyearpnrdetoetdh.erIcfltihneicparlossttuatdeiecsasnucgegremsotrtthaaltitCy8exmcaeyssiniscrreealsaeted to prostate cancer mortality through endocrine alterations.
VI. DISCUSSION OF ENDPOINTS
VL1. Discussionof TargetOrgans
dogs, re`gTahrepdlreismsaorfyrtarogeotfuoerxgptaonsfuoerer.C8T-hiendhuecpaetdottooxxiicciittyyimsatnhiefelstisiavnsimeniccrree,asreadtsl,iavnedr
``nweecirgohstiss,ofhetphateoclievlelru,laanrdhyipnedrutcrtoipohnyo,fplievreorxdiesgeonmeersat(iroatns, ainncdrmeaiscees oinnllyi)v.erMeannzyyomefst,hese
epfefreicotds. wEevrieddeenmcoenofsthreaptaetdottooxbiecirteyvewrassibnloetwehveidneanntiimnasltsudwieerseinprmoovnikdeedyswiotrhhaurmeacnosv.ery
g
Incontrastwiththerodeat,thetarget organsinthemonkeywerethe
2&
LLEC,
-- "242450 CUACRACACASTSRERREEIGZISASTTTIROYYNNNO| O.OR.38ME2US5-MI2A661NLHEALTH C8 EXPOSURE
tgahsetlriovienrtedsoteisnanlottraacptpaenadr ttohebereatipcruilomeanrdyotthaerlgieatlosrygsatneimn(hGurimfafnisth, aenxdpoLsounrge,to19C880).appWehairlse
to modify the hepatic and immune response to xenobiotics (Gilliland and Mandel, 1996).
VI.2. Discussion ofDifferences in Species-Specific Sensitivities
a5aninc`rTheeasiendiunctthieonaocftipvietrioesxoifscoemrteapirnolpiefreroaxtiisoonmeb-ysxpeencoibfiiocteinczsyimsegse,noerraalslyadneitnecrrmeiasnee.d pirnotlhiefenruamtieornici alasosrocvioaltuemd ewidteha:siitnycorfepaesersoixnisnoummebserinantdhevaoflfuecmteeodf poregraonx.isPoemreosx;isaonme sicepnleclcrieteaussm.eoriWsnh.DilTNehAerastpyshnaetnnhdeosmmieisncaoenndaorlfeipvpeaerrrtgoirxcouiwlstaorhlm;yeaspnerdnoslliiiftveeirrv,attLioeotyndhiiss gnpohcteelnlu,oniamfneodnropmna,naccgrrueoiastnsieacallapciigns,ar
cats, dogs and primates (including man), are predominantly non-responsive.
VL3. Tumors Associated with C8 in the Rat
intheraCt8whaassbfoeuennd tdoemboensatssroactieadtetdo wbietahpteurmooxrissionmteheprloilviefre,raLteoyrdiingtcheellr,ata.ndC8paencxrpeoastuirce
`acinar cell. Peroxisome proliferators, in general, were initially recognitzoebde associated with hepatocarcinogenesis in rats. However, more recently peroxisome proliferators have been associated with the induction of a triad oftumors in rats: liver, Leydig cell, and pancreatic acinar cell. Hyperplasiaofthese cell types istypically
`opbesreorxviesdomperiporrotloi,fearnadtoarslo(ncglowfiitbrha,tteh,eHoCFcC-c12u3,romrfetneheyolnpcllacosfie ean.apSaetvee,raalndknWyoewtnh-14,643)
are reported to induce this triad of tumors in rats. Hence, this tumor profile appears to be.
prcoolimfmeorantoprhs.enomenon for at least a subsetof compounds that are peroxisome
V13.a. Significance of C8-Induced Rodent Tumor to Human Risk
V1.3.a.l.Liver Tumors
`The abundanceofdata indicates that there is a hepatocarcinogenic hazard of
peroxisome proliferators to responsive species (rats
the carcinogenic hazard to non-responding species,
and mice) in chronic studies,
such as humans, is clearly
whereas
Questionable. The epidemiology data, albeit limited, strongly supportthat the relevance
`ofthe hepatocarcinogenic effects of C8 and other peroxisome proliferators for human
hazard assessment should be considered negligible.
V1.3.22. Leydig Cell Tumors
Leydig cell hyperplasia and adenomas are commonly observed in Isboratory rats.
`The incidenceofspontaneous Leydig cell adenomas in Crl:CDBRratsranges from
`approximately0-12%by2 years of age, andrangesfromapproximately 64 -100 %in
=
&
F344 rats. Incontrast,theratein humhaasnbeesnreported tobe approxima0t.4epleyr
g
*
009534
EID080831
"LARD CHARACCATSERREIGZIASTTIROYNNFOOR38S25U-M26A-1N HEALTH C5 EXPOSURE
msiulglgioensat(0s.u0b0s0t0an4t%i)a.l dAilftfehroeungche aidnirtheectsucsocmepptairbiilsiotny iosfsroomdeenwthsaatntdehnuuomuasn,sthteodLaetyadig cell tpurmoodruicgeenLeesyidsi.gTcheills tius msourpspoirntreoddbeyntesptiuddeimesiobluotgayredactoamfmroonmlcyominpgoeusnteddsbtyhaht ucmleaanrslyand are not associated with Leydig cell tumorigenesisin humans.
Leydig Cce8llasnadndotehreer hpyeprootxhiessoimzeedprtoolpirfoedruacetodtrohsesneottupmroordsucveiaiandcirfefaesreesnitnmpeecrhoxainsiosmmes in anthdanthteherelfiovreer truemloervsan.ceThtoehmuemcahnasnicsamnonofttbumeorciogmepnleestieslyisrunloetdcooumtp.leHtoewleyvuenrd,eristtisood, kalntoerwinngtthhaet neonnd-ogcerinnoetosxyisctecmo.mpTohuernedfsor(es,uacthhraessCh8o)ldprfoodrutcuemoLreiygdeingescielslitsuemxopresctbeyd. If tdhoissei-srtehsepocnassee,asusseesosmfeantm.argItiinsoifmpsaofrettayntaptporcooancshidiesratphperosplroipaetoefftohrethdeosqeua-nrteistpaotnisvee at the lowend ofthe observed range in determining en acceptable marginofsafety.
V13.3. Pancreatic Acinar Cell Tumors
the pancCr8eaasnadnodthareerhpyeprootxhiessoimzeedprtoolipfreordatuocrestdhoesneottupmroordsucveisiandcirfefaesreesnitnmpeecrohxainsiosmmes in trhealnevtahnecelitvoerhtuummaonrss.caTnhenomtebcehcaonmipslmeotfeltyumroulreidgeonute.siHsoiws enovteruntdheerrsetoisod,garnodwitnhegrweefoirgeht osfheovuilddebnectertehaatetdthseimpialnacrrleyattoicpearcoixniesrocmeel-lptruomloifresraarteorh-oirnmdounceadllLyeymeddiigacteeldl,ttuhmeorresf.ore they
VIL SUMMARY
guineapiCg8hstaosm6o8d0emrga/tkegaciuntaedourltalmatloxeicriattys.wiAtnh aLqDuseoosusrapnagstiengoffrCo8mp1r7o8dumcegd m/iilndkmteogle `asmoldoerwaatse d1e0r0m0amlgi/rkigt.atiIonnsiilnlraatbibointsofseonldicdliCni8cailntsoigtnhseofratbobxiitcciyteypwreordeuocbesdemrovdeedraattdeoses `hciogmheaaclutoepiancihtayl,atiriiotins,taoxnidcictoynjwuintchtiavi4t-ihs.ouTrhAeLseCoocful0a.r8emfgfe/cLtisngrtahdeuaraltl.y Sruebceehdreodn.icC.8 has inhalation exposure to C8 produced reversible liver effects at concentrations as low as 8 `tmhge/hme'p(amteaostuorexdiocafsiC7t.By6imngt/hme')r.at.OIrnalcharnodnsikcinfeabesdoirnpgtisotnudisesubicnhrraotns,icC8stupdrioedsuccoendfianrmed indcerveelaospemdeinntcaildetnocxiecofortmuumtoargsiennitcheinlsievvee,rpaalntcersetsasf,oarnmdutteasgteinsi.ciCty8.wesfoundnottobe a
rodents`Thhaesrbeeela tehevftoaochunsuocmfaseenvehreaallthinovfetsutimgoartosrisn.duRecgeadrbdyipngertohxeilsivoemr,eptrhoelriefeisraatosrtsronign.
atshseoscuibastieoqnueanntddpervoebleobplemelnitkofbreotdweenetn lpievreorxtiusmoomres-.proAlicfoemrbaitnora-tiinodnuocfedinlivvievrogarnodwtihn avnidro
studies as well as epidemiologydata, has ledseveral investigators toconcludethat
`hhepuamtaincseafpfepcetasr, taondbethienrseefnosrietitvheeosre unnornegsepnoontsoirviecatogepnetrsopxiossoeme-liptrloeliofrenraotor-induced.
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HAZARD CHARACCATSEBREIGZIASTTIROYNNOF.OR38H25U-M26A-1N HEALTH C8 EXPOSURE ehveepnattso,cawrhciicnhogleenaidctohatzhaerddetvoelhoupmmaennst. oEfvLiedyednicgecieslallasnodacpcanucmruelaattiicngactihnaatrtcheellintiutmiaotrisng oafrtefhreotmescthisanagnedspainnctrheeasl.iveAr.ltThohuegshe thheepsaetircelcahtainognsehsipasppneeaerdttooabletecrotnhfeihromredm,oniat licloinkterloyl t`hAadtditthieosnaelelxyt,rparheopgartaimcstmuomnoirtsoproisneg ltihteteheoarltnhoocfaCrcBi-ncoxgpeonsiecdhawzoarrkdertso haunmdarnest.rospective. CcoBhoerxtpostsuudrieesaonfdwaodrvkeersresheuxpmoasnedhetaoltCh8pefrfoecvtisd.eno evidenceofan association between
opportunOiftpyrifomraerxypcosounrceienmtihnehwumoarnkspliascteh,easnldotwheclmeoadrearncaetoe-fhCig8hfarcoumtehtuomxiacnityb,lood, the regardlessofroute of exposure.
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H4ZARD CH: ?CTAESRRIEZGAITSTIROYNNFO.OR38H25U.M36A11N HEALTH C3 EXPOSURE REFERENCES "DuPontCo,HaskellLaboratory ReportNumbers(HL):
55-61, AcuteOral Test.1961, H. Sherman.
56-61, Subacute Feeding Study.1961, H. Sherman.
123-65, Effects ofFluorocarbon Disbursing Agents on the LiversofRats andDogs. 1965,
J. R. Bames and H. Sherman.
124-65, Two-Week Feeding Study. 1965, H. Sherman.
128-68,Acute Oral Test.1963, S. B. Fretz.
160-69, Acute Inhalation Dust Toxicity.1969, F. O. Tayfun and R. S. Waritz. 253-79, Inhalation Subacute.1979, G. T. Hall.
635-79, Eye Irritation Test in Rabbits. 1979, D. F. Edwards.
636-79, Skin IrritationTestonRabbits.1979, D. F. Edwards.
659-79, Skin Absorption LDso - Rabbitand Rat.1979, D. F. Edwards.
589-80, Rat Skin Absorption Subacute Study with FC-143.1980, L. S. Silber. 682-80, Skin Absorption LDso-FemaleRats. 1980, J. E. Henry.
205-81, Subacute Inhalation ToxicityofPentadecafluorooctancic Acid, Ammonium Salt.1981, S. D. Nash and M. A. Britelli.
291-81, Oral LDy; Test in Guinea Pigs.1981, J. A. Hall.
295-81, Oral LDsoTestinRats.1981, J. A. Hall.
329-81, Oral LDyyTestin Mice.1981J,. A. Hall.
560-81, Mouse Feeding Study - 14 Day.1981, L. S. Ford.
565-81,AcuteOral Toxicity ComparisonTest inRats. 1981, L. Hinckle.
567-81,Oral LDypTestinRats.1981,J.E.Heary.
2
Btu seacae PerfluorooctanBoloaotde Leiv ntheeFl emas leRat.1981, Kennedy,
&
n _eoniy
EID080834
cAHAsZARm D CHAeRACCAo TSERREIm GZIASTTIvROYNNFoN.OR38H2o5U.M26A-s1N HEmALTsH C8aEXPOeSURlE
600-81, Liver Weight Comparison in Castrated and Ovariectomized Rats vs. Normal
Rats. 1981, L. Hinckle.
537-82, Fourteen-Day Feeding Study in Male and Female Mice.1982, J. E. Henry. 788-82, Acute OralToxicity of FC-143 as a Functionof Age.1983, L. Hinckle.
138-83, C-8 Liver Weights
Females. 1983, C. N. Wyle.
in
Rats
and
Mice:
Oral
Administration
to
Males
and
DuPont MR 5686, Investigation of Hormonally-Mediated Mechanisms for XenobioticInduced Leydig Cell Tumors in Male Rats. (1989).
3MCo.Reports:
Personal communication, J. Long to P.J. Gort, January 8, 1979.
3M Report M-601 (1981).
3M Report 0681TRO110, 1981.
3M Product Toxicity Sheet, May 24, 1996.
Biosearch, Inc. Report No. T1395, March 4, 1976.
Corning Hazleton, 17388-0-455, May 16, 1996.
Corning Hazleton, 17388-0-437, April 25, 1996.
Hazleton Laboratory America, Inc. 26-87 (Submitted to EPA, TSCA 8CAP Submission, Fiche 536984).
Litton Bionetics; LBI Project 20838, February 1, 1978.
Riker Laboratory Drug Metabolism Report 1-20 (1980).
Riker Laboratories,Report 09790AB0485, March 15, 1981.
Riker Laboratory 0281CR0012, April 1981-May 1983.
University ofMinnesota Environ. Path Lab, T2942, April 9, 1981.
PublishedReferences:
`Appl.Pharmacol, 134; 18-25. g Biegel, L. B,, R. C. M. Liu, M. E. Hurtt, and J. C. Cook (1995). Effects ofammonium
`perfluorooctanoateon Leydig cellfunction: Invitro,invivo,andex vivostudies.Toxicol,
Zz
g
28 Loan EIDO080835
.
HAZARD CHARA`CCATSERREIGZIASTTIROYNNFO.OR38E25U.M26A-1N HEALTH C8 EXPOSURE
Cook, J.C, M. E. Hurt, S. R. Frame, and L. B. Biegel (1994). Mechanisms of
eTxotxriachoelpoagtiisctt(usbmsoirraicntd)u1c4t,ion by peroxisome proliferators in Crl:CDBR (CD) rats.
Caodoekn,omJa.sC,byS.amMm.oMnuirruamy,peSr.flRu.orForoacmtea,noaantde:M.AEp.oHssuirbtle(1e9n9d2o)c.riInned-urcetliatoenodfmLecehyadniigsmce.ll Toxicol. Appl. Pharmacol, 113: 209-217.
Fayerweather, W. E, Liver study of Washington Works employees exposed to C8: Results ofblood biochemistry testing. DuPont, Epidemiology Divisionof Corporate Medical, January 15, 1981
Gilliland, F. D. and J. 5. Mandel (1993). Mortality among employees ofa `perfluorooctanoic acid production plant. J. Occup.Med. 35: 950-954.
Gilliland, F. D. and J. Mandel (1996). Serum perfluorooctanoic acid and hepatic Ameenzryimceas,nJloiupropnraoltoeifnIsn,daunsdtrcihaollMeestdeircoiln:eA2s9t:u5d6yo0-f56o8c.cupationally exposed men.
pGerirfffliutohr,oFo.ctDa.noaantde.J.AEm.L.oInndg.H(1y9g80.)A.ssAonci.mJa,l 4t1o:xi5c7i6ty-5s8t3ud.ies with ammonium
Johason, J. D,,S. J. Gibson, and R. E.Ober (1984). Cholestyramine-cnhanced fecal e{l1im4iCnaltpioenroffclaruboorn-o1o4ocirtnpraoatntasosasatieturemad[mi1n4iCsltpreartfilounoorfooactmamnoesnuilfuomnate.Fundam. Appl. Toxicol, 4: 972-976.
Keanedy, Jr, G.L. (1985). Dermal toxicityofammonium perfluorooctanoate. Toxicol,
Appl.Pharmacol, 81: 348-355.
:
IKnehnanleadtyio.nJTro,xiGc.Li.t,y Go.fATm.mHaolnl,iMu.mRP.erBfriltutoerlloio,cJt.anRo.atBea.meEsd,.CanhdemH..TCo.xCihce,a24((11928)6:).1325 1329.
Kenedy Jr, G. L. (1987). Increase in mouse liver weight following feeding of 3a0m0m.onium perfluorooctanoste and related fluorochemicals.Toxicol,Letters 39: 295-
Liu,R.C. M, C.Hahn,and M. E. Hurtt 199T6h8edi)re.cteffectofhepaticperoxisome proliferators on rat Leydig cell function in vitro. Fundam,Appl.Toxicol, 30: 102-108.
g Liu, RC. M,, M.E. HuJ.Cr.Cotok,,end L. B. Biegel(19E9ffe6cto)ft.he
pacetriovxitiysoinmeadpurlotlimfaelcaetoCrr, la:mCmDoBnRi(uCmDp)erraftlsu. orFoocutanonaAtpepd(lC.8)Ta,oxoincmhoelp.3at0i:c 2a2r0o-m2a2t8a.se
2
s
Gaon EID080836
|
HAZARD CHARACCATSERREIGZIASTTIROYNNFOO.R38H25U-M26A-1N HEALTH C8 EXPOSURE
(O1b9o9u7)r.n,MJe.cDh.a,nSi.sRm.sFfroarmteh,eRp.anHc.reBaetlilcJorn,cDo.geSn. iLcoenfgfencetcsokfet,hGe.pSe.rEolxliisototmeanpdroJl.ifC.eraCtooork `Wyeth 14, 643. ToxaindAcpploiedlPhaormagcoloygy 145: 425-436. mPaosrtpohoorl,oTg.icPa.l,Ks.tuPd.ieLseoef,aM.mmAo.nPierurmi,paenrdflPu.orJ.ooGicltlaineosa(t1e9-8i7n)d.ucBeidohcehpeamtiocamlegaanldy and
peroxisome proliferation. Expear ndMiolemcule ar Pnathtoloagy4l7: 98-109.
Perkins, R. G. (1992). Investigationofammonium perfluorooctanote effect on hormone
levels and peroxisomal proliferation in the rat.TThoexicologist 12(1): 52.
tSetraaplteosg,enRi.c Ep.o,teBn.tiAa.loBfuragmesmso,nainudmW.peDrf.lKueorronosct(1a9n8o4a)t.e (TAhPeFeOm)briyno-tfheetraalt.toFxuincidtaymaenndtal and Applied Toxicology 4: 429-440.
Ube, F. A, S. D. Sorenson, and D. E. Roach (1980). Health statusofplant workers ex5p89o.sedto fluorochemicals-a preliminary report. Am.Ind.Hyg.Assoc,J.41(8): 584-
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30 } casa.s EID030837
Date: 11/16/99
5: BOGDANMS
Time: 11:09:28
OGDANMS
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General HumaPnroHpeoaslatlh taondCoEnndvuicrtonamental Effects Risk Analysis on C-8
Pupose: eTnhveirpounrmpeonsteorfotmisexpprosoujreecttofsoC-e8vadluuraitnegtmhaeniusfakcsttuoreh,umraannspheoari,thpraondducttheuse. aSenmdiqduiasnptoistaatoifvCe-e8s.tiTmhaeteasnoalyksiss wislolbtehactoenxdpuocstuerdesinyaiefladsihngiotnhethhaitgwhielstprroisvkisde Gaenvelboepeidc.enRtfiisekdsafnrdomremcaonmumfeancdtautrei,ontsraonnsproerdtuacnidngptrhoeduscetriusskes wcialndbeeveloped in atewranyattihvaet.wilTfhaeciptraotjeecftuwtiulrebceomcponadruicsioends oinftrirsekseepsarttism.atTedhfofrrsptotwenotiwaillCb-e8 cchoanrdaucctteendzeind.paTrahleef,inianlwphairtchwihludmeavnelhoepalctohncalnudsieocnosloogniceaxlproisskusrewsiltlhbaet cStornattreigbiuetse athnedhailglheemsattiivseks csaonbtheatdreevceloompmeedn.daTthioenpsroojreicstks mesatniamgateemdetnottake 12 mbeolnotwhswitlorceoqmupilreetcealfarboomratthieotnimweiotfh anpaprtoiporni.ateTphleanEtxppeorssuornneela.nal(yTsheesdlaitsetesd prosentod assume a Feb. 1, 1997S8Uapproval date.)
S1cope:Human Heal Risk A Hazard dentfication
anTiamselTine Est 8C0o0s0ts)
Hcraiztiacraldsoxtiolhtyumeannhdeapltohofwiirlelbneevtarnecsveietwoedhuamnadnsuhemamlatrhiizsekdwiinltbheiisdeecnttiiofnie.d Tahnde TpohteentHiaaslkedlolsitmoxeitcatrysstuombmeaursyewdiflorbeinutpedrsapteecdieassepxatrrtaopfotlaitsiotnaosfk.isk wi be discussed.
8. TDhoesed-Reosponsse Aenaclhy-asriascrtrisetcssofCp-8wolbneevaslua3te0e0d9.7Thismayinc4l3u2d0e0 cdwoehnvederulecotpnieencdgebsbaseasnrecydh.moAanprtpkhreodpolrisikeealtayenmadolodyssieemsoeftteaorcistdoeonnrt.itiTynthneeor-spophbeacsriemerasvceeoxdktiarnadepvtoeilracstsieooenffCwfi-el8cawliselvoealblseso bapeprreovaicehweesd.wiIl pboessdiebvlee,lorpueddimteonftaarcyiaptheysiinotleorgsipceaclileys-beaxsterdappohlaatrimoancookfirnisekt.icRsisks vs dose relationshwipislbe developedinthis phase
C. EaRixerpabososomunera,ebdlArenianelkxyipsnoigsswuarteers,cednearrmiaols,afnordCo-t8hewriolrbaeldiengveesl9to1ip3oen0d1.p8a7tThhwiasyas.e kInetay1ke6sr,to0a0ti0necslaunded frdruoarnmasttpiohorentps,lopafrnoetdxiupcoetstuuosrheee,wlaiplncdbhaewradasectvteeelrdoiipzseeptdo.hsaelHsaaoespexkrepalotsiwouinrlsew.poarTtkhhwewibahuyssaifnnoearsssmsawinigulnfepadrcotpvueirrdisenogn,(s) HTa`hesexkpseeecldtleadwtuiatpwhpdiealrtbcaeotonabcnuolnacfteneitdlr.iadMmtiotieonfntsoneorCftcahCrel-eso8etIeenxctphhonesiuaqrfufeeessc,tmdeaedypmeebndediuiansge(tadhlt,eowaacvtaaellrca,busilolaitt)y.eof data. Thecostassociatedwit thi takincudeonyHaskepersonnel ime.
D. RRiisskksChwairlabcteesriuzmamtairoinzed according to the major routess2o1f1e5xp7osure (a,1w6a.t0e0r0, dermal, otheroral) or eachC-8application (manufacture, transport,productuse,
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I Recommendations on Risk Management Strategies and AteTroatnvess aso cecpoelroagdicoanlsrceTocheuipdtsorbssee,cttiaBornageswteielddeotvonaftlheueadstescatnaaellyclsatersvg.eesrttlehsycekoimsmkefsnrddtaheteinoltneesadswtcloosbhteu.mmTaahndisehweiaallsfbtoeawanidvcehry Siafocive exercise (nanaive) and wil require some inpu rom the plant peopl.
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INTEROFFICE NENORANDUN
:
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DTeelpt:Mo: E8-N8G6I3N-E4E4R1I5NG POLYMERS
To: 7 addressees
CC: 3 addressees Subject: EPA REGION I11 ECOSYSTEM ASSESSHENT OF DRY RUN CREEK
06s. i
0 Epos 7
Fv1,
THIS EPA,
MPOHRINLIANDGE,LPHWIOAO)DY FOIRREALBAONUDTAANDHA[LFMETHOUWRITHTOSARREAVIECWASPHAERR
(REGION I11 PLANS TO OBTAIN
SCRAEMEPKL.ES TNHEEEDEPDURTPOOSECONOFDUCTTHISANASESCEOSLSOMGEINCTAL IRSISTKO ALSOSOEKSSFMOERNTPOOTFENTTHIEALORY RUN
CTOOXNITNASMINWAHITCIHONMAIYN BTEHEREDSRYPONRSUINBLCEREEFKORDRTHAEINAOGBESERANVDEDIDDEECNLTIINFEY APNODTENTIAL
APSHYASIOSLOOUGRICECALOFABWANTOERRMALAINTDIEFSOODI.N CATTLE WHICH USE THE DRY RUN CREEK AREA
SARA FROM
AND A TODAY
TEAM OF THROUGH
4 TO 5 FRIDAY
PTOEOPCLOELLWEICLTL SABEMPLIENS THFEOR DRTYHE RURNISCKREASESKESASRMEEANT.
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PPLEARNFSORTMOEDSAETNDMIUSCHISGOAMNE SITNAFTOER.M)ATION ON RESULTS OF COW TISSUE ANALYSES
SSEADRIAMEPNRTO,VIDWEADTEMREAANDCOBPIYOTOAF (AANDIRMAAFLTSPWEOCRIKMEPNLSA)N FFORROMCOTHLELECDTRIYNGRUNSOICLR,EEK. AADDCIOPTYIONOAFLTHIINSFOWROMRAKTIOPNLANNOHTASSUBMEMEANRIZSEEDNTITNOTHTIHSE ANODTDER.ESSES AND CONTAINS BDARSAEFDT OWNORKOURPLADNI,SCULSISSITOENDSBTEHLIOSW MAROERNITNHGE WTIYTPHESSAOFRASAANMDPLIANGREVWIHIECWHOFWILTLHEBE PTEHREFSOERMSEADM.PLESV.ARIONUOST ATLOLXICSIATMYPLEASSSEWSILSLMENBTESTAAKNDENANFARLOYMSDEUSPOWNITLLPBREOPEMRADTEY AONND EXACT SAMPLING LOCATIONS HAVE NOT YET BEEN DETERMINED.
- OBTAIN FIVE SEDIMENT AND SURFACE WATER SAMPLES FOR TOXICITY TESTING.
- UFSAETDHEAFDORMITNONXOIWCSI,TYEATERSTTHIWNOGR.MS AND "HYALELLA TO BE
~ PERFORM BENTHIC SURVEYS WHERE SAMPLES ARE TAKEN.
- WPAETREFRORMSAMEPLLEICNTGROSLHOCOACTKIOFNISS.H SAMPLING FOR TISSUE ANALYSIS AT SURFACE
- OBTAIN FROG EGGS FOR ANALYSIS OR LIVE ADULT FROGS FOR BREEDING.
- COLLECT GRASS SAMPLES FOR ANALYSIS.
- CWOORLKLECPTLANS)MALFLORANTIIMSASLUSE A(NDAELEYRSIMSO.USEEAXNADMINMEEADJOAWW VBOONLEESIAMNPDLITEEDEBTAHSEFDORON DISCOLORATION.
- UPSOETEDNTAITAALOBHTEAALITNHEDEFAFBEOVCETSANODN AAPPRLOBYINT,O RAEDF-OTOADICLHEDAIHNAWMKO,DELANTDORAESDSEFSOSX. ST ADRAIDINNTDISCEAETEDTHITSHERMEENTWIOOUNLDEDBEINANTHEATTWEOMRPKTPTLAON.CATCH THESE ANIMALS BUT
w : THE WORK PLAN CONCLUDES WITH A LIST OF
QUESTIONS, WHICH THE STUDY IS DESIGNED
17 TO
TESTABLE HYPOTHESES, HELP ANSWER.
OR
COG 35
EIDO17891
73 000589
* Potesta & Associates, Inc.
Telephone: (304) 3574990
Engineers and Environmental Consultants
Fax. (304) 3574988
TT
UniversityofCharleston,CoxHall, 2300MacCorkleAvenueS.E., Charleston, WV25308
July 28, 1997
+2wnertnzuekoorv,e
Mr. Daniel Weber Senior Engineer E.L DuPont DeNemours and Company Washington Works, Building | P.O. Box 1217 Parkersburg, West Virginia 26102
Sub 35s
Dear Mr. Weber:
RE: DRuepsopnotn,seDrtyo ARfufniliLaatneddlColnPsterrumcittiAopnplTircaadteisonF,ouFnodraUtsieonatcoPumbmleinctHseaornintgh,e
Trades
[was asked Foundation
to offer my regarding
thoughts on thefourcomments made the Dry Run Landsill draft permit.
by the These
Affiliated Construction comments are offered
gweintehroaultirnensaetaurrceh.inMg ythfeirssptetchiofiucghftediertahlatanDdu/Poornsttastheoustladtuntte oarteremgputlattoiorne,spaonnddatroetihnetseenqdueedsttioobnes
iatnttehgerihtey,arwihnig,chbuwtillletbteheadadgreenscsyedainnswtheeratgheenmc.yT'hsefsoermaarleraecscpuosnasteiotnosctohmamtecnhtasl.lenge the agency's
COMMEN1T
aTchceorddraanftceawliltohwsstaftoerrengeulwatliaonndsf,iallndonsttaotpe sohfouelxdisntoitnagl.loTwhea leaxnidsStiilngonltahndefairlleam,uwshtibceh icslaolsreedadiyn impacted as is indicated by the elevated fluoride levels.
backinTg"hoeffaacinleitwycheallsonnotobreaegnacinlsotsaendeoxuits,tainngewceclelilniostbheeirncgaasdesd.edT.hTehree sitsanteobaprsoahlilbiotwieodn a"gpaiigngsyt
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:
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, Mr. Daniel Weber
Page 2
July 28, 1997
IfIT
occurrence.
uTndheersretgaunldattihoensfascptescciofryrewchtalty,atfhaeciflliutoyriisdetovdaoluwehienntmheongirtoournidnwgawteelrlswasshoawoenleetviatmeed
levels. [would assume that the agency and the company are following the procedures as required.
Ifelevated fluoride levels are shown to be a problem, the appropriate action will be taken.
Act is encouraging DuPont to move to a "green fields" site for the new cell. The agency
slhogoiucladlleyncboeuirnagtheetsheamuesepoflatcheotsoeaefxfiescttitnhgeibnedussttrcioanltrsoiltepsotsositbhleed.egree possible. The waste should
COMMEN2T. Additional treatmentofleachate to mestwater quality limits.
`The available information on qualityofthe discharge into Dry Run is based uponthequantity
and quality of the leachate, as well as the efficiency of the existing treatment system. Those
performance levels cannot be used to estimate the effectiveness ofthe new system. The new system,
`with its larger area and baffled aeration area, is expected to have higher removal efficiencies. In the
event that the limits cannot be met, DuPont can eithertruckthe leachattoe their plant on the Ohio
River (I
to the ex
assume they ha apv ermeit modification in place
isting site. Thereisnoproofthat the new system
to allow
will not
this)
meet
or add additional treatment
the limits. The bottom line
is DuPont will have to meet them or apply to Environmental Quality Board (EQB) for a variance for
Dry Run. It is a compliance issueifthey fail to meet the limits.
COMMENT3
Limits for fecal coliform, boron and formaldehyde.
The director must first determine that these materials are, or may be, discharged at a level
to contribute to an excursionofthe water quality standards. The director or his representatives have
reviewed the information and determined that they do not need to be limited at this time. The
agency should evaluate the effectiveness of the new system and, if additional limits are needed,
modify the permit accordingly. Thereare
boron or formaldehyde. EPA suggested am
nowaterquality standards promulg
bient goals are not regulations until
ated by
adopted
the
by
EQB for
the EQB.
`The inclusionofthese as limits are discretionary onthepaorftt he agency. They can be added if
they are felt to be a problem.
COMMENT
WET testing on 2 continuing basis.
Potesta & Associates, Inc. :
[IEREEY
EIDO52804
Me Daniel Weber
Page3 July 28,1997
`The agency is requiring the initial whole effluent toxicity (WET) testing on the facility. It Iistisstaanwdaasrtdeoprfarcteiscoeurtcoedsistocornetqiuniuree sthuacthrteeqstuiinrgemwehnet,n isthdoouelsd ntootxiacpiptyeabretsohboewanpnrootblteomb.eTahperaogbelnemc.y
tchaen aetffalnuyentt.imeSthaokuelWd EthTteeasgtesoncnythdeeecfifdleuetnhta.t tTohxeiciatgyenicsyacnanisrseuqeuiorfecDounPcoernnt,tothdeopWerEmTittcesatns obne
`modified to require it, but to require it where there is no history oftoxicity problems is useless.
Tam available to discuss these issues further,if you feel that wouldbe helpful.
sus'
LEMsrs
ce: Mr. Ronald R. Potesta Mr. Mark Kiser
7 J
Zz
Laidley Eli McCoy
:
Potesta & Associates, Inc. 8
000nsn
EID052805
oo
74
009585
CONFIDENTIAL
C
AnticipaDtreydRuQnuesLtainodnfsill-- TaFsIkNALTea(m1/29/97)
A. Genmeral Information / Physical Features / Operation
1. Wchoynstwrauscnt'etd,a alnidnewrhyinsistaltlheedWVwDhEe?n mtahkeinlganydofuillinswtaasll one now?
(Quoted material is from the draft permit.)
TRheegullaatnidofnisllofper1m9i90t apnrdeda"ttehde dtehesigSnolirdequWiarsetmeenMtasnagofemetnhte SWMR a1rlaendnfoiwllbeitnogiimpnrcoovrepogrraotuenddwianttoertphreotdeecstiigonn..of the Dry Rum
2. How long will you be operating the landfill?
Por the foreseeable future. |
3. aWhneonthetrhearceuar,reaotpencelalnotisherfulcle,il?vill you expand the landfill to
Deceocniosmiiocnaslabcoountsideexrpaatnisoinosn ainndthtehefurteugruelawtiilolns/dreepqeunidreumpeonnts in effect at the time.
4. Why were those new tanks installed at the landfill?
TTohiscolplreacctticleeacishatreequfiorredtrabnysptohretSttaotetheinSitthee ifnotrerdiimspousnatli.l modifications required by the new permit are completed.
5. Wahsathe'asbouhtaulalilngthtehewiwnadsbtleowdnowntratoshthtehatlacnodmfielsl?off Boso's trucks
dAlilrttfrurcokmseaxrceavactovieornesd,duwriitnhg cthuerreenxtcepctoinosntroufctitornuckactliovaidtsy.of Btlhoawtinwge mcaatnerfioalllowi-supu.nusuPalleas-e- cwael'ld 8l6i3k-e20t0o0.be contacted 80
6. mWoharte asbeocuutre?illegal dumpings at night? Why isn't the landfill
OPpreortaetceteddobnylyldoucrkiednggadtaey.lighNto shocuhresd.uledIfaycotuivwiittyneasfsteranydark. activity after hours, please contact us at 863-2000.
7. oIftheyrouldaondfsiulclhs?a good job, how come you had to close down your
LLoectaalrtl-a-ndfTihlelam-o-unrteacofhedplacsaptaiccitwya.ste being landfilled has
dceocnrseoalsieddatoevderfortheecyoenaormsi,c
and landfill reasons.
operations
are
being
Cadet
EID0g1089
2
{general formation, continued
8. Aacrteorysoutghoatingusetdo stotargto delusmepwihnegrei?nto Dry Run some of the bad
only Run.
nomhazardous
solid
waste
materials
are
landfilled
at
Dry
.
9. Why were materials taken to Letart in the first place?
Teflon* because
wastes of the
wpoetreentsieaglregatatetdhe ftriommeotfhorera walsatnedfmialtlerfiiarles
rinevsoullvteimnegntfroofm Ttehfelodni*spowsaaslteofinhoatlpaonldyfimlelr wfaisrtee.hadThtehe
potential to is no longer
release dangerous landfilled, there
ifsumneso. lonSgiencreahnoteedpoltyomesregrwaesgtaete
the Teflon wastes.
.
10. What determines what is landfilled and what is incinerated?
Tawnod hfaancdtloirnsg.primFairrsitl,y wiintfhlueonucrewatshteedmeitenrimmiinzaattiioonn: effpoerrtm,ittwieng
prIoycetsosraesusemucohr nreocnyhcalzeardwohuastevwaesrtewemacatne.rialNexats, pwoessitbrlyetothat is
.
abcocielpetrab(lAePB)andsopetrhamtitwteedcafnorrbeucronvienrgheiantouvraluaeltefronratpelanftuelsteam
npereodcse.ssedFintahlrloyu,ghnotnhehaAzFaBrdoaurse wlaasntdefilmlaetde.rials which can't be
11. Leachate
a. What is leachate?
Any liquid that might have contacted disposed waste.
b. WWhayshiinsgttohne WSotraktse rfoerquidirsipnogsatlh?at yWhoauttirsanstphoeritr cloenaccehrant?e to
mTohdisifipcraatcitoincse riesqurierqeudirbeyd btyhetnheewSpteartmeitinartehecoimnptleertiemd.until
Tshuespecnodnecdernsoliisdsa,bouatnd subcihochceomnidciatlionosxygaesn idreomnancdontienntu,nlitnoetdal lthaendfgirlolundowpaetreatriotnos.theThgereaStteastte iesxteinntteproessstiebdlei,n panrdotweectianrge complying.
.
.
s3
EID081090
:
BLLDRERY
EN
C Leachate, continued
c. How long will you be hauling leachate out?
Wies dcoonm'ptletken.ow -- at least until the new permit comstruction
4. Do you have DOH or DOT approval to haul leachate?
Trheequiorpeemreanttisonfofrorhhaauulilnigngnotnhheazlaeradcohuastemamteeertisalasl.l SStuacthe croemqpuliiraenmceen,tseticn.clude licensed drivers, weight limit
e. I saw it leak out on the road: did you report the leak?
MNaoterreicaolrdhoafuleadnyisleamko:mhavzeahridcoluess. inHsopweecvteerd, foifr cionntceegrrnietdy,.
:
let us know. Call 863-2000.
. Is your contractor licensed to transport the leachate?
MAleseot,s aclolntrraecqtu,irenmoetntcsommweirtchiianlhihsauleexri.sting PSC license.
B. Black Water Issues
1. Why did the vater turn black and smelly?
Tbheiesn wraessoalvetdempfoorraraypprsoixtiumaattieolny (tawboouyteafrisv.e moTnhtehsc)olotrhatandhasodor wseurlfeidcea.usedAerbaytitnhge ptrheespeonncdesof-- itrhoantsuisl,fidbeubbalnidnghydariorgetnhrough rtheeappweaatreerd--sinecleimaienrataetdionthbeegcaonlorinaJnudneodo1r9,95.and they have not
2. What effect did it have on the ecology of the stream?
nFergeaqtuievnet simtpraecatm osnurvtheeilwlialndcleifheasoprrovveigdeteadtinooneovfidetnhecearoefa.a
3. wIef byeou'svueremeysosuewdonu'ptimnestsheuppasatgawiinthinthsaotmebloatchekrwawtaeyr?, how can
Wleandafriellcontofidceonmtplythwatithournewworrkeguwliatthiotnhse, WViDnEPcomtboinuaptgriaodnewittheh
.
Sitnactree,asewdillroeunthinaencesurthveeiolvlearnaclel (ompoemriattoriionng)ofretqheuizfeadcilbiytyt.he
.
g
. 065.2.
EID01091
te
c. contents / Materials Lanmdfilled
1. bWehiatngcpalracicneodgeinns,thehaz*adrudmop?us wastes, toxic wastes, etc., are
mThaeterliaanldfirlelquiisrinagnosnpheacziaarldohuasndlsionlgidisw,astase wleanddfeislclr.ibedThe only etahrolsieerd,iraescbtelsytoesx,powsheidchtoisit.conHsoiwdeevreerd, aapsobessstiobsleiscaracihnaozgaernd to opnrloypewrhleynanitd bisuriiendthoer aweitr, anidt cparnesebnetsinnhoalehda.zardW.hen handled
2. pWhaartameetlesres?is Wihnatthaartenl'atndfyiolulretphoarttiinsg?mot om . the list of 19
mWeustdisrpeopsoertofthoeinrlyamtohuonstesmaatnenurailallys; swpeecairfeiedsubijnectthetpoermit; we uopnearnantoiuonncse.d inspections by the.WVDEP to monitor landfill
3. gIosintgheirnetofeDrrtyilRiuzme?r or other chemicals in the landfill vater
2CodndsifsetretnitliwzeirthfSrotmatetimreegutolattiiomnestoandestraebcloimsmehndvaetgieotnast,ionwe do growth. We use no pesticides or herbicides.
D. Toxicity / Other Harmful Effects
1. Is the antifoam additive toxic?
Nsop.ecifEiCc-a2t1i0on(sA.ntif(oMaSmD)S sisheeutsedis ionnacfciloer;damnicneerwailthoimla.n)ufacturer
2. Iisn tith?e algae poisomous to cattle if they drink water with algae
The algae are not harmful.
.
b(lRueep-ogrrteefnaxaeldgaferobmloHoasmketlhlatLacbaniscauonsefilleetharlegaporidsionnginfgr;eshmoswtater
pFruorbtlheermmsorree,porittedishalviekeolcycutrhratedthiinsnoqrutehsetrionnpwlaoiunlsd bsetataessk.ed
.
cfornotmactthsisaplegrasepeicntitvhee: str"eIafm,lewaocuhladtethferopmolyoluurtedlaanldgfailelin the stream be toxic to cattle?" Suggested answer: To-date,
bmeetiwteheenr tthhee DlEaPndnfiolrltahendEpPoAorhasaniemsatlabhleiaslhtehd.)a connection
:
L0GPOR0. 3
EID081092
s-
D. Toxicity / Other Harmful Effects, continued
3. cIsonttahemignraotuenddwgartoeurndwnaetaerrtgheet lianntdofilmly cdornitnakmiinngatweadt?er?If so, will (Quoted material is from the draft permit.)
ADuprnoyanlyRsguirnsousnoidftweaqthueaasrrtmreoertllaytcigavruesoeudtnodwabaatscetkragtrdioastutanidca*glhrlaosyunrsdiewgvanetiaeflriecdantthatimptahcet concentrations.
4. cIsomiintgpoosustibolfeyotuhratlasnodmfeilclhemaincdalcautshiantgyohuarmd?on't know about is
Iftorisa lunalrigkeelnyu,mbesrinocfe ptohessipbeirlmiittiersequiinretshe.qluaanrdtfeirllly In addition, we do several nonspecific chemical and
slceraceheantien.g biological
ootrxegystagsne,incmdeocmnaarinbtdoo)nr,si)n.gCODsuc(hchienmdiciaclatoorxypgaernamdeetmaenrds),asanBdODTo(Cbio(cthoeramlical
Wliatndhfirlelgaorpdertaoticoanusiisngchaaursmi,ngweharhma.ve on vegetation or wildlife.
Wmoe
heavviedeonbcseertvheatd
mtohe impact
W1e993c.onduThcetedrestuheltsStwaetre'eswistthainndaredstaacbultieshetdoxilicmiittys.testing in S. dCeagnratdhee ntoonhoatzhaerrdotuhsinmgsatetrhiatalscoutlhdatbeyomuorpeuthaiznarydoouurs?landfill
M(attheartiails,s bpulraiceedd gion observed to degrade
tthheataonxaeyrgoebniccanennovtiropnemneetnrtatoef) ahalvaendfbieleln extremely slowly. Excavations at mumicipal
mlfaoatoneddrsfitiaullflsfsshtahtvaheatt uwenhcapvouevterseiudnrtvoisvuecthdhe iiDtnetrmaysctRausnfornLaenwddsecfpaiadlpelesr.sareaTnhdatevalreiasotusas
dtruehrmeaaybilnweo.utlodo Iaflpopwaenaytrodbseeogrdsaeldtoarwtilimyoennttpharalot.dutchtesirfcoornmceednttrhaattiownesrewohuarlmdful,
6. Alraendftihlelr?e hIafmfsuol, bwhaecrteeridaoesinitthecowmeatefrromdisc--hartghee ffriolmtertchaeke? pbWeeermchiahtveeckrineoqnugirrfeeoasrsonmtohantttohlabsyelmwieoelnvlietoatrshiantogthtefhroerrpeafreiascmaaeltepcrrosol.bilfoermm., Tshoewen'elwl
009:h2E3:
EIDO81093,
i
"6
L
D. Toxicity / Other Harmful Effects, continued
7. W1hayndfdiolnl'tanydouwhtyellyoue'vreeryosnoewoarbrouitedthaebouCt-8 itc?oming out of your
goCuo-r8v',erTneomrfelnaotmnm+oaganerineucamy.,peADrulfPtlouhonortuogohccotnCa-tm8rooalitsse,intotivsorlaeugnsutulararftiaelcdytbabnyetcaaunusyseed
in of
oteuhxerperhliieegvnheclesinwdtieettrhenacltheadnsdtalantidnagtrhdeist.laatnBdfatishleeldPloaanrneto,unrowte4h0aaryrmeefaurclso.nfoifNdoent(11that
effect in our employees has been observed to-date.
Atdodoitailoanramlinginffoorrmtahteiongenfeorralourpubulsiec:that may be too detailed or oIfrgaC-n8wwoeurled bteo htaheveliavenre.gatWievehhaevaeltcholliempcatcetd, eptihedemtiaorlgoetgic data oloafneniamcolahuilarvteerceamrtcpcoalinoncytoeehgereesnWi.VsoDvEenPWro.ehtihhgaevheelrirfeetphooafrnteetdxhpeetcphtleeadnp.tr,eseCan-n8cde itoshfeaCiowngecaikdiennctehe . EB. Filtercake Issues
1. What exactly is filtercake?
vPfarisoltmteertcbhiaeoksesoiltiiesdsaw,ascmtoienccrveoanottrergraatnetidrsemafstomremfnrtoofmpltsahlneutd.gveasttIethatwiastiescromrpetomroseveaedtdmeofnt
plant, fly ash, and water. It is different from sludge in that excess water is removed and fly ash is added.
Tmhuenicciopmaplonewnatssteofwatfeirltetrrceaaktemenatreplsainmtislarandtocotmhmoosenlyproediutcheedr by
disposed of. in municipal landfills or applied as fertilizer.
2. Wshtayrtdidtaykoinugstitop todistpheosNionrgthofwesftielrtnercLaaknedfiilnl?the landfilland mTohdiisfipcraatcitoincse risequrierqeudirbeyd btyhetnheewSpteatremitinartehecoimnptleertiemd.until
3. How much filtercake have you put in the landfill?
tons: 1994--568.57
1995--3,888.27
1996--3,952.81
4. How long did you dispose of filtercake in the landfill?
From late August 1994 to mid-November 1996
I
i
000.27
EID081094
}
000.:00
75
.
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----
-
.
(AN)
7CAy
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ao 0-8 rion wisMieIchacSeolnesTu.eneHrE ozronne,e wiPmh:.iD.at nesponse sens
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08a. 0c
USFW 0579
TAOFBCONLTENETS
ESFORBABLES o.
teeter
USTORFIGURES o
sw
SECTION
e vii TECHNICAL APPROACH. SUMMARY OF FIELD EFFORTRESULTS,AxDPRELIMINARY
RISKSCREEN ....... 10 INTRODUCTION .
ER PPPS eee
BO
Ia BE estate
RC reer eeeoeeeenn
MEMODOUOOY
: 21 Soil Sampl eosin rr enone
'
3 39
S Smaae irnt gSm une g.S ....ao ...p...l ...o .e. g SerrrrrrtcrreT innnaT .
"ol
34 BS
Del Vee Wl Sigg BlogSumpley
oes
.
BL SmMamma Snay
352 VesewioaSamplag
Bo
333 34
FAdCioelMmactreoanve.se.t.ra.e .Su.gi.i.g.................
TelyTeg
Td
28.1 362
Eteeniafoceeidaa((pBivaortTTtooxxiicwictT yoTere wms).s..s.c .e .
37 Se3o6v3lasPEinmipplreesnpDroenceomMaimiscosTionx.i.y_.. Tes...)
FE Satt Operating Prose
s
a Domematon
5
383 383
SFuealpdlSeaPmapclkianggiosgo,tSAhispmaain,TSoresg,tPreaseva.ion,.wd.Handing
3
Be Mellmdiey
30 RESUL
TT J
HE TSe..n.s.o.l...a.n.t...dimen ArT as D 6
BB eT 6
0005
USFWos80
302 TALMetls. Loon soniye
7
313 Pesicides/PCBs
srs sere bbhtss pats
3
314 VOCs ..... crgonnens srressretitsiese 8
5.15 ToulFluoride sobeser stearate. Le
5.6 Orgasofivorides
snsseerpessias cs
3.1.7 ToulOrganic CarbonandGrainSizeofSoil20d
Sediment... 10
38 WaterQuality PAAMESTs
eee
10
3.19 Bovine Fecal Samples+ -...uiniiiii ieee
IO
32 Biotic SamanpdTislsueiASAlnYSiSg o.oo... eeittiiieii 10
32.1 Beathic Macroiaverebrat+e+s ... +++ evunii ees
1]
-
322 MABEL.
2
323 Fan...
. ssrrresssvesatstsacennun rnold
324 BARWON ....iiitniiiii ie
13
325 VeRRHOR...... iii.
1
33 Hiswlogicalassayofsmallmammalliverand kidney ....................14
34 TORRY TERE eeveeee eee eee
14
40 SUMMARY OF PRELIMINARY ECOLOGICAL RISK ASSESSMENT SCREEN
15
500 DISCUSSION ...oiuueeeeete teat ee eee e eee 1S
SECTION It 10 20
ECOLORISGK AISSCESSAMELNT .......................eeeu. 16
INTRODUCTION ....
rorrrssvesitrristtees snes aunssine BE
LI Objective ovine srorsevone
16
12 Sie Background...
rrreresssrtstersacsinncnselh
PROBLEM FORMULATION ......iiitneiiiinnniiiiia.,
16
21 EcolRioskgAsisescsmaentl
srrrrssvorass erste assna dh
22 idemoifthfeCointacminaanttsoifCOonGenrD. ........................17
23 Exposure CRAREIEAZANOD oo... oeiii eis
tl
24 HazardCharactToexicritiy AzSaSEiSSo:n/ +... ..................17
241 Fluoride .
errsssvrrres cost opassnsall
242 OMEROMU+O..R.AES evita
1B
243 AWRED oele
13
244 Amenic
sertsssrrrssssarbbs betas paesrans sed
248 BeylUm .eiii
19
003505
=
USFW 0581
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CCoorpomyiug, me
S tren, .-
tt
SE0 FL
hae Mig,
C e re, "eran, 1
a,e
28
25
EP1432
iNangyg zg
CC ee e Ce
Cre cen ER ey
-
26
tt
pong re
a2
2.8
S ,y tegeTC netee ,
Creel tires
29 S em
251 on
Cee
CH Heren,, Trt
292
phipog
Sl
y
yaliesg SDRerpreesegl,
ATT rea,
te. 26
OfBeas. averteprycgeye.29
293 Fatheay`.Mianoy, Pim
4 aps
Amer py Te rgfa ephayy, Promeias) oRepre senta, of FishComa
'
256 = oT -- omcating gigsp,i
29 S
298
E
ny 299 Short.sgjeq Shrew Blarina g b
5 as
J <0
2910
SAIFur
MMaemrmya, ce
VE
Cne "eres (bic, Parneviicaucgy a Representa,of
-. 37 ectivorey
"FlToS gpr,om,
en Ce rl Rebresenaive oRy EHeTrbivore,
Tree Cee
ell
Tree ea
0o404
42 Organofivorides
Ce
ee .
a
43 Aluminum
.
sorortearreottts pa snnes
El
=
44 Amemic
Ce
-
ca
45 Beyllivm.....
aereennnn rest g a
46 Chromium .......iiieiiiiinns
-
rea
47 COPREr eine
eds
48 HOB ilies
49 Lad
.
4S
410 Manganese freer
46
411 Nickel oon
46
G12 VAG.
d6
a1 zis
.
an dT
-
5.0 RISK CHARACTERIZATION .....veiiiiniiit iii. 41
5.1 Benthiclavenebrate Community Struc and Function
..................&7
-
52 Soil laveCommmunistyeStrubcurre anad Fiusieon .................... 4
53 Fish Communities
a 48
54 Wormeesting Birds oo. .iiuii ie
"
-
5.5 Camivorous Birds
88
5.6 CamMiammvalso(Temr esiciollyu feeds i0g) .........................48
57 PIGiVOroWSMAMAS eit
4
53 Omaivorous Mammals ............ err
49
59 losectivorous Mammals
iii
kl
5.10 Herbivorous MARAIS
iit
49
60 UNCERTAINTY ANALYSIS ................. .
Ce
70 CONCLUSIONS ....
a 50
7.1 Benthic Invenebrate Community Structureand Function ............. 50
72 Soil lavertebrate Community Structureand Fuoction ....................5%0
73 Fish COMMUNES .....evttiiiiei
LLL SE
7.4 WOMmeMing BItdS outta SL
7.5 CamivorousBirds .....
LS
76 Camivorous Mammals ..........
SPR
st
77 Piscivorous Mammals ...........
rrr
8
78 Omaivorous Mammals .....
=
ee cst
089.25
USFW 0583
30 TTooo ecroors Maammmgy
CUT,
summary.
Te Cree
APPENDIAX
to 2 5
Srl MaDuma Sa he APPENDI5X
Tee
. fore Reger
APPENDIX
Te
Tory Testing Repos
APPENDIX p
Te a
FldNaes
APPENDIX Sisied Anas
ttt
.
Ce
069.05
LIST OF TABLES
NUMBER IOLE
:
Conesaion of BNA's a Water
2
Coneesaionof BNAa'Sasl.
5
Concenuionof BNiAnSi'ness
.
Concescaions ofMeaaWlesr
s
ReofCosnsesnsofMeas iSi
c
Ress ofCoscenaionofMeiaSelinse
'
Ress of he Analysis fo PeicideilaWPaCteBr
.
Ress of he Ansys fo Pesiide/PCa iSoil
5
Ress of Assis ox PesiidinrSePdiCmeBac
.
0
VOA CosceataiaiWoanrs
u
VOA Cescesaions i So
2
VOA ConcessiniSeodinmesnt
5
Coneenaons of ForindWaete
i
Conceneaions of Flore iSoi
is
[EY p--
i
Ress ofte rgano-fuerice AsalyssinSediment
"
Concerns of TOC i Soi
EB
Ress of heAnsys or Grain SieinSil
Conceeuions of TiOSedCimes
0
Resuls ofteAnsys for Gran iein Semen
u
1a Sin Water Qual Parameters
2
Concenstions of Bromide, Chloride, Nite, Phosphor, and Safe in Wate
[IL
USFW 0585
23
2 CConcentrayign, Of BNg:s @
ts fp 2
FecySample
Fel Sy, Conerg
2%
Frequenc, yOf Fluorige. 8 Fecyy,Samp
27
ang.Abundage, OfBenge les
Ar
28
Conceatryjon, Of Mery.
ey
Concentygign
in SengMammy
PH Cott, efyFluorMigaez@zSyay1pM,,azzy,,
Fl 2
Comet Pe
TPiTti Fiige Tig
3
FECOfotpteyy Fi Tig
3s
CFPECf oep n or PToALriMgerEoEnsvo Tie
is
,
Concentrao
Eton Tie rie
ECoPneCntorntiotgn,oOffPMege;inVegVetearigan
WhRecut of hoenpPlt Tig,
ite-foooforfeiqToMoruaspeyg)TeSsctreRenenu Merton yi, ts yg, Mon ju
Clon, 0 Wet Wega
Tue, 4g
= N
fan oy
NUMBER '
LIST OF FIGURES
me Sampling Ste Map.
[RENE
USFW 0587
SECTIONL RTIESCKHNSICCRAELENAPPROACH, SUMMARY OF FIELD EFFORT RESULTS, AND PRELIMINARY 10 INTRODUCTION
11 Objective TAhgeesoebyjecRteigvieoonfIThisRpermoovjalewcPartsotgorapmroivnidceontdeuchcaiincagl 0supepvaolruattoitohne oUf.Se.colEoagviicraolnimekasiarloPmrfaegcieodn oCfonaamseifiltli.onTohfeseofl,orserdeismuelce,d ainndthweactoelrlaetcuaownoorfksionig,bseeedfiptraotd,ucstuirofnacferwmtelroc,ataeodddboiwo gsraamdpileeess pfroriscmoanytagmionaalntofantahleyspersoj2e8ctd swoel,ss0e:di1m)esd,e2n0dyscuorfnatcaemiwnaatnetrsfporresleacbso,ra2t)ordye(toexmiicniye etshtinxg.tcThoef Conamizaion. 12d 3) produce a ecologicalriskassesment based 0 te collected aa.
. 12 Sie Buckgrowd a"onTfhdtehhesietfeaUir.smSa.bwaEsoPrfkAliaenldglbaeeugemifenprgrotouhdasutcccotominpornlaamfiiaonsranwlsioacdaetbebdeieinWaegWsdatissVkciihrngagironginea,dDfWoeomopdaanCroitundnuoysft,rNiWaatlYu.lraanldTRheesooouwwraoceseeds pbryihmaeryDusPoourwcteocforwpaortaetifoonr.hii ocaDtrey,RuTnh.e fDarrymeRrumn afliowssttraotunguhmeherofuasrmeear'tss,probpieardtayesasa,d b1s23d oditshcehrarugneudsuialolDlreysReusnorbsoemrvtehde iDnubPiosobterldaanrle.reIcbyas aalrsboubaebenlere(p0orhieedcaoncamfisnana'nsd wiiltdlairfee celaltse.ave also occurred i te area, whichmaybeassciaied with the brormaliis observed ia he
20 METHODOLOGY e"Tchoeloagipcparloarcihskusaesdseisnsmteinstsdo(cUu.Sm.entEPfoAllo19w9e7d).curBaa:sedU.So.n EhPeAprgoubildearnaceffoormudleastiigonninpghaassed ocfontduectriinsgk assssseessssmmeenntt. deAsis,rechaeingf-ollelvoewlinEg RfAedwassudcyondwuacsiedcoandkuectetdhetfoieplrdoviinvdeestdigaaationne,ctaesdlifonecodmatpsle0t0e shiee icnonthaemicasualie,onhawdasbeaevnairaebpolreiperdiporrio(0r htoeiesfoarc.ivaNtuimoenrous ish and wildlife kills, in addition t problems 20 Soil Sampling Saruerafa(cFeigsuoirles1a)m.plSeasmpwleerearceoalslewcetreed satel4ecseadmpblaeseadroensdailsoanngceDrfyoRmutmheaandsinfonoewtraelflerenacne asapee 1h0eidsterneatmabecdo.namTihnraenescroepnlcieciatceatsiaomnplgersawdeer.e aSkaemnpliinngeawcahsscaomnpcleinntgrawteeda.inReeplmiecaatdeowsasmpsllionngg lfoorcasiaomnpsliwnegrethdreotueghrmtihneeudsebyogfr3idrdainndgotmheumsbameprlsinagblaer,eaSaanmdplrianngdogmrlidy ncohdoeossiwnegethdreeeicgirmiidoseoddbeys using 4 random sumbers ubie 1S0u9rfa6ciencshoeissoafmpthleessowleraecccoorldliencgte1d0 uEsRinTgC2/dReEcAonCtaSmainndataerdd sOipseirlaetsisngtePlrorceodwuerle o(rSOsPp)00#n20f1r2o,m Shiel Sampling. All oi samples were analyzedfo ol organic carbon (TOC): gain sae: ges aie ' o0 in
USFW 0588
cliostmp(oTuAnLd)s;metTaClsL;
vToClaLtilpeesoircgdaneisc/PcCBosm:pouTnCdLs
B(aVsOe,CS)N,eurtaol,l
12d Acid fluoride,
Exracuble (BNAS) and organofiuoride
cinom0pouendasr.woArddmit(iooKniaclHYsi(lexw.asAcovlelegcetueaddofnrosmamtpelesawmapslealosoodke eclnoseasttetxochheofsttreeasmoiblesdafmoprliunsge
zodes
22 Sediment Sampling
2S0eddiamneentarseaampilneLseeweCrreeecko.lleSciaemdpalearseaamspwleeraerseealocsuiesdiebaisnedDroya Rduiss,inocneefrreofmertenecelasndafmipllleoauvela, dienpaonsiatinoenmapleroeasidaelnoinfgy tahecosniarmeiamnabnetd.conceauraion gradient. Sampling was concentrated 1 te
`AAlvlesaecdhimseanmp:slaemspaltiinong,wsaesdicmoenndtucwtaesdcaoclcloerideidngfr0omEtRheTCo/pREiAnCcheSsOuPsi4n2g0316c,ecSoendaimmiennastSeadpcloiwnegl..
d"iThveidseadmpilnetowtahsecaoprparpoopsriiadeisiaomapldeeccoonntaaimoienrastefdoSr-cgaacllaoincaslisalzeaslsysees,l bucAkdedti,iohnoalmosgeedniimzeendt,waansd
-
`cHoylalleecltlesdsitnetchaewrheofleeresnecdeimaerenat,bTioraisbsuatya.ry A, Trbuuary B. Area I, 10d Area IV, for use ia 3
23 Surface Water Sampling
Ssuarmfpalcee wscaattieornss.amplSeusrfwaecreewcaotlleerctseadmaptlleoscawteiornes wcahlilcehciceodrdriersepcolnydeidstto etawcoh oLf-lheerspeovleynprsocpyileenne VboOulCe)s faozralmyesaeslsasanpaelrysEeRsTaCn/dRnEoACI-SlOiPe 4gl2a0s1s3,boSwulrfsac(oeFWoartgearniScam(ip.l.i.ngB.NAWSa,tePsesstaimcpildees/PwCeBrS,e choelescaimepdleprr.iorOtnoecoslalmepclteiang esxecdhimleonctatsioanmpwlaess faendreudpsttrroeuagmhof30a.n4y5smtriecarmondi(suumr)dafnlceesicnatuesedfieblyd wpreiroer atnoaTlyAzLedmuenafllseraendal.ysiAsl:laslumtphleesreamzaailnyiznegdTfAorLmmeeaallsswesarmeplpersesaernvdeadllbyheadodrignagni4c0spaemrpcleenst nTiAtrLicm2e6adluaanalayspisHwoafslpersesBearnve2d ianftehretseamspalmepwlaeswaobsiafnierde.d.ThAellfsiurrfeadcesawmaptleer ssaumbpilmeisedwefroer bsruobmmiidtee,dmfiorcaT,ALsulmefaal,s,andTCphLosBpNhaAtse,anTaClyLsesP.estAcdiddiei/oPnCaBls,saTmpClLe VwaOsCsk,ecnhloinritdeh, tfelfoerriecnec,e aprheaas,eT(robxuiarcyteAs.t Tebuary B, Asea ll, 0d Area IV, for se in a Pimephales promelas aquasous
Wtoatmeeraqsuurleiytpeamrpaemreatneurrse wienredemgeraeseusreCedlssiiunsg(aHC)o.rbpaH>, wdaistseolqvueadlioyxymegteenr, (mTihlleigmreatmesr wpaers slieedr ((Vm)a)/.L).Teeconmdeutceirivwiays[cmaillilbirmahtoesd ppreirocrentiamnedtearfi(e@rundhatoasiceoml)le]c.tiooxni.datIino-snitruedwuactteironqupaoltietnytidalaa[vwolatss "wTahneseHroirbiebdaTMfrwoamstuhseidgiinalacdciosrpdlaanyceoftthheemHanourfbacaaTMureinrt'osoapfereadtilnoggbmoaonkuaalt.th time of collection.
24 Drinking Water Well Sampling
W25atoeurliwzaeds asbaomvpe.ledSfarmopmleasd0ribnekianngawlaytzeerd wweelrleotnaktehne rTeonmna2nttpfatrhma.t wPaasralmoectaetreds dwiercetlaynaolayztehde pump head ahe the wel had been purged for a period of approximately five mines.
2
009.3%
USFW 058
25 Biologic Sumpliog
250 Small Mammal Sucy
cSmoenlttalalmsinmaaannmtdsm.atlToisusswleuvreoebruircddoeelnl3sc0ideodf10sfmreaolvmlamlhauemamsiaiseltsotCopaadpbeoptleeadrgomiincnaelsbtoHdweyecrtbesucroodfmepneaxlrpeoevsdeultrsoeosf10TtsAiLe
caoclcloercdtaendcefrwoimhtEeRTcCef/eRrcEsAceC aDrreaaf.t Marimal Sampling and Processing.
SAtlalndafiredldOpterraaptpiinngg
Parcocieddusre
wSeOrPe
4c2o03n9v,eSnci1
lRFooocuardionwnasspimpiiAlaagfrifmaterhaegsdriowdwwearhesabeesistatabballsiitsshhhaeetddoobsneasriveeefdeianrloaocrneegatasreecaoslroeecsaaptmaendcdoJirunmstd1too0rth(eeFingsuaorrie s1ao.mfplTbiornyng. asreuefraefrraecDnercwye aaRtrueena,fwraaosnmdchDborescyeanuRusbnee.ciat uwTsahesetohleuesaBigadaeboitfheptreaerseweaastptphwiaatasgcoSpuzelmrdiiolbdae140d2idrhehtcdeliyncrnhafpeupeionsgcaeodffdbeyn rwveaaqrsuiieprdeerdafmoornmcgeadperwxricenhgaosMfuuftfshieeciuuemnatpSupamercbeiaeaslroasnfadmpawamapsmsablassseedifonrognsiactsn.eielaAalllgeasvpiolsfudwtoienmre.e asSnpugapccildhion1ng3 evfbeisactieiaedpdaaallnya,dnodrnbecaekaead bweeciemtsohsraanrriyo.lnlge1dR0oedtcoosvn3ecnredeidpn eahaennaevblenuiwnregr.meixDatuburerilene.gdrTwahpeicathhpeesck5swp.erseaacpcssh,ewccekrerdae' sumbbeers.isapgeicnigeasr,eaanodErtperocoefscsaipnugr.ewhile ithefed0dtheawerernstened nsoci,
waFeoirnghesa.cebhodratynoivalmsaeelma,apdl,plramilalrtemogapele,drfacoarsmhieenaegtgt,(heAlpsipveeecnrrdwoiepxisgyAh,)s.,daaBnuoddfyKrimodemoccrtyiecwsesiigpnhectcluiwdmeiernnge tlmaobleelbawoadssy ancliodvnetrrenatnsed oKficdtnhoeoenytg(ahrssetpdodraioanxeseshiiemendtrae.llDryuar0c.5gienwagectrhee)rneewcmerrooevpersdyeamfonrvoyemdbafrcoohrmhsaiplteoicpeiamstewhneo.lroeSgenisoosaieoansnoaofeose ReTehrfeearsleencbciuefofnPesartewhdeofrloeorgmpyall(aincA.eRdPP)irnefasoerlrahvbieesdlteoldpiva4ehs0ol-aonmgdLicKgailldanseesvyavlisuaaeltciiaoonnn.dspwTreherseeertsveuemdbsmnwiiitnesgd 1s(00cpaeenricwemnsat stiupbidmiatnaeldysfiosr,homogenization ad TAL meal, oral lorie, perce mse, and percent
252 Vegeuton Sampling
sVVeaegmgeepttlaaittniigoonnloAcwsaatssieosncssomlewlneactsteFtdiaerblgdeytePhdraonftdoorcofrloe.rsirdeTusheiedaunmealoysasntiss.yssbiuGsnrdapasenrtsEagmrRapTslseCs/swRseaErAeoCbtsaeSkreOvnPedio4a2e0aa3cl8h 2ps5tl6ea3mnss3a:ftrhhoeemshsaoemileismgumrreifddaicneawotdieetsvhi3cai5nditethyecoosfnoiatlhmesiasnmosipleldessafmwpeelr.iengaAknlelond.seamTwpehlreeesscwbooelvrleeecgatenrdaolubynysdecdpuotoririnogSsAtooLef meals, onal Mluorice, percent moisture, an percent pics 253 Aquatic Macroinveribrate Sumpling
3
000-3"5
USFW 0590
T#2h0e32infBaeunntahlicmaMcarcorioaivnevmeerbireabtreaiceomSmaumnpliitnygw1i0sdsUa.mSp.ledEPpAer (D1r3a6f3t,E1R9T85C,/R1EndAC19S90O).P
iMoivcersotiigaavteinozn,bramtaecrsoaimapvleersiewberraieecsowlelreeiddefofrineevdal1u5atoirongaonficsmosmmauntitiympsiwaugceedue0.812
is 0.5
iseldiimmeetnetrsa(mpwlmi)ngsileovce.ationAs (tFoilguorfe 1r.ee replicaes were collected fom each of fve
cAelnotnimgehtaenrdsleadl,l, Dw-iftrha0m.e5kiacmknemte,shmewaassuruisnegd.appTrhoexiomeattewliys4u5secdentoimdseerusrdwisduebmaeardge2d0 Vegetation and debris 1nd collct dislodged vertebrates. Exch replicate collection wis wpeerrfeomramnesdtoevreerdatou5si0f0oarm aproelayaedhcylaecahesjaamsplainndgplroecsateirovne.d wBieahti3e70avpeerrcieenbtat2e-parmoppalseasl solution.
. -
apotlyeethlyalbeoarsatporayn,wtihtehjsuasmtpelaeowuagshrwiantseed aiddcleed1an0awlaltoew32cdomppllaeceeddiisape3rswihointeofh12ex m1at8eri5a.l 2wikriatyheanpdani.nspLeacrigde fdorebain,acshieodueos,acldigiotahgeorregxatnriasnmeso.usAmlaltoerrigaalnsiswmesrepircekmeodvferdomfrhoem pcaorwdeerdeonideantaibfoierdao(0ryhebelnocwhesstheepto.skTihveesyiziedeomidfIifedethrisotnoorymiscagleeovefl,heeaourmgearnaiisemd,s 1an0dd osrageaniosfmtsaxwoeproemiicdeknmiofweldedugseinogfatpperogprroiuaptedteatxeornmionmeidc trehfelreevnecleosfainddesaifriceatpirone.seTnhte' sCounbtsraomlpl(eQAwe/rQeC)idreeaqiufiireedmbeyatasosfetcoeodsiondnivoidrueal atnoalmyeseits.the Qual ityAssurance!Quality
25.4 Fish Collection
F`ciaslh fwleuroreidceo.lAlecCteodfffroembDarryryRupnowoerdeedtebramciknpeacbkoedlycbauorsdheonckleervewlsasofsTedAaLndmeoaplersaiaendd 2c5pepreatritnhgetmhaenueflaecctiurrsehro'cskeirnsatnrudctoinoensindTihveidusaalmpcloillnegcttienagmsrcioatsseidsefdishofwainthe i3nddiivpidrueatl. Sfitsuhnwneedrefsidhenwteirfieedpltaoctehdeilno2w5e-sgaalxloonnboumcikcetlefvielledpowsitihblseiteinwattheer.fieFdolalnodwilnvge csopleleccitmieonn,s wsoelruiorenleaansdedr.ewVomuecdhe0r tahnedEdReaTd/sRpEeAciCmebnisolwogeircealprleasbeorravteodrwyifhor1codnifitrmaftoiromnalocfebfiyedled tmaexaoln,omtioclnauloyrsiedse., F%ishlitpiisdsu2enwda%s hmoomiosguerneizaendalaynsdiss.ubmined t the laboratory or TAL
26 Toxiciy Testing
261 Eiseniafoeida (Earworm) Toxiciy Tests
sFaimvpelesosilwesraempalkeesnweinrehetamkeenadfoorwesvaamlpulaitnigonrienssanaleoanrgtDnrwyorRmutnoxaincditoynteesitn. iForuerfeorfentchee mmoeraadloitwyaarnedaagsroouwlsiniendaacbhovoe. fheThteesttesstolwsawsarsuennfuomrer3atpeedr.iodEoafrt2h8wcoaryms,tiastsuwehirecshulitimneg mforiosmtueraechanoaflytshies.raFimgeurne |wadseasulbtmieneedarfotrhTwoArLm mtoexailcsit.yoteuslt sfolluorsiadmep,li%nglilpoicda,t0occs. 5
262 Hycllla azteca (Amphipod) Toxicky Tess
`
eaiiy
USFW 0591
sFaimveplseesdiwmeeraettsaamkpelieansDwreyrReuamkaenadfoorneevaialuaaifoenfeiraeaancaemaprehaipstordeatm.oxicTihyetetset.st wFaosusroufatohre e2paeurmeiroadteodf.10Fdiagyusr,eat1wdheitacihlsitnhee ammoprhuilpioyd3t0odxicgirtoywttehsiseedaicmhesotf skaemptlesitngseldoicmateinotnss.was
2.6.3 Pimephales promelas (Missow) Toxicity Tests
FFiovuer osurffhaecesawmaptleersswaemrpeletsakweenirenDtarkyenRufonraenvdaluoaetioinn airae2fefraetnhecaedamrieanssoewamt,oxicTithyetetsets.t wwaatserrsuwaafsorenaumpeerraitoedd.of F7idgauyrse,|adtecwahlischtheimfaethmeoardtamliintyno2w04togxriocwiayhteisnt ewaactherofsatmhpelitensgt locations.
27 Sampling Equipment Decosuaminstion
sTuhbeseqfuoelaltowtiongsasmapmlipnlgiinngteequifoplmleonwtingdencuomneiraimcianlatsieoqnuenpcreo:cedure was employed prior to and
21.. pohnypsihcoaslprheameovdaeltergeat wash
43..1p0ortpaebrlecewnattenrrrcizsaecid risse
.
5. distilled wate rinse
6. solveat rinse [acetone]
7. airdry
28 Suntard Operating Procedures
28.1 Documenation
Documentation was conducted in accordance wihth following SOPs:
""EERRTTCCI/RREEAACC SSOOPP ##24000021,, LSaomgpbloeokDoDcoucmuemresnatiaitoinon "ERTC/REAC SOP #4005, Chain of Custody Procedures
282 Sample Packaging, Shipment, Storage, Preservation, and Handling
Sample packagicg, accordance with te
sfohlilpomweinntg, SsOtPosr:age,
preservation
and
handling
were
conducted
in
"ERTC/REAC "ERTCIREAC
SSOOPP
#22000034,,
SSaammppllee
SPtaocrkaaggei,nPgraensedrSvahtiipomneantnd
Handling
283 Field Sampling and Analytical Techniques.
Field sampling following SOPs:
actviies
and
field
analytics
were
conducted
ia
accordance
with
the
ERTC/REAC SOP 42001, General Field Sampling Guidelines 5 006-15
USFW 0592
""EERRTTCC//RREEAACC SSOOPP 4#22000056,, SQauamlpiltiynAgsEsquuriapnmceen/tQuDaelcioyniCaorrmuirnoalriSoanmples ""EERRTTCC//RREEAACC SSOOPP ##22001132,, SSauirlfaScaempWlaitnegr Sampling --REERATCC/SROEPAC#20S2O9,P #S2m0a1l6l,MSaerduimmaelntTSraampppliinngg.and Processing "REAC SOP 42032, Beruhic Sampling
284 Health and Safery
Health and Safery was conducted in accordance with the followiag SOPs:
<"EERRTTCC//RREEAACC
SOP SOP
3001,REAC Health 43012,REACHealth
and and
Safety Safety
Program Policy end Implementation Guidelines a: Hazardous Waste Sites
"ERTCIREAC SOP 43020, Inclement Weather, Hea Stress and Cold Stress
30 RESULTS
30 Water, Soil, and Sediment Analysis
301 BNA
`SurfaceWater
Analysisofthe surface water samples from Dry Run, the reference sizeam, and Les Creek
Tprroidbuucaerdy onBlylooncaetidoentecctoinotnaionnedtheansunedsatrmdaiBedNAcosnccane.amaAtiosnampolfe 2takuegn/iLn tohfe UBipsp(e2r-
EindcilyuldhienrgyDupnhkihnaolwantea.lkanIen aandddiatilokne,aencuommeproouunsdsTewnetrdeivfeoluyndIdiennttiefiesdurCfaocmepwoautnerdssa(mTpIlCess)
Results for ia Table 1
the and
BNA analysisofsurface in Appeodix B.
water
samples
akei
ia
ia
Dry
Run
are
presented
Well Water
l`iTth.e sSaemvpelrealtaTkIeCnsatwetrhee TiednenniafnitedF,ahromwweevlelrpornoldyucoende noof dtehteedcteitoencstefdrcomomtphoeusnadnsdacrodulBdNbAe. tweenltlatwiavteleyrcshaamrapclteertiazkeednanatditdheenTteifnineadnt3safanramlkiesnper.esenRteesdultins Tfaobrlteie| BanNdAiannAaplypseinsodifxthBe..
sail
`Analysis of the surface soil samples from the meadows adjacent (0 the streambed and the
reference meadow area produced a few isolated bits from the sandard BNA lst.
rFelfueorreannctehesanmeplweass. deCtaercbtaezdoalteanweasstdiemtaetcetdedcoatncaenntersattiimoanteodf c2o3ncuegn/tKrastiionnoonfe 4o1f utge/Ktgreien
2o6n.e aondtfh30tuhge/ekgAsineaon|esosilasm.plDeivfnr-obmurayrlepahiIaI,laotnewsaasmpdleteecftreodmatazczoanctehnrterea,tiaonnds towfo22o.f 2t7h.e
2
teshtriemeatseadmpcloenscefnraotmioanrseaofI2V7,
respectively. Bis(2-Edhylhexyhphthalate and 62 ug/Kgin one sample from Area Ill
was and
derected at one sample
6
009.15
USFW 059
clUfoarmoscpmeo,uAnnvcdeossycwIooeVf.rnehaepfDsoeiauonmldpcleyieaupshf,heoidsamilcaaereedaI,wsVao.sls1rdssuseia,cied.do,b2m,m rePxeGiEs,tTeididsc,om sceaandoa n of 1300 samples is preseted ia Table 230d i Apes 5. Ress foto pho seo FS
Sedimeng
opArzotadluicyesidnonfhletyAhevaesfeedIwiVnsseoesdlisemademnptdleessasmcpifloeonms 2oif0ecBfNivmAe scdioempG1o0oudnedwsso. Ecyberyphiaue ws detect ln he Are
fDfaosposoecma soaions
.
ctConrrsokae,cnurafcioseominparoonufs,n2dyssueyveaKemsre.e, ,oNfoteDsircyaRa,ndsmsbyedldden,ecsoaIesmTrapomdo,edinrdm:ttewslSee.smfppoaotgi,eo1mo0sasncr; AS
isa3pAlpepse.adiRx el fo he BfNoAundcaiytse oDfreyciRumse:sLsipeiCerse.pandrwepnmsgae
302 TAL MeNas .
ebfAerollreydlnesiodncs,odasttcehaetdesemidituiumrc,2 aewcnaodtneboetfre,tshmrd eaeledrerrseysad,fmorprloiemcsfkDefelro,yrrsTReeAuLde,,wimhne,ersseifsveer,yeem,saelapimn,iaedrLeesreCer:ee
assul
cf0mo4eirrneinsuccmasw,ieaormanepltiuenseh,eidcDcaraiylpncReihuoesn,lCcGroeapetpedekrsd,wiaactmsner,sis,o,ampelceoss.pe,O, F1moea.nIg3oaosf,dpeoopssnri,asein,
Cres.
ungte rere sens
Ra2Nuu4lnmilaaoiheuemow,sesprbeeicieemusiemes,cucceroadecedeiinnuicrmha,LieecoeonfspCiproelferei.rdnons,iimmp,algensoe.sni,OumF1,dhmesaTnnopgoefp,aspbory0sspoams,nscodE0,e: pDreecseunltdedienlTsaloef te3nTdAinLAmppeenscinan5.ys in fered nd nse wes samples se ell Wer
CeaWomenpnlllcuee.mwnac,taeAtrasotisniavmmmeap,enlyse,daurlwfeureomfimo.r,thhe3ebxewr0reeylmllvaliiiounnamid,nhigecuIamsdTmesivseuarmns,s cnfhorrrommdiweuacms,isdcnaoynbz,endmaasrm2oemonfered
in Appendin 5.
ofTAL meetssrpresent est 10s
'
009.45
USFW 0594
Sail Three replicate surface soll samples from te four Dry Run meadow areas aad the rseefleerieunmce, mseilavdero,waaordeaGawlelrieumanwaelryzeedooftordeTieAcLtedmeainlsa.zy Aosfttihmeossyoi.l csaamdpmlieus.m, Omenrec-urwya,y ahsiaglhyesrisinoAfrevaar[iIanccoempdaerteerdmitonetdhe trheatfersoeialcemaarnegaa,sbeustetcheonscaemnzeaat5iotnossewegroeresdi1gufairceaasatIy, Ico.ncaenntdraItVio(nps=0f.r09o4m).the AortehearIarbeaadsthreanhgiignhgesftrmoema6n3m0a0ng1a3n1e0semgc/okngc.entFruarttihoenrwiretshulmtesaonf the TAL metals asaysis of site and referecce soil samples are preseaied in Table aad Appendix B. Sediment wSeerveeunkseendiimaetnhte ssuacmpalremsbewdeorfeDsruybRmuicae,dofnoerwTaAsLwamkeetdailnsLaecaelyCsrise.ek,F1i0vedoofntehweassamtpalkeesn winertehegortefdeerteenccteedsienaamn.yofAtmhiemosnedyi,mecnatdsmaimupmle,s.merIcnurcyo,mpsaerliesaoieum(,0 stielvelre,velasd metahsaulrleidu.m in the Lee Creek sample, it appears the Dry Run Creek reach may be cariched in `amlaunmgianneusme,, arnsiecnkiecl,, bpaoruisusmi,umc,alcsioudmi,umc,hrvoamniaudimu,m,cobaanldt,zicnoep.perB,asierdono,aletahde, rmesauglntseosfituhme, aluminum, barium, chromium, coball, copper, iron. lead, mangasese, nickel, vasadium, daeacdsezaisnec waintahlysiinsc.reatsheiraeg dailsstoanacpepefarrosm1t0hebelaandfigleln.eraFlurwtehaerd raestultsmeoaflthceonTcAenLtrmateiaolnss azalyss ofsite and refereace sediment samples are presentedi Table and Appeadix B. 3.13 Pesticides/PCBs "
No pesticides or PCBs were detectedin the Dry Run samples, the Lez Creek sample, or iz the reference stream sample (Table 7; Appendix B) oil Nopesticidesor PCB were deteced in the Dry Run meadow samples, ofin the reference meadow samples (Table 8; Appendix B). `Sediment Naohpeesrteifceidreesncoer sPuCeBasm wsearmepldeet(eTcatbeldei9n,tAheppDernydiRxunB).samples, the Lee Creek sample, or 3.14 VOCs Wage CNroeevkolastaimlpeleo,rgoarniicn tcharbroenfecroemncpeousntdresamwesraempdleete(cTtaebdlein1t0h;eADprpyenRduinx Bs)a.mples, the Lee
8
000.3 or
USFW 059
Sail
TtoricDhrloyrofRluunoroamethcaonnecewdaisaidieotnescterdainagienvgeryfrsooiml s0a.m9ple10ke3.a6 inutgheg.meadoInwsaadddjiaicoeant
te4wacugh/lKogr.oetbNeoaeotwhaesr dveotleacdtleed oirngoaneicrcepalribcoantecAormepaouInIdssoiwlesraempdleeteaciteadcoinactehaeirDartyioRnuonf.
asazmapllyessi,otfhesitLeeaenCdrreeefkerseaomcpelseo,ilosfaimaplthees
reference seam are presented in
sample. Table 11
Resuls of ise and Appecdix
VOC B.
Sediment
wAacestodneetewctaesddaet ta ecocnictneeatrhdreatAiroenaoIfV0s.a5mupgl/eakgt
aconcentration ia te Area III
of 7.2 ug/Kg. sample. `No
Chloroform otker volatile
oorrgainnitchcearrbeofenrceonmceposutnedasmwesrameplde.eteRecsiutlttehsdeofDrtyheRVuOaCsamapnalleyss,isthoefLseieteCaredekresfaemrpelnec.e
sediment samples are presentedin Table 12 10d Appeadix B.
3.0.5 Toul Fluoride
Water / Well Water
.
Fsleuoarmidesawmpalse,nootfdientetchetewdelila sthaempDlreyaRkuen s0aamtphleeTs,entnheanLteefaCrrmee(kTasbalmepl13e;. AtphpeeraedfiecreaB)c.e
soll Fluoride was detected in the Dry Run meadow and in the reference meadow samples. Soll finluAorriedae Icloln.ceTnhterrateiaonpsperaarng10edbefrpoomsaalioswicoafly18s0igmngi/fikcganitndAirffeeareInVce1s0iaa hitogthalofso3il70flmugor/ikdge cosesauration. Resultsofthe soi fluoride analysis are presented in Table 14 and Appendix 5.
Sediment
Fluoride was detected in the Dry Runcreekbedand in the reference creekbed samples, bu
fot IV
in Lee Creek. sampling area
Fluoride concentrations ranged from a low of 290 (0 a high of 450 mg/kg in the Upper Tributary
mg/kg in the A sampling
Area asa.
FwliutohriindcerweaassinngotdidsettaenccteefdrionmtLeheelCarnedefikl.l.OvSeerdailml,enftlsuosraimdeplceodncieantthreatiDornys RtuenndCtroedeekcrreeaasceh
saepdpiemaernttoflbveoreindreicahnaeldyswiistharfeluporreisdeen,tewdhiicnhTaibslneot1SfaonunddininApLpeeendCriexekB.. Results of the
3.16 Organofivorides
Sediment hBiegchauvsoelaoifltmyetohfodsoolmoegystapnrdoabrldes,ms,onslpyecailfiimcailtleyidnsuoibtueionfinogrgaapnporfolpuroiraitdeesctaonmdpaordusn,dsaccdoutlhde. be scanned for in the sediment samples. These compounds are presered in Table 16. OF Ge lis tat was analyzed for (Tewaflvoroethylene, hexafivoropropylenc,
? 060..55 USFW 0596
CChhlloorrood-i1f,l1i.r1a.m2e3c.b3asAee,xaplevrorlouporroopcayscel,obuasned. |_-PCehclfolruoo-r1o.i1o,b2u.n2y,leatse)a,fivsorooeetbaosfe, h1eLozrlgyasniosfiosniredpeorcioemdpo1unTdbslweer1e62d0e4iiecainAdpnpesodeixsBe.dimens. Resuls of ee orpasoflvorids 3.1.7 Toul Organic Carbon and Gra Size of Sol and Sedimeat
1S2udm1m2arAipepseoofdtBioax.l oTrOgaCniinctchaerbsoonlnradnggedrfarosmizaenanaavleysriasgeaoewproefse5n.t6e%diinATablrelsl1sa7o-l2s0 i0a1T0abalveer18a.geThiOgChoifnt9h.e2isneAdriemeaatIVrasoniglesd. fSriolmg2alnowsoifz 1d.e9r%ziiaaLteoenCsreweekstuom3mairgihzeodf 215% in Avea IV. Seimeot gra size deiemination is preseed a Table 20.
308 Water Quay Parameters
.
eWamtpeerranquriel,itry opiarda,metcehrlsoriidnec,luadiiaoige,pHp.hoscpohoadteu,ci0vidy,sulrfuibeiwdiays,medaissusorlevdeidnohxeygDera.y
wReirmeCiretekcornedsuc,iitvheiyr1f0edrsculefasteeacmoc,eoardrianoLneedecCrreeaeske.dTwhiedmiocsressosuibaglediosbtsaenrcveatfiroonsm
`BDeealsaunrdfeimlela.tsO0thderanpaalryasmeesteares parpepesaeraetdd tioTbaeblienst2e1aenxpdec2t2e.d range. Resuls of hese
=
3.09 Bovise Fecal Samples
=
iSnitxhfeecdailgessatmipvleesprwoerdeuckeofnhteo dafefseectmeidnciafdeemvironmenial copaminans were showiag
axa
mPhge/ckogl. wAadsidteotnecatleyd,in&-amlleishiyxlfpehceanlalsawmapsledseexciceodnciennaulaliioxnssarmapnlgeisnginfrcoomnce2n.t6ra0tio8n.s0 cFounnsgeinnirfarioomn 9o5f t3o0 1m1y0/kmsy./kg. AdBdieinonzao iancfidorwmaasiodnetiesctperdesiesciweod ionf Ttahbelseam2p3le2s2d3i3n `Appedin B.
Tal Meals
SAolduimuimn,uvma,nabdairuimu,m,1ncdaltciinuem,wecroeppdeer,ciirdon,inltehaed,femcaalgnseamspiluems,. mAadndgiatnieonsael, ipfoorsesaiio.n presented in Table 2 and in Appendix B.
Eusride Fluoride was not decid in any of the fecal samples (Table 25: Appeadis 3).
32 Biotic SamplingandTissue Analysis
521 Beatic Macrolaverbrates
10
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005.55 USFW 0597
AOftoeas,oft2h7retwoansam1 iOcliggorcobuapcsiw,e|reMcoollelc,ed|Tfurrobmeltleran,loc3aCtirounsstsaacmepal,ed1(dTa2b1leIns26e)c.t. sCaale.opieOrfiathwhilcahnwees,reherepdreosemateid bgyro7uapr,a.in TtheremsDipoiferwiiaonwoemriecredpirveesresaittye,d bwyer4eaGxea iTr=copGteeriEap,h0emderMoepfiaelroipatewrearewerreephreeslceeads dbiyver3sexgaro.upsTahned Pwleerceopireeripar,esHcemaiibpydtearcae o"rhetrweo1x9aa.xaTwheeregrceoaltleescttead.xogFomeic wwdvaeaerwseirrcye wsaesrovbesedravedocaa:ihoensf|erGeoaucgehloIcVa,ti1o2n4, bifetrleonwceesitndisveormsiotynewadisveorbssietryvbeedcaweleotceaiornfeIrVacwehelroecat1i1onxnad lwoecrateiocnosl1lecIe,d.I, Tahned IloVcawtiaosn.primanly due to te preseace of a eater umber of are axa ate former
T(raeploicuamtbeerA)of0in2di6viaduallosccaotlolnectIeVd (preerplriecpaltiecas).rangTeodefroobmse2r0v3edadheeasrieyfoefreinedilvoicdautailosn
:
({aExraou(gThaobultet2h6)s.udTyheresaumiserpircsamlalrylydohweinraneeaorfaltchlelemcutmeedriralomabthue nsududoayfoaorcleyaeinscelvuerdaels
Laencsacdraonctuos1rgdanisvmlsiadaed.wWeehernepprreessseetd,bhye2se1a0sda w39e1eintdyipviicdaulallys,heresmpoecsttivoeluym.eriOablelry
Lsespao.philncelbuidai.ngBePeesr,la1.54CPheiurodroalmiindnaoep,hiFiya,lwelels, pthreesTeunsbaetlamroisat,loacnadti1o0ns3 iensceotnxsciss,
Sfiegpairfeiscaenattbepyrdopfoirvteoionsf.eweInr igenadeirvail,dumaolass:maorsat lcooclalteicotnesd. wFeorreerxealmatpilvee,lyorfatrheea1n2d9woerle
{oavxootnoomfiivce oibndsievrivdaunalcse,s,134bywseirxe10re1p0risndciavitdbueaydls,on1e5ibnydiv1i1du1a0l,2036indwievrideuarlesp,re2s0cdate1d3 bbyy
sreaer han 21 individuals
SCehvierraolnotamxiadw,er1endcolAlseccltieddafero(mTaablllelo2c6a)t.ionsSesvaermaplletdsianclwuedrieogoLxeuccoolrlreicctae,d Pferormesa,ll Algocaabtuiso,nsHbyuatllwlear,e3bnrdoTaudrlbyerleaprrieas.entOefdthreoauigsehaoxtaotbesedrraviendagae oinnlclyudoinneglLoecapttiaopnh,lfeobuar,, {forcolmudtihneg rEelfmeirdeancce, lSocciavtiiodna.c, TPhreeamdoosltincaoopmhmioln, d2i0sdriSibcuaitoinomGybisdearevewderweascoolneeciWehderonely3 uHyadrowpassyccholel,ecLtiemdoionphelialtdiavce,lyNliogwroniuam,bernds,Ce2rnadoaptofneiwdaloccawteiroens.colFloercteedxaimnpflree,queEnltmliydaaes,d iHaislceorwidnauem,bePrrse.sdoSliimnilnaarplhy.il,LiSpcoagioommpyhisd,aeD,ynisdciPdhacy,iaCuwrecrueldcaoel,icEeldmiidnsel,owScniunmibdeare,s arly one locaton.
FRievseultfiunngcifornaolm ftheeedipnrgesgenrcoeuposfwserleicdolelecatnedd Hfyroamlltlhe, DormyaiRvournesdrwsienraegeth(eTadbolmeiz2a6)n.t fscurnacpteirosnawlegrreocuopnsatismtoesntt cloolclateicotnesd.frAolmthaolluogchatlieossnsdionmitneasnr,udcyaorlleeacaonr-dgaitnhcrleudresdahned mPraedfaetsorsLewueerroecudtoami1ndantLepattolpohclaetbiioan.s TIhaesddomIlinaannd swcerraeperrewprsestehneseadyplriymaLreiulcyrobcyust.he sorely Perlesta
Tuhleio.veraanldl saescsoensdslmyenotn otfhezacalnogiacalolfcyboionsldoigiiocnsalfceotmpfooncuesnetssoin itghheteovfalubaitiao.n ofHhabbiiast,
un 009.29
USFW 0598
aa8 the30prdinccainpabledeutseerdniasnaantgeonferbiaollopgriecdalicpoortenotfiabli,olsoegtischalecsonadgiecifoonr.isHiiegrphrqeuiaalgitbiyosbuarbvieayt. wsuiblllseu1pp0odrohfilgihtlqeucaolnesebqiuoelnocgei.cal Hcoomwmeuvneirt,ie1ss a3ndharbeispaondseecslitnoemsiinnorquaallitteyr,atidoinssczwrialalbblee bcioollloegcitceadltoigmeptahierr,meenmtpirreiscualils.relaWrihoensnhiphsabcaina baendquabniiolfoigeidcaalnddasaubsaerqeuesnytsltyemuasteidcalfloyr wscarteecrasihnegditmapatctdraainndsdhisecrDirmiynaRtuinngswtautdeyraqreuaalbiaysebfefeecatsmofdriofmiebdabaisata dreegsrualdtaotfiopn.as Tahned preseat 32d use, paricularly with respect 0 cane grazing aod other agriculural pracices, 5rowueglhatreeplacseirimaegaotfbycosmpmeecriecsiarlesanidstindourstardiaalpifeadci0legr.azTinhge, loorssoelfirmiipnaartiiaonn bveygegartaizoinn,g as several consequeaces that shoud be considered when evaluating te distribution of benthic macroiaverbraes and macroinvenebrates ia the current say.
-
qTuahleitayorafitnhabelbeabbiioloagicaaplarptoitceunltaiarlloocfataosnw.rTehameDofryriRvueraisswpudryiamraerayssdieuteartmeidniend abryurtahle
area uslized primarily for graziag cate and, although historic indications of grazing are
`weivtihdenat,csoimgpnliefitcealnyt poopretnioncsanoofptyhearnidpaerixapnosaeredasroielm. ainPovretgieounastedo,f tahned DthreyreRaurne fderawiaaraegaes,
cBoomumgunhitsyo.mewThhaettdaesgorandoemdi, dsiuvpeprosrittyaasnudrpnruimseiargilcyaldiavbeurnsedaanncde aopfptahreenmlaycrrooibnuvsetrtaeqburaatiiec
was relatively bigh at the refercace area. In contrat, the diversity and abundasce at
locations I. 11, III, and IV was reduced substantially. Since habitat considerations at all
locations in Dry Run are similar, the presence of contaminationa the lanes locations may
be significant.
322 Mammal
aFnodurmsepaedcioews joufmspmianlgl mmiacmem)awlesre(mceauagdhotwdvuorliensg, tshbeotrrta-pipliendg sehffroerw.s, Wwhhiotlee-fbooodtieedsmwiecree, submitted for lipid, TAL metal and tol fluoride analysis.
e"TxhterermaeplpyinlgowefrfoarpspirenvgeasluecdceastsilenaAstreonae Ii,mhpoeruaarneta ineeadresotbstehrevlaatnidonf,l wohutifcahll,waass ctohemrpearweads 1`0matyheinodtihcearteaarenaes.colTohgiiscails htihgrhelyx irFrieegludlanrecgriovpesnietsheisdeinmiiilfairedhasbeivteatrsalprseisgeninfticsaintte-pwirdoeb,laenmds. wsihtrhewtshessammapllledmafmrmoamlsallcolalreecatsedishnotwheedmbelaadcokweneardeaasndadjdaecgeenasertoarDirngy Rtueent.h. ShorSth-raeiwls Cceonmtmtoianlayrehaavleighwthabtroiws nkicoolwonr.asThcheesbtlnauctk,timpopetdedte,etah,ndWhdeegreenetrhaeteixntgrteemeethpooibnstesrvoefdthien whais smtiudsysiansgenthoetlneofrKmiadlnleyy,oabnsderavneodthienrsahrpepwesa.redOn0ehmaeveadaondwevxotlrea skiadmnpelyedoffarnomexttrea alroebae on the right kidaey., independent ofthe adrenals.
SHuLffiacnideAntrneuambIeVrfsorofsamteisatdicoawl cvoolmepsarwiesroenscaoufghitssfureomcotnhceenRterfaetrieonncse. ALriepai,d AcronecaenIli,raAtrieoan of meadow voles was significantly depressed in the Reference Area, Arza Il, and Area Ill, cloomwpeariendheto RtehafseroebnsceervAerdeain, AArreeaa IIVL (apn<d0A.0r0e1a).I, BcaormipuamrecodntcoentuhaastioobnsewravsedsiignniAfriecaantIlVy.
2
685. 05
USFW 0599
(p=0.087.
{Sourtfsiainesaiaclumcboemrpsaorifsohnos.rTihersehrweewrsewueoredicfaeuegchtcefsroimbtoedyRecfoepscesecaeaiAroenaoafnpdidA,veTaAILl Zeal, 10d fluoride n shrews hea from ese two areas
R37e.s2u9l,sonfdhien cAappppeiandginsuBc.essR,esTulAtsLameetaplrs,es1edaifbseyodrisdpeecaineasly1s2isd CaaepppirensgelooiceadtiioanTables
323 Fa
FcoosuerrsopeedicnieAroefaishorwehree RcefoerlenecefArroems.DrCyreReukachinubAsracnsd1faIiLl, nddacTsV.weNroefcilslewceireed
chuAbre,aFIaVn.ciCarneeeks,chucbesnm3aldsroinveerrcolhluerbss, w2e0rdelcaoclklencotseed idaacaerewe1re1alClrceetkedchfuabAs,reraivIer
-
Fiipsh.suTmAplLedmdeuarlinagdthfleloerciudofiasmhliynsgse.fforAt cnomDproysiRteemswaemrpeles(uabt iwars ftoarkewnhoulreibnogdy4
biorical fish Kill a Dry Run was als saalyzed.
`"`SaAillnycuesmiicssruecemok,nccaherunsbtesrnaiwtcee,rdebtoarhnieudomin,flfybreesrmpyielaclitieiusnmgc, boceomvbwamelotet,nnoitralosln,ethlreceaeodns,caemmnpailniagntagonnelssocea,itaioGtnaisl,slsisuupimes,ctiie1csa.5l \TanaandiuImV.werLiekeswiigsief,iccoantcyebnigahteonisncofrthesceehmbkesalfsroimn aArreeaa]IIhacnrtecoksechsuabmspwleerfeahAirgehaesr ((r2e0nd,oswihintAsveea IcVo.nsCeonavaetrosnelsy,icnaAdrmeiaumIVssnidgnsiilfviecrancdoyncebnitgrhaetriotnhsansthhooswe emhedeasruerveersien R`Aud.eanWeaorrerI.(0 hIneslpiatenolftiarserbeeisnugldtossedclweiatrht3shigfniisfhiciannhtalbyihiinghueprpearmoreuanctheosfaefaDrly caonncenttrhaotsieonin te lower reaches, There were no] differesce {a lipid or Muoride Results of the chemical analyses sre presened in Tales 30.32 ad in Appeadix B.
324 Esbwom sToolsseamrepplleiscateOenea-rwwaoyrsmnlsyasmpsleosf wvaerrieanpcreodwuacseudefdroom elxocohkoffortshigeniafricwaontrdmiofexeinsctsesitn (Ciastsumeicuomnacnedntarliloinusmbceotnwceeenntraetsirohnswoirnmtsheeexspeostewdor1m0 seaucheowfatshesifgiaviefiscoialndryebaiegnhters.n iweereAvleoswe|rexipnowsourremssatankehnofsreomitn AereraesfeIr,en1ce aIeVa,,bourtttheenRdeefderenicnecrseosilsse, wiChobianlcrleesvienlsg a{fnomceheroremfeheencleandfsiolill.s tChoapnpteros1edonbiscekrevledconncewntorratmioanskewaerferhoimghtehre ionthweorrmoslarkeean exposures. CFounrctehneircarteisounlsscofprheeseeneadriwnoTrabmleisss3u3e.35anaalnydseisn Afpoprelaidpiids, 5T. AL meals and fioride
325 Vegeion 5 009.2%
USFW 060C
Tloacraetieonrse.pliOcantee wsaamyplaesnoaf mloefyavdasoriwiasgcsreasswawserueedtakteonloionkefacrhdoifffhereenfcievse asoipllsaatmpelsiuneg
chiognhceerntirnattihoenAsraecaro|svsehgeecafiioven sthaapnliingthearAearse.a IBlaraindumIVcovecgeecaaatitoon.nbwutassismiiglnairfitcoanGtalty
oSibgsueirfviceadndiyn
hpilagnheesritnakteihe
AtrheeaR|ef2e0rdeeacfeeraandceiaveAgrecaaatiIlo.n
Manganese tan t he
concentration was Area IL. ll 12d IV
Vbeegeottahieorn.arCeosb.altThwearsewsiagsaitfoicadnilfyheicgshaecreiian tAerfelIuaVorivdeegeoiratliiopindtchoanncetnhattraatkioena in any of
RAepspuelntdsioxf3.the TAL meals and fluoride analysis are preseated ia Tables 3638 and in
33 Histological assy of small mammal liver and Kidney
jHuimstpoilnoggimciacle,anaanlydsiwshiotfefloiovetredanmdickeiTdaapcpyesdeicnioensaoofcftmheeadfoivwe Tvaolpepsi,ngshaorrte-aaiclonschlruedwesd,thmaetatdheorwe 0wedrecthoe psruebssteaancteiovefcahannegexsainlolbeioonvrkthieedroiregyh mkoirdpnheoyloogfyn.oThheeraprbovsidoeefaaaaeiccddaoeueylienviodneencaeniomfaaln, eofffhecet,hBiostwoepvaethrolwoegiacrael uwnoarbkleartoeapsrceesraaiedtien Tiambploer3a9nacnedofinthAepspeeonbdsierxvaB.t.ions. Full summaries
3.4 Toxicity Testiag
-
Eaghwomn
Beaasretdhwooarmtshetetsotxeidciitnyaeavyaloufattiohnsooiflssoalms,pltehserceolilsec5t0edaevidtehaeceDrfyorRguraowCtrheeokr ssiuer.vivaSlurevfivfaelcswaosn e1a0r0t%hwionrmalltwoexaitcmetnetstraerpelipcraetessenainedd ginroTwaabhlera4n0geadndfrinomAp3p2e.n4di0a5C4..3%. Further resuls of the
`Eatheadmiozow. Bsuarsfeadceownatteher tkoesinciiyn ehvealUupatpieornTorfisouurafrayceAwalotceartisoanmipnldeusce(d0 shgeaiffactahne:admomrianlnitoyw., iStursvpievaalrisnhtahke UlopcpaetironT.rirbauntagreyd Afrsoammp87letowa1s005%.8% Twhhielree sauprpveiavarltionbaellnoothgerrowstamhplreelsa,teidncelfufedcitnsg wtahieerr,efoerneatchee mcoirnrneloawtsedipnoaunsysioufmtchoencweanttreartisoanmsp,lheoswetavkeern tfhresoemcDorryelaRiuonnsCraereeka.o sSautrivsitvcaalllwyassignniefgiactainvtel3y hcoenc0e.n1r0ailieovnesl.in Tthheerfeerweads waastiegnsifaimcpalnets.posFiuirvtehecrorrerslasioofnthbeetfwaetehneadfamkinendowsurtvoixviaciltyanedsiarroen presentedin Table 40 and in Appeadix C.
Amahizod BHyaasleedllosnactehecar,esgulotswofofthtehe10ordgaaynissomlsidwapshaisneibwihcoeldeinsetdhiemseendtimoexntiscamtpelsetswittahketnheatahmephiUppopde.r TsraimbpulteasrytaAke,n,anTdhAeroebaseIfrvleodcatnieognast.iveThgerroewtwheefefecntoweafsfestisgnoibfscearndvleyd noengastuirvveilvyalcoiraealniyedofwihteh
1
009.25
USFW 0601
Sftluroornigdeg,egaaliuvmeinausmi,cciaaolncsu,bemnawgeaeenshiuemr, ooicwkel,capdoposis:u1md, c30od msomdi,um.copFpeurr,sI,e,eraeadwTenree Cboenacmepshaiipoosd.toAxlibciotuygehsthearreepardeosnehciepdsaweTraeblceol4g0 3andafanApaptehacei0x.C10. level. Further resus of 40 SUMMARY OF PRELIMINARY ECOLOGICAL RISK ASSESSMENT SCREEN SEePdAime19n9t9,),soiHlaszanrdwqautoedecnosncweenraeigones owereebrycodtmipveiadridengd tahgeima:asRioonnsiltelCBonTcAenGcrsaciroenenmienagsvuarleudesa(Ua.cS.h Cmoanttiiexnrbayionthse ecxocmeeesdpeodndbienogchiRmeagrikosn fIolr sbeednicmhenmta,rksovla,lueasn,d wAaltlercoantatmhienainnttisalfosr ewrhiecah imvnaexglimruismk tfeesrsmeevnalauraeteldsiiead3iihael froilslkoawsinsgessemcetinotnsf.orCBoenstiea.minantfledthe inal screening process will be
`Sediment
cTaobnlaemi1nalnisst,s mTahxeimmaurmimcounmcecnounatcieonnrsa,iosn rreecoerdecdriatertiae, sntdexqcueletdyedchrietebrieaocfhamctaorrks vfaolruessefdoirmehnet fsorleleonwiinngg bceonmcphomuaardks,: treeafcol,locwhinrgomcioummp,oucnopdpsera,remasnilglanceosnes,ide1rdedwai5ckerli.sk fBaecctaoursse3oftweel: lfalcukoroifde,3 imi, Sarum, beryllium, cabal ron 20d vasadiz Ver "mTaabxlie1mulmisceomnacexaizmauimoncornecceonrrdaeidotnst,hebesaicthmearkxs,cadteequebaelindtcyhcemaedrkivafalcuteosrsffootweefrollcoownitnagmicooamnpso.unTdsh:e pmotienntuiaml,isckopfpcer,.12d iron. Becauseof he lack of screening benchmark, fluorideis considered 1 be 3
Sail
T"Thaeblemaxliisemummaxciomnucmencroancieonnratifoencso.rdsecdreaetnihngecrsitteriax,caasnddeqdua(lhieybcernicthemafrakctovraslufeosr sfooirl choentafmoilzlaonwtisn.g cofotmhpeouancdks:odfausnriesan,iagbebreynlcihumma,rck,hrhoemifuoml,locwoipnpgerc,omrpoonunledasd,rmeansgealnecsoen,sivdaenraeddiausm,iakndfaicnteo.rs B3ecwaeulsle fluoride aad wichlorollueromethane. 50 DISCUSSION "aTthehedaDsrygeRneenrsCerdeedkursitneg.thMeifniiemladlelfy.orthseuegsguelsttstohfttthheerseedairmeepnoteannidalwpartoebltermsicsotctiaettedsuwgigtehscopnodiietniioanls puraoblleomfstien tahsedtfe,arsw.ithtSoosmeelmeveeallssprsopgereasrsiivnelhyigdherr toswepitcpohnceiernetnrsaitngigonsdiisntabnicoetfsrsoammtpeledannedariestartehae CLoinkecweinster,aisoendsimaenats staomspelesdaminplDerdy Rfuurnthenreadrotwhnesliaendafmi.ll ouAtfalplrealpipmeianrartyo shcarveeenhigohferpoftleunoraildeiasnkdfmaectoarlss bSeuggpersetssenthtataoewerll.probDlaeras,gasptehceirfeidcaldluyreilnegvattheed flieevledlsefofforltowriille,beorfugrothfelruarniacleyz,edantdhsrooumgeh m3eablass.elmianye ecological risk asessment for he Dry Rus Creek sie
15 009.24
USFW 0602
SECTION!
ECOLOGICAL RISK ASSESSMENT
10 INTRODUCTION
LL Objecive AehgeeennacbyjcRseiogviboofnsiedIsilzimareinsc,konasdnsudectwsiasntgnereaanwtae3vsafwloourapktriioonvngidobefeetp!oetpcernhotiidauelctseiucoponploofgraitrcmatllhtoercaetaUet.dSd,duoeEwantvoigzerxoaindsimteeianntgtolcofPvraemlsissndfiaionlnt Sndovesdtimienw,atatuwteareevcaotlel,i0e4fboirolsabosraamtpolreystwoexreiccolsliecgte,d fTrhceoinnafmoirmnanttionnlgyasbeesretdaddsioalgsteidsimeenltd, for was incorporated ao ia 2ecological risk assessment (ore Dry Run Creek st.
12 Sie Buckgrowd
TThieeshiaesifl3edwosrukmisnrgoubsecfopmrpoldauicntsiownifharhmelWoecsatedViinegWiaisakiDnegpiaornu,neWaotoodf NCoauuarrayl,RWeVso.urcTehseaowaedhre oUft.hSe rEPaAioalneg.ingtotaDtrscoRnuanm.ipaDnrtysRusnz fbleoiwnsg rdoiuscghhatrhgeed ffarrmoemr'2sapirnodpusetrryial12adaidf3llproiwmaareyd sboyurtcheeofDuwpaonrt {faoinsishaenrtde.aeTihevefcarymearnmcabiuntbaliensttohtahencuomnearmoiunsadnetastas,tbalienddaiessc,haanrdgeodbiesro uDaruysuRaulanfersosmestheobDsueravneed JRaunndfslilnceIntaeddictoinosnttruocteisoneobfmtoermlaanldifeisl. numerous ish 1d wide kills ave also been repored a Dry!
20 PROBLEM FORMULATION
"cfTodhneistnatrimfsicknaaainostn.osf CeDOusrCwisanssgadmnetdhseeigncpnoremtedplaitrmoiinesavoarnlyuoartifeshtkehemaspasoxteesinsmtmuieanmltc,tohnrtcehaeetnstprtraootebicolonelmoogfifCcoaOrlmCurslecaewtpiittoohnrsapcrfcorecopemtseesdxpbionescnulrcuedhemtdoasrtithsee. Tahcseionlfoogrimaetlifoencwpatsohreanndutseeitsdpperonpyritccommpelaestuereexmpeonsutreenpdpuowinatyss ofampannds exceeding benchenirks wTahrfidutrsinteotfehfeiperewliitmhiensaarbyliisskhesdetsosximceonlotgipcraolcebsesncchommaprakrse.d Blelncchhemmairckaslfaorlsyezdeimdent saonild. ssoeidliwmeernte.uasnedd TxMoeoerindgedanintnifg1y9b3pe0on,tcehLnaotminaagglhecstoawlne.mr1ei9nr9e5at,naiPsneeodrffscouroanfducretahnle.rf1oe9rv9at2lh,ueaUtp.iSro.onteEucPstAii.nogn1io9nf9g2qe,sutSaiuottnee-rbiaansoeddMe(bxUrpSoe.syuErPe19Am94o1)d9.9e5lC,ofmLoparanitggihnsdensdr Semcoraies, and direc exposure assaysfo fish, benthicand eresial nveribrais,
20 Ecological Risk Assessment {"oTisseecroeloagidcaclorinsakmaissaensss.menTthewafsolwlroiwtiinng stoipdestweermrienceotmhpelreitsekdafsosrodcisatepdrewliitmhitnhaeryexopkosusreessomfebinott:a (1) ASpelceiersa,rurteo sdeesteecrhmwianes ceocnodruocxtceodlotogilaoclateeflfiefcetshisotforysiitenfocromnattiaomnifnora,seleacntdedtiondilcoactaotre Bioconcenmation factorsfoie contaminant.
(An evaluofaetcoliogoicnal receptors was pepaced. This consisted ofthe fallow: + aEnxdposmuargenisncuednaerioofs wceormeamdientaetrimoinn,edabnadsetdheontsoixtieccoloongtiacmailnamnetclheavenliss,mtsheoefxtetnhte
1
0e9.05
USFW 06
+ oInndiscia,tohrespsevcaielbwieireyosefleictcedybasiendfoornmastpieocnieos pmrestehnetlaendalorr,ponsednttihlelyprpreensesnat {or exposure to it conaminants based on habit se of behavior
+ Exposure pathway(s) were determinedfo ech indicator species.
+ cEoxnpaomsiunraenatn.d effec profes were wrinin or each indicator species and exch sie
QAuroitikenctha(raHcQte)rifzoartieoxnchwasspeccioensdufcteaodrawnrhgichofeixnvpoolsvuerdethsececnaalrciuolsa.tion of hazard
-
tBharsoeudghontthheusreeosfuscoof nisseevarluvratiaisoktnm,oihdeveCleOsCsidentifiedin he nial seven were urhr valued
22 WentofithefConitamicnanatsotfCooncnern
"fTohre cthoinstasmiitenatnhtastofwpeorteentrieailnceodnctehmrwoeurgeh dtehenipreedliumsiinngartyhesciraeeln cionncalumdienamnetaslcsr,eenf.luTohriede,COaCnsd
organofiuoide compounds
:
23 Exposure Chanacerzaion
"rTehceepotbojrescmtaivyeboefetxhpeoseexdpoosusree acsosneasmsimneantniss.Ptotdenettiearlmienxepotshuerpeap thwayh s aanrdey dmeepdeins adatnhrtoounghhwahbiicah irnd arecepnotforCsOsCpsre.senItn otnhissibea,seelxitennetecaonldogmiacaglnriinskdeaossfescmoennttam,inawtiilolnb,encodncelnuvdierdomtheantt"aalproteentniadl iEfkfe"ctexLiesvteilft(hNeOHAQELc)leeuqluaalesdaroemxcteheedmsa|x. imum ste oncentaion ind he No Obirved Apparent
Ewoxpphoiscurleevetlo oCrOgaCnsismpsr.eseInntaindfodraigteotsenxipdopsoruernye svipaeccosnsviumpitnigoenstoficoonncaomulidnacatuesdefoorxagei, olinoghiigchaelr rTeehsceeapestoxropsfotmshaeeytaooflbxsiocebieycetxespvtosesredebthareosug,heirnegessitilonionfvweatneer banrd1aiidnceisides,nhtwalasindgesstieon orfsombiylie/sxeandmiimenenitdn.g
24 HazardCharscuriztionToxicity Assessment
to"xToicdieteyronfitnhee hcehfefmecitsaconfadtlchosentsaymsitneamntssthoant btihoy,aftfiecst.neKcensoswalreydtgeuonfdterhstafntd,teheffmeecsc,haannidsmmosdoef aofftahcetogneonefrtahletoCxOicCosloaglilcoawlsifnrfotrhmeatsieolnecftioontohefpCOrCospirdeentsifeisedsmineSnetcteinodnpo2i.n4t.s. Next i 3 review
261 Fluoride
2I5normgaannuifcafclaorriindg caonmdpomuinndisngarheauvebicoqnturiibiunttenodautuos.thHeoewnevvierro,nmnednutsarlaolapdroocfessfelusorsiucceh, primarity trough amospheric depositioJnn. low doses, i 1s aceeped ths fuori 5
"
609-35
USFW 0804
aTroeelesirvesonefenwpeeatd anmnTaaenrd5scwnoellBna4sius2e3ps%ilp,pansweo.wisdnelsiIhe.evDoooesslfu peTrreodpSrumipkonrisoLapo,l, cp1ooarrdeniyAnmoto s,FpsseOmanK,nhowsreonav,popsaofheomoeas. eeedptitmeeinnigewacdloSyciii,, E9M0no;rpmi,cnderaeoeet9o0g:wsGdiesso.ndodeHsTrenodt19shppeonnod
242 Organofiuorides
DoOrenaognieponapaeplows,etvwedenetdy.smrvai,elsvaofaiiAtn.uogAfseecIs tasu3Sicnrethelerceooncfcooensrnosf
cmreheiaooarvtTouedoiasfnolupoodofrpmseeatnhpassnesspsprsoodsSuecee.dgdbuesceerveeaesseetdnmyatMeserionnanmledaadnsld faiemnthaBsdl wGseoiHgeShDtws8o,fai1s5wh9eeal7nlseaGsrAaRnoGivnce1re9a0os0eo,d
243 Amini
-
BoRneciaumsreiaaif oisnrsyhoenotmrooeasatidh,heltSein+ua,nu(nAtci1onb5teinfn,oiund11o6TclnmoerlpnSeenaeplry
-
bSeseh danhraecaocnsc henxenoofsYa.miI,t wait5e,iioqn (uATSoDR.i190). Pt
aF fobpeladnoaere.ngepnpertal easeaar Tno.e Bldomnsgiafaionbofosari--nni--nomf se--sm--fod
Sone oot hath ATSDR 1990
eThe lraroonasse sDaNynAmgfeomaryigYieen8etxwprienesiAronsRsndEGorp"mriiinnuefm,,riAA.lNiMnaemSasyenesnsaiemseth40
s oeeratepofdasrtinsgaodmaorleo(sRGTSatDR t199fo0t, 2ASlhoaumstaea4sk4mwadvmsrssTioh!r$s1
Gon
244 Aric
SNCeavoebrenalt1r9ev3ii4enwgAaainxlsosnea.rdeeeseaasl,ewowihmneaddsis1suh(sEerratnn1em95ee.fsec(PtohocylAisso(ri1o9e7vr5)e13s900d88,
rpoonergansssti,oStsovcetrookettia d4immameesaweihs ALMoeso.SoHooawnen,,eesotrooSraetlrsaeornee
nes semen daar, pi 1nd 1 Concession ofaves ompoun
0927
USFW 060:
n(EeiFrlrrmo19im8n8a4ns;aerAobi2c0c4ond21i9t8i1o7.n, Thae US2. EPAnd(1981)sneendit(hsoarse)t penraveadlnotn)eis fsfaoectmtores3f1or0ni7tvfesoribgarnsseisefaypgcoeonrcoetmnepa3.e(dpien17qtfuaoarlteesxpiovseAunreembfrosatAemm;eiwsehobvleeoSbooxdeys(asscoaonmlEneaenid2omnned Sorigeamnaigsamisfiacioocnobcaeums(oUftS.hEfPoAod1c98h5i.n Rowever, a 40no indiste tag 245 Bentium
12CTohmebursmotaiujoognrh.itdyBepoerfritiyhoelnboeafrgymulrolasilulpmyhSe(Breee)sbiwenaytlthlteuemae,yasvUiBpreooonnumgeehnstthhiisnwgtehwesrtesohualnntdoofseefocc,ohablnaeondinom.il
p
Cmhoarrd,auyotree,imnierde,tnpoholsephfnodasSttuhel,e Ggenmaanryldrsaee see.il Hwohweesr,oeelolso
(ATSDR 1993a).
tlDausye. otTahsacrsgsteoorcasth,eobmwicypalols,imniildarpi6etymca0tyesedlummiaanvumpe,ribeecerpydlaleimduma5mbaGyybSeineIsxoplecc(otmRepdEltSeo eRss 1ed9i9g5oh0tto
"nB0erwiyalirlminuwmabeisonfmoaat gienxaspoiefcfttwceidsWrtiE,ooATbnhieofocdoeodgnraceenensaofeiosxiibeaenqny udforauendsa.snieBmsaelwsirth1mnmdec7s0sienveigdeenscleoifsoer
(ATSDR 19933).
msMnaodmmrsaelsdiipmaeonnsty.estA.letshsoufogrihaseeuvenraalkcoseluvoidgosisaepedoistnptotorruetslntahoednneheyggabetosetwieeoTnnooscfdscioomnfcaoemsisinearesdiinl
Conceneaion1d observed txt beni organisms could ve found (ATSDR. 15938)
246 Chromium
Chromium (Cca1x)is in oxidation sas ranging fom -2 0 +6, buts mt feqently iic1om9an8psv6oec8rrc.tteuadImntupobriotohotcehnersfeselraesteisrtveehallyeirsvcuetablnleydemmmwiiianvnroairln.seentrse(ey~c3n)ima,pndedhysh4derCxMoalrveyasliheosynfdatrnCo(rdx+.6ip)dweeocosxiieepdamastiiioosannbsatsatdoeisrie(pmEimesolonedr under seri conditions. Foweve,unds sno and low A conden. Cr hydroeges (rmEaniyiscrol1uc5boi8lm6ip0zl)eeaxsnidingreesm,uabitsnhaeanssceilson,iacayoCru"sgaudhnlBeoossgevonxaiiidaiSzbeaidmyptooifCCscrrsprtiherosuogvhmemomirexedinSsg ealndoanFcrtatraiioden mes sd Baris 19835: mes and Buren 1983) maTnheevsssaelntaeinalt(SsceltveeemnesnthteiLnfmo1ma9m7s6mi,alllCyhbrfyoomumniaduiminaisiilnboiengngidseSaalclimbeatncnsogth.iscoeTeh.iisnpfiottro,mbsugohnbe,cmpoioasnms.
(Eisler 19863). The biomagnification and toxicity of Cr" is low relative to Cr because of
w
coon
USFW 0606
. : .
-
N
iascculmouwlamteiomnbrbaynaequpateimceaanbdiltteyresarnidalitpslannonscaonmdosainviiemya.ls inHotwheevleorw,er3oplahrigec dleevgerlesehaosf ubnesennodnonc.umented (isle 19863), though, the mechanismofsccumulaion remains ely C{horxoimciurmelaitsivmeultyaegesniic,ocwarncinaobgoeunitct,heantdoxticeisttyoogfniCcF,.wiAtht Chirghceoxhnicbeintginagiotnhes,reCsriost Spaetshooigaetneidcwiotrhgaanbinsomrsm,albeehnazvyimorealacimvoidyi,filcearioendsb,lodosdncphieemdiszfye,edlinogw.erheidstsoipanthcoleogy(,6 Eimoregulatry upset, erations i population scusere, and shin afphotommihens Rmuacbobpioslysfaedcchdaireiadreys Cirn tahcecusmoufltattiesdsuehsy,alcuaruosnisnegs,pecrhcoanpdirloainiynscsluelrfoistiess,(Kaundchenreuaenadl nShearbaonomv a196c7o)n.ditTihoinss,apccrumeulvateiotnnhetblnioocrnkmeagdlbalnosodpotrissoufembeutmiaerls.s.whiOcnheamreanpieremseaaibolne Gofathmsacoogntdhieetibonecwaacseltshecionnhaiiaiedntheorfeiinn.sulin production in the pancreatic Kits due 16 Cofihnmarcelolaulmsaroilvaacuduoslmes,pmihtoocnhonddarmiaalgeswveilaisnwge,llainndgyatndoplolsasosfcmiqcureofviiclt,iotnhe3fdorm1a5t8ioonf Celliningthe nephron surface (Evan tnd Dail 1976),
a"Tvheeoptrreltiimsisnua,rfyolsleopweidn bCyritnhdulcieidardeospniorfatiornyflcaamnmcaetroirysrpeecausloantesdifnolbuengthtessuceareixndginogf tDoirberctonsckihnopcnoneiuamcotnwiist,h ahilgvheloylcaoempriodshilviaclhrcohmanigceasi,dattrnodphiys,aahnyddbredneigpnrotduumcoersfsokirnmautlieorns
`and necrosis by a mechanism independentofany allergic response (Steven etal. 1976).
247 Copper `(CRopTpEeCrS(C1u) d9oaensd9naop1oasspi)bpleteocaharacvrienomguetna(gVeenincugporpoaplerainedsLIuRcIkSey1919907)8,).buCotppseratisesctaougse,n
and acute toxicity is primarily related to this property (Hatch 1978).
`rCeosppipreartoraypniegsmesntas (elDeememnatfyeoortanali. ma19l8s2)a.ndtsiasc3o5m0poensseennttioalftmoarnoynm(eFael)luoielnizzyamteons nandd f(uVnecntuiognospianlenazndymLeusckfoeryen1e9r78g)y.proEdxuccetsiosn,Ccuoninngeecsitvieontilsesaudesfotormaatcicounm,ulaantdiopnigimnenttsastuieosn, emsapeycilallye0iniantaebidllevyefhHieghlvleerve0lsosofr CaanmdodeixcfryetheepsatdiicdmoneatlabCoel.isWmh(eBnrovoekrs1c9o8n8c)e,nwzhaitcohn eHixghcCeua celeedvaeilssn allesvoel,inthhiebimteteaslsiernteialemseeabiatloictheenbzlyoomde,sca(uDseimngayhoemoetlyasl.is1a9n82d).jaunTdoixcei.c seyamlpt1o9m8s2)s.ppear when te liver sccumulates 3 to 13 imes the normal levelofCu (Demayo pArtohpoousgehd:thfeoremxaatcitomnecohfasnaibslmeoifnhaibitoi ryicsonmcoptlkenxi oewsn,witthhecfyotlolcwhirnogmmeePc-h4a5n0is(nWsiheabvee aSe.en 1fu5n7c1t)i;onimopxaiidratmieonntso(fRfeuinnceirisoanlo.f N1A98D6P)H:-acnydtionhcihbritoimoneofrheecmuceiaisoesynmdihaelstser(aMtiaornieolfm9i8x1e),d Inanucles inclusions may act 3 3 detoxifying mechanism where Ca is complexed by
n
009.2%
USFW 060
protein ligands, protecing eyoplasic organelles (Demayo et al. 1982), LmRuoucrmkeiendyaine1tt5as7r8ay)rC.uthtehamnosotdseernasniivmealmsanmdmaalesmpoerceiesntosiCauveoxtiocaCias.toxYicoiutyng(Vaenniumgaolpse)reesidn 248 ten rpIroroninms(aFarey)cioisnntchsoeempnmrtoodnoulfchyteimdooencogelfcosetbdeienlinancndodonitcshesenerantatililoaonlysso1f5pwSlealpnelracanesdn3tamonarjamolarrsHeotusirnacseoawifellhItoianurseeyd 2rie1ngibumilopaatoeridabnnyottcaoecxmoppemocpntleeednxttmienbcceehlaalnusliigasnrmifoixtcioadnmattaiipvnretoacpiernsoschfeososemos.ne.TshGe.endeiTrshapelorlseyt,fioaorneb,oofbito2ntg1ae0nse1t5sssptneastnotr 0foaf0ii1lnugrpeeesraiceneddntrhooefnptahtisiescbocoridhyboebsudirsfd.eonmTpheterhedmaaeysc.vhaoAnidimvseermsstoeifeltforfxaieccci,otynfbdfeogcnilntisomxwiiinctidhtoysnmcbausyespimpursooerssid|mnooily ednadmoatngeeliaanld.ceslbdraormpaigoenoofthfeerlrivoeurs(iSohnsacdkirleectlayndinBooecmigrceunlat1i9o8n4,),resting in sapiay 249 Lad aOLneddaedradnooircmgsaalnnsiotshmbasistoybmpeaiegcnnalilefyxyctteoonns8iavgrneelaytthdeeohxciugehmeesintttfiesodod(WcPihasbisncoson,nckaetnnhtdroaDutagivhoinsssc,c1w9ui9mt3ih,lhtEeisotmnearjboy1r3ip6tl0ya0no)sf the accumulation in the bony tissue ofverebrats (Eisler 19885). baPivroeelrioygciilcnaarglgevthadereissgbcrlceeu,sm.ulliIantvigoeennetaronahld,teooxrrigcmiaetntycailosef,adPbycioimndtpieofrfuaicnctudilsotnassriaencmmeoainsrgetpfhfoyexstisctaharlaencihinnefomlriugceanancliecdnPtdoo sc1eo9s8ma8pr5ot)u.inondI.ns,pTlahnnetdsm,eyPcobhunaagnh,iisbimimsbmgyartwouhwritechhobrypghraoentdoiusscyminnstghaeprtheiocmtocosstiymsvhuesrceepradecbdtliuevciettydo, smfsim(eiTsroeeasndd(tEwoaiteenr pblroecpkoirnpghytoifnosguelnfh(yHdarlyll ngdrouHpas,mpipnh1i9b7i5i)n.g the conversion of Coproperphyrinogen 10 bTmeohhreaavltiiootxriyac.lrecefhdeaunccgseedso.gfro?Hwotowhneavaneqdru,atrmiecapnraoyndduecfefteeicsvteesioeauxplhuiotbir.tgbaglenonieosrdmaschreeenmiedsxsecyeinmateehlreyattvoairrisee,dmlaeensdciohniasn.cnl1iun.dde cGaaecnucesurianmlgllmtyo,ersaPloiattyih,nehmmiabaitrtokspeotdihecethiafcnogromerasgtaoinostnh(oEifcselnheterrmael1,9n8e8ar5dv)vo.eurssAestlyyistgaefhmfeoccctocsnucrbelponroitodirohnsedemeatashr:(lEeivaeenldrs 1988), ohPrleagnartnosi0ccsa.mnauTrphraekcseoinlPttbeynt.horfoLuegpahldasncutrafntaociuenphdiaebkpieopshPiobotonfsryionnmtahsenso,ilssd,uspsl,nannesrdsgsreiollw,trhoe,swtbaeytdeu1rp0tsasokoseiortpphFtrooauncg.dh 2410 Manganese
2
080.0%
USFW 060.
leMangesanesevma(piMoanr)tsdseosslosetmebenckeaualryamaenafxgratenenesmieean3l8disniptnehoenrgdeaenndivcipomnramniegnactneebsumetascsoe3mrcpGoomeuprnovdnsgenfhsaovomef
ocnaaisneg.orTthoe raotno osafnodilp.piRoeomonrvalfoofmmatnhganaeTsmeosipnhwearts8 moosntolreodugbhy
Teoos(ioGHin10asfaTttyhess1pmeacy3ib+,ecbcioamarelo1x2if.dirzDeivpartleesneHtn.magTnehgseatnmeeesaenl(mrMary.)ExpirteMdaonimgiatnneaesesseniinan yofkof
ionmnepoegunotosrigtnaoanmioocvricnogwmpiseoessosandsopfseedthinemdenoetis.sdeedpiimenenndgtsasnm,aeiTsnehlyieonnndwtehanetcceyeomfnaOyexlbceheasnimggaennipfgiacananetcsley
iaootnbeeseingnaifeicdanstt(oAwTeSsDsRo1p9h90)e.vel. However, iomagaifcion in he food ha may
-
nShoekeaapmpeoaurntdtoobefemeanmmgiassnkeesodfesdhsiifooerrrbepneicdoenbacaerpoepseseahnremoagnbogiadneesesieyonarloneaackisneif,ovoawidriitoahbrleeli,onwwaTdithoeerne,ledOvoeneless
mianngginetos rceresoesodroemdanbgyatnheesseumdbesTarapnisopn.ortTyhssem5inptrhoebgaubty(AbeTcSaDusRe 1b9o9t0h).ron 3nd
2401 Nickel mpuorrnetnibiusckneedle))clieasmnenhNdtairndc,dowmbhifinoeumdnedwaiitlhhtohethteerinsveulisermaoelnnlmtyesnutsse1fdsoouixnnidtdhneesafloorrsmsoauilltsfi.iodneNsio.cfkeaNllilcsokyhesle(sm2ua6cyh DTFeoovnreeesecaposhendnn,iinnntgdthFeenceoinrnvmeiarrnaognomaren.netsNierc(okaeulng.whilmUniadndegrh,acotiidlisco-iuclmooinfndsgieodpniosmw,eenrNtippamiarniy,ibece,ocseolsm-pebeucmmioiarnlegy aaoie snd sep to he groan: Th ypc Ni concenraton eporied nis from 4fm-p8o0raminltligcraamnsspederskiinlgog1rabmesh(amvgi/okrg)n. tTheheensvpiercioantmieonntanadndphtyssivcocahemiical0stbaiteotoafNi is ToghermioosntopfrobNaebcloenemxupmoisnuarieetdesosilo. fNTihaerertersopungohrydesaylseomnisat,heaprilmaory aofrdguso,f3Nnid aoernonpehiagtfelshoywcpeiepnlassoeibdaa,ltoanoNdni,ctrrMoeiueglhdsonolgneswxepiosgsuhuctrheh2aswvenerbeemneonicodtn1e hoinafvateneiemiaanlrgsse,x.pvoasoessdi.t,o {egos eating salivasion, and suing (ATSDR. 1996).
2412 Vanadium E{fleiemimnieznctsaO.lbTveaorneapadniibucrmiadpdooegsoenenitocfovcsaconuuarrcdneisuamirnscylaudbseuntaatcldaornwmicenxeoitnleisance$ha0,ted,eisfpfsereecvniatagleoyrissnisadncede,foTasshniedl Tiheoanveraofgveacnoandcieunmaitoonseoflvaredmiovuems xiyngoene1rdincirzusotgen,15W0himchgimparnodvens ethUsS.esgis 25200 mys (Bema cal. 1970), oThme rseoetsreooifonv.anaTdhiiumprtoocweastseursaanldlysocilooncvceurrs 35 r5e.s4ualltuobftlhTeivwaelsenhterfionrg of trhaeckmsorned-
2
009.25
USFW 060
ipsnolonuebsulrecalpaaeonnrdalvatal,hlkeaelpnirtneesoesrnomcil.esoafTnphdaeriiscmuomlaobibeiisl.lyoRfedvleacatrnieavaedseiosumoitnhiaencrisdmoiiicnlersiasollass,ff(evAcatTneSadDdRbi.yum1p9Hs9,1m:roevVdiaoenx Zinderen Bakker and Jaworski 1980).
vaidnadntiahtdioinut,emm,veaspntHar,dailaunsmdyscgtorenomcwse,intnbrgiactoioconondnsicdeionnntpsal.tainoVtnanairasedmdioeurpmeenscdpoepnematmroosnnttohibenealmporoweeusrnetnptloaifnntwaaslipceescmosel.surbalIlen
cmoanmcmeanltsaiobuntoftvhaencaodnicuenmtriautsiuoanlslyarfeouunsduailnltyhebelilvoewr athnd sdkeelteetailoinssluiemi(.ATTShDeRhi19g9h1e)s,t
vVaannaaddiiuumm oinvetrhyeporoerspliyrabtosroyrbsyesdtnemtitsshiemiglaasritntoesottihneralmcettasan(dCatshetotnoxoivcameetcahla.n1i9s8m6)o.f
.
iVnatengaridciy.umDdaammaaggeedsmtahcraoipvheaogleasr minahcirboiphhaegaesbibyldoeftcrheasriensgpitrhaetomryacsryosptheamgoecmleemabrtaoneed oftherpanicles.Invivo experiments indicat thatthe mechanism of toxic ofvandium
pisumbpy. inThihbsitpinugmspiosdinuecme-spsoaruysfiorumthAeTcPasae nactsoifvpmia,toewrhirialchaciraohssbicselhemesmobdriaunmcpso(cNsescihuemy
ind Saunders 1978).
2015 Zine
itZnirneecdu(cgZinn)bguyihsmeleesatsoleaxnoitctiiicatloynfoeoefiZndnnso.orbmMaoletahglvrloowehtihroanneedaasbrnedpcrrtionadavuetctrtesimboepnroarsieansrpy(lOaZlnnstsssoatnoncrdaagalenis1me9a8sl9s)s.sndnZdisnides iZsnniostkenliomwinnattoedb.ioaccumulateinfoodchains,because tsregulated bythebodyandexcess
ZoainfndZgcnhasaibndoiuslciperrCitmaearodfyefmibecocianebnuocclyilcaenedff(eiRcnNttoeArn)faeZrnce-dwdieatpnhednmddeeacnoatxbyoerlnibzsoymnmceoesftlcehairlacciieudm((gDCNaAu)t)h.neldiHoFiasegyhn(tiGlhoeevyeeselsrs am19at8m6hm).a(lLsTu.haenPdpaaCnnoccrmreebsasisc1a9en8fd8f,ebcoKtsneainszceleuaamdenc1dc0oyVboaespntlhiVesepierctim1va9ar8cy5u)ro.lgaZetiisnoenopf<rleZflneurleoanrtxiaairllocypahicync,buiamrnudldsaneteids pinhobsopnheo.ruasndandinodtucheesmionsetreaolmsa)l(aKcaiaje(xas.of19e8n8)i.g Goifllbopniechcealuisuemdisbythea pfriicmiareynctyargoeft sCiat,e i1n58f1i)s,h. Zine toxicosis results in cesruction ofgill epithelium 3nd tsue hypoxi (Spear
25 Selectionof Assessment Endpoints
Ad"TsihsseicsuitsasnnifcooenrsmGarwioiuopnh.gtaahtlehleoUrwSeed.d fdouErrPtihAnegsoeasnl-iescetcieronneecoofcsnoenoarsdisisnmaanetcnoertaaennndddpdtouhirenitnRsgettghihatonfcioer1lr1dewsBopirookln,odgeaidncadtlostTuhbeeschehqanubieicnaat oftfoyrbeeissdisep,draenmsedantomladtmftehaedalnDdurspfyil.saRhnudmn,aCygrrueasesskytshmieees.acdoTfwhoser,fsteihdteiinrsgeceaokn,mdpanoenssdteisdnsgoo.cfiLsiikveeadwriirtsiyepatorefienhsatabriieaaasls,sndAincbvlaeurdinienetgy ofirongcvauensrieesdbmrttsoeuwsravairrvdeabtkiheleiysteeylwfeeamrueennasltelgierncotiuhepedasf.snacVsisioeanssisomlfeynhtosfenetdpeyorisenitsssaf.,ortTahhvieirsaenrf,iosrakena,dstsaheqesuasasmtsiecenstpsmoLeipnsttleeadnrndepsxotiwsnnteds
z 8532
USFW 0610
the specific assessment endpoint selected fo this ecological isk assessment.
Ten assessment endpoints were chosen 10 evaluate the rik of conmminants at the Dry Run Creek sie:
1 protectionofbenthic invertebrate community sruerure and function
2) protecotfisooinl invertebrate community swucrure and function
5) protection of fish communities to `potential negative impact on growth,
seunrsvuirvael,tohrtrediprreocdtuecxtpiovseusrueccteossc.onurminants
does
nok
have
4) protectionofworm-cating birds 10 ensure tha ingestionof contaminantsi forage does not have: a potential negative impact on growth, survofriepvroaduclti.ve success.
5po)tperntoitaelcinoengoafticvaemiimvpoarcotusonbgirdoswoth,enssuurrveivtahla,toirnrgeepstrioodnuocfticvoentsaucmciensasn.ts in forage does not have 3
68)pportoetneicatlionnoegfactiavmeiviomrpoaucst
moanmgmraowltsh,oseunrsviuvrael,thoat
ingestionof contaminants reproductive success.
in
forage
does
not
have
7) protectionof piscivorous mammals oensurethat ingestionof contaminants in forage does nokhave 2 potenial negative impact on growth,survival,and reproductive success.
8) protectionof omaivorausmammals 0 ensure that ingestion ofcontaminants in forage does nothave 2poteniial negative impact on growth, suravndirevproaduclti,ve success.
9) protection of nsectivorous mammals 0 ensure that ingestion ofcontaminants in forage does nok have2 negative impact on growth, survival, and reproductive success.
h10a)vpaerotneecgtaioinvoefihmeprabcitvoonrogursomwtahm,msalus tro envasnudirerevtphraaotdiunlcgteis,vteiosnuocfcecsos.ntaminans in forage does not
26 ProdofTuescublteHyipotohesnes
Tonhethteesmtaebclheahnyipostmhoefsecsoanrteamspiencainftictroisxkiqcu,estthieonnsuthmbearorefbeaxspeodsounrethpeaatshsweasyssmetnhtatenmdapoyineixsi.st Bfoarseadn assessment endpoin, or other factors, there may be mare than one question for each assessment endpoint.
Astrreuclteuvreelsaonfdsiftuencctoinotna?minants sufiient 0 have negative effects on benthic invertebrate communicy
Astvreuclteuvreelasondfsfiutnectcioonnt?aminants sufficient to have negative effects on soil invertebrate community
Arerperoldeuvcetlisveofsuscitceescso?ntaminants sufficient to cause direct toxicity (0 fish growth, survival, and
Ate levels of site contaminants sufficient to cause negative impacts on growth, survival, oF reproductive successof worm-eatingbirdsduetothe ingestionofcontaminated forage, soi, and water
2
009.25
-
USFW 061
on the site?
Arerperodleuvcealisveosfucsciteessocfoncaammiinvoarnosussubfifricdidenutetto tchaeusinegensetgiaotnoivfeciomnptaacmtisnaotendgfroorwagteh,,ssiu,rvaivnadl,waatnedr onthe sie?
rAerperoldeuvcelisveosfucsciteessocfoncaammiinvaonrtosussumfafimcmieanltstdouecatuosetheneignagteisvteionimopfacctosntaomningartoewdthf,orsaugrev,ivsaoill,, aanndd water on the ste?
rAerperoldeuvcelisveosfucsciteessocofnupaimsciinvaonrtosussmufafmicmiaenlts1d0uceatuosetheneignagteisvteioniomfpaccotnsaomningarroewdthf,orsaugrev,ivsaoli,, 1andd water on the ite?
rAereprloedveulcseosfucsciteessocofnoummaiinvaonrtosussumffaimcmieanltstoduceatuosetheneignagteisvteionimopfaccatnsaomningtroewdhf,orsaugrev,ivsaoli,l, aanndd
-
water on the site?
Arerperodleuvcetlisveosfucsciteessocofnitnasmeicntainvtosroussufmfiacmiemnatltsodcuaeutsoetnheegiantgievsetioinmopfacctosntoanmignraotwetdhf,orsaugrev,ivsaoll,, aanndd wer on the site?
Aretperoldeuvcetlisveosfucsciteesscoofnhtearmbiinvaonrtosussumfafimcmieanltstdouceaousetheneignagteisvteioinompfacctosntoamningartoewdahf,orsaugrev,ivsaoll,, aanndd water on the site?
27 Concepmial Model
`pTahtehcwoanycsep0rutahlemseoldeeclterdemlieeassounrecmoennttameinndaponitnatnsd.haAbtitthaetDcrhyarRacutnerCisrteiecks stiotei,decnotniafmyicnraitnitcaslienxtpoessuoriel mmaamymcalosm)e iinnhacbointtiancgt twhiethwosoudbesudr,fwacee(tealratahnwdnoordmpse,)na(nidedabaorveeas-ogfrotuhndsitteer.resStruibaslurrefcaecpetotresrr(esstmrailall rinecseoptmoerscaisnesh.estheeairnetaesntmiaonyalbeinegexstpioontsoofsesotdle.coAnbmoivnea-ngrtosutnhdroteurgrhesdtriiraelcrceocnetpatcotrswmitahythbe seoxiplosaendd. 0thecoinngteusmtiinonanosf tohtrhoerugahbdoivree-ctgrcoonutnadcttewriretshttrhial sroecletphteori,ngtehsetiionnciodfseunbtaslurifnagecsetitoernorefstsrioailaodrhgeanriesdmst.o food items. and the intentional ingesoftsuirfoacne water from anyofthe on-site surface drainages.
a`Tvhe waooordfedtieraeresetar,yiarlipaanrdiaanvairaena,reacnedptmoersa.dowForareexaampplreo,vidsemdailsltionmcntihvaobirtoautstympaemsmthaalt mmaayy soucpcpuopryt thorneeoerhaalblittshedhaibliytaitn tsyepaersc,howfhfeoreoads,itaenms.indAivviidaunalpicsacmiivvoroersouasndmcaammmiavalremsaymaryegubleaerlxypoasveedrtsoesiatlel ccoannttaammiinnaatneidspirneym.utchehitnhceidsenatmael iwnageystai5onanofasbooivUese-dgirmoeunntd,taenrdrestthreicalorencesptuorm. opTfhtseuircfooancnseuwmaprteisomnaoyf transfer conaminans o these receptors.
p`Tahtehcwoanycsep[r0uatlhmeosdeelelcteeldemseoansucroenmteanmtineanndtpoainntds.habiTthatecphraerlacitmeirniasrtyicrsitsok isdcerneteinfyicdreinttiicfailedexmpeotsaulrs,e sfeludoirmiednet,.3onidl,wraincdhlwoartoefrl.uorBoemnetthhiacnemaacsrothienvperriembarraytec,ontfashm,inaanndtsteerxrceesaeidailnginbveerntcehbrmaatrekssmianysibtee
2
00.34
USFW 0612
eexptostede0rc.ohenacmoinnaeinerdstsieodnimofenth,ecwoantaem,ionrasnotilsdofocuognhcdeie{otutnodxincithy.e sFoermtehne,puwraptoesre,soorsofiilswiesrke Coovmeerlcabtreadtewsithhtooxricitteyrelseiveallsiindveennteifbireadteisn mthaeybcoerartesFpisokn.diTnegmteosxwiiciatlyreecsespttoorsdemtaeymibneeexifpboesnetdhitco ceovneamriencatnodrsbymfy ealoeboendoerigaxnnispg1mscowohnitscahmiehnaavndetsacrcuommulfaotoeddiCngesO iionntaeC nid viiss asuiensc.idHeingtahlerigersocpihoinc oPfastolhlssctaoimtehntreifnerdenwcaera,raTsheapmathmwaayy ionvtohleveregfreoruenndcweaatreera amnesapdoorw. isTuhnekfnoolwlno,wihngowpeavtehrwatyhse Tere evaluated in tis risk asessmenc
I 2B)etheDiinrveecntcberaxespoosseudirmeent
I 2SoilinveDricbsratieesxposure tosoil
mo Fais Dist expostouwarteer
W. WomeatiIngnbigrdeofsetxviwaormns
b) Incidenalingestion ofsoil
Incidenalingestion ofwater
:
Vv. C5amiveroIusbningd oefssmatllmiamomanls
b) 9
Inicniciddeennttaallininggeessttiioonn ooff woialter
VI. CamivoroIunsgmesatimomnaolf small mammals B) InIcniciddeenntaalliinnggeesstiioonnooffwoialter
VIL P5iscivoroIusnmagmmeaolsfftoraigeoinsh 59 Iinncciiddeennctaall iinnggeessttiioonn ooffwsaetdeirment
VIL. 9OmaivoroIusnmgamemoasflftoraigeoisnh b) IInncciiddeenntaall iinnggeessttiioonn ooffwasetdeirment
IX 0InsectivarIounsmgamemoafselatrtihwoornms B) IInncciiddeneanlliinnggeessttiioonn ooffsewdairment
X. Herbivorous mammal
.
2
008435
USFW 0613
9b) InIcnigedsetnioanloifngveesgteiaotnioofnsediment Incidental ingestion ofwater
28 Selection of Measurement Encpoints
Mcheaarsacutreerimsetnicts esnedlpeocitendesasaraessmeesassmuernatblenedpeocionltosg.icaMleachsaurrsecmeernitsiecnsdptohiantasrshroeulladtebdetiontkheed v1a0luheed aseesussmeedntdeernivdepaoqiubanynitchsaetimveeexcimahteoafotfpnooxtiiecinttsyiaalnmdetehcetr,ouatendoffeoxrpmoasubraes.isMoeraseuxreeampeanltaieonndpoinhte,
assessment endpoints.
pMoetaesntuiraelmefonrteexnpdoposiunrtestwoerceosnealmecitneadnotn tohfecboansicserofnp.oteTnhteiaalvapirleasbeinlcsey ooffrheceepatpoprsroopnrisaitee, taonvdictihtey
.
sienlfeocrtmeadtiwoenraen wdheitcerhmiisnkedcatlocublaetiroensprcesocnbuievbleasodefdewxapsosu1sraenpiampworsan2tncdonssiedsersamteionnt. Eenndcppooiinnttss
entiied for he site.
iNenxtSies catliosn o2.5fspecific measurementendpoints thatcorespond othe assessment endpaias identified
Measurement endpoints for assessment endpoint:
:
protectionofbenthic invertebrate communides sructure and function
TcoolleevcatleudatreotmhefisvreulcotcrateioannsidnfDunrcytiRounon.ftEhxeisbienngthciocmcmoumnmiutnyicsyz,ucbternetheiacsmeavcarlouiantvederaibeaatcehsowfehree fgirvoeuplso.cations by deeming taxonomic diversicy and rough an evaluation of fnctionl feeding
aSteedciam.enTthweaesnadspooicnoslloefcheedsien tceastcsh woefrehe sufrvvivaarleaansdfogrrotwotxhi. cCoelsltoiangteudsisnegdithmeenatmspahmipploeds, wHerae l31e50 Csiozlel,caiendd aontdalanoarlgyazneidcfcoarrabrogne(aTnaOlCy)t.e lTshte(TcAhLe)mimseadaylsr,esBuNlAs'sw,erPeetshtePnCBcso,reVlOaCtesd, wfiutehriodeb.sesroiend adverse biotic responses inthe toxicity tests in order to determine risk potencal.
Measurement endpoints for assessment endpoint:
protectionofsoil invensbrae commanity srucere and function
"mTeoaedvoawlualotcatthiesonusearntdeteasntde ufsnicngiothnoe efstrhtehwBoernmi,icEsceonmimnfiocyr.asoiiltwoxaiscictoyltleesctst.edTfhreomenedapcohionftsthoef htaersgeetteasntaslwyteerelsstur(vTiAvaLl)amnedalrso,wtBhN.AC'o,llPoecsatvePdCBsso,i sVaOmCpsl,esfwlueorreidae,logrcaoilnlescitze,danndd taontaslizoregdanfiocr carbon (TOC).
Measurement endpoints forassessment endpoint:
pnergoattievceotfiimfopiasnchtcoonmmgunriotwi,esstuorveinvsaulr,eatnhdatrdeiprsocduecxtpiovseusruecc0escs.oniaminanis does not have
z
065.35
USFW 0A14
iFnatDhreyadRumni.nnTohwe,enPdipmoeipnhtasolefstphreosmeeltaesst.s xweirceisyurevsivsalwearnedugsreodwttoh.detCeorlmlionceatheed wtaoxtiecritsyoamfptlheeswwaetreer
algrsaoincosilzlee,ctaenddnodtalanoarlgyazneidccfaorrbaorgne(tTaOnaCl)y.tTelhsetch(eTmAiLst)rymedraelssu,ltsBNwAe'rse,thPeenscuoPrCrBelsa,teVdOwCish, afblsuoerrivdeed,
:
adverse biotic responses in te toxicity tess in order to determine isk potential.
Measurement endpoints for assessment endpoint:
hPraovteecatinoengoaftiwvoerimm-peaxcitnognbigrrdowsttho,ensusruvrievatlh,aat nidngreesptrioodnoucftcivoentsaumcciensas.nt in forage does not
5F5o1ofdeecdhaiinng aacrceua.muTlahteiosenlescttueddiemsewaesrueresemleenctteedntdopoeivnatluraetceerpitsokrtsopeacviieasnisptehceieAsmewrhiiccahnuotibliinz,e tTheurstde
migratorius. Appropriate forage species (earthworms) were identified fo the sbove receptor, and the
dieary exposureof for these, or other
rcloeselcy reelaoptceodntstpaeomciienrsa.nsts
was
quantified
and
compared
to
existing
toxicity
data
Measurement endpoints for assessment endpoint:
hPraovteecatinoengoafticvaemiimvpoarcotusonbigrrdoswttoh,enssuurrveitvhala,t ainndgersetpiroondoufctciovnetasumcicneassn.ts in forage does not
Food chain accumulation studies were selected t evaluat isk to avian species which utilize the site:
jaa5m.acfieeardsiinsg. arAepap.roTphreiasteelefcotreadgemesapescuireesm(esnmtalelnmdpaomimnatlrse)cewpetorresipdeecniiesfiids tfhoer trheed-sbiolveed rheacwekpi,orB,uraenod
-
tdhaeadifeotratrhyeseex,poorsuortehoerfcrleocseepltyorrseloatecdonspteacmiiesn.ants was quantified and compared to existing toxicity
Measurement endpoints for assessment endpoint: Protectionof camivorous mammals to ensure that ingestionof contaminants in forage does
ot have a negative impact on grou, survival,andreproductive success.
Food chain accumulation studies were selected to evaluate risk to mammalian species which utilize the sie and adjacent areas. The elected measurement endpoin receptor species is the red fox, Vulpes dvuilepteasr.y eAxppporsouprreioatfefroercaegpteosrpseciecson(tsmaamlilnamnatmsmwaalss)quwaenriefiieddentified for the above receptors and the
Measurement endpointsforassessment endpoint:
Protectionofpiscivorous mammals to ensure tht ingestionofcontaminants in forage does ot have anegative impact on growth, survival, and reproductive success
-
tFhoeosditcehaanidn aadcjcaucmeunltaatrieaosn. stTuhdeiesselweecrteedsmeelaesctuerdeomeenvtaelnudaptoeirnitskre1c0emptaomrsmpaelciieasnasrpetchieemsiwnhki,chMuusitleilzae
evixspoon.sureAoppfrroepcreipattoersfo0raCgoenstpaemciineasnt(sfiswha)swqeuraeniifdieentdified for the above receptors and the dietary
Measurement endpoints for assessment endpoint:
8
00027
-
USFW 061:
Pnortotheasvieonaonfegoamtniivveoirmopuascmtaomnmgarloswttho,esnusruvrievatlh,atnidngersetpiroondoufctciovneusmuiccneasns.ts in forage does
hFoeodsitcehaainndacacdujamcuelnattiaorneass.rudiTehsewseerleecsteeldecmieedatsoureevmaleunatteenridspkotionmraemcmeaptloiranspescpieecsieiss whheicrhacuctioloinz,e Pirdoenctyiofnieldotofro,r tasheamaobdoevle froercoempinoirvsoraonuds mthaemmdailetiaarny sepxecpioess.ureApopfroFperGieaptIeOrfsora(g0ecsopnectiaemsin(aanht)swwearse quanifed
Measurement endpoints for assessment endpoint:
:
Pnortohtaevienanoefgnasteicvteiviomrpoaucstmoanmgmraolwasht,oseunrsvuirvealt,haatnidngreesptrioodnuocftiovneasmuicnceasnsts in forage does
-
tFhoeodsitcehaainndacacdujamcuelnatdiaorneass.tudTiehsewseerleecsteeldecmteeadstuoreevmaelnutateenrdipsokitnotmraemcmepatloirasnpescpieecsieiss wthheicshhoutritlitzxe
sspherceiwe,s B(lcaarritnwaorbrmesv)icwaeurdea,dend3femdodfeorltfhoeraibnosveectrievcoerpotuosrsmaamndmatlheiadinetsapreyciecxsp.osAuprperoofprriescteeptfoorrssgteo
contaminants was quantified.
Measurement endpoints for assessment endpoint:
Protencothiavoenaonfehgeartbiivveiormopuasctmoanmmgarloswtfho,esnusruvrievatlh,atainndgersetpiroondoufccciovneusuumcicneasnsts in forage does
tFhoeosditcehaanind aadcjcaucmeunltaatrieoansstTuhdieessewleecrteesdelmeecatseudrteomeenvtaleundaptoiinstkrteocempatmormaslpeicainessspetchieesmwehaidcohwulvoilzee, (Mviecgreottautsipoenn)nswyaisvaniidceunsti,fi1e5dafmoordtehefoarhbeorvbeivroercoeupstmorasmmaanldiatnhe sdpieectiaersy. eApxpproospurrieatoefforreacgeeptsoprescie1s8 contaminants was quantified.
29 Life HistonyExposure Profile Information
seRxeepcloespeetcdofrtooscpeoevncaitleausmaitwnieaornnetisnsbeteliecscatuiesdke foarfsoesmpsescsmieefvinecrta.blehTmahovepioharivsc,allpaeavbreiellsr.nyos foOfhragpaparnboipasrmiaustseew,hsoiofcxhfceiweydeirinengfohlirakbmeialttysioownearbnee siwpnhevicecirethsebsrrieasltkeecrtceeacdelpcftuoolrratthsiieoslnesicstckeoaduslfsdoersbtshemisebnaatssaseerdses:wmemansetaaidslosthow avenoalri,tmhspwohorortrmat,nttiTlhcseonhtsreierdwee,rsarrtiaiacolcno.voenr,gTmbhirenaktt,eramenceedsptrtaeoldr hfoax.wk.ThTeheavaiqaunarteiccepvteorrcespbercaitesrescleeptcoerdsfpoerctiheiss froirskthaisssiessksmaesnsteasrsem:enAtmiesrtihceafnatrhoebaidn mainndnroewd.-aiTlheed aquatic inveriebrate receptor is. xteca.
29.1 Theamphipod (Hyallela cecaa) RepresenotfaBteintvhiec Inversebraes
cHosnatlalcetlawiatzhtesceadiwmaesntfsoelrecatseidgnaisfirceapnrtespeonrtiaotinovefotfhebierntlhifieccyicnlvee,reubbriaqtueistdouusedtiosttrhiebiutdiiornecitn aquatic systems, imporance 2a food tem for aquaic-invertebrate consumers, and eas of
009.35
USFW nR1A
usseediinmelnatboartatthoeryDtroyxiRcuitny Cevraeleukatsiioens.. These species are also likely to occur in the surface
-
LifeHistory(Fvallelo greed)
Trihveerastmhprhoiupgohdo,uHtyNalolretlhaacnd StouitshecAommcemroicnaal.yIfnopurnedfeirnrreedshhabwiattaet,latkheesy, sareeakmnso,wpnontdosr.eaancdh daenndsidtiitecshiens,exbcuetsgseonfer1al0l0y0inpelroswqeuranruemmbeetresr.(TU.hSe.yEmPaAy 1a9l9s4o),be foundinsloughs, marshes.
THhvealylteylpaiceatlelycabsurreoewpiinbteonsthuircfadceewisteidviomreenstt,haantdfeaevdoiodnbciogahrtselipghatn.iuBlecaatuesoergoafnthieci mafteeerdiianlg.
aFnrdesbhewhaatveirorsaeldichmaernatcst.erisAtviocsi,datnhceye
are of
ilidgehatl
bteystmoorvgeanmiesnmts
finotrototxhiecosleodgiimceanltevkaeleupastitohneosef
organisms almost constantlyin contact with sediment contaminants (US. EPA 1993).
`Rgraethoppodrs thoitntadrheispucrreuscsuamctaebalniyiussoseedxfnuoalh.oMladliensgatheelfaermgaelrtehdaunrifnegmsamlpesleaxnudshaanvde
larger ont copulation.
`SDeuprairnagteasmtpelmepxoursa,ritlhyemwahlileeatnhde ffeemmaallee fgeoeedsttohgrefaoomtruoalhpgteiernhigordpoerfioudp. tIomomneediwaeteekl.y Tahfeteptahier
-
mthaek,tfehmealtew'osremjaoirnsuapniducmo.pulaTthieon fbeegmianlse.Dsuwreienpgs ctohepuspleamtthiienomtoanl,heerrelmeaarssesusppieurm.mneaanrd
.
spliamcuel.aneTohueslayvreerlaegaesebsreogogdsfsirzoemohrerfeomvaildeucyta,ilnltoltaheazmtaercsaupisiu1m8,wcghgesrpeefretblrzoaotd.iobnutatkhei.s
umbcaenvarry with environmental conditions and physiological sress (U.S. EPA 1994).
uDnedveerlgoopiensgaesmebcroynodsmaolntd. haAttchtheadtytoiumne,gatrheekjeupvetniilnesiHdyeatlhleelfaemaatleec'sa maraersreulpeiausmeduinnitlo sthhee Sounreroburnodoidngduernivnigroenvmeernyt.tenUnddaeyrtfismveorpaebrlieodco(nUd.iSt.ioEnsP,Aea1c9h94f)e.male produces approximately
fFivesytageaastealrceajhulavevneiealemsiltnagiemsa;uminsotaf9rs i6nsaanrds,7wiftohrm t1h0e8apdroel-ersecpernotdsutcatgievse; satnadgesst.agTehse8 fairnsdt higherare considered adult (fully reproductive) sages(U.S. EPA 1994).
Expowre ProfileforHvallelaGteca `rSoiuntceeodfierxecptoscounrteacftorwiHtahlclolnataamziineactaedinstehdisimreinskt aisnstehsesmteonxtic,itthyeerveasluualtsoiofnthis ttheestpWriilmlarbye used to indicate exposure.
292 Earthworm (Eiseniafoerda) as RepresenoftTaertreistvrieal Invertebrates .
Ehaabrittsh,woubrimqsuiwteorues sdiesltercitbeudtiaonrtehprroeusgehntoauttimveaonfythearmbeisttartisalanidnvseoritlecbornadtietsiodnuse, taondtheiimrpfoersadnicneg imiincprrofolvoirdai,nganad fmoiocrdobfaasuenaf.orcommabniynesdmawlilt-h tdiormecetdciounmt-ascitzweidthprtheedastuorrrso.unAdidnigetsaoifl eprietsuenst,s 2 potential link benveen soil contaminants aad soil-inveriebrate consumers. In addition.
0
009.09
USFW 06
exhwarms wer observed in both the waoded ind open field ares ofhe Dry Run Creek
Life History
Empliaacrnrthofwlliaonrreram.sndNfeemxeidtcortnoofdfaeouanoad,.atThnidhredemecopasrytiiminagmrpypolsraoanrtnetasardeofqaufnioiromedamierndetemsaadionpslsannkderoanmftartees,tlrveei:sngwpaseirl crinoonsusiegrlhvawttiithohnbvomederycyhwcaaonalirsswemhsitecaxhrteumrpueo,sotirlbyesodKielesvpetwlimotpoheidhs:i.grheEslpaaiyravtcioeonntsdeenpwexendFgseegnoonenadsloifyffusishigeohennoefnofgtaamsles.s and in sil wit api of es h4(nLec 1985).
.
Emocaacrnudyrhwwsoiprehcmaisuetsaarcalhneiarllmaoip,phrrooovddauircdiecsa,cnoodcvoimodonussetsp,saparehnceidnesoogresenpbercyoidctuahcleey.bvyiscSareosxs,su.ablfurteipmlraiozedtuoircoginao,nnsskwchoeomunegothu
aeinsmedanLdtaoelf.,y w1Te9lh7le.7g,proopwunlaitimomnatorfean(sedaorltehcweonrtm, Aspreceie,s iatndanseyneosnceenitmdeiicdounnsilos (ofwayoruensg
edEeassniihsccwadoterismoinsacnhaadtvoaenmsbaeivneedrnattlemcwpoaelyrdsaatonufsdruehreevaixtv.eimnIegn seadrmveusrcoshefpmeonopvruielraoetnaimseoilnnytsatulhrvacinovnamld,aiitoneescisonccohhovni1sduscsoaisln.. Worms may also migrate to deeper silo undergo satesofinaciviey unl nvisonmenta
conditions become favorable once again (Edwards and Lofty 1977).
JpSoroeolmiidefae,rsaptpeeocdsisfeesrsosomafthwroaodrwumilstngngurzmoobnweertlohofcraostueegdghjmoseuttntitsnhuferproonnltiovhfeastthcbheyianngcusoa.nntidOnuinaneclrsleyasspaeedcdiiinenss,giuescewghimatehnotust. ainpcprreoaxsiinmgatteelynu4.5mybeearrsoufnsdeegrmelnatbso.ratTohryeclonfdistpiaonnso(fEEdiwsaerndiasfaondrdLsafwyas19r7e0p)o,ried 1 oe
Exnosure Profile.
D(r0iisrekevcaatslscueaostnsemtearncits.wkitStouhrtvchioenvstaealmoinrngdaantgiersdomsswi.elhTei inshdsepuoepirrnesisicfdoyulelrooawuniatnlegyofseiesxxpwoipsluaar1setof1obsrecasorlntsdhuwwcoitrlemdsboeinnvtitheoides Worms to determine exposur to higher ophic level organisms. 293 Fathead Minnow (Pimephlespramela) ss Representatiovfe Fish Community
Alustification
cTaqahumeaptofisacithdseyaasndt,emmisir,nentiomwcopnwotaarscatsnewlic2ete5chtew8dao2eordrteehprrmoeusgfehomorauttsihtveeeoftfoiemnngciyvcclooenr,sousumbseurfisi,tshoaudnsudedessoesietosouftadiioeetnariny laboratory tock evaluations
Life History
~
a
069.7. 5
USFW nae
. :
-
"vTahreiefraytohfeahdabmitiastsnsowu,c.h5prsommaelllss,caisnwsi,deploynddsi,sgainodutsedllin Nlaokrest.h AImtesriucnacaonmdmoisnfoounadbsiennat ainndselaowmsooxfygmeondecronacteentarnadtiiognhs (grUa.dSi.enEsP.AI1s98t5o).lerant ofhigh temperature, high urbidiy,
aTahceplfaatnhceoand,miAndunlotws fieperdiomnarialqyuotmiaiivnosreocutss,.woYromusn,gstmyaplilcaelulsyafeceedaonsn,daendnsot,hearlagna,imaaln,d Ths species is considered an imporaant food sourcefo oher fish and birds (U.S. EPA 1985).
SAduumlmtera.heTahdemmiinnniomwusmspsapwanwniintghetsepmrpiengraaundecsopnpteianruse o1 sbepaawpnptrhorxoiumgahioeuyt m16asCt. ofTthhee aovsahrieeesgogfsthmeatfuermea.leTshceoanvteirnageegngsumibn elrl osfeaggegssofpdeervseplaowpnmepnetr,fenmdalethiesy1s00p1a0wn15r0e.peLaatregdelry afveemraalgeesambaouytlsaxy 4da0y0s.toI5n0w0acrgmgswapeterswpiatwhn.an Haamtpclheinfgootdimsuepspdley,pesnpdawonnintegmmpearyatoucrceuran3ds ucarrilnygastthheesfecsonydeayre.ar.IncSouorlveirvawlaotetrhweitthhir3dmyoedaeriratreelfaotoivdelsyupupnlyc,osmpmaownni(nUgS.usEuaPlAy o1c9c8u5r)s.
ExonsProfle
oSfienxcpeodsiurreecfcoonfaachewaidthmcionnntoawmsiniantehdiswartisekr aisnsheesmteonitc,ihyeevraelsuualtsioofnthsethteetprwiimlalzbyeruosueted
to indicate exposure.
:
29.4 American Robin (Turdus migratorius) 1s Represenativeof Worm-cating Birds
sification
bTehceauAsmeeroifcaisn urboibqiunitwoauss sdeilsewcrtbeudraisonreapnrdesdeineaatyivcoofmpoomsniiivoonr.ousThaendprceafmeirveanrceoufsobi5r0dis cnavmeirveobrrotuessreince6psioormniivhoirsourisskdiaestsaelslsomwesnth.isTshpiescisepsectioebseiusaeldsoiskoetlh taonoocmcnuirvaotrothuesDarnyd Run Creek sic.
LifeHisory
`"TChaenaAdmae,rwiicnatenrrionbginin(tThuersdoaustmhiegmraarlofisof)tohcecuUrSs.voMuegxihcoou,tamnodsCeonfttahle cAmoetriincean.alGiUvSe.natnhde tiinmcerse.aseHaibniotpaetnrehqabuiitraetmeanntdslfaowrnsb,retehdeirnogbrno'sbibnreiendcilnugderaacncgeeshsatsoefxrpesahndweadteirn, tphreotreeccteendt nfeorsetsitns,g ssewsa,mpnsd, oppreonduwcotoidvleafnodrsa,gianngdaortehase.r oTpheenseesrse.quiNeomne.nbteseairnegcormomboinnslaycmceutpyinsimmoiilsatr habitats altough proximiy o rit bearing wees is of more imporance
"vTeheliprnigmairnyvfeorrcabgritnge,taecihhnoiuqguheftoheyrocboimnmsoinltyhsoepacahloonrg hseecgsroaunndd finutseianceheofbgrraonucnhde-s Sa5omweellf.uiT,hbeurtofbiun'siditehetpdruirmianrgyhfeoobdrceodnisnugmesdeaosuotnsicdoensoiftsthsembarieneldyinogfsienxvseonr.tebArastersabainnds ewexihgihbtitainlroiwcdiogemsetievtetehfefiircmieecnacybofloircfnuele,dsth(eUySo.feEnPAco1n9s9u5m).e mare than their own body
2
069.11
USFW 0619
Btreemeodriensg dtuerriinogritees bwreeceisntagbsliesshesd;bwyemvalee,rodbeinn.siMioessoffroroabgisngweochciugrhs icnlasgivteontahrsee oOrusiifdfeooofdtrhesoburreceedsinagrepleirmiiote,d.roabdiulntyrpoibailnywirlalmav1e thoeeumpmoerfaorrsagionrgssgveesnedwreoro
within |to 3 kilometers (km)ofthese areas (U.S. EPA 1993).
ExposureProfile
AT(eUdrSur.littEoPArAmy.esra1i9ec9s5a)nv. arTyohbfeirnloomware0es3trre0po1eraecdrpeb,tooWdoiwylewhiegrfihogrhfaetgr(ion7mdg.7h37o.gm3 eatnoadn1gt3he5es.8sragplo(erUseSd.rpeEPpA.o21h9s9o3ms).e ange of (0.3 sere) wer assumed for tis isk ssssmene. ABAmfeWoroidicaiarnecgrreosbpaiionorncyearndabtfeo ofetx0hpi.esc9stpeetdc0it1o.5c(2UoSn/,sguEmBePWAi11d17a9.9y53)ag./nddAaysasowfufamotionegdin3ng7eds.t5i1o0bn8otgdeyowaofefiw0g.y14ahgrag0 "(Tch3e.d.iectaorfwtohermAsm,ersniacilas,robbienecosnsicsttespoiflsaensss,osnplildyerv)ianbdleFpirtop(o5rd.ondsoopfainvte,ridbreamt,s sSaunmduacm7,mphaeanreccdkerbneatrl,rlif,etrsei, driainsaptrbheyerrcisoepmsrp)ion(sgUi.(iSno.ensEriPnAgesp1e9a9os3o,rnt)oEthcr1hl0eai.nc9dgh3eept9 Eeoralc.en1t988pu)e.rtcenDatunrvdiengrpseoprrcniennagt, piencvceretnetbrFautets1i0ndf3al (pmeircgernstoriynvseetrscobna).isT(hUeSs,uEmPmAe.r1d9e53c)a.yFporrophoertipounrpiosreespofoirseadsi6k3 Tscssment. adie of 100% ertormswillbe asumed. AHWoonwoecdvicedorce,kna3wlilssliolbeiinungsgeeessdttii1osonn3arseiuefbosoiftth1ee0A.i4mngeperesritciceoanntoaboeifnftoceroutdlhdieenAomrseebpreairfceoadunffdooribntth(heeBeAtpmeeerraitrcaa,.n A15m9e4r)i.canAsrsobuimninig1222fogo/ddayi,ngestion ate of 117.5 g/day, th soi ingestion re for he 295 Red.uiled Hawk (Bueojamaciens) as ReprsentivofCarmivorous Birt,
lustification
TcCohrmeepsrosseictd.iiolndsedhaeatwvkaellwosawhssusnfdoarenttheldeisvssaebluuetacptirioeotnsn,eonefaanciddovneltiakomeilfainhacotaoidmoinovfoioncrsociuuesrseboinrscd.eduIentdheittsDirdoyineRtahurey dcoosnceentozatthionreodfctoinlteadmihnaawnktswhfiucnhdalilnoswmsalflormtahmemvaallainsisuoenwoiflcolsncparmonvitdse sinn heeufrooed
LifeHistory
R15e7d7)a.leThdehisawhkasbisaeithheimghlty vcaoimamblo,nabuntdhweiyderserecsodmmAomnelriycfaonuBndurnew(oBoudledsnadreFaasrreasned oCfpoGerneS.la1nA9d8n.7)a.TahpeThyoirslsnsipeticeniheasFbeiidtesprlv,aeihnnse., hpeorGwieciveeegrdr,ovfaeosw,mkatduRnudGresae,RrasnominraahrpeeeriwncehsxtsoeernnosniUvtneietuewndibnrSgoikrfeeonsr
5 000.55
1I]FW NAR2N
-.
wfoeoldienrg sspescuicehs),a tsempailllesm,aimnmseacltss, (aen5d.ocmciacsei,oncahlilpym,upnrkesy,srpaebcbiie)s,thbaidarse (0us0uahlelayvgyrotuonldfs offhe ground (Burton 1999).
2Thpeerberneeadnidnngessecabsuonidianrgswbyitbhotshersieaxlecso.urNsehsitps dairsepplalyasc,ecdoimn mtaollnleysfsohlilgohwreobycdkmlaetdigensg,oonr {aoltl ecaeeegags asnr codfteanorureftubreybibsodhtehd asenxensaunadfaolrltyfosreinacpopnrsoexciumtaitveelyyea3r0sd.aysI.ncuTbhaetiyoonuonfgwarae Babulronf1e9e8d9t)hemselacv4etso weeks and fledgien about 45 days (Bul and Farrand 1977;
ExcosreProfile
FAdeupletcimvaelley(DaenGdrafaefmaalnedrReudd-iusil1e9d83h;aUw.kSs. EaPreAr1e9p9o3)r.iedHotomeweriagnhges9v60ayfraonmd 114.82.3256 1g6.
395.36 acres (Kirkwood 1980). Smales reporied home rangeof
1T48h.e2l6aowceesstwreerpeoarsesdubmoeddyfowretihgihst
roifsk0a.s9e6s0smkegnta.nd
the
"iTmhpeodriaenocfeawrietdhasielsesdonhaawnkdcaovnasiilsatbsiolftyma(mU.mSa.lsE,PAb.ir1d9s95r)e.pilFeo,rnthde ipnusrepctossewshiocfhtivasryisikn faastseessasrmeenrt,etpheohratotwkreawndgie.llbferoams1s3u6me0d.040c0ogn/sduamye(K1i0r0k%wosomadll19m8a0)m.mTalhse. hiFgohoesdtirnegpeosrtiieodn oofopdpironximgateelasty0i.of0o5490n0g/gg/dBaWyiwdaasyahsassubmeedefnoetshtiismartisekdfaosrstehsismsenstp.eciAeswa(tUe.rS.inEgPesAtio1n99a5t). rTeopoerxtperdesbsodtyhswveiaglhutionfun5i6t0so1fgy/idealyd, thweawtaritnegeisntigoneastrtaotiefwo$a6ns.6m4ultidpalyie(d3b6.y64thmeLUldoawye)s.t
nAesoaimloiungnetstoifonsoriaeprfeodricttheedrteodb-ealeendtrhaaiwnekdicnotulhd ndoitgebsetifvoeuandctinofthaewlhiitetr.atfuoroettehdermeofoursee, hwaass bueenstorceapelocruledadte(Btehyiservaltues.l. A1s9o9i4l)infgoersttihoenwrhaiteceo-ffloesotedthmaonu2sep, erFrcooemftnthhteisovtalaued,it3 Tcooontseedrvmaotuisvee.soTloienxgpersetsisontirsatvaolfue19inpuenrictesnotfogftahy,ttohle sdiieltiwnagsestaisosnumaetdfoof 1t9hepewrhcietnet w1a9s9m3lt)oipyliiedeblsyodtleinfgoeosdtiionngeasttioon frte0.0o9fgt/hdeayw.hiTth.ifsoovtaelduemwoaussaes(s4u.m50edg/tdoayr)ep(rU.eSs.entEPthAe Caomnosutnatntoofvesroiltiemen.aiTnoedexpinretshse 0d.i0g9estiivneuTniatcsk ofogfrtahemswhoiftes-ifloopreerd gmroaumosfemtohautsreembaoidnys emioguhste,(tMheirsrvial1u9e8w7s)tdaivyiideelddbyvatlhueloofw0e.s0:0r7epgo/rgteBdWo.dyThwiesigvhatlu(e1 wag)sotfhtehnemwuhltiiep-lfioeodtbeyd he food ingesrtteiofothne red-aled hawk (400 g/day) 0 yield soil ingestion rate of2.3 way 296 Red Fox (Vulpes vulpes1)s Representative ofCamivorous Mammals
Justification.
cTohmepocseidtfiooxnwraelsatsievleeactbeudndaasntredpriessrebnucattiiov,e aonfd lickaemliivhooordouosfmoaccmumrarelncdeueatttoheisDrdyieRtaurny cCreoeknsitce. elsonfdcimoenattlalmioiwnsoafnnotstfeouenvadluinatsimoanlolfmacomnmtaamlintaitsisouenwiinllsiiesosoiplsr.oviIndead3diaicocnu.ratthee
3
009.015
USFW 062
dose to the red fox which allowsfoth evaluation ofcontaminants in the food source.
Life Hisory
lRaekde bfoorxdienrhsa,baintdopfeanmlmaenaddso(wHso,fEdmieticshibcarn1k9s8,9f;iJelodneasndawndooBdiemdegyes1,988f;enMceerrroiwts,19s87e)a. mWiatnhd tghreouenxdce(pStcihownaorfzatnhedbSrcehedwianrgzs1e9a8s1o)n.,Ardeedn{,ouxsuhaalvley nmoodipfeiremdanreontmhaonmeexibsuitngsiweocopdcohnutchke oDravfiosx d19e7n4).is dTuhgesdeursicnegntth-emabrrkeeeddidnegnssehaasvone maunldteixpcleeprtoioomnasl,leyncgoalndcewsin,taernsd(wBaairlbolueradainndg 1m0al2ensdafnrdofmemhaulnetsinwgillardeeafsen(dScthhwiasrseczenntd-mSacrkhewdahrucnzt1i9n8g1)t.eriInorayddriotimoninogutdheerirs (deJnosn,esbaontdh Bimey 1988).
-
o"Tphoesrseudmsf,oxmusspkrriamta,rislkyuannkso,pproordaeunnti,sibicrdcsa,miegvgosr,e,cacroinosn,umnivnegrefboordaeist,emssnaskuecsh,aasnrdabfbriosg,s
(alBsaorbcoounrsaunmdeDdawvhien19i7n4;seMaesornc(J1o9n8e7s).anSdoBmiernveeyge1t9a8b8l)e. maDtuerrinsgucthiamesoffiasbaunnddannuttsfoaorde
(suSpcphlwya,rtzheanrdedScfohxwawrizl 1b9u8r1y).surplus food to retum to for consumption at a later time
`bMeaalreoannedlfienemrapleerfyoexaerspauisrufaollrylibfeer,wreeemnaiMnairncgthoagnetdhAeprrfirlo(memridiwin1t9e87r)t.o sGuemsmteiro.nFpeemrailoedss "aTshtefpruopmsaabroeuwte4a9netod3a6t adabyso,uw6t0itdhamyos,stleaavveertahgeindgen53indtahyess(uSuchmw,arazndanardeSscehxwuaalrleyzm1a9n8u1r)e. bhyawtkhseainfdrsotwwlisn,taernd(pMoesrsirbily1c9o8y7o)t.eNsat(uMrearlrpirted1a9t8o7r;sSocfhtwhaerrcez afnodxSacrehwfaewrzbu1t98i1n)c.luRdeedlafrogxe may live from six to en years in the wild (Schwarz and Schwarz 1981). ExpoureProfle HAdoumlterraendgfeosxvawreiygfhrformo2m425.70to1,723k5ga(cBraesrb(oMurearnid 1D9a8v7i)s 1974; Jones and Bimey 1989). T1h0e.1fo6odg/igngBeWstiidoanyrfatoers oafjtuhveernfeiloe x(U.Sr.angEePfAro1m9905.).069Tgh/egwBWeirdaiynfgoesrtaioonnrbarteeefdoinagnaadduullt.t ethdesefovrailsueesstiinmautneidsotofbge/daapy,prtohxeihmigahteesltyre0.p0o8r6ige/dgfBoWoiddiangyes(tU.iSo.n rEatPeAo1f9930.)16.g/TgoBeWx/pdraeys.s banoddythweeiwgahtetroifnge27sikogn(r2t.e7o0f0 0g.)0t8o6yige/lgd BaWfiodoadyiwngeersetimounltriapelioefd 4b3y2thge/dlaoyweasntdre3pwoartteerd oinfge1s0t0io%nsrmataellofm2a3m2.m2algsawyil(2b52e.a2smsUudmaedy.).Forthe purposes oftis risk assessment, 3 diet tAhesorieldinfogxe.stTiooneaxtpreofss2.thispevracleunetionfutnhiesotafalgiddiaey,htahsebseoelnirnegpeosrttieodn (rBteeyoerfeta2.8l.per1c9e9n4t)wfaosr maliplied by the food ingestion ate of432 g/day to yield a soi ingestion race of 12.1 gay. 29.7 Mink (Mustela vison) as RepresentativeofCamivorous Mammals ustification
3
005.14
USFW 0622
. .
CThoempmoinikonwaeslsalseudnasirnerbesuetnaitoivne,of1 ckamihvearousofmoacmcmuarelncdeu 1hefsDdyieRaurny GCeoonvSceon:onuioTmneionifktcwoiomcwuhmsailnolttowstsefforvunihdletCe iohnofv ncodonfaocma nionsauinoen naw3inl asssisp.rooovIidndssacnoisoune,chue
LifeHistory
MU1n5ii8tk8e.daTrShadetyeiscaasnnbdte ifnoovoueenrdmwiuectihm1o0afolCrayelsfsoymNaia,bsNaAewmneMierxniicsoo,opauncdtaThneds:vsswu(gaahnsoeusits2h,deicBainyescrry nroerccoamimarnytyaGofundexn ends ipoemsidn daoyn(sHondfBmiemseey 11998889)). AFoughpmAT roruml HDneeesnmsciaanrkersKtheeatlyhamnneeoarnnswadtaecrBc,apamineddh1bey9y0e.ameiMssala(eBlee3nsdls1oy0lnddmDu1asvnssi1b9or74wo)snboHuormrcoeowsrnahnsigiecshdernbedy tmobeeinesosesncemtkeoevsyfslproawyingsh(orOeldinee(l1o9n8g)s,andBimey 198). Mink ar sfiry iSesasomnasyocodonasvofaciralylagho,eosgh,efdhi,easraykceosm,prroideinotns,(aBabcbio,ur1snnddpDlaavniss 1a9m74o).n Taboecr aBfifmmstesJso1u9e8ms8;eanMieeBraiamn19y8179)8r;eSgiocnshofroardt SAcmhewriaan(1B98a.buCr3anydfiDsahvaiss1a9j81rJopnoeriaonnd BBroemdi4n0g40oc7c3urGsayfso(miJrainusar1y9087cSacyhAwpael nwtdhSgclayrsva15i813l. gAesNtigohntpvearriioadbslaegSinngg Hvaoye aamfon11g1e7iyonusng(mBaayyboeuraondcDeedis(1S97a4rFoafnidmSecsra1r981,98f1o.nsAvnedragBeunitnyet1s98s8: Nofaigers1n9d8s7,eSschnwalrzmanarSecbhyweanrm19o81r).c (YoMuengear1e98w7e;aSneedkasrhaonudiSvh0asr w19e8e1k).s c15e8a7:iSomnelayrrsaandhaSmeedaorwt90{1x.eAckohavuegshboomsesd, 1indudosgshwvilepvreeydonupi1k8(eMeur. ek sido eed wa yer of 35 nh wild Sewer and Sevan 1381)
EffectsProfile
dfruoml1m91ink 1w5ei0g0hs5ems (2005.10E1F.7A30199(9)Mer 1987 US. EPA 1995). Home ranges vary Afeymaelaetmouin(fUo5.d gEePsAti1o9n9a5.e Tofo0c.a2pisg BiWsdaalyehaisn bunnssoifmgante,dtferobood nmaelseiaonnd Fre1e1w4aguiy.lAen smelowwistFienpgreesidonboidey woeifgh.t11(5530B8W1c0ay11w4a4s feopdarrgdsfioornGarte Tteaswaesmmaii(lU1ebEPhAe1o99w3e:sTpo aaprresbdosdvwalee ifnS3oi0f5g5sa0.5143 wwaatss minfgeistoionn oenawril3l73 sgiunme(,5 mUiog. For hepurposes oftis rik ssss6m1aofn10,0%
%
009.015
USFW 062
2orAe5ndFinmccipierdd1eeyinbneacelimtdhse(enpad1rliimi)emnngawterasysiimnoegnecehsditaifeoonrorrhsitseeiwsdaksisoemtshseasmvmneaantlytbblCeeoeFnrvosmuntmheoironaorfep;peehserrneonsn, deersaetriveodnnoefxt.he rice level noifsimncbidyewnthailcshedmiimnekntmainygecstiiondvisecoinsnumgeperoenrme
GamLoinofnguesenebatiitnoisfsvsaeiezdesiinmfpferonorptmmar4c1io0oof0nm isf1o02b3ta e0hie mnbly mguss(iAlbl(ygLeeiprsomk1i9sv7ims5accShomrinotcshhiu1rm9u8sp%)).owfoasIhnus:eeApditnegsprwpedeiucttsse
abodlylsiizeeoobfde10103.m11m 1582)
in secinsghki based on
tawhseasslesopmrweeincnitcgtehdle.gaoTrmoietohwoerfiuesgehidtninometefn+ntg1ci0n0ntomwavarSehehinces
.
logWeight(5) = -5.374 + 3316 log Length (mm)
c({1oKSmo1elanhtlmoalfifhdno.eoevdnAiuiS1ns9ug7es0as)nyt.divoTsnahelidrsiutmeipennorgtf to1h.e7v5sapiprmeeraddccieehncttcseBodWnmieandksaeyofhaa1s53tobfebe0een.5gr3iploorrfedfeoofpdoropohasrefalgapcegisl
si3ycsaotnnesme.brevaptrievediacsesudmhptaiotn shmaodf e0tibsaesr9i.z.6eppmearecyencrtooocffmthaehee0nto.oo0tld35iinosgfess(teKecdoiilmeeenrsnmaaicnsco19rs7m0p:S .
ipiFnorsureneitdtihisevocpfsugsyrrhspatobmesomsedoofoysfswieesishgdhmrtoed(m1ea8l.i,1n5)icewoaxnspsatrsseouvmserdstiehmdaei.tmteThnhetieesvvieallnuoefes(e0di0ni3m(5e)nwtdaicsgopnetsatigsnepd yeinort.she oa8fskefidsih(m1ie1sn40.dd2sadbryo)d.ythweeipghrtc,iicWmephdeeesngnerdtaitimmseonfvtfailiusnehgebissotmiyonweaiieghftlo.byTtihthihsmprfkoovoidrdioednugga ehantcosoormormneprsrs
298 Raccoon (Procyon tora) Represenaive ofOmnivorous Mammals Lugtificaion.
{SoThehmeeepkcosorsnaciseinaoinnLasiweodaanitstoifvaselelleoacwbtsuenfddo1ranttheepderivseawsliueoanutaiioionnv,eofaocnodf3naiamkmiennliabvtooiorodonouisf movcaecmumsraeelnmcedenus. too1efssprdyeipeogiy accurae dose thecroancacmooinnawnhsicfh aolliouwsfnofroardgteheTehvailsusauteio3nndofccamosntwimlliannsrronayuo)
Life History `0RR5eaa8ctc5ccnoodaoosnnn,dssianpardmreefsiealmrneadm.uaiarusmth-cessihz(aeKdbaauo,fmmnpiaavnroir1ce9u8sl2)aa.rnydRhaaacrcreodowanbosuondadvsawentaamtpihsr,aodufsglphonooeductpwlNaeilonsph. ferAamempreirecsa.
Raccoons el heavily on surface waters for forging staes ee 57
600.15 HeEW nao
:
a
o1f5d43)rbiu wnwaitlkerk(ieSrtnutehgire1a94c3)t,iRvaicctooonosppaorruanctiisviecparlilmyarfileyedroonm wduhsaktetvoedrawisn (aSvatiuleawbeer r(Seadnadyer1s0on(a1k9e87a)d.vaFnotaegxeamopflfee,edriancgcooopnpsorsvuinnitgineesadruarsianlgt mlaorwsthidmea(yvbeeyc1o9m4e8)c. iRvacdcuoroinnsg FTeoewdleprri1m97a5r).iolny fuk, nuts, acorns, rans, insects, frogs, crayfish,and gg (Palmer 3nd `RAadcucltoornacsciootnhsessroeustoherrmnalrleygsioanlsiaofrtyhbeuUnwiiltledcSoamteestoagreetahcetrifvoersyheoarropuernido(dsGoolfidmman d1u9r50i)n,g maatyinmgat(eKawiutfhmasenve1r9a8l2f).emMaalteisndguorcicnugresscrhosmesMsaorc(hSatndJerusnonin1s9o8u7t;hKearnufrmeaans a1n982)c.acYhomuanlge Saulmemsera,rewnhoilremaflemyanloetssmeaxtuuarlelyimatthuerfeiitnyteheai(sStanbdreeerdsionng1s9e5a1s).on but mature hte in the "sTehaesoHno(mSeanrdaenrgseono1f9a87)r.accHooomnederpaengnedssaoenttyhpeicaanlliymaalfsewahgu,ndhraebdith,ecfaorosd (rneas)oubructesa,ngaensd s3oladregepeand3fsreowngtlhyoaunsatnhdehaamohuanvteobfereensoruprocreiseidn(tSheanrdeear.soNnum19b8e7)r.s oPofpul0.1a0t.i0o.n2daennismiaelss per ha are common (Hoffman and Gotschang 1977). HRaavcecoionncsreraseefdoruenadlneyar(Seavnrdyesaaqunat1i9c87h)a.biItn.AlDaubraimnag,tahdullatstma0leyaeacsersacscowoenipgohpeudlatuipons (8.o8hkniiloognra1m97s0()k.g)A(dmueltanra4c.c3o1onksg)wwehiigleh badeuolwtefeenma2lenscdan1w2ekigg(hNuopwak5.199K9(k1m),e3andnc5o.n6s7ukmge) 0.5kg offoodperday (Newell tal. 1987). uRnadccFooownlsefree1d97p5)r. IinmaMarorynylrainsd,fuorte,staecdobronso, mgrailnasn,d,nhseecds,eafrogssc,ocmrpayefsiisih,onegogfsr(aPcaclomoenrs Burlinagcthkesbue(m1mreprrericweaensts)p,rcinrcaiylfyims(ah8deprucpenodfs).ecsntaisls(3(9 ppeerrcceennt)),, hwielrdpcehser(3yp(e1r7cepnedr)c,enfti)s,h p(2okpeerbceernrty),(rLoldeewntesly2n paenrdceUn)b,ecrom195(21).percAetn)W,asahnidnrgatcoenmstoatue ntidoefSwamtielraaxr,eaacroamcscoaonnds C&irsupslascyeed,tshe hfolarlnowdiicnagbmdsie(pa2rypceormcpeos)i,tifohn:(m9oplrlcuesncs,),mmuasrsienles wnodrmosys(t2e0r p(e4r4cepnets)c,eann)d, Echiurida worms (1 percent) Tyson 1950). sTehaesohno(mSeanrdaenrgseono1fa987r)a.ccHooomnederpaenngdess aornetphiecaanlilmyala'sfeawgeh,unhdarbeida,hecftoaordesrebsuoturrcaensg,esan5d. aladruglet 8m5a3lfeewratchcoouosnanfdouhnedcianecsoahsatvael bGeeeonrgripaorriaecdco(oSnasndiesraspopnro19x8i7m)a.teTlhye65hohmae(r=an1g8eSfEo)r ("Lhoitlzeeth1e97h9)o,mePoapnuglaetioorn ddeunslitfieesmaallessoidnetpheendsasmoenagrlayiosnatphperoaxmiomuantteloyf3r9eshoaurGces1i6nStEh)e area. Nambers of 0.190. anipmeahelcasreis common (Hoffman and Gorschang 1977).
Essosure Profle Fgo/rdatyh,e p3unrdpo3sedsitofotfh8is0 rpiesrkceanstsefsosrmaegnet,fi3shbaonddy2w0eipgehrtcoefnt2clkagm,saweirnegesstuimoendr.ae oA fsoi0l.5 Minagelsitipolnyrittenhgofnge.6spieornceanteobftyh9e.4pdietehsrbyeieeclndsreespeondriemdetontrirnagcecsotoionnsa(Beeyer e0t.a0l4.7 kg19/9d1a)y..
38
009...
USFW 062:
eAqudaatiliyonwadetreivIendgebstyioCnalrdaeer0an.d1B8raLuine(r1p98e3)d,yA(dLiaeyo)fw1a0s05e4 l5hewcaluaseineg amnearloe 295 Sharniled Sheew (Baring brvicauds) 3 Represeataiv ofInsecivorous Mammals
Lusifiaion
plTflishkaeednlissiehaahosrowyodecolafololmacpcssuihirnrisreeoecwnnts,wc,aersteahsleeyitlhveteceetnDesdrdhytuaonsRdfruaaennvpotrCredrsieesenckciabsttuieiv.oofniAinlnstehbcoottuihgvhmorotothuiesramdnaidmesdmayale s bsecoay usneoof
Hasesnecses,mebnyt,astshuismisnpgectiheastmthaeyedrieeparryescoeamnpeisnsisicelocinivncovoermroptuersbirmsaeatsemssoawlh]eleynntvheynsabemare eoec:
LifeHisar
mwTiteahsererdsfahsineegshle,do(sbJ,ologansdne,ds smpahnaadseulwBriiesfsmaoern(yeBe:a1rx9fbe8lo8omu)os.resaynwdaioctcDthcaiuvvapeimislpelsreg1,vdaaecinaeyHyienogfwmmobaocrdesise,danbdsahdrhreyiwpaco,rmmfeonownithsin
(suHhiorfvefwemseaiansrte(earMcei19vr8ei9)b.1o9t8h7)d.ayDaunridnigghhatrsdhrwoinuegsh,1t9i7t4s;esJypoeenaceri,seshamnoaduyBginhsnremyogs1t98a8fp)heesSdessofsepryenr.es
iITnhmeeaehlordmyeeenarsrai,nemhoiasfytbshpeiescgiseprseecmiceasytvhahraive2es awinintadhintviihmdeauilaldsrapemraiccrepo(puSleaownayrelds.SIcn pheakFyoeoatrys, -
198)
density ofon individu pes ce pers
asA1en9l7adb4e)owa.iublgllheTvhmosearhsateocei,rfooesuoesddedcsiso,hensrsnseuawkmseisesno.wcnhlsaagutldlaeymvcpaearnrderfefboreosrod,ansnesmimam,lasllslamuegast,inen,maphsle,ey asieuncpopepp,o(raBnraiersvbioecpoostmn.agiovoonrress TDcaaovnniessurm1me9d7a4ty:o JcognorenseassnsedxBueipnmtyoiy21w09i8n5pt:eerrSccSehnewtavroatfzrtnzeadnsSdhmrhaSemcwamhsawrladsri,1ze9a811(n9)Bd8.a1yr)oPbuloannungrksbmanosad sDe(opsaipe,eaJnpoayisa. SPriebymiatseimlsihytlsanrdsotprcoodnusceumevdeinommmthetdquiiwcnkslyestmlorbyediitn3eascthheeripr s(voenra)s 183) a(UefSsacrishunegnvowaefarcyahssomaleanolndclda1Stnicolnhoecawaltnaeassfr1coe9eo8ndc1to)a.nmnasdrrTkutiwcontogme,odvsuhesourbtaoluyitljes(dtHosfhTrfmeeewwirisneccyrheh1se9a3bv9ei)lloywAonnthtsegihiobhuensasriwonogmeennrds {a1a9v8de7),meusliipnig nnesrta.nBcost.h nTehsesabrresbduiilntgpunneedssetriogsfrnyopeuisncsdalbrleeynbaeguatethsbytlohgia.nsrhosecpkercoeies,oitnheearecsodvues nrnes.
(iBHertoeifeofdnmsie.nigsbiarpeepa1ed9ai8rn9sg:0JmoacnyoesmsmauenbdnsciBdeierininenyeac1ra9lr3yl8y)s.parniGdnegsmaainiddosenuxmpimeeneidrodibsnuotahepeesspakplr,osngatalmtnshtoeulgeyhu3ii1es-o3nm2e 3
08915
USFW nana
.
ayndsScwhitwhalrezr19s8i1z)e.soTfhaeppyroouxnigmaatrelfyllfyoumrattoutreen yrooumngon(eJo(n0etsraensdmBnitrnhesy o1f98a8g;e S(cBahrwbaoruzr a(nSdchDwaavrizs a1n9d74S;cShcwhawrazr1z98a1)n.d Schwarz 1981). Both sexes may breed thei frst spring Noaptousrsaulmsp,rerdaactcoorosns,offotxhees,swheoarsie-lsa,lebdobcsahirse,wskuinncklsu,deanfdishf,eraslnackaetss,, aolwtlhso,ughhawmkoss,t osfhrtihkeess,e pmruesdkatogrlsanddos n(oBtarcboonusruamnedtDhaevsihsre1w97(4o;rJaonleesasatnadllBofitmheeys1h9e88w;)Mbeercraiuese19o8ft7;heSichdwisatrazsteafnudl Syecahrwa(rSeczh1w9a81r)z. anTdheSclihfewearxzpe19c8t1a).nofcay shorv-aled shrew i the wild i approximately one ExposesProfile A1d9u87l)t.shHoorm-ealreandgesshrveawrsy wferiomgh0.f5rtoom11a2.c1e0 (3M0egmrmaims19(8g7)).(fTohnesreafnodr,Biitmweays1a9s8s5u;mMeedrtrhiant Fa sahcorottfaoi1lr)e,dsisnhcreetwhceosurledaocboimapirnis1i0n0pgehreceonnt-osfic sadimepslfirnogmlotchaetcioonntsawmisnastpedpraorxeaim(tweelayu2s0e
BFoWoiddainyge)sthiaovnerbeesenrarnegpionrgiefdro(Um.S0..49EP10A0.169923)g.ramAnpearvgerraamgeoffboooddyinwgeesitgihotnpreartedaoyf (1.99g5 induanyitshaosfga/lsdoabyefonrrceopmopraireids(oUn.St.otEhPAla1t9e9r3)i.ngeTsotieoxnprraetse,stthh ffoorrmmeerr ifnogoedstiinognesrtaitoens waetrees m5u.l8t8i1p0l7i.ed byg/tdahy.lOowfeshteseepovraileudesb,otdheyhwiegihgehsttfoofod12inggreastmison10ryaieoelfd f7.o9o5dgi/ndgaeystwiiolnlabteeusseodf forthe purposes of tis risk assessment. {Ahiwsavtaelruiengiensutniiotnsaotfg/odfay,0.2t2h3eg/wgaBtWeiidnagyeshtiaosnbreaetne rweapsormiueldt(ipUlSi.edEbPyAth1e99l5)o.wesTtoreexpporretsesd b[omduyeawse)i.ght of 12 8 1 yield a water ingestion rate of 2.7 g/day (2.7 millers per day sheoislolinigenstgioneastattfooirftothehnesohpoosrstuemdwashsrueswedw.asThneotoapvaoislsabulmesodmit tihsesilmeirlaarutr,tthhteroeffotrhee, sanhimoalrmeadnseh(rSecwhwsainrccezthaeyndaSecbhowtahrzop1p98o1R)u.niAsiscoilominngievsotrieons awitthof s9a.4npegrcpernetfoefrtehnecedfioert wfoaosdreipnongedefsorrattheeoifootpnhoesssuhomr(-Baeiyleerd esthale.w1(9974.)9.5 gT/hdsavyat)oluyeiewladsasmouilltiipnlgieesdtibony rtahteehiogfh0e.s7t4 1i0d0ay.peFrocernttoheftpheurdipctooosffttehhese sfhooord-acihliendmsohdreelwiwahsiscormipskriassesdesosfemaerntthiwtowramssa.ssumed that 29.10 Meadow Vole (Microtus pennsyivanicusas) RepresentaiveofHerbivorous Mammals
lustificaion d"iTehteamryecaodmpoowsivioloen.waasbusnedlaenccteedin1sNorreptrheAsemnetraitciav,eorfehfeerrbeinvcoerfooursmomiastmmreaslss,abnedcaluiseeloinfoiotds ofoccurence at the Dry RunCreeksite.
"
009.15
USFW 0627
Life History
B"Tihrenmeyea1d9o8w;vMoelrersiann1e98o7f)theAlltrhgoeusgahntdhmeysatrcsbmnodraenctovmomloesnlinyNfoorutnhdAmierRicaai(sJonueschnads m{onisatbmecaudloawts,edbofgesd,ss,warmopadss,ideeadimchebs, aandnnfdeInksckeerssohwosr,e(s,BhoeyuhaavnedAlDavibsee1n9K74n:oJwonne1s0 aSpnpdeaBrismteoybe19n88e; oMfetrhreiema1j9o8r7;prSecrehqwuaisriztens dforShcahbwitaartzion19(8H1)o.fFDmeeniseerv1e9g8e9a;aiJovneescoavnedr Bimey 1988). T(jhoeneosmanedrBainmgeeyof1t9h8e8)m.eaPdopouwlavtlieonsvtareineds tiosfizleucwriatthesdsrsaostni,cahlalybivae,rayntdwpooptoulfaitvieoynesairzse `Jwointehsp1ensdk pBoipmuelayti1o98n8)d.ensAicctyivliecvyeolcsceuxrcseedduirnigng1b00thvodlasypsenrdacnrigeht(.BaarnbdotuhrraoungdhDouatvitsh1y9e7a4r;. arlutnhwoauygshiutinsderretveesgteaatidvaewcnovaenrd rdueskdi(sBtairncbtoiuvreaonfdmDeaavdisow19v7a4)l.e iWnehlalbi-twioorni(notnecreecainndg tBuismseocyko19f88r)a.s,Elaalbtohroauteghspuhnedreircgalronuesntdsnreescsomamaolnsoiybubuliilnsrbiovreagrreosun(dBainrbthourcaenntdeDraovifas
1974; Jones and Bimey 1988).
"The meadow vole is herbivorous, feeding primarily on grasses, sdses, legumes, bers, and crionoodmtipsvoi(dnuMeaenlrtsri(otfBat1r9eb8o7du)ir;etahniondwseDvoaemvrei,srie1ng9si7eo3cn;tsiHvlooafrnyFemasenldasntcdarnBn1ii9m8b9ae)ly.is1mB9l8hu8as;gvHreaosbfsefem(nePiorsaecpsrorpt1e98di9s)i3.nmsaTojhmoiers Species hoardsfood forth winter in above: nd below-ground caches (Meri 1987). "sTuhcecemsesaidonow(BvalrbeoiusroannedoDfatvhiesmo19s7t4)p.rliBfriecedmianmgmaoclcsu,rsprcoudruincgintgheliwearrmafeerrmloinvethisn orfaphied yoeamr (J1o1n0es11anydouBnigme(yav1e9r8a8g)i.ngTfhoeugretsotsieovennp)e(riaordbiousrboauntd2D1iGvaiyss1w9i74h;lJvoneessizaensrBainrgnienyg D1a9v8i8s) 1T9h7e0)helpless young maturerapidlyand may breed by 25Gays ofage (Barbour and (MBeaarbdoouwravnodleDsavairse 1p9r7e4v).edTuhpeosne bpryednaetaorrlsyailnclusdpeecoiwesl,ofhapwrkedsa,tosrhyrkbeisr,dsblaucnidayms,amcmroawlss, foxes. weasels, mink, ca, raccoons, skunks, possums, shrews,and snakes (Barbour and pDoapvuilsati1o9n74e;xcMeeedrsrisix1t9y8d7a)y.s oDfauegto(ShcehawvayrzpraendadtiSocnh,waorntlzy 1a98s1m)a.ll proportion of the ExaonueProfle Aradnugletomfetaidsoswpevcoileessvwaeriigesh rfoomml2e0ss0tha6n goranmsac(rMee1rr3i.21a9c8r7e;sU(SM.eErPiA11998973)),. TThheerehfoomre,. ictonwtaasminaastseudmeardeathaarea3 umseeafdaoctworvoofle1),cosuilndceotbhteaianres10c0ompperricseinntgotfhei ond-isetc fsraompmlitnhge locations was approximately 20 eres. A00f.o2o1d igniggesBtWioindratyeirsarnegpiongrfirdofmor0t3hi0s1s0p0ec3i5esg(/Ug.SB.WiEdPayA,1n993)a.mdeTaonewxparteessinhgeessetiovnaliuees in unt of g/day, he highest reporid food ingestion (i of 0.35 g/g BWiday and the wer
a 669.20
USFW 0628
ingesionra 021 gl Bday were mulled by te lowes repre body weightof20
5d 3 ood neon eo7.0 ey and vats neste of 42 py (43
-
p5esricee lnit nwagso emnalrutpelieofd2o.yptehrTecfeoh08oafgtaehSeioanl a(dioieisoSfoSeS7V.0agSoaTryenotomswWielSdEmYgEeoEahi1oknlrer1ne99o8o) fifo2r4
F017 gay.
Fpoerrtchee pofurbpeosieseafwhaes cfoomopdricsheadinomopdlealnsi. his ik assessment, twas assumed that 100
50 ASSUMPTIONS T is ska assesmeeonmtaoveaaliuveessseuxpmopsieosns0wcaornsmimnaadnettsodcvoonudugchtohosd arnkd nsceisdsemneanltseadhiemesnetnsciengoesfti5o6n.. specific da Thuesedmnasiikmulmloafiohensc.omaminan levels messed in sediment, sil, or wate cllsted on site was Tbehpermeasesnitmsucm-wciodnecenaions of COCs repored i sedimen, soil, water, nd io were assumed ; + Ansres use factor (AUP) of1 was assumed for all species using the sc for fcding.
;
.
Conaminants were assumed to be 100 percent bioavailable.
DietSaimprliyficcaatmipoonssoidfocnoimnpfolremadtiiosn wwaesrebpienrfeodrmferdomfoththre raecrepetofor th receptor species. However,
+ CAVaellunieesirrunroepgoseneabdnyrcfhtorhwaaiscnlcdoisoealnynsrpdeeciiuteeosdd.cets1teprencmeoiiendtseowxethireeccuvhsarelodun.eisccAoloxlldisubceoeofsctawheteerceofncriiatmahilnelacnyiesproeofvrciosepnweeccdieesn,
eoortcmraibnolef ew10,h0eLwraDs,du(symeeddeitasonciloetnahvnaedlrmdoetsteeh)odtvsaolwureerseewaeprLpeDro,upsreitao.te2.FNoWrohpeOunbrspvoeasrlevuseesdoffAotrpicshpriaosnrikcatEsofsxfeiesccsitmteyLnwete,vreela
((oNLiOOAAeEELL))v.ailoueAAsNwfOaaArceEtoLpo.oan1n0dewaaffsaocrutosreedo1fp010icownssvpeeructiseeesd,poioecromenovdsetrLscoaownreseseptrovmOaebtdisveLerDvv,eald1u0Ae3dwvLaeOsrAsuEesLeE.dffienscethveLeerrviaesllk
eeueivoiendsinepgrfiaeesneoftotoonvicemaecnhaanmsdm,roTmoxsiicnigtlyevdlouseesoroabladiniesd,roNmoloongh. eamfefreefdaicntgorssuweerse
incorporated io tis isk assessment
lCnosnovmeenecae,ductoynammaiknean(cindmoielsigwrearmesrpperonkeildogarapmarbtapedy wmeililgihotnpceorndtaaym;inmaen'tkgn-ddaiey.) bTyheussienwgehree
formats
{tsk (mgaday)=Conaminan Dose (mgkg ixeInges)tion Rae (kg/d)x /Bocyweight (<9)
a 000.55
USFW 062
converseionsallovwsidietoasrystotxyiiwyeeiv.el ciFtoedforonpeustpecoiesofosbercoknverctedetona d,ailypdeoserfsor
oFiRsCeediBmentLiLngestion4w1a0s,adlooseimncalyudtehdeninbte husceadlctuolaetviaolnuattedtehteerimsikneothoethoeaspdeaciileys iifnankoespfeocritfhiec toxicity dai 5 available 078 hor secehrcr tSooxminescwohennmiinngeesmtoedfetsthte epr(eesg.eanlulmevienlus.m) ar nokfoodchan accumulators, but instead are direct 40 EFFECTS PROFILE fMuartnhyerccoonntsaidmeirnaatnitosn dientteicsterdisak atshseesDsrmyenRt,unbuCtrdeoeekssniotekdeoxcnloutdheatvheebmeanschpmotaernktsi.al Tchoinstaemxicnlaundtesodfthceomncferronm. tBhaesiretdooxinetehfefercetssualrs porftehseentperedlniemixntafrlyuorriisdkea,swscehslsomernotf,lutohreolmoeltlhoawnien,gacloummpinouumn,dsarsweenriec,cboenrsyilldieurme,dcChrOoCmsiuamn,d wcoiplpebre, fruornt,helreaedvamlaunagtaendeussei,ngnifckoeold, cvhaainnaaccduaimnuudlazmitni,co.n mBodaeslesd.onCotnhteacmhienmainsttsryexrceseueldsi,nhgetsheircormesppoeuctnidvse cboemnmcuhnmiatrikessarien athsesuameqd tuoabneadateftrfreecisttirncigalreececpotsorysspteecamisstahnedDnreygaRtuivnelCyreiemkpascitte.ing species, populations, and 41 Furie Mflauuorriedretfaorlap(e19r9i0o)diodfen9ifiweedekssk.eleTahleaLndOAdeEnLtalidaebnntoimfimeadliicnitehsisinsnrautdsytwhaatsw4ermegeFxLpoksgeBdWtiodsaoy.diuAm 'suNlOtAsE.L3wLasOAcaElcLuolfatedmrg/okmgtBheWiLdOaAyEaLndusainngesatniamcacteepdtNedOcAonEvLerosifon0f.a4kcgorBWofid1a0.y Bwaislelbdeosnetdhesfoe evaluate the tisk posed by fluoride mammalian receptors aF5lelmoiwngasea1l5.m(g19F8U7k)gfoBuWniddasyi.gnifNiocanetffgercotswnwheraeteobrseedurcvteidosntin10EumrgopFeUangsBlWiidnagy.fedAasdiseutchc,ontthaisiniinkg a1s0smesesmgentBwWidllaiym.ate fluoride related isk using a LOAEL of 13 mg/kg BW/day and a NOAEL of 42 Organofuorides Ncoomsprouduinesdpwearsaifnoiunngdtinthtehediliaerryautroex.icityofgichlorofluoromethane or any other fluorinated organic 45 Aluminum
aDliuxmoinneutmali.n d1r9i7nk9i)ngcownadtuectfeodr 9a0sdtuadyys tphraitoretvoalburaeteeddintgh.e Trehperohdiugchteisvtedsouscecaesdsmionifsrtaesreedxwpaosse7d7.15 ambinlolrimgalriatmisepse.rkLialloegtrala.m1b9o9d3y)wceoingdhutctpeedrada18y0(-dmagy/kdgriBnkWiIndgawayt)eraund ydidinnowthriecshulrtatisnwreerperoedxupcotsievde stoign5i5fimcaynteedBucWtiidoanyinofspaolnutmainncuomu.s lAotcotmhoistodrosaec,ivbiethyavainodrasligenfiffeicctasntwedrefeicoibtsseirnveadc,quiisnictliuodninagnda etsetteinmtaitoend oNfOlAeEamLedofre5s.p5onmsges/.kg BBaWsieddayonwitlhlesbeeruessueldtst,oaevLaOluAatEeLthoefr5i5skmpgoskegd bByWiadlauymiannudm atno mammalian receptors (Table 1)
a
009. 57
Hews ann,
'NBoWiedfafyec)tsalwuemrienuobmsfeorrvfeodurwhweeenkJsa(pHaunsesseeinqueatila.we1r9e88)f.edWahdeinetqcuoanitlawineirnegf0e.d05a dpieertccenotna(i8n3imnggi0k.g1. Fpienraclelnyt,w(h1e65n mquga/iklgweBrWe/fdeadyad)ieatlucmoinnauimn,iangdec0.r13peeasreceinnte(g2g57shmegl/lkbgreBaWk/idnagys)eanlgutmhinuwma,s aobdseecrrveeads.e uinsibnogdcyhiwceikgehnts,ceogngclsuhdeleldtshuaetngdtihe,arayndleevgeglssohfel2l8.p4romdgucktgioBnWwiadsaoybsaelruvemdi.nuAm r4e3s-udlaeydfiencdidnegcrsemausdye (Huwsesiegihnt 1ga9i9n0,).feHedowientvaekre,, oannldyptlhaesmalateirneodrgmaentiacbpohloisspmohofrcusa,lc2iuwmelalndaspahnosipnhcorerausse cionuplldabsemaarcsabluctieumd B1ectahuesdeiraecrtaenfgfeecotfs coofncaelnutmriantuiomn,s wTehreeaussseocdiaatneddtNheOAenEdpLoifnotrsthwiesreeffeeccotloigsi2c2a.l8lymsgi/gknigfiBcWaintdaayn.d LreOlaAtEedLtvoaltuhees.dosAe,NOthAeEstLudoyf8b4ymHgu/sksgeiBnWeitdaaly. (a1n9d8a8)LwOaAsEuLseodf11063thmegd/ekvgelBoWp/dthaeyNwOilAl EbeLuasnedd 10 evaluate the risk posed by aluminum to avian receptors (Table 1).
4s Amenic
cSaetvserianldisctautdeidesthwaetraeclhorcoantiecdowrhaicthoxdiceitteyrdmoisneedwtahse 1e.f5femtgs/okfgABsWItodmaaymm(Paelrss.hagAenstaunddyVcaohntdeurct1e9d79o)n.
LInDad,ditchoant.raNnagteiornaolmRe1s0otu0rc5e0smCekoofuolefaCndanaracsdenaa(it1e.97lA8)stsutdaytecsotnhdatucmtaemdmoanlmsicinegienndeircaaltehdav3e1 oorraall
d1o5s7e7)L.D,Foroft3h9e.4pumrpgo/skegsoBfWithdiasyriasnkdaasnsoersasdmoesntehteL,Dc,horfon1i0c.4vamlgu/ekfgorBtWh/edcaatywaafserus9e6dhtooucraslc(uNlAaSt.e
Qs for mammals factor of 10.
(1.5
mykg
BWiday).
This
value
was
convened to
a
NOoAEL
by
dividing
by :a
.
EiIsnloregra(n1i9c8A8s5)isrmeovrieewmeodbsielveertahlanstourdgiaensiicnAwshainchd mthaeyptooxsiecigyreoafteirnorrisgkanbiyc laerascehniincgalisntwoesruerfmaecaeswuarteedr..
tShtautdiseesnswietrievealsspoecdieesscriinbceldudien twhheicChaloifrogrannicaarqsueaniilca(lsicngolmepooruanlddsosweerLeDm,eoasfur47e.d6. mSgc/udkigesBiWniddicaayt)e
(pHurupdossoensoeftalt.his19i8s4k)aasnsdescshmiecnkte.na(vsailnugleeoorfald3.3omsge/LkgDBWoIfd3a3ymwga/skugseBdWi0dadeyt)er(mNiAneSt1h9e7H7)Q. (0Fobrirtdhse.
"This value was converted10 a NObAydiEvidLing by a accor of 10.
45 Belium
GTuuyoarseerpaarlat(e1c9h3r3o)nfiecddilaertgaeryaexmposouoruefbsentruydltielsisuumsicngarrasbroenpo0arrtatetdsesaitmicloanrcemnuzsaecuiloonsskeolfea10l,e2f0f,e4c0s. o80f,th1e60,boanneds2v4a0rymign'gkgdiBreWcitdlyayw.itRhattshefreoxpmoaslulreexpcoosnucreenrlaetvieolns.devSeilmoiplaerd rriecskuelss,wweirteh rtheepofrrtaegdilibtyy Jleavceolbssoofn1(21193a3n)dw2h62o mreep'okrgteBdWsiedvaeyr.ely weakened bones in rats fed beryllium carbonate at dietary
bFeorrytlilsiurmitso tahsesesshsomretnat,leaddisehrteawr.y eAxpNosOuAreELlevoefl 0o.f1010mgm/gk/gkgBWBiWd/adyaywawsasdeursiveeddtfooesmtitmhiasteLOiAskELo.f using an accepted conversion factor of 10.
No suudies peruaning to the dietary toxiciry of beryllium ( avian receptors were found in the lierarure
46 Chromium
"
86:.55
USFW 063
H1e0i3ndzieatndcoHansneilinnge0(,12981)0ofe2x,0po0smegd/2k-g,0w3e-tyewaerigohitd,b(r0e.e2d.i7n7g,poaris2o.f7b7lmackk sducBkWsi(dAanya)sorfubCroiopesa)s conhsveotmofieugmg-ploatyasisnigbumystuhlefatfeem[aClFesK.(HSaOtcshe2dH,du0c]klfionrgaspweerrieodtohfeanpfproex3immadastheldyive econmaoinntihnsg, tuhneclsatmhee Cinrrceosncpeonntsreat(i0oansftrihgahtthsetipmualruse.n wNeorneeofefd.thSeeCvern-codnacyoenltdrcahtiiocnkssrweesrueltteedsiendafeorraatviooindaonfceavboeitdaavnicoer bHeohwaevvioerr., Haseline eal. (1985), in 1n unpublished study reported by Eisler (19864) noes that black d5u0cmk dugckolifngns suunfsfepreecdifrieedducCerd?scurovmivpaoluanndd ianlttehreidrgdrioesw.ehTphaenpeesrcwenhtenreeduxcptoisoendi1n s1u0rvmivaol ndand3 cetiled explanationofthe alieredgrowth paerns were not availabiin this unpublished rudy,
wFoarstuhseepdu3r5po8sLesOoAfEthLisforirstkheasasveisansmsepne,cidesi.eaHroywleevveelrs,odfu1e0tmoet/heksco(n1flmigc/tikngg BrWeilda,y)aoNfOCArEiLn pwriesy
-
dreergiavreddinfgrtohmetChresspaemcieessuedvayluiantwedh.icAh NthOeALEOLAoEfL0.w1amsgs/eklegctBeWditdoamyaiwnaisaidnearidveedgrferoomftchoensLiOsAteEnLc.y
using a conversion facor of 10.
(AStsetvuedny cetoanlduc1t97e6d).witFhordotghse ipnudripcoasteesdotfthhai2s.5rimsgk/aksgs/edsamyenotf,CraiLnOgAesEtLedofi0n.t2h5 adinedt caaNuOseAdEdLeatohf
0.025were used orthered ox, raccoon, nd mink.
.
47 Copper
:
`dOonseestofu1d0y0wamsgl'ockategd/twohdaidcahoygdectaeursmeidndeedatthh (efOfeHcMtsDofi1n9g8e7s).tiFoonrotfhCepuutropomsaesmomftailssipesckieass.seAssnmeonrta,l 3maLmOmaAlEsL.of 10 mykg/day was used and a NOAEL of | mg/kg/day were used for the exposure of
S(e6v1e3ralmesukdgi/edsawye)recaluosceadtedawshiigncihfidceatnetrdmeicnreedatshe ienffgercotswoefh Caundonfocohdicckoennss.umpAtdioosneo(Sfmi3t5h0 m19g6/9k)g. A19n7c8)t.hrAssusdumyifnoguntdhatrehsapdaiorastteooryfp3r2o5blmegm/skgar(e2a3.5amcyut/ekge/ffdeacyt), caaLusOeAdErLeospfir2a.to3r3ypmryokbgle/mdsay(Haantdcha NOAEL of 0.255 mg/kg/day were used o determine risk t avian species.
48 tron
Nleorastuurdei,es pertaining 0 the dicary toxicof ron to mammalian or avian recepios were found in the 49 Lad
"inThe sgiansgliecomroatlildiotsyeofwaasduelvtamlaulaeteadntdhrfoeumgahletheed-ucseiolfedsuhragwikcasllfyedim0p.l8a2natnedd r1a.6n4sdmugerPshifkog BaWpierdiaoyd ofgehsteieonowfeeuknsdifgoelsltoewdinmgattehreiadlospee.lleNtesit(hLearwclonecrenetal.ra1t9i9o1n)h.ad any effect on gasic contractions or APbspuoidsocnoinngdu(Rcetioseendr raendd-aTielmedplheaw1k98f1o).undAthsaitmi3lmary'sktgu/ddyayfooufndPbthcaatus3edmgt/hkegc/ldianiycaflesdytmopstaormisngosf causeda reducion in muscle condiion and altered thei feeding activity (Osbome etal. 1983). For
as 00034
11QEW naan
ShpeecpiuerspnosdesaoNfOhAisErLisok af0s.s3eswsamsenuts.ed.LOAELof 3 my/kg/day was ustodeetermdine risk to avin CSeovnedruaelesdudoniemsicweeriendlioccaattededhwahi1c.h5 mdeytge/mdianyeodfthPeoecfafeucstesdoafrPebduicnigoenstiinosnutcocmeasmomfalism.pliAedsuodvya p{rCelgankan1c9y79w).henAntohtendeoesestwuadsy afdomuinndisttheare2d.23 m(0g5/ddaaysyfoclaluosweidnga meadtuicntgio(nClianrkhe197f9r)e.queFnocrytohef sPuerdpo0sesdeoterfimsinieskriasks(0smeamsmsalmasNe.OnAtEL.of 0.15 myg/day and aLOAEL of 1S merkeiday were
410 Manganese
mTahnegaenffeescetseeledve.lsRfaotrs emxapnogsaendes0e1t3oxmicikty vBaWriydwaiydoelfym,anmgoastnelsiekelays Maarw3o0uSabiinethtiortdheiffoorrm22o4f
Bvasye,xiatlseodofrecMus3ed0tefton0orodnareysleeveslls(iLeadsiknedyeectraela.se1d98a2c).iviIyn m(iGcrea,y adndeLaarskleeyve1l9o8f0).140Ammguc'h
-
dhiogphaemrienxepolseuvrelesc(oGnicaennturiastoisoannfd M2,u3r0r0amyg1'9k8g2)B.WIday ofmang1aMAnCEeressuleed in reduced
a1nctoengraesspilratoerya,vciaegrhdolv5a9ss5es0lmrg,/gkagsBwWoiindeasyionfaml,haemantloggaisacMla,nSmOueHscfusol1oes0k3eiwaele,kshehpaadtinc,o refefneaclt, dermal, snd ocular sysiemsofmice (Hejamancik etal. 1987),
:
Foesrimhaitseirisskk aofsmasnegasnsesmaedeionettthaer,syeelxepcoesdurmeamlemvaellioafn1r3ecmegpt/okr.g BAWNiOdaAyEwLilolfb1e.3usmedg153BWL/OdAaEyLva1s5
Gerived from this LOAELusing a accepied conversion facior of 10
Nloiastnudeies pring to the dietary toxicicy ofmanganese fo 3 avian receptor were found in the
a1 Nickel
fSeeveidralssulufdcieesinwdeirceataevdaailNabOleAEwhLicohf1d8e7t.e8rmminged/hkegef/tfoedcmtoassoyftNsiysitnegmessteixocnetpt mfoarmbmoadlys.weiWgihsit.arTrhaitss SleivmeillaorfsNuidswuiltfha cbaeuasgleed,a2N7OA1E2L9 opfe6r2c.en5t mdegckrge/adsaedybwoadsywneotiegdh(tA(mAbmrborsoesteaelt.al1.9761)9.76).ForItnhae hpuirspovseuseoftwaisscskoansvs1ee3rsLtsaOeAmNEOedLAnEoLtf 6o2f562..05mmykgg/a/y bkywamlsgiupsel/dyitondgdehtaeerNmiyOnAeELrisbkytoamafmamctaolrso.f 10
sNpeocisesefsrowmeriengaevsatieldaNbie wtihlalt dneatebmeidneetderhmeidnedoofNsi 0 avian species. Therefore, the risk to avian
412 Vanadium
dGoasveagweassncdioes nin mvi0ce.e3hnaLvOeeAfEdLouonf3d1 3L.1 CmSgO/kofg 341ndmagNVGAVAKEgLdioef(S0c.3h1 ruoseidnegraanndacBcaespsead f1a9c6t1)o.r oTfhi1s0 Ccoonnvceernsmiaotni.onTbhyisanfoiondgedstoisoenwaatse ccoonmvmeorntledytoobsaderavieldyidnomsiecbey(0m.u0l0p3lkygionfgfohoed LdaOyA)EanLod rtheNnObAyEthLe inverseofth body weight (0.025 KEKRTECS 1985). This calculation sesulied na LOAEL of 0.372
a
005.55 USFW 063
tmigskVtoimgaBmWmiadlaiyananrdecaepNtOorAsEinLhoifs0r.i0s5k7a2ssmegssVmienktg.BWiday. These values wil be used o estimate
Rorseoplmiecsat(e1s9o6f01)3excphoiscekdencshivcakreynisngtocvaorynincgecnotnrcofaevtnantiaroodiafnuvtmsaniafodoinarums.perTihodeodf 2y1 dianyvso.lveTdhefesedmindg effofuincdietncyohafdfaioeoadtrytllezvaetlioonf.40Amt lkevelisnotfh2e0d0ietmgr/eksugl,iemdaritna3limcaywraksedndoetperdesisniaolnl tineswecihgichktengsa,inTahned "aTuhtishodrisetraerpyolretveedl wthaastacodnivaerneydl1ev0ealdoaf2il0y dmogse/k2g5 acboouvled bbey mtoulletriaptleydinwgitthhendoierteasruyacnotncoexntircateicontbsy (a0.re8p0r0eksegnXtaRtTiEveCcShi1c9k8e5)n.inTgiessticoanlcrualtaeti(o0n.r1e4s0ulktye/ddiany)LOanAdEtLheonfbymtgheViinkveerBsWeoidfayreanbdoadyNOweAiEgLh of 3.5 mg Vikg BWI day. These valueswill beused o estimaterisk t avian recepiors.
a3 zine
.
oSefve1r2a4l.5sdmig/eksgw/edraeyacvaauisaebdleawdheiccrheadseeteinrmgirnoewdtthheanefdfeacntesmofiisngiensctheidckZeansto(bSiarhdls.eAa.co1n9c8e9n).gaiInona
wseimiiglhatrDsteuadynctoaln.duc19t9e1d).onIcnhaicskteundsy,caoncdonuccetnetdroatniJoanopafne3s6e1qmuagl/3dcaonycecnatursateidon roefd1u3c9timoyn/ikgb/oddayy
pcuarupsoesde7s poefrtcheinstrmisokraalsisetsysminencth,icaksLaOnAdEreLduocfe1d39fomogd/kign/tadkaey(wHailsl unsdedCtaomdaertdeersmeine19t8h6e).feFcoersthteo
aSvfiaacntosrpeocfie10..This value was converted to a NOAEL of 13.9 mg/day by dividing the LOAEL by
yAesatru(dyNAcSond19u7c9t)e.d Fonordtohges,puirndpiocsaetsedoftthhaits1r,i0s0k0amsgs/eksgsm(e2n5tm8,g/LkOgA/dEaLy)ocfa2u5s0edanndo aefNfeOctAsEaLfoerfo2n6e mweirkeeusdeady tcoaduseerdeamdiencerreisaks0inthfeoofdoxiannadkethaenmdowuesieg.htlIonsas.stBuedcyacuosnedtuhceteedraen ifsevseirmsil,aar tdoosheeomfi3n7k0, 2 LOAELof370 mg/kg/day was used and a NOAELof37 was used to determine isk to the mink.
50 RISK CHARACTERIZATION
tThheeDfroyllRouwninCgrmeeetkhsoidte,waimspluisceadtiooncsaolfcutlhaeteerxispko.suTroeecsotnicmeantterathteiornissknteoewditoldbeedienttehrmimnoedde.l TsyhseteHmQs umieltzhiondg r(eUpSr.oduEcPtAive19f8i9,leBaomrirendouucesdegretoa.wt1h986T)hceocmpoarmespexaporsruiereesxcpoornecnesnstserdatsisornast0ioseocfoplootgeinctailaelnidnpaokiensvasulcsh a1s6 population effect levels, or:
Hazard Quorent (HQ) = _No _ Observ_ eEdxApdoM vseurrseeCe oEnfcfeetoa rLaetvieoln n(NOAEL)
hAeHoQrgagnriesatme.r tAhaHn Qonelesisndtihcaanteosntehadtoeexspnosourined0icattheeacoanctkamoifnraisnkt. hTshethHQpostehnotuiladlbteo icnatuesrepraedtveedrbsaeseefdfeocntsthien severiy ofthe effect reported. The resuls of th risk characterization ae presented next,
SI Benthic Inverebrate Community Sruerure and Function
c"aTsohcmeombmuepnnatihryiecdsiutnrovvteehrytesbRhreoaftweeerdecnoacmedmerucnerieaatmsye.iinnSDicrnocymeRmuuannnidtauypspteeaaaxrnosdntoaomvibacieldaatibvlieesrshkiatbfyoiracantdwaorsebruetanhsedoasnnsac.meeaTilhnoeDnrbgeybnotRhtuihnc
@
009.55
-
osrternenainmsomi,nnthsaeperddeeiscmeremnentatissienliinTneDidroiyvueeaarersniy.styAIacnnasdannddabbdeiuinpndAr,arondehcuseeceIaildn.mpDihnrTiyhtpehoReduobnbxsemeinravyeiedbceeossmaetmrgurlinsubiruetltyye,gd rdtsaoopmwecocsoninasmflamletiyne:asatnwhidaaoestnr
miSeiauntsscoapcpFgeeurir.vie1el,ydcronerdniweedrewcizhooonnieeesg,a,isvhesmihanosumiu,aicnelsrueb,lateiConesahigpGseewe,grreiookwte,cSaEdppRooIissEstSu1md6
hed10 vwiehrmSeilnc,ehthee osebdsiemrevnetdsXcaiss tmeayarnedprlesesnltongsihgeniwhfoilcea rDre.Run eschsppes abe
$2 Soil lnvensbrae Community Sears aad Funcion
Rhne.siTlheianvneonrcoommkuniity doecsninftiepdenoparobbeeaskwibassurevoidnvacluoreoswol.condiions a Dry
53 Fi Communides
rbTheeectfyehsvcecsoosnoicmiornmesad iwuDni rUnypRspyneeTmorf bcaoeonyAtuiymkid.nuacRteesmnulathrofltayhmepthhilepasoddltmfihn.bnusotTwhsois,unmvocrwbaaoslsecsgoaaulidsvhenolowyt
CCSomoelis0e.dc10woietvhenp,oeaTsfiheuermewcdaosnvcaaetsssriaisiafominpcslae,nstB.opwLoesovtwievrsepieccoirersceoldraitvdeilroasndibcoyenrnwwdeaesaabsfuoantdshaenacdaesuorabvsievravslegdnadfduirreiaonsng
ne eecohocking effortmaybe reflected by he resus ofhe aniciy test.
'
54 Womeaing Beds RAfaocraogCenr.essoleatrenivdawesatdas,esiThnesemomdteoehdltespwl boasseerdmtohdnnatwesebtiaiwnesmisigsahy,tbcceornaeaFitsmki,odnucseatpopfiecronneadgm,ioveafancnssandcfiiiuommhi,roezZiDnner,dy nCoeamkpBouonardnds.eeaoFrrofsoukachrfaaocntmoierssikbhacaslencdlwoarniacionsnsksescrnvdoatrsievseduulieannputthsc.azkaBroydfdqteuoofitaicuea,nltbsoeisreelsipubrmee,scehrnrtoenmd,rkimnsaTnfgolarnehess4e2e,
55 Camivorous Bits AfRocraaogCenr,seseeoknlsaaineihdrviwsekadaerssrsTmihienmem:dodhmeoaldepclraembdiisvieocdcaooutnswmiesuwmmga,hybcceohtrnoicmstikuimod,unecso0popfioenrngealsstrdiio,nrioanfon,snnfdorraeidnDrey LeheneasFdciioamenptoneurdnsdesaihsFiodoordoocfnhlaucioannrisosemkrevcaaniaveelscicnupiusltksaafdtBcriyerosdunedllustloh,alzbarcekdorufiro,xniorslno,greimpaarlnegbsaeennncsehsdm,aiarikTksoelo,er FS
56 Camivorous Mammals (Terestially feeding) CRAoucmonnasmCeirrnvsaetteidvseefiosraakgsea,ssdseeosesmremsnitnnsdemwdoadlheesla.baTcshaeemdimavnordwoeeultsrwemeiagcmhmtsaclhosantcmelnauaytmiibonenasao,tficoshnkrtodmauiemuim1,n0 acnogpoepesrei,o2nDr.oyf
" 006-87
B
USFW 0635
rmainhglaonreosfel,uovraonmaedtihuamn,eaanrde rfilsukorfiadcetoarrsedruisektfacltaocrksobfaosxeidcoonlocgoincsaelrvbaetnicvhemianrpuktss,foBrythdeesfeauclot,mproounnadnsd Food chain risk calculations andresultanthazard quotients are presented in Table 42. 57 Piscivorous Mammals A conservative riskassessmentmodelbasedonwet-weight concentrationsofconaminantsfo tie Dry cRounntaCmrineaetkedsiftoerahgaes, sdoeit,earnmdinweadtert.hatThpeismcoidveorlopursedmicatmsmtahaltschmraomyiubme,amtanrgisaknedsuee, taondinfgleusotriidoenaoref rbeickaufsaetoirtswbaassendotodnetceocntseedrviantiivceeisnpeudtism.entTsr.ichFlooordofclhuaoirnomreitshkancaelcisulnatoiocnosnsaindderreesdulatarnistkhfaazcatrodr quotients are presented in Table 42. 58 Omaivorous Mammals RAucnoCnresekesrieivshkaaasstsdeeistsevmremenitnmedodtehlatbaosmeadivoonwroeutswmeiagmhmtacolnscenmtaryatiboensaofrcioskntdaumeinatontsinfgoerstthieoDnroyf. cvoanntaadmiiunma,teadndfofrlaugoer,idseoial,raenidswkaftaect.orsThbeamsoedoendlpcroendseircvsatthiavteairnspeuntisc., cThrriochmliourmo,flcuopopreorm,etmhaanngeaniessneo,t creosnuslitdaenrtehdaazarrisdkqfuaocttiorebnetcsaaruesepirtewsaensnteodtidneTatbeleci4tn2.seed sediments. Food chain riskcalculationsand 59 Insectvorous Mammals Aconserivskaastseissvmeent modelbasedonwetweightconcenzations ofcontaminants or the Dry Run Creek site has determined that insectivorous mammals may be at risk due to ingestion of c`moanntgaamniensaet,evdafnoardaigue,msaonild,falnudoriwdaetear.e iTshkefmacotdoerslbparseeddiocntctohnatsearlvuamtiivneumin,pucths.roBmyiudme,fauclotp,perro.n,leaandd,. criocmhploournadfsi.corFoomeotdhacnheaianeisckoncsaildceurleadtiroinssk faancdtorressduuleanttohlaazcakrodfqtuooxtiiceanltosgiacraelpbreesnecnhtmeadriknsTfaboltehe<2s.e 5.10 Herbivorous Mammals RAucnonCserreveaktisveierishkasasdseestsemremnitnemdodtehlatbahseerdbiovnowreotu-swemiagmhmtaclonscemnagaytiboensatofcroisnktadmueinfaontinfgoetsthieonDroy.f contaminated forage, soil, and water. The model predicts hat aluminum, chromium, lead. manganese, arincdhlfolruoofrildueoraormeetrhiasnkeafracetocrosnsbiadseerdedonrisckofnascetrovrastdivuee 1i0npluatcs.kofBtyoxidceoflaouglitc,alirboen,ncvhamnaardkisumf,o athnids compound. Food chain risk calculationsandresulant hazard quotients are preserved in Table 42. 60 UNCERTAINTY ANALYSIS cTohnesriedearreedfawchteorns iinntheerrpernettining trheesulrtiss.k aMsasjeosrsmseonutrcpersocoefssunwcheircahinctoyntirnicbluutdee(naruunrc2elrvianritaybilaintdy,neererdor.toabned. insufficient knowledge. Error can be invoduced by useofinvalid assumptions intheconceprual model. Conservative assumprions were. mpoasdsiebiilnitlyioghftocofntchleuudnicnegrtathianttynoasrsiosckiastepdrewsietnhttwheherinskaatshsreesastmaecnttuaplrloycedsose.s Texhiisstw(a5s.doenleimtionamtiinoinmoifzealtshee negatives). Whenever possible, isk calculations were based on conservative values. For example, NOAELS
"
000-155
usedtocaleulate HQs were the lowest values found in the lieraur, regardlessof toxic mechanism.
Aasnseismspmoernatnstbcaseod. nRimsktbcoauulnccaetlrraooinntsryaeibtahsedinocnommpalxetiemnuemssoCfOtCheledvaeltsaionfsiendfiomremnatt,iwoanteurp,oanndwhoiichsatmhpeliess.k
;
LdietneirfayrrseruvaileusesusfoingthcelotsoelsycrieyloatfedCOspCesciewser10emnaotkeavraiislkbelsetifmrateaslforertcehpetosreslpeececds.rceApnrorasn.emSpptecwiaess mreasdpeontdo
iwfhfircehntthleytooxiecxitpyosduacraeatroetroexipnrse;dr.espMoentsheosdotoloCgOicCaslbpyrotbhleeimnsdiwcearoearlsspoecpipesasmeanytbien sdeivfefrraelnotftfhreomsusdpeiceisesSofomr
Wfhoiucnhd NfoOrAsEoLmeSowfertheeosbealiencetded. rUescefpotrocrn,ately, swudies which were mre suiable for tis assessment were not
AValluiteesrautsuerde steoacraclhcuwlaastecHanQdsucwieerde0theidleonwiefsytavpaplruoepsrifaotuenNdOiAn EthLeSliaenrdauLrOe.AEILnSmaforntyoisftrhisksamsusieesssmreenvti.ewTehde,
-
aapdpvreorpsreisetfefNctOsAEweLrse foobrsserovmeedraetcetphteorlso.weIsnttehxspeoscuasrees,coanfcaecnocradoofn1.0 wTahsisusmeaddetoictoinmvpeors:stihbeleLOtoAiEdLen1i0ty3
NOAEL, which adds uncerainty to the NOAEL-based calculations.
cDoosnetsamiinntaonxtiscolboogdicyalwesitguhduideasy.canAlble droespeosrreedpoirnieudnaitssmofgmg icnodniettamweirneanctosnvedireste,dotr iunniutsniosf omfemgg t'hBiWsidcaoyn.verbsioodn.y wOetihgehrtwsiswee,rethreepboortdeydfwoeitghhettaenstdaninigmeasltsioinnagraievefon strhce,sptehceiseesvraelpuaesriweedreinsoethderforlmcaekraiunrge sources were used.
Aonomthseirnsgoluer-cseopfeucnicse,rsaiinngltey-acroisnemsirnaonmltahbeoruasteorofytosxtiudciietsy. vParleudeiscrteipoonrotfeedciostyhestleemraefufreectwshfircohmslraebdoreartiovreyd. s34u4isto isthdeifiecfufletc.tsLoafbocroatnoarmyinsradnitesswceasnsn.ot aNkOeAiEnLtoasccwoeurnettgheneeeraflfleytsofeelencvteidrofrnommesnrdfiacetsorusswihnigchsimngalye Ccoonnttaammiinnaannts.exposure scenarios. Species wilizing the Dry Run Creek sit are exposed to a variety of
Tfohrewsieldslivfeeryspelcviels.infIonrtmhaitsiiosnkavaasiseasbslmeeinntt,hmeoesrtaotfutrhesreegvaarlduiensgwtehreerabcaessoedfionnciedsetnitmaaltessolrespedoinneedntforinsgpeesctiieosn similar to the indicator species.
dEextpeocstuerdeincosintceemneadriiao,ndsalwyerfeoocdalciunlgaetsetdiofnorrateeasc,hitnacrigdeetnarlecseopitlorsesdpiemceinets ibnagseesdtioonn rlaetveesl,saonfdcboondtaymwieniagnhtts repored inth literature.
"rTihsikseevcaolluoagtiicoanltisskcaosnscelsusdmeedntthwaatsa"cponeduncateldewciotlhotghiecailnrtiesnkt"ofexcisotifmthpe laHQbeascteallciiunlenaitsegkd farsosmestshmeenmt.axIintmhuims caarleeaulcaornicoennstrwaetrieonmaadnde tuhseinNgOLAOEALELeqtuoaxlisciotry ebxecnecehdmsaroknse.. Within the calculasion spreadsheets, altemate
70 CONCLUSIONS
70 Bembic Inverbraie Community Structure and Function
Dmaatya bferoamsbigontihfitchaentbepnrtohbilcesmurivneDyraynRdutnh.e tNouxmceiryotuesstsfiisnhkdiiclatle htihsattofrilcvarlildyeraepnodrmteetdalincDorntyamRiunnatailosno
0
0090:89
USFW 0637
provide evidence for potential effectson the beathic communi.
72 Soil Invertebrate Community Soructureand Function
TcuhreensttrccornudrietiaonnsdffouunncdtaitonhoeftDhrey sRouiln iCnrveeerktesbitrea.teHocwoemvuemru,nisciyncdeoeeasrntohtwoarpmpseacromfporibseeata rsiisgkniufincdaenrt `pmrooublnetomsftmhaefyorraesgueltbafsroomfscoonmteamoirngaanntissbmesi(ne.gg.tiAedmeurpicinanthreobeianr,thshwoorr-maitilsssuher.ewBs,ascecd.o)nfoooudrcfhoaoidn. Chain models, it appears that this may be the case.
73 Fish Communities
IcownatasmisnhaotwinonthcurroruegnhtltyheprreesseunltsonefatrhetefaltahnedfaidllmionuncaolwabtiDoarsysaRyu,n.thaTthliasrvfailndfiinsgh wisefruertshuesrcseupptipbolretetdo bloycatthieonr.esuNletgsaotfivteheebfefnetchsicofincvoenrtaembirnataenttsoxiocnitythteesbtse,ntwhhiecrceotmomxiucniitytywamsayobsdierrevcetdlyataftfheectsafimseh cbeomrmeumniotvieeds,frionmthtahteasypsotretmi.on RoeftphoretsfoisfhhifsotoodribcaaslefiinshDkriylsRuarne (ailes.o baenntihmipcoritnavenrttepbtrcateeso)f mevaiydeanlcseo tphraetsesautggpersotbslaenmsetcoolougpipcealrrliesvke.l Icnoansdudmieorns, hdiugehtoledveilesaorfymteotxiaclistyw.ere notedi the fish, which may
74 Worm-eating Birds
.
Rriesskultdsueoftthoemfeotoadlsc,hafilnumoroiddee,l faonrdwoircmh-leoartoifnlguobrirodmsetshuacnhea.stheThAimserriicskanisroabsisnoicnidaitceadtew2itpohtetnhteisael cecoonltoagmicianlanrtisikn0theavsioainl arencde/poirorisn.earthworm tissue. Reportsofhistorical wildlife ills also suggest
7.5 Camivorous Birds
Rdueesutlosmoefatlhse,ffolouodricdhea,inanmdodTeilchfloorrcofalmuiovroormoeuthsabnier.ds sTuhcihs arsistkheisraesds-toacliahtaewdkwiitnhditchaetsee3cpootnernatmiailniasnks in the soilandorin small mamma tissue. Reporsof historical wildlife kills also suggest ecological risk t0 avian receplor.
76 Camisorous Mammals
Rinedsiuclattse oafptohteenftoiaold icshkaidnumeotodemedfaolrst,efrleusorriidael,lyanfedewdiicnghlcoarmofilvuoorrooumsetmhaanmem.alsAissucihskasitahsesroecdiaftoexd with these contaminantsi th soil and/or in small mammal issue. Reportsofhistorical wildlife kills also suggest ecological isk to mammalian receptors.
77 Piscivorous Mammals
Rdueesutlosmoefatlhse. ffoluoodricdhea,iannmdoidceh!lfoorpoifslcuiovroomreotuhsanme.ammTahilssissukchisaassstohceimatiendkwiinthditchaetsaee cpootnetnatmiialnarnistks. in the soil andor in fish issue. Reportsofhistorical wildlife kill also suggest ecological isk to mammalian receptors.
78 Omnivorous Mammals
~
st 005-30
leew NR38
z-
tReesnulettosmseooftttalhas,nfohouroadricinhcaeainhanmdtoidmseseulh.lfoorrRooefmpuaoiorvrsoormooefuthshinsmteao.rmimcaTalhliwssilsiduslckihfei1ksihlselssorcaslisssosedosngwgiienhsdittchaeetcseoe3lcopgooitnceaanlmtiiFanlkainstsk5
mammalin receptors.
75 Insecivorous Mammals
pReosurlntssorf lthedfootdo mcheaailns.mofduoerlidfeo,r ainnsdewciicvholrooruosflmuaamrommaelthsanseu,ch Tshsitsheiskhasraasislocsihatreedwwiintdhictahteesea SFoomanmienaontsfheinsthhreeswositaaknednoroninsieea,ruwrohrrmstuigssguees.tPehcyoslioogliocgailciaslks.soIonrmdadliivsieosn,tsopetchiefidciarlelcyt ptoeteontaitahl sFukesfor Tthhesschoruelwds,prseosemnet pofrotbhleesemsantoimoarlgsanhiasdmsighhacofneceednotnrastihorneswsofanmdeaolesransdmafllomraimdmainlrsiosn mhaesmstmealdiune rteocedpiteotrasr,y toxiiy. Reporesof historical wilde Kil also suggest ecological risk
710 Herbivorous Mammals
pResoulvs orfistkhdeufsotodmcehalasn,mfoudoreildef,orahderrbiicvholrooruasflmaaomrommaeltshanuec,hThai5strhieskmieaadsosowcivaotleed wiindtihcatthees3e
ESeommveaamfitnhaetsse ianhiemalsasilhaadndhoigrhicopnacnetntirsatsiuo.nsIonfmaeddailtison1tnodthfeludoirriedcet ipnottehnetiiatlisrsiuseks.forTthhies lceousl,d
.
frosieen,prRoeblpeamnss0ofhairorgicsa hwtidfeeedkoimllsvoallsso ssnudggteshtrecsomlaolglicmaalmrmiaskltsoomnatmhmeasliiteandureec0eptdoirest.ary
80 SUMMARY
HSDeuivrneidrnnegesstbshnoipnmsantleiswjebevoesrrainln ahyinesdarhsae,drudal.tfTuchmaeensese,wnehorroramtgaialczibeteisheahsviishoaarv,leseiinflfcaelnsusgdaeotfdhgnracetcehisnosafdduDilrntycciRdaeuennlc,eCorafebesnko,irmhlaaslorpecopasavurerisee,,d
mTmhionnftaesrmrdeerita,nnadgndarthohrmisgDhhramyvoerRaaall.istoyTrhaeepeorraetcserduossnsuolfmlethraiogsuersciasisahessskeioslfslismeinthDesrrudyp.pRoIurntn,aisainsdoewriilodpretohbakltieelmfsf(lwueei.ntt dfheirseo)hmertfdho,er
EeDelrhayitdReuduontuosCrefneorrsiesctah,endmdellaevdemolaws,yofsbeemeahdamavl,isn,agnfaldduovfreiiprdasere,ieaafnnfeadcbtmsiiocehsltohtrehaaeftlcauocelroapgmrieectshecanontemontmhuattnhsessipc.hpatTohiehbsaeebirecfefhseuecltsaoinmdoaffyetdbh,ee
co{oanknsidsslstaednsntmiweniantgthe.,hneuAmcteoanrcomluiusnsiioomvnuesmorf,cttohhmeepssoyukmnpdaissoewmsessrmmeeannptir.feesseItnnbaiyndtDdhreiyhnRerafdno whsepeeSccihfaoirmcaacplileoyauttinheodoshefastfidwueenrtriifdsieuoddxi3seidTcIi,Cn snhiodsr
oTeynmaileytryesdeenitf3ierdeaCto0mpounydssieinnh,eanBcNeArssnclay)mtaetrcfourltdhenrovtebsetaicgcautiroant.elyThideenDtiufPieodn.t lTahnedsfiellcohmtpoduranidnss
-
rte Dry Run i he only apparent source ofichiorofuoromethane in sil adjacent o he eam.
=
080.37
LISFW 0836
LITERATURE CITED
bAygeSncciyefnocresToIxnitcemSautbisotnaanlceIsnca.nUdnDdieseaUs.Se. ReDgeipsaeryc(mAeTnSoDfR)H.eal1t9h90a.ndTHuomaxniSecrviPacreolsfiCloeofngorraAicltucmNoia.nu2lm0,5-9P3re-p0a6r0e6d Research Triangle Pak, NC. ALygeSncciyefnocresToIxnitcemSatuiobnalsItnea.andUnDncdieserassUeSR.egDiespaayre(mAeTnStDoRf).Hea1l9t9h0.aTnodxiHcuomloagnicSaelrvPircoefsleCoonraaMcatngNaon.es2e0.5-9P5re.p0a6r0e6d Research Triangle Park, NC. AbygeSncciyefnocresToIxnitcemSautbisontaalncIense.anUdndDiesreaUs.Se. ReDgeipsatrrym(eAnTtSoDfR)H.eal1t9h91a.ndTaHsuimcoalnogiScearlviPcersoCfonlomeracVtanNaod.iu2m0,5-9P5r-e0p6a0r6e.d Research Triangle Park, NC. bAygeSncciyefnocresToIxnitcemSauibosntaalncIensc.anUdndDeirseUa.sSe.ReDgeisptarrytm(enAtTSoDfRH)e.alt1h993a.ndTHuamaxniSecrviaPcreolsfiColoenfgtoraicBtecrNyola.ia2lm0.5-9P3re-p0a6r0e6d Research Triangle Park, NC. AScgieenncceysfIonrteTmoaxtiiconSaulbsrac.ncUensdaenrdU.DS.iseDaseeRpeagirsaomyfHe(eAnaTSltDtR)n.d H19u9m6.anTSearvisceis CconatPrrlaocftoiNloge,fio2r0c5N-ia9c3kl.e0l6,06P.reRpeasreeadrbchy Triangle Park, NC. dAmobgrso"seJ, FAoMo,d Sci5. TLeacrhsonno.la1n3d18L1F-.18B1o7.rzaieca. 1976. "Longterm txicalogial assessment ofnickel i rats and Barbour, RW. and WH. Davis. 1974. Mammalsof Kentucky. Lexington, KY: UniversiofKentucky Press, 3225. B19a8m6i.hUosuesre',sLMWa.nGe.fWo.rEScuotleorgiScaMl.RBsakrAeslslessm1.enBte.auPcuhbalmicpa,rRonHN.uGmabredrne2r6,79E., LOiRnNdLe-r,63R5.1V.. OENneviilrlonamnedntAalE.SeRrovsiecens Division, Osk Ridge National Laboratey, Oak Ridge, TN. sBe3ye2r,)3W7N5.38EE. Conner, and 5. Gerould. 1994. "Estimates of Soil Ingestion by WildlifeJ". Wid. Marae. hBerpoaotkost,oxiL.cicy19b8y8.cap"pIenrh.i"biPthi.onD. oDfisNseArDaPtHio-nc,yRtuotcgherrsomUeniverresdiu,cuNseewaBnrduansnweincuka,tNo.nJof acute diethylnivosamine BYourlk,JN.YA:nAdJl.fFreaAdm.aKnndoIp.rf,,1I9n7c7., The AudubonSociey Feld Guide to North American Birds, Eastern Region New BurtonP,. 1989. Birdsof reyofthe World. New York, NY: WH. Sith Publishers Byemum, RU, RE, Eckaret, LL. Hopkins. 1974. Vanadium, Washington,D.C. National AcademyofSciences.
5 005.02
CParlydsieorl,ogWy,A.244a:nRdEOE.IJ-.RBErDaSu.n, 1983. "Scaling of osmotic regulation in mammals and bids." American Journal of
-
CSiasscarnoopnvaag,esV.a,ndL.AlBvoewolmaarnT,yapnedILJCRelWtrsigJh. tTox1i9c8o4l.. E"nTvoixrionc,ieyHeoafltMhea13l:i8c45-o8n5s6.in the Lung: Effects 0a Alveolar
CSleiarkT,ecDk.r.13:3139789-.341"Lead Concenaions: Bats vi. TeresialMammals Collected neaar Major Highway." Emiron
DCheiacnks,"C..T.oBxMic,olHaLregtiss.nd$T3PS0.3H-a3rg1i8s.. 1991. "EffoefcZitne ToxioncTihytroyid Funcion andHistologiyn Broiler
"DTehGeraUanti,veRrsMi.tyaonfdMDa.sD.saRcuhduisses198P3r.essN.ewEnglandWildife: Habit, Natural History. and Distribution. Ambers, MA.
+ DDeemMeasyuoia,lAP.anMt.sC.anTdayAlqourataincdLKifWe.." TCaRvClrC.rit1i9c8a2l. Re"vEifefwecstsion fEnCvoiprpoenmreonntaHluCmoannisrd,l,Lab1o2r(aGt)o1r8y5-a2n5d5.Farm Animals,
EDnivxiorno.nRmeLn.taRlJ.HeaSlhtehriPness,peacnidveLsP.. 3Le0e5.3-61397.9. "Assessment of Environmental Factors AfTecing Male Feral."
Edwards, CA. 2nd IR. Lofy. 1977. The BiologyofEarthworm. JohnWileyand Sons, NewYork,NY.
!
Ewh.rlich, P.R., D.S. Dobkin, and D. Wheye. 1988. The Birders Handbook. SimonandSchuster, Fireside. New York. 785
-
ESiesrlevri,eR.Bi1o9l86o,gi"aC!hRreopomritu,m8H1a.z8ar6d.s t0opF.ish, Wildlife, and Inverebraes: a Synoptic Review." US.Fishand Wildlife
SEeisrlveirc,eR.Bio1l9o8g8i5c,a"lARrespeonritc8H5a(z1.a1r2d)s, o Fish, Wildlife, and Inveriebeats: A Synoptic Review." US. Fish and Wilde
=
EWiisllerd,lRB.io1l9o8g80i,cal"LReepaodrtH.az$a5r01d.s14t)o.Fish, Wis, and nveribrates: A Synopic Review. United SatesFishand
-
EI1v3ma7n6e,. sA"EP3,f.0f.e72c0nt4sdo:W7f1.3CGh.IrnD.oaiSmlt.ieuv1em9n,i7n41tDh".eThCLeaJnE.afDedacivtaisneosEfSn,voEidXrio.numSmetnaCtnh.le"ryoN.amtRt..eAR.oesnA.btbhCootusPn,rco.Mx.iCmaIannl.k,aT,NubRLu.ClBeCsiNodof.tsh,1e50Ra1a7nt.dKi1Ld6F.n3epJ.ya.w"arLasbi..
:
FCloenmcienngi.atWiJo.nsainndJepC.Aa.nSecsheulQeura.il1.9"88E.nv"iIrnfolnumeenncteoalfTtohseiMcloegytoanfdhFClhuooermididseeAd7m(i1n0)i8s3i1a-i8o4n6.on Toxiciy and Fluoride
-
FEluermoipnega,n SWuJrf,inCg.sE.." AGrrcahe.,ECmA.. CoSncth.uleTors,icaonld. C1M66.):B4u8n3ck-.90.1987, "Effcsof Oral Doses of Fluoride an Nesting
L
GMiasnnguatnsoess,eGA.dmaindniMs.aT,iiMonu"ayNe.wro1r9o8s2i.co"lA.li3e7r5s-i8o1n.s in Brain Dopamine and GABA Following Inorganic or Organic
Goldman, E.A. 1950. Raccoons ofNorth andMiddle America. Washingion, DC: U.S. Fish and Wild. Service.
54
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USFW 0641
fects on Aquatic Biota: 1994 Revision. ESTER/TM-961R,Martin Mariera Energy Sysiems, Inc. Sure, .W. 1977. "Effoif Fluoride on Livestock." JournalofOccupational Medicine. 19(1):40-45. Tyson, E.L. 1950. "Summer Food Habitsofthe Raccoon in Southwest Washington." J. Mammal. 31144844. UWaSt.erEnRveigruolantmieonntsalanPdroStteacntdiaorndsA,geCncry i(U.atSn.deESPtrAa)n.diara1d9s81D.iviAsnioenx,pWoassuhrienagntdorni,skD.Ca.sseEsPsAm=e4n0t/f4o.r8a5r.s0en0i5c.. Office of UReSg.alEantviiornosnamnedntSatlanPdraotredcst,ioCnriAtgeerinacayn(dU.SSa.ndEaPrAd).s Di19v8i5s.ionA,mbWaisehninwgattoenr,qDu.alCi.ty criteriaforarsenic. OfficeofWater UF.rSe.siEwnavtierronamnednMtaarlinPreotOerctgiaonnisAmgse.ncUyni(tUe.dS.StEaPtAe)s.En1v9i8r5o.nmMenettalhoPrdootsrecMteioansuArgienngcyt.heEAPcAi/eSOTAs-i8cSi/t0o1f3E.fluents to + UWass.hiEnngviiorno,nDm.eCn.talEPPAr/o5t0e/c1i-o8n9A1g00e2n.cy (US. EPA). 1989. Risk Assessment Guidance for Superfund. Volume I.
LUi.Sf.e EFnevdierroanlmReengtiastlePr.rotVeocltiuomneAg57e.ncNoy.(U2.4S6..EDPeAc).em1b9e9r2.22Ambien: Water Quality Criteriafor the ProtectionofAquatic USStSs.esEnEvnivriornomnemnetnatlalPrPortoetcetcitoinonAgAegennccyy(,U.OSf.fiEcePAo)f.R19e93.sWialendidfDaeeEvxerploospcumreenhtF,acWtaosrhsiHnagntdobno,oDk..C.VoElPuAm/eGIOoOfRI9l.31Un8i7tae.d oUf.SS.edEinmveinrto-nAmsesnotcailatPerdotCeocnttiaonmiAngaentnscywi(tUh.FSr. eEsPhAw)a.te1r9I94m.veMrteetbhraoedss. fUonriMteedasSutartiensgEtnhveiTrsoincmiesnyta]ndProBtieocatcicounmAugleatnicoyn EPAGQOR 94/026,
UReSg.ioEnnv[IilroBnTmAeGn.taTlecPhrontieccatlioSnupApgoerntcSyec(tUio.nS.. EPPhAil)a.de1lp9h9i5a.,RPeAv.ised Region lll BTAG Benchmark Values. US. EPA NVaatnioZnianldeRreesneaBrackhkeCrouanncdilJ.ofJCaawnoardskai,.As1s9o8c0i.ateEfCeocmtsmionfeVeanSacideinutmifiicntChrietCerainaafdoiraEnnvEinrvoinrmoennmtenatl,QuOalriatwy.a, Canad: VPelneunguompaPlr,esBs., aNenwdYTo.D.rkL,ucNkYe.y. 1978. Metal Toxicity in Mommas: 2. Chemical Tasiciy ofMetals andfesaloids. WMiiecsreol,som1e.s f1r.Co.m LRaetuTtizss,ueLs:.DiDamiofnfdceannidalHVI.nhiGbeiltiboonina.nd19S7i1m.ula"tAiroynl bHyydBreonczaorfbloanvo(nBeesniznod(aO)rpgyarneince)SoHlyvednrtosx."ylAarschin Biochem. Biophys. 184:78.86 Wixson, B.G. and BE. Davi. 1993. "Lead inSoil" Lead in Soil Task Force, Science Reviews, Northwood. 132 pp. Woolson, E.A. 1975. Arsenical pesticides. ACS Ser T:1 - 176 (a cd in Eisler, 1999)
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.
INTEROFFICE MEMORANDUM
Date: 17-Feb-1998 11:20am EDT From: R|IRTCOHBEERRLT L. RITCHEY DeTepftNo: E8P6-3E-n4v27.1
TO: See Below
`Subject: EPA Visit to Dry Run Landfill
11,t1osDrhyosRtuend tLoadnadyf.ila, pre-scheduled visit by Mike Taino, EPA Region is aMFiuknedwiOgns-aSscseingeneCdootordEiPnAa'tosrD,rRAysusnuche,ffhoertsgseetvseirnavlowlveeedkusnadgeor. He Sexupplearifneudndth/aCtEhRiCsLrAolwehies ndetahleirneg iwsiathpsoitteunattiiaoln"srtehmaotvraelq"uiprroeject. He ghieamfnmidenldeeiswahtraeetmaetrdteeisnaptloionrnsees(ptihosunrsseerqseumiworhevidaclth)oaaarsgeiolvpoepnnogesiremdmteetdromitahitneeinrangteruerodeu..p MtHhieaktawosuald Givi Enagris.neer with an Environmental Masters and has been with EPA
What drew Mike into this Dry Run effort is thegercepionby EPA tfohratthoiusrislaonbdfviilolumsalyyibnfeluehncaedving bayn cilmapiamcstoofnhiDsrtyoricRaulncCartteleek,.fish, The basis aasnsdeostshmeernwtildrieipfoertimopnacDtrsywRhuinc.h aMriekereifnldeicctaedteidntthhaet EhePAhardiskread the c{oGnc4luisnifoonrsma(tairolny)woefsiubsmiterdeportoanndDraylsFgunh.asWaivtahiltahbaltebfaochkigmrotuhned, he wasPrperseednitsaptoisoends taondbeQli&eAvestehsastiiohnesrewiatrhoprWooboldyemIsrealtanDdraynd DRunaCnrWeekbeer `crweedriebisluictycoefsstfhuel EinPcAarsiisnkgasssereisosumsendto.ubtMioknetahteosnceiepnocientasntdated sTiokmeetrheialnlgy ickane'*tsroel|y oanmthdiesceidsingo!whWteacdiidonasckanroewnleeeddgeed,thiattsionunds tg1hi9as9ta5sitswohceaisathnaeoddtarinefoercpocimusrforldeuedorosifiden"scb,el.aecxkplwWaaeitanesre"do,odbuiurstcceuoxsrprsleecadtiitnvheeedancutthmie oecnarsuosauens,d {duheicshignwiilmpbreovinecmoernptosraatnedd ianddoiuironnaelwmpoenrimtiotringwhaenndi pfsefrimniatllryequirements issu\ebde.liWeeve Miindkiecaistoefd ohuerodpeisniiroentothbaetgwihnawtowrekinhgavoen atlhroesaedy AdSoAnPe. Hgedrwehsaertvwedeplthe arifngohtdtooudnedcedrethoethneerwwipseer,miintclwiuldlinrges2aldveecitshieonisfsoued.o emolrsWowesettuocdooyuk.lMdHidokoweetavonedtrh,wehhLaeatnwdeaflissledawenoaudrldlhyehbgaeovtiunasgtgterooudobld,e toutrh.inHkoingdoofgwshnaott thaalvkienga abnadckhgerohuanddfienwdeqauleisnfigownist.h lEavnedrfyiltsh,ing lwoeokdeiddgmooosdt.ofDrytheRun AGsreDeakndisdunmomlarhiazveedthaeftaeprpwearadrsa,nMciekoefcbaeimnegtaodvseereseugllyy eacndteheddaitdna'ilt.. 1 beMliiekveewhilel cbaenathealuprsmteabeitliinzegEwPitAh'sEPunAatnteaxcthMedoenmdotafiyonnaPlhirleaadcetlipohniat.o
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TO: WILLIAM H. HOPKINS
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TO: H. DAVID RAMSEY. JR.
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CC: GEORGE WOYTOWICH
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|
May 14, 1998
RETURCNERTRIEFCIEEIDPTMARIELQUE-STED
HUs..S. SaErnavhiroLn.meCnatsaplarPr(o3tHeW3c2t)ion Agency 8P4h1ilaCdheelspthniuat, BuPAildi1n9g107
RE: EPA Draft Report, Ory Run Creek, November 1997
Dear Ms. Caspar:
rreepgoarrtdTihnaagnndktyhfeoourvamfleoierdtiiptnrygoviwodfiitnhtgheDuDPuroPenoptnotrton'WsasFhceiobnnrgcutlauorsnyioW2n3os,r.ks199a8,coptyo ohfeartheoursucbojneccetrns
time pTrheohipbuirtpeodsereovfietwhiinsgleinttoeurrimseettoindgo.cumAentsumtmhaorsye provided, followed by a more detailed discussion.
ocfonckeerynscomamnedntostheirss
which
dreipsocrutsWseitoornecroeongmnoviFezeebsroutmaheraytof2t3hethreariespieomdrptlitchwaeetirpoernvosisepwetechadtt oiftsheamakc"ioDn-rgaaufttc"hhoarncsgoepsyi.ndtiocWahtthieildse
doruarft they
dtoidacncotompilnitsehnd,thiusp.on Wreevdioewnowte bbeelliieevvee tthhaatt apromsapjeocrtrweawsritoeffewroeudl.d beThenreecfeosrsea,ry
we have elected instead to limit our coments to this letter.
beingWeadvsehrarseelyanafifnetcetreeds,t ainnddeitfersmo,inidnegterwmhientihnegr Dthrey our opinion that the conclusions of the draft report
RcuanuseC.reekHowheavserb,eenit oris is with respect to' these
2q3uesmteietoinnsg,areitnoits osuurppoirntteendtbytoawvoariklawbiltehdyaotau.toAsdesiingdnicaatneddcoantsioduerrFaebruary
cbeohlilnadborthaetivreisknexats-ssestsempentto. advance a scientific understanding of the issues
|
Sincerely yours,
SRro.berEtnviL.ronRmietncthaely Control Consultant Washington Works
Attachment how: 196751
09.7
USEPA 062 |
|
BE Roger Zola <ZPFELOWMWPS.ATEMALOUPONT.COM> on 091419 Tor Roger J BfeAERupone Sie (6:8 ENVIROMENTAL SAMPUNGI24- u1r998FC-143 Results Avaas ------------------------ SFDraucobeuj::ectWV:eEdR,PA1L2164W3IJGuRAneLs1u<9l9t8Ws1IA3v:Ga3i8Nl:u0Lb0lVemrLTo-eEpmaawtiel.p.d(usMpeo-tnotaw.i1ccoh.n)> T ERToI:TBCHNREUY"RRE<NOR5.IAHTGAaRCmTpaTHiELN.aE-duR-CpHoLaanAnt&iRLcwlTo.u.pTdsuE,apAo-nS-tLaEcENoClRuGSOs.D0,X0,"-DDAIUANRPLIEOLENEALTNN.DAC"A.ONLWSEL,BER"~ROBERT L. SSIRRELEIANRDIOSpaCPaaiHL.FRaenmAaeaLmliRa.lidlwGduupappouonppnatotcn-co.emocasuo,sn1,s,"R"GIRECoOHgReAGrREDJ.HAOYKTTIiORpSNfCeEHiCNtHER, TR* DCAHoeDnlEtiOevvneetrTa-yit-ydoTpanet::e:OI1aWL:1eN0T.dI,PeTmA2aR4iSC/JNudInuRXpEo1Dn9p)t98cBoe1Om3Us:N4D4A:R0Y0=-BSOoTundary_(ID_2NbORBOXIUENFSQRO/NTA)NFTioospttoyirpntaga:ndcaeHt:AeI:LnoWremda, 24 Sun 1998 13142100 EF ----------------------------
RSDauitbzej:evcetWs:eedi,Foon-2:1643g1u.n0Dac1a9.98fro1m1:L0a7n:d0f0il2l0s7 ACTooenpytoparnteae:n-cteyB:poe:ncoartmesaxlt/plain
June 24, 1998 Details of FGri43 Sample Data Prom CHEN HILL Available To-date: tocation sitbea'cseaspled lossesteiaonn Result
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EID082057
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|
INTEROFFICE MEMORANDUM
TTOO:: JLOYHNNWOOR.D MK.ATHIERWESLAND CCCC:: GRaIrCyHAWR.D AKleKsIeRlSCHNER, JR Subject: Dry Run Landfill
DFartoem:: TDeelpt:No:
T08h-oAmuags-1R9.98Wal1d1r:o3n3am WAPELDD-RPOOTWRER/SERVICE 304-863-2485
(( MIARTEHLEARNSD))
(( KKILRESSCEHLRGAH ))
sLlaonwdfirlalt.eI. caTTmhheeepiolnenvdtehliissofbmeoirtnhngeinpdgroanaidtnehadbaoduttdorot0ph8ep30edsttraoebaolmuo,tokaatatfoaoDtvreyorryR.usno. chOahndecmkoyipnewgnaeydonouttht,ehevIparlrovagenreaisnstl.iottolHneee, aoeflasorRliicseharairddt'hhseiswhamasonrdistnogla,dndtaonhedtuwsraansidijhtuest pcorofomfppaebrreitfsyoornel)idnaear.tk.#0R(0i71)c,haroIdnetCooaotnksttsrohumeect2i,wo0a0nt0ehrafscsamilpenlvseetlsalla(enjddustaonecfoouraptlveitshuoeafl ntcohhteeckaolultdfaamtlshleatsitosl0ei0l1dfs.awnedrTehaelssowtaatyieinrnsgtwaalbselheidrnudns.niiltngThfetenhcrseotsurgehaanmdtwhahesamybtobutarhlbeisdbutin Lcdilonewean,r.to`anTadhbeWouritelbuairs tEshatoriullslanhdaas flooitontsotfaolrlaescdotiabvuitmteytbeadyloowngnda.theethaaratt,tthheweasprloifpnaeeirrtlyy hpfiresnocpeee,nrdtymqywuihgteueensshaewloostuo.lddesbIiefretIso.gegtivSeomaehocinhmeanecaiess,ireurI nmancaicnyegscshteheocnkiotlnol otuhfrirnogms down there tomorrow.
Tom
000.7%
55
EID030998 -
|
INTEROFFICE MEMORANDUM
DFartoem:: DTeeplt:No:
T0h9o-mAaugs-1R.998Wal0d3r:o5n7pm WPAPLDD-RPOOTWRE|R/SERVICE 304-863-2489
TTOO:: JLOYHNNWORO.D MK.ATHIERWESLAND
(( MIARTEHLEAWNSD ))
cCcC:: GRaIsCyHAWR.D AKleKsIeRlSCHNER, JR
(( KKLIERSSECLHGRHA ))
Subject: DRY RUN LANDFILL
has now dIracianmeedidnowtnodaabyouatt 3140t0o t4ofceehte.ck oInaDgraiynRutno.ok Tshaemplpeosnd d(ifdoryevsitseuradlayi,nsaptectaiboountontlhye),2,0j0u0s!t bleelveolw athned a#0g0a1inOuattfatlhle, as I aptrotpheerty2,l0i0n0e. levTehle oiustfaallslo sisligsthitllly tpurrebtitdy. tuTrhbeidsaamnpdletheatsatmheple ptrheopsetrrteyamlinjeustisbesytiolnld tchleearf.enceWaitlbtuhre'sprcoaptetlretywelrinee.wallIogwoitng in osdeoverraflrompicttheuressampbloethatyesttheeroduatyfaalnld btuotdayi.t doYeosu cnoatn nsomteillcelaikne yloeuachaaltle.haveTI awilllookb.ringItthaelmkeddowntointhethSeemcuirnittyheGmuoarrndinagt tahned lfeitll aanndd hweentsabiadcktheupsatmhee cooludplreosadasjusltastbewyeoenkd cthaemeodlodwn1,0o0n0'4-wshaemeplleers psooimnet.wackIy,awmegeodipnegrhtaopschbeecikngthgatrowountupsootnheraen.d sePerobiflemI icsa,n Ifind wdoint'htmekln!ow whIatheatrhethsetuyffgrolwookasloltikeo.f thIatmaysthuaffveovteortaikneMReoiggser Ciotunstuyr.e loAosksIawrliottelitkheisrmaeisnsaogne,thelowoakyi!ng oJuutstmywhaotffiwceenweienddoawt, the landfill... More solids in the stream...
Tom
00.34
EIDO17500
| |
AGENDA 8/11/98 DRY RUN LANDFILL
Commitment to work together Purpose of Collaborative Effort Materials Potentially Landfilled DuPont Inputs on what to look for
* Mammalian effects * Organofluorides + TICs 7/22/98 split Sample Results Collaborative Program Proposal
009285
USEPA 0821
scope devAelcooplmleanbto,radtaitvae ecoflfloercttiboent,weeannd EiPnAtearnpdreDuPont, including
undertaken
to
characterize
environmental
tation, will conditions in order
be to:
1) investigate potential causes of environmental effects
2) dcoentsetrimtiuneentisf caanudseesxpoarseurecpoanntehcwtaeyds to landfill
,
8/11/98
- 5 035..8%
EID017942
8S
-
dG2fio3rsl3opl4uoo2pws4ia11nl1:g.hiiMnaTtsheiirgsinaillfsiicsatknintnogwqnrueaopnrrteisstueisneptsescattaedgsootomodehaftviaemiethbeieenfnfhoisrsettnotrCyotosiDvnreciyivudoRecuenthe
story for materials meeting this criteria.
bdfoiiirylts/esrrhubb(bocltoetaolfm-rfoaimsrhepdl(abcnooitallee-rxfsci)arveadtiaonndsalternate fuels boilers) baiboscoarkbeed biosludge bsiupoe-rwnaasttee ptornedatmdeinrtt settlings (equalization tank) paoyllyoancerteaslinsresins peollaysetsotmeerricrepsoilnysmers paoclryyvliincylpolbyumteyrrasl pfolluyoertohpyolleynmeers wcoaorddboard gslcarsasp metal asbestos
8/11/98
I
009-25
EID000244
-- qe-- eye
- Group 1 Appendix: Major monomers and constituents of Group 1 resins.
RESIN polyacetal resins aylon resins
polyester resins : elastomeric polymers acrylic polymers
polyvinyl butyral fluoropolymers polyethylene
MMAOJNOORMERS/CONSTITUENTS formaldehyde hadeixpaimcethaycliedne diamine dcoadpercoalnaecdtiaomic acid ettehryalpehntehaglilcycaoclide butylene glycol*
eetthhyylleennee/-mpertohpayclreynlei-chexaacdiidenceopoellyamsetrosm*er+ butylene/poly (alkylene ether)phthalatet meetthhyyllamcertylhaatcerylate ne-tbhuytlylmemtehtahcarcyrlaytleate miestohbauctrylylimcethaaccirdylate pbuotlyyrvailndyelhyadlecohol tetra ethylene glycol diheptancate hteextarfalfulouroorporeotphyylleennee ethylene
ethylene
* = mot handled at manufacturing site as monomers (already polymers)
9/1/98
009.8%
EID000245
:
7 OcGhSreoSmwiicla2y:lsheuLsoSewrceasinesdatstorigavtceenttivseo,lOurptyleaRscuthinecmii"zcaeanrlcssr,ilolrfefi{rinnitcgeleruredasentttswh,heicsfuhorlfclaoocuwtliadnngts.
mgataics.nk.ettesnw.dhnicciehnscuchloeaumtliidconab.les.rpargessT.ehnetabTsiisontrbde1e5ntmsin.noitmecitcso.m.palneooutrnetassdslotnaoboFcrirlateteaortrsey.osruch a
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faocretmiicc aacciidd
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ccahrlboornoftoertmra chloride
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dbiipfhleunoyrlochalnodrobniepthehnaynle o(xFi-2d2e)
trmeitchhylloernoetrcihfllouroirdoeethane (F-113)
ttreitcrhalcohrlooertoheytlheynlesne
methyl chloroform
mp-hcerneoslol
hbeyndzryolxyeatlhcyolholcellulose
Tmeotlhuyelneethyl ketone
pshiyoldlirycoeoctnahryboloienlnseoigllsycol ethers
asumcmcoinniiucm ethylene
paglecyricfdollyorooctanoate
dgia-s2oleitnheylhexoate numerous hindered
pohfenpoollyceotmhpyoluenndesglycol
B alkaIlaitniEec baantShtnyecdrriiecse AdlietseerlnatfueelFuels Bofler flyash (one time event)
8/12/98
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EID000246
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--
000.21
a "RRogoer gerJ. Tota"Zotar" <ZPFELOWWPS.AT.EMAILD_UDPUOPNOTN.TC.OCMO>M>oon 03114199
To: Roger J ZplelAEDuPont Siblect: (C8 REVIEWS/10-55-19981C.8 Review Date
SDPuarbtoeaj::ectT":hRuO,cB-E8R1T0RLeS.veipReIw1T9C9DH8aEtYe1"1:<28R:I0T0CHEORTL&wps-al.emsil.dupont.com> <TZGoAArNRIZKBOAeSOr,Tn@awrPpd.aEJ-.aR1<e-ZieAlmNlaIyiKlO<.LRdJEuEIpCLoSLnO2tCB.-JcAEoLNn.A>EN,MOATIE"LSR.LoD.gUEePNrOAKLJT.L..CDTOUiNPp>Of,NeTls.TCROINN>I,GA*RIZSAIDOROS J. <<HAITTPSORTREEuvpLs-Oalew.meamipla.ialdu.pd-ounpatonct1o.mc.>on,>,"RO"BDEARNTIERL. A.MATWTESBOENR-<<HEIBEAROCAGKuwSpaO-aDl.DemaEaniawll.p.ddueuppoo-nntt.acco1onn>,,s DAWN D JACKSON <CeHr I"GH.LDIAOVITDERwANpSEeY-, aJlRd..u"pso<onRtAucNLSoEmlY>@.,uwpAsn-dazle.semVaiMla.ldiunpoownstk.icos>, JOHN K NIGLIORE <<SMRAALGIGNZZLA11,C.GEEMEXANAINLLAL..ADNUDRUNOPONOOTNT.TT.CEOCEMOS>NS,S,LMCaruariigceSAksatgogrsga <ASTORGNEISCOCVS>, RIoKbEa-cvtez7aiPoinn:cho1t.0<PINCHIRPENANOTESI.EHALL.DUPONT.CON> CDoenltievnetr-yt-ydpaet:e: tTehxut,/pl10aiSnep 1998 11:56:00 207 PIonsptoirntga-ndcea:ternoTrhmua,l 10 Sep 1998 11:43:00 EDT A-type: MAIL
TuphsetaCi-r8srsemvailelw hcaosnfebreeenncesatrocfao.r 12T:e3n0-t4a1t3i0veOcAtgoebnedra 5appineartshebeBl2o1w.
Vciescietpotriso:nietI wciallll early enough.
bmee. arrWaengciannggyooutro
pcaasfseetserainadfyoorulusnhcohuldifplyoaun
taorrihvaeve
Craig and Andrea: Please feel free to attend. Let me know.
AGENDA: 10/5/98 C-8 Review . - Funcctioo:n awnhdatusein te 7
=- VMeonldeocrulaanrdsctoraupcattuirteorandinbfiocrpmeartsiioentence - Toxicology
. 60w9n5s
[EID082020
. - GlobaFlLEtReaMasnasgtermuecntturesystem
--
RGPoeradoludsuc,cttioPnSrotgaarnaadrmdreeShpuilmpamcaervmyieewn;t
emafsfsortbaiparnocgeress
+
--
DPrlyuohcuonpoLlyamnearrsindisposal Sampling daca
history
. - 1040Government Communications - rPeerrmits = Drinking Water
. Risk Assessment Program
- Crista Kanagesent Plans
(069.35
ED082021
|
+r ou. . .:
nen
oWeaare es PPot mwe r11
September 11, 1998
RETURNCERRTEICFEIIEPDT HRAEIQLUES-TED
MIrn.dusJtorhinalG. WaBsrtietveSce,ctiGoenologist GOfofoisceeRuonf WRoaatder Resources, WV-DEP Fairmont, WV 26554
Dear John,
LandfiDlulr,inygououraskSeedptmeenbteor s1e0,nd1y9o9u8 to EPA's question about changes we
cthoenfesreevnecne ictaelmls had made in the
wI itshummEaPArizreedgaarsdinogurDarynswReurn 1993-1994 timeframe.
changeAss iinndtihceatendatuwrheenof1 tchoeverweadstethoisr attempting to correlate these changes
mthaeterpihayls,icawles aorfe to any effects.
sthiempllyandrfeiplolr,tiwnigthout It would be our
ceJcouond-fgeemfrefenentcctet.hacatlTlhmiosstthwatooufltdhtehebaesellfecughraattnhigeoersnsswuoopfuploedrftfehedacvtbeydTaoEtPweA'pstroobraaetbveilllaiettaisytonofthdeuanring the
atnniiydm-e1fq9ru8ae0ms'etsi.opnredaEabPotAuetdalcstohhaencigroemsuennddtueerrdisntgathnadttihantgthooerfqouttehhasettriohnitsitmaeobfroryuatmoeftshaelils1e9gp9ar3to-ib1oa9nb9,l4yanndot that
baeplporwo.priate. However, since you had asked for the sumary, I am including it
1) Si1o9mm9pe2rovtgeorapdaersoddiufocffterpeponeltryafcoserttmaaablnicleriezasetirn.sp.r.owceerpseosliytnargcarnystlieatmmpiieodrneaetdusrtbeaesbg.iilninzOiennrlg.y.a.rotuond ipfionnltiyhsaehcerdyTlesarimenis.diensTphrhieassveenwtotuhleidn stptrhaoebbimalibizlseyr.,n5wotta%n,dprwemhsaiexcnihtmuwamnoucloidsnscuebeentrsiaintncicooernproeorsfaitned is stable.
2) mApatrtoedtruhiceatlss,amiwseeatlcishnoaengiaesndcotrhteopaorsattbaeebdtitleiinrzeatrhnetcih-asontxgaiebdlaeanntdp,olfyoimrregrta.hnooxseT2h4es5a.ammeouTnhtisin the finished product is less than .lwtk.
3) Aifsinncditinhneegrartneiesouwnltoufotorlfetarsegclofovoberarlysalpoefrogohefraatomfvftao-lsupreee,cdusmcaietgenprioiflaiylcmaenartndtrotehldrauonudcgftihilloinbnsy TthaendfqiulalnetditaytoDfrypolRyuanceotcaclu,rrendyloena,chpyoelyaerstferro,m a1n99d3eltahsrotuogmhers199b5e.ing
Srv vn
009.35
EID000228
:
@ enim
N
John G. Britvec
-2-
Septenber 11, 1998
4) AisnstianldliicantgedtheprenveiwoubsiloysoltiodsOWRfialntderEpPrA,essinat199t4h,e pilnanptrepsairtea,tiotnhefor aSmiogunnitficoafntsloyrbeidncsroelaisdesd bienintghesSepnrtintgo Dorfy1R9u94n.landfill was
5) Ablisoosolaisdsindiincaftieldterprecvaikoeusfloyr,m,iwnhiAcuhgusitncr1e99a4s,edvebiobneagatnterdisposing of ncoenwcefnitlrtaetriopnresasndwapsutmmoorreeeftoftiaclienbtiomianssremtoovitnhge lsoalniddfsi.ll because the
6) BseecdaiumseentsofwesroelidrsemaocvecdumuilnatAiuognu,st,the199l3owteor mpaoinndtawians pdornadinecdapaancdity Wre-qOuMiRr,emenSttse.ps Awseryeoutakkennow,fothpirsevweanst dtohneereinleacsoemmuonficsaetdiiomnentwittho the receiving strean.
7) WSeeptbeemgbaenr,lan1d99f4i,llihnagvinagt cthoemplleotweedr stheectifoinrstofpatshse olnandtfhiellupipner section.
not ha1vealsionfionmdaitciaotnedonduwrhiantg tchheangSeesptetmhebernei10g,hbo1r9i9n8gcofnafremreerncmeaycahlalvethat we do iinnvtersotdiugcaetdinign tthhiiss saraemae.tine period and that we would hope that EPA is
Sincerely,
SRro.berEtnviL.ronRmietncthaely Control Consultant Washington Works
2070-2
009.25
EID000229
| N
INTEROFFICE NEINORANDUN
.
PDartoem: D3A0N-ISEeLp-A1.998wEs0E9R:26am OT
TDeeplt:Nor
WENEGBIENREOEARING PoLvERS 0-863-441s
Tor DANIEL A. WEBER
wemsRo)n
Subject: C-6 INFO SLIDES FOR RLR MESTING: 10/5/98
gg
EID091595
009.25
DRYRUN LAVDEILL: FC-143HISTORYStawRy
SUPERNATE POND SOIL DISPOSAL: - O7F100NETAORNSTHOEFBSOOTITLOMCOONFTATHIENINLGAND-FI65LLPPIMN F11C/-8184.3 DISROSED - ATNHDISBSUORIILEDWAISN LAATCELRAYM-OLVIENDEDTOSETPHAREATTEOPCOEFLLTHIEN L1A0N/9D1F.ILL
FC-143 GROUNDHATER AND SURFACE WATER MONITORING:
- BEGAN MONITORING ANNUALLY FOR FC-143 IN 1991.
- GROUNDWATER CONCENTRATIONS RANGE <1 - 15 PPB.
- LEACHATE CONC. AT O.F. 001 RANGES 30 - 200 PPR. + PRARNOGPEESRTY2 B-OU2N5DAPRPBY.STREAM CONCENTRATION
- DTAHTEA1R5E91PORATNENDUAALNNREUPAOLRLTY. TOSTTHIELLWVMDOENPITOBREIGNIGNNIANNGD WITH REPORTING ANVUALLY. + 1398 RESULTS: oLuETALCKEATTE001 == 5167 PePmB sSTtReERmM ##12 =- 14.6 ePeEsR PROP. BD. = 0.88 PB
0-7 POWND/YR FC-143 DISPOSED OF WITH BIOCAKE (530 PPB).
61/0906M; PODOUENSDS/NYORT OCFONTFALIUNOROFCP-O1L4Y3M.ER WASTE DISPOSAL BEGRN gg
z
EID091596
8
009.29
;
88 :
000556
INTEROFFICE MEMORANDUM
Date:
13-Oct-1998 05:11pm
ii
From:
DANIEL A. WEBER WEBERDA
Dept: Tel No:
ENGINEERING POLYMERS 8-863-4415
Subject: POTENTIAL FOAMING MATERIALS AT DRY RUN LANDFILL
FYI,
BASED ON A REVIEW OF GROUP 1 & 2 LISTED MATERIALS, BELOW IS A LIST OF MATERIALS WHICH MAY HAVE GONE TO DRY RUN LANDFILL THAT ARE KNOWN TO
CAUSE FOAM.
-
N-butyl benzene sulfonamide - this compound was identified in a sample of foam taken from a Dry Run Landfill leachate discharge.
stearic acid and salts polyethylene glycol ethers ammonium perfluorooctanoate
Triton X-100 (tm) - not specifically listed but contained in supernate dirt and possibly empty containers ucon ofl - not on group 1 & 2 list - biological foams - from biocake and bacteria growth in ponds
:
c09ses
Ei016841
o
INTEROFFICE MEMORANDUM
DFartoem:: DTeeplt N:o:
D2A9N-IOEctL-1A.998WEB1E0R:29am WEENBGEIRNDEAERING POLYMERS 8-863-4415
TO: See Below
Subject: FOAM AT DRY RUN LANDFILL
Jom,
I WENT DOWN TO DRY RUN LANDFILL TODAY WITH TOM WALDRON.
I NOTICED DISCHARGE
FOAM FORMING PIPE. THERE
DIOSWNCURIRNETNHTELYLNOWOERPONPDONDDIBSECLHAORWGETHETOLDERAYCHARTUEN
CREEK.
BLEAARCBHAARTAEDDEIESMCHWAIRLGLE.BE TAKING A SAMPLE TODAY OF THE FOAM AND THE
DPELTEEARSMEINTEAKEISACALUOSOIKNGATTHTEHESFEOAMSAM-PLSEASMEANMDATELREITALMSE AKSNOWLAWSTHATTIMYEOU?CANCAN THE LEVELS BE QUANTIFIED ?
TPOLEADSOEADRDEIFTRIIOGNEARLATEANTAHLYESEUSNUSLAETDERP.ORTION OF THE SAMPLES IN CASE WE WANT
THANKS FOR YOUR HELP,
oan
Distribution:
CTCO:: JROOHBNERTF. L.DORUIGTHTCYHEY CCCC:: LRYINCWHOAORDD AK. KIIRRSECLHANNEDR, JR CCCC:: TGhaormyasW. R.KleWsaelldron
{( RDIOTUCGHHETRJLF )) (( KIRIERLSACNHDR)A ) (( WKALLEDSREOLTGRH ))
1 000:-
2
EID030763 R
1
90
009508
|
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DPraotme:: G0E2m-aovu-K1e9w9E8dY02:36pm bet: KAcewenoL Tolmer des-sass
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Subece: cee vowkey sTUDY
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a2g
EID 088762
g3
009.07
91
000505
`
:
TO: See Below
INTEROFFICE. MEMORANDUM
FDraotne:: DeTeel tsfo:
J0O4H-NNoFv.-19D9O8UGH0T8Y:10am
DOUGHTJF
(P3P0D4) 863-2801
Subject: SAMPLES FROM DRY RUN LANDFILL
tPhauel FTR-oIwRa.n tahnde MIashsavSepescpenatnd stehveeraxl-rmaaynondatysheoneletchterotnwomiscarmopslceospeu.sing
wTahse afnoaalnyzseadmptloe ciodlelnetcitfyedthferacnautshee oLofwtehrePofonadm.on 10-29-98 at 11:39AM
Because the foam was very concentrated and stable, we were able to
wiassohl.ateTmhaetemraijaolr mbaytedrriyailnginatthreoomfoatmempiserathteuresodainudma saslitmploef maenthaacnroyllic
polymer with 3 become a major
high acid content. As You know these resins have product in recent years. We have never identified
this
mTaatbeorriaatlorybefuosrieng501vtaocictoenf2i6r2m7thaned isdoendtiiutmy,hydIromxaiddee.someTheinsctahnes were a
match. enough
Later we did our total material to
normal extraction procedure and isolated be very roughly 3500 mg/L in concentration.
ba1ercesapnmeaecduelsoaltauerbeltehb.eeinWhgeighkcnoonawvciedrttheeadrcertyloisicthseordeissuiomndsiuinwmhitschaheltfalrieyn
tihnesolluabnldfeil3ls tanhdey ash and the fly an
orIrsesibfanrsoimic.tascerlyf1licacomuplnodoltyomraeiwrgasirneatthoeafteainatychceourtmhuelfrartomenajtiohnrethfseoiulrbtceierossclauokdfegesoidaninudAmC.FtyhleicsThe
bottom of the equalization tank
oMarstshoSpaencd wpaorrak tdoolnueenoen sthuelfoenxatmriadcetsanadlsDouitdyenbteinfzieendesnsaulllfeornamaimdoeu,nts of mniyxltounreolitghoamterwse, bealifelvueoro1scarbbioonlogtihcaatlweinboerliigeivne. isLoCt8s anodf a compiex
microbiological organisms were evident under themicroscope.
cpXoo-turalasdysibwuoemr,kfraoaml]usmdoiinrdutemt,oerctSteihldeicsoofndl,iyumas,suhlfcubhrul,toritinhoeed,inimeoadgiannneedsiifunrmo,np.arcatliMccoiusutlma,rOfisthneoste 3ue1xs5pee0dctsaesede.msstatbToihleiiznsedoriuscracteienmauZnsytteilobdeipnrtoehdecucoptnostt.aaisnsOiinnuegm coiofomdpoioudurendMa.ansdscuSppercousscainosdide
The other sample was taken fram the discharge of the 4 inch pipe at
the Lower Pond at the same time.
We did
sample.
our
We
nworemiaglhedexttrhaectrieocnoveprreodcemdautreeritaol
itsooldaetteertmhieneorgtahneics
in
the
bEceoomlneicaeenvnieternatistwiuobsnisolwnohygilicochnalwoalslignarnooerurigsgh.ilny| Aa3ls5swomegl/plLr.sasenWtoerwtfahosoundasnodntehpemamasatjetororijauentehat we
000.6
BIDU0TT
. suTfonanice and buty) benzene sulfonamide
distribution:
0: DANIEL A. WEBER TJOO:: GREOOBREGRET WL.OYTROIMTICCHHEY
( HEBERDA ) C( WROIYTTCOHNEIRGL ))
00005
EID030774
SECC:: PCAHUALRLESRJOWARNEFSHAUGE CCCC:: CPYANUTLAHIGA CHRAKWILRESYCHNER CC: RICHARD A KIRSCHNER. JR
(( RROEHFASNHPAEC]) ) (( CKRIARNSLCEHPCSH )) C KIRSCHRA )
009. 01,
EID030775
92
0005:
INTEROFFICE MEMORANDUM
:
DFartoem:: VT1hA3oL-mD3aRasOnT-R1&.999wal1d0i.o2n6am
eDelpto.: 3P0PaD--aPeosNE3R4/ssERVICE
To: Jon F. wooRE
ooResr )
cCe1: uRIaCwHoAoRpD A&. KIIRRSEGLRANNEDR, JR
({ mKRmseCLHaRA )
Subject: Dry Run Landfill
bSitcepsof tosWohcliioldnestaitinnouartsihengmusctcrhheeaamsf.awceilI ciottuyalldyk.eesdteTtrhodiasMye,lwvouiIlndwiBtobonesestseaenddadduqueiftcreoeoskha
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a -------- :
that I'm proposing and giving me feedback on how to upgrade the process.
3
Comments are welcome and needed...Here goes.
L
EID087029
009. 1%
AssuOmupttpiuotnso:f the Risk assessment will ba a series of results that will be eixnpotshueref.o"rm of "for toxic endpoint X, the risk is Y cases/1000ys at 1 Weexpowsieldl hpaovpeuleatxipoonsurien dthaetaftohramtofwillY' allcaoswesc/a1l0c0u0latyri.on the risk of the AennydpoCi-n8tsrepaslaCc-e8m.ents will have at least 10X less risk for toxic
Proposed Approach:
Select a base case and 4 alternative cases as options for our C-8 strategy. wCiotmhpartehethreiskficnaanlcciuallastioofn tfhoer ftihveesecacasseess.( using NPV as the best indicator)
UtilizAebstohleutfeolclhoawnigneg idnattahemearissukresforashutmhaenchoemaplatrhiseofnfepcotisnts:
Relativi.ee.chasntgreateignytAhererdiusckesforrishkumabny Xheaclatshes/e1f0f0e0cytrs ve. strategy B
Relativi.ee.chsatnrgaeteigny tAhe rerdiusckesforrishkunbayn
Xt va. health
strategy B effects on
a
financially
weighted basii.se. utilize the metric of X cases reduced/1000yr/SHM NPV change
ve. the base case
Cstornastiedgeirest.he WDouuPolndtthiemagsetrvast.egitehse choolmdpetuiptotro'spubilmiacgesbcarsuetidnyo?n the various
iCnodnussitdreiralthoeccrueplaattiiovne arnidskevoferythedayvarliifoeu.s C(-J8uststrfaotregyioeusr wiintfhoromatthieorn,risskosmeof ernilsikghntuemnbienrgs)are listed at the end of this note. I thought that these are
Consider the premise that the goal for exposures and emissions is ZERO. Croendsuicdteironthaectirveiltaiteisveinriosukrrbeuduscitnieosns.of the C-8 strategies ve. other risk
Options to Consider
Base CaRseep:lace c-8 where technically feasible and market conditions allow. and cuAsgtgormeesrsilvoeclaytimoinnsinize exposure/enissions at our manufacturing plants
AlternDaotenoctasreep1l:ace C-8 in any application.
and cuAsgtgormeesrsilvoeclaytimoinnsimize exposuce/emissions at our manufacturing plants
=
AlternRaetpelaCcaeseal2l: C-8 use
8 2g
Aggressively mininize replacement emissions/exposure
&
00031
EID087030
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|
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|
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|
|
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|
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BROCKZWJ, KOENIZMC, C8 MONKEY STUDY
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LCAALCLK WOIFTHDOSANEYRQESUPEOSNTSIEONSAND ANIMALS.
060-129%
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Cattle TMeaarmchKi3c,k1o9f9f9Mesting Summary
aTNnnyde paBrotolvttidoeinnTCgaenttahaemrc.omneMftaerfnoeyrntctnehearnfoikrossmt.ttoimNeeownBMoaltrocnhC9enattetrhefoUrnniavstoifnPganrnesymiveanaias's Attendees
Q{SREaorRlaRih)n.sCLaasbPpoerararrtyo(rHEya)P,bAeLciRksoeagriHeo(lnUleIrolf)(.pPrMai)vi.akteeBpoHrboacmtPieocep)p(,eUGSnrFgeWagS)(S.UykoMefasrP(kaD),uSPpoPrenettnegsPehrMasa(eEc)Pe,A RFaadllphRSotsahsl ((DDuuPPoonntt CHoarspk.elRlemLeadb)i.atRioundyGrVoaulps)n.tina (DuPont Haskell Lab). sad Expectations
aaIndhvyeisaCesasEtoclPieAatTaeendademxDpuioPssouenrxtepsaacsotretdopatrthoaembeeextiesratsnintgohbacjtoencmdtiiigvtehi,otniiomnfpdaeMcrpt.entTdheeennotavnebtroa'ldslyhheterhaadltthawnidl Lpioehseascihhbelraed.fcuotnuTsrheaenismTupeascatomsn tisoteethxepheehcretdr'des'ds cthooenadblietthi.toenchnaincdallryecsoomumnedndian tiitsonaspptrooamcihllgaantoyef Tom Structure and Logistics
> cToafhlelveeC.tateTtmlhaeerTiTaeenasammainswidallscsucobinesdneutticstotfsdtehwteiaitDlhreydexRepvueanrltuTiasatecihoninniscaolflarMTgree. aTamneinamnnaadlnsti,'sscehosepmerpcdoiasalnelydy w1ri8elPpOorrbttetbhaapctrkedpe1at0raeitldhs.e tTheaTchhfnienidciTanlegsaTmoefatmmheeimnbTeaaprapsmroaxarinemd:atreaHlacyboem2cm-ke3enrmd,oanttHiheolsnl.esr,fAorMwoarscisttaiennn fVaolpepnetningea,wilalnsdupSpyokretst.heWTheearme. needed, Caspar, Hom, Sprenger, Stans and
> PhDraa.ndrGirneHggablSeoygckikseetsircswaacatsnidnegloetachsteertdhcetoooSrbcdeiientnahtteioicrcodoLuretdaiidensea,rt.wohriGolrfeetPgheerwrCiyaltwtbiiele rbTeaesarpmeo,snpwioiinteshiDfvroe.r othrelfeianddiinnggsiahendherredcoevmamleunadtaiotni,onisnt.erpretation of the resus, and the drafing of
> TsOrhe.eamLwi'islsal aHbcoteilvlireterisewpsio.llnsIaincbtaldead,sititwohhnee,rloebceancleaveuedsteeadm,oifafrhoierarnepxaraonmxdiimnwiiiltnlygbteoaniMyrn.vooTlfevntehndeawnihtte'hrsdaiflatrthmha,et
2
might exhibit untoward signs or that is found dead or moribund. Mr. Tennant
2
eas EID042172
.
EE IPINT EWIRNETVEL saxsce-ssz-ee
sz 3
fwiolunbde responsible for notifying Or. Heller when such animals are noted or
rSaenasdrpaohalnldCacstoopmamarunnywiicllqautaeicstotnaisso.ntsheNforiontmmeerMfmra.bceeTrweintohnfaMntr.the ToCerantnoltalhenetrTsoenaretmghaeirsidniientxgapl afsciinttdeeidvnigssti,ot fcioenlcdlinugsiaonnsy oqruersetcioomnsmenfrdoamtitohnes moendithae ahnerdd.resSpaornadhinwgillobne breehsaplofnsoifblEePfAo.r JRaaclkphsoSntaahtlDwuiPllonbet Wraessphoinnsgitbolen fWoorrrkesferwrhinogwtilhlerseasmpeondquoanstbieohnaslftoofMsD.uPDonatw,n
>
EPA will be responsivle Poppenga; DuPont will be
for supporting responsible for
the work supporting
Oorfs.DrHse.lleHraabencdkMeorisaann.d
aAndamliyntiisctarlatiwvoerskupcpoorntdu(cctoepydingo,n matihleingh,eertdc.)inwcilludbiengbilbleldoo5d0%antaloysEiPsA,, 5at0c.%
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this effort at tie or no cost.
>
While noted
ctohanttahcetecdurornenMtlayrchhas9
by 40
hSeaardahofCacsatptaler,
and 36
Mike Home, of which are
Mr. Tennant expected to
rceaqluvierethiesxsapmriinnga.tioTnwobycoOrw.s Haerlelecrurirnentthley enxehairbittiernmg.sigHnes ohfadsisatrecsisndaenrd-bmloacyk
bbearusfeoduntdoahtoilodnctahtattlecdaunribneg uexsaemdinaastiaonc,orral, and a steel head-gate that can
> wEhPitAe-tdaaitleerdmdieneerd itnhWatoothdeyCowuonutlydafnudndothaenrdaruenadsertthaiksesparinsgt.udyEPtAo emxaaymiunsee itnhteerCpartettiaetiToneoafmthfeorrecsounlstusl.tation on this study, including its design and the
Action items
1. Tofhethivsisidtattoe Mbry. STaernanhanta'nsd fMairkme.is TAphreilT8e,a1m999wi.ll Mcro.ndTuecntnaanntewvialllubaetiionnfoornmealdl V4i0sithethaedgorfazcianttglea,reoabstaiinnclauddientgaitlheodseheorndohrisnteoarry DfrryomRuMnr.LaTnednfinlaln.t, and may
2.
Dr. Hellerwill are safe and
avpispirtoMprr.iaTteenfaonr tu'sse
finaemxatomiennisnugrethtehahtetrhde.
corral and head She will report
gate back
10 Greg Sykes and Perry Habecker on this point in the next few weeks.
3. dTihffeerTenetaiaml wdiilalghnoolsdtiac ciondnifcearteonrsceprcaoldlutcoerdedvuireiwntgheth1e3Mpaortcehnti9almeptrionbgle.msGarnedg 2Q
and Perry are responsible for setting this up.
g
009.5,
EIDO0S2173
4. `MmiakemmHaolrnseamwpillilnpgroevfifodret the Team with a copy of the Woodward Clyde small
S. dReaplopshitSetdahiln wDirlly pRruonviLdaendtihiel.Team with the lists of substances and materials
6. T9T6ehtaemam.najoermiatiylofactchoeuTnetasmo'sthcaotrrsehsepocnadnenccoemmwiullnioccacutre beyleecmtarioln.icOarl.lyHawliltehr twhiel
7.
dHiostmreibutpehdosnoe evneurmyboenrescouofld tbhee naTiefiaemd ianntdhe morpidity or mortality prior to or after the April
seuvpapnotrtoifngan site visit
ianndiimvailduaelxshibiwteirneg
8. `aTwfhtheeernnteahxneatlAymptreiiecltali8nsgvuisloitftsttohaerMerT.oebTatemanianaennddtfssruofpmaprobmlr.oionTdghseianmdepixlvaiecdstu,aldesatct.weilalwinlbdledweshopetmehenetdriomoner
SnoatratnhewilTlecahmichkaswitchraGfrteedg when this maaing may fake
iatsndfinPdeirnrgys place.
aaftnedr
trheecoAmprmielnd8atviisoitnsa.nd
Rdaeltpehrmainngd
Phone, fax, email information
Sarah Caspar WFaox::
Home:
Email:
PerryWHoab:ecker HFaoxm:e: Email
Mike HWoon:e FaHoxm:e: Email:
122110558.878113441..32322858703
Cllplne
PEGE
2221055--337i05--94,5720f
caspar.sarah@epeapmaagiolv
610 610
444444-.50680902,
ext.
2385
h6a1b0e3c8k4e-r0@4v5e2tupenn.edu
773322 332211..66772147 h61o0m9e2m3i-c6h7a0e1l @epamailepa.qov
Peter MWooi:san 919 733-3986
Fax:
a
EHmoamile:: 919 363-3523
2
g3g
009.2%
EID042174
Greg WSyok:es FaHoxm:e:
Email:
330022 336666.-66006750 610869.8469
areq.p.sykes @dupontpharma.com
Bob Poppenga
FaWox:: HEommea:
Mark Sprengar
Wo:
FaHoxm:e:
Email
Lisa Heller FWaox:: HEommaei:l
666111000244644448-.454186101027, ext. 2217 poppenga@vet.upann edu
732 906-6826 732 321-6724
sprengermark@epamail.epa.qov
304 684-9495
l2a0d-k615@Yj-u7o%,0 com
RalphWSota:h! 302 892-1369 :
Fax:
302 892-7641
HoEmmaiel:: 3ra0l2ph478s-t9a2h5l3ir@usa.dupont com
Rudy Valentine
Wo: Fax:
HEmoamiel::
302 366-5315 302
rudolph valentine@usa.dupont.com
009.0524
39
EID042175
L
INTEROFFICE MEMORANDUK
Draotme:r D1A0N-IMEaLy-A1.999WEB0E8R:08am EDT Dept: WENEGBIzNREoEARING FOLVMERS Tel Nor 8-863-4415
TToo.. JRoosmERTM LW.iGLRIIoTRCsHEY
(( rwzaccuumzRosm ))
cer auzsow A crave
(camera)
Subject: Ca IN EAST FIELD WELLS
sono,
eur,
GPCECRASPEISO,NALOLUYR DUSREIDNKIFNOGR WDARTIENRKISNUGPPWALTYERW.ELLS ARE 331 AND 33. 332 IS ALSO
Co CONCENTRATIONS MEASURED IN THESE WELLS BY CHMHILL ARE AS FOLLOWS:
ELL
ue 1593
ABRIL 1996
ray2997
a
2.5 ug/L
0.52 ug/t
0.55 ug/L
26
0.5 ug/n
0.48 ug/L
0.75 ug/L
2
3.3 warn
oa
000.0
g 2
EID0S1591
?
INTEROFFICE MEMORANDUM
DFartoem:: DTeeplt:No:
A2N1T-HMOayN-Y19J.99 [1TO0N:Y1]1amPLAYTIS PLAYTIS 3P0O4L-Y8M6E3R-S22S2H8EGEA
: TO: ROBERT L. RITCHEY
:
( RITCHERL )
:
CcCc:: DRoAgWeNrDJ.JACZKiSpOfNel
(( JZIAPCFKESLODD) )
Subject: C-8 In Drinking Water Communications
Bob, on C-8I cihnedcrkiendkimnygfwialteesr.forTahenyocnolmympuenritcianteinotnsdotchautmenwtesmiIghctoulhdavefinidssaureed atthteacshuebdj.ect.I don't believe we ever actually released any communication on ThursdIa'1y1mesettoipngbyiynouWirlmoifnfgitcoen.on TRougeesrdamyamyoronrimngayatnot8:0b0e atboledistcousmsaketheit. Tony
000,24
EID089418
Flom: Dawn D Jackson an 06/23/99 07:55 AM To: RZoibpelretULAAEiDtucPhoeny@/CDLuIPDounPtont@0uPont, Anthony J Playtis/CLIDUPont@OuPont,Roger J Subject: Outine of communications with GE Plastics regarding C-8 Gentlemen, t1 hhearveeaarettoamcihsesdioandsraofrteorfroarns,ouptlleianseeolfetpmoientksntoow.be |mwaidlleaitntecmopmtmutnoisceantdioynosuwaitrhevGisEioPnlabsetfiocrs.e |If leave today at 4:30. | will be out of town until Monday. Dawn
`GE Communication
006.54
EID082078
6/22/99
Bob Ritchey, Tony Playtis, Roger Zipfel, Dawn Planning for Communications with GE Plastics
Jackson regarding
C-8
Scenari1o: Resultsofearly June testingofGE drinking well show <3 ppb Ranedcospmemaeknfdreodmctoamlkmiunngicpoaitnitosns:ucJhohasntLhitotsleecbaellloswD;alJloahsn SaillsvoeorftfheorrsnteotosernedpoMrtStDesSt roensults C8 and Community Exposure Guideline (CEG) information.
Outlineoftalking points (in brief form; to be developed further).
cWrhosyse?s-siWtehbyouwnedadriyd;tmheodsealmpslaiynsgn(oR;FWT;WC-w8ainntgerdotuondswaamtpelre;tnoebeed stuorek.n)owifit
What? Whatis C-87 (Explain what itis: detergent-like material; surfactant; used
in manufacture of Teflon fluoropolymer resins)
`Wphoenrdse?con-stWrhuecrteediisnitmcido-m1i9n5g0'fsro(mo?ne)(oalnddsumpiedr-n1a9t7e0p's (otwo--)na;ndadeercoobsmimcisdsiigoesnteidonin
1988)
Re: concentration -- represents TLV; below the CEG.
dose
lower
than
TLV
would
allow;
it's
__%of
the
Tacouxtiecihteyalptiheceef:feRctesfeervetrooMbSseDrSv;edo;ffheorwetoveprr,oviitddeoecsoppyeorsfisMtSinDtSh;e batlotohdessterleeavme;lsi,nno
`animal testing at high doses, iver is the target organ.
Path forward: concentration
Emphasize that in WW drinking
concentration in water, WWwill
GE well continue
is comparable to to monitor;ifthere
is
an
increase at WW, we will contact GE; Site Qs/As, in the eventofmedia inquiries.
EA
will
prepare
standby
statement
and
Scenari2o: Test results -3-25 ppb
R(1e2c-odmamy?e)ndwietdhcSoimlmvuenrithcoartnieona:nd JhioshnPlLaiytttilse,cRailtlschDeayllcaosunStielrvpearrttsh;omtoe attotreenqdufesrtoma WmeWeti--ng Little, Ritchey, Playtis, Zipfel
Outlineoftalking points (to be more detailed than for first scenario):
WRFhIy?ab~oSvaemEePAinsfcoraesenaibnogvel,ev+elss;oamsesudretaanicleatbhoauttWitWs bewiilnlgwtoherkonwliythchEemPiAcatlo idneftihnee
levels acceptabtloe EPA and methods/controls to reach those levels.
What? -- Same info applications outside
as above DuPont
+
a
reviewof
the
C-8
molecule
itself;
possible
other
Where?-- Same groundwater
info
as
above
+
hydrogeology,
including
river
recharge,
plume
in
03900
EID082079
Rmea:jorcoenxcpenotsruarteiorno:utePsro(viinhdaelaMtSioDnS, ;skdiinsacbussosrtpotxiiocno)lvosg.icinignefsotrimoan;tidoinsciunsdsetCaiEl,Gsauncdh as
intent to reduce or eliminate human health exposure route. * Toxicity piece: Talk through elements of MSDS, vs. just providing a copy; provide
ioncfcourpmaattiioonna,l Uh.eaolfthMibnanceksgortoaunpdap--eran(ifmlaalwesdtusdtiuedsy)d;etraielvsi,ehwuwmhaanthweea'ltvhe-rdeolnaetewdith our
own employees since 1981, including employee communications; share Pace Team
strategies?
Path forward: DuPont will take necessary action to protect human health and meet regulatory requirements; Site EA will prepare standby statement and Qs/As, in the eventof media inquiries.
Anticipated Qs from GE: 1. What kindofengineering controls are effective to handle elevated levels of C-87
2. What exposure routesarethere besides drinking water?
4 3. Do the levels in GE drinking water indicate a probabilityof measurable levels in
employees' blood?
eas
EID082080
PSremma awe
RETURNCREERCTEIIFIPETDRMEAQIULE-STED
Mr. Martin Kotsch
Project Manager
U.S. EPA, Region Ill
1650 Arch Street Philadelphia, PA 19103-2029
June 24, 1999
RE: Permit WVD045875291 Dear Mr. Kotsch:
for yourPlreeavsieewfiannddenccolmomseendtt.he RCRA Facility Investigation (RFI) Reportof Findings
[Fou have any questions or comments, please contact me at (304) 863-4271.
Very truly yours,
Anachment
R.L. Ritchey Sr. Environmental Control Consultant Washington Works
.
CC: OMfrf.icMeaorfkPWraisdtdeyManagement `WV-DEP 1356 Hansford Street Charleston, WV 25301
MOfsf.icBeaorfbaWraatTearylRoers,oCuhriceefs*
`WV-DEP 1201GreenbrierStreet Charleston, WV 25311
Ms. B. F. Smith, Chief
Officeof Waste Management
C1h3a5r6leHsatnosnf,oWrdVStr2e5e3t01
* cover letter only
-
z
:
<
et peanotenng
Devas
--
EID0735,,
Gwe
Come
HEALTH.TBAABSLEED S68CREENING
.
FOR PRODUCTION WELL WATER
Fone | oii | tats [semmampions sie|sr2sr|
cle oor = ose ] =fx]
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so. o -nec
fPCSLLr=Praomsiinma CScorennegtLoLvaoerv:mesfooierdTnkaieang6nw6aatntedrScio84.n2 "R=CNet=atmakbaassse concantation fo 3pwater USEPA gion 1, 1985)
H0)ase:n 336 wor. s@ePwroecresswatervies KCiirsomwaort LViorsowwoorr VLoosaepwworr Lowman
)6) FT14o3e enx eooxeceperrdt eadniaoryHCtSLLihrpocyrucioolndwweeeutsVcKOn1Si6--PFosWHOOnT1, VOSPWO1. 304 Lob-PWO1.
=
8
0F0E0T2E5
EIDI09784
000535
-- Wiliam-- R Bert-------- oar1/93 02:11 PM cTeoir GRougaetrliJonZiCpfKerleAaEmDeUrP/aAME@DOuuPPaomn@t0uPont Subict: Estimated C-8 in ver Hi Roger, concentrAatttiaocnhsetdhaits twhee tEaxlckeeldfialbeotuhtaet|arlpiuetr.together on Ohio River flows and estimated C-8
Estimated C-8 concentrations in Ohi Best regards,
Bill DVouiPcoen:t(3C0e2n)tr3a6l6R-e6s7e6a2rch & Development PFaagxe:r(.30(23)883)6564-86-6902264 Intemet e-mail: Wiliam R Berti@usa.dupont.com
080:
EID082037
`Ohio River monthly average flows at Pittsburgh, PA ARsisveurmef:low1 dfatta/fsro=em:c<A0p.:0/2A8w3wmw3/.sIercd;-w1e.mu3sac=e.1a1r0my%. mciml3M;o1ncthml3y_=hi1m/m>L.
Long- Estimated
Measured flow.
termof nomnal,
nomal flow,
Mor Mlsec % fidsec
Jun98 28480 120 23733
JUSS 17192 124 13865
AugS8 9111 76 11988
Sep98 7312 72 10156
Oct98 7066 66 12070
Nov98 6144 28 21843
Dec 0440 25 37760
Jan99 53865 124 43440
Feboo 46314 94 49270
Mar99 52898 77 68639
Apr99 60741 105 57840
May-99 23053 61 37702
Estimated nomalflow,
mlsec 672E402 3.92E402 3.39402 287E+02 3.42E402 621E402 1.07E+03 1235403 1.39E+03 194E+03 164E403 1.07E+03
Estimated nommal flow, mmo 1.74E+09
1.05E409 9.09E+08 TASEH0B 9.15E+08 161E+09 286E+09 3296409 3.37E+09 521E+09 424E400 2.86E409
Estimated nomnal
flow,Umo 1.74E+12 1.05E+12 9.09E+11 TASE11 9.15E811 1.61E+12 2.86E+12 3.20E+12 3ITEHI2 5.21E+12 4.24E+12 286E+12
Total flow Jun-98 to May-99, L
2888413
C8discharge to Ohio River in 1996, bs
40800
080535
EID082038
11-Aug-99
Ca discharge cEosntciemnattreadtiCo8n cEosntcmeanttreaaticoan SoOuTImCaENtteradtiCo8n
10inO1hi9o96R,ikvger in OhikooRiver,
in Ohio River,
mol
in Ohio River,
ugiL
18416 69E10 6.30E04
0.639
f
coo: ag
EID082039
Ohio River monthly average flows at Bellevile Dam, WV.
River flow data from <hitp:/alerdata.usgs govinwis-wIWN/data.componentsist cgi?statnum=03159530>
Based on USGS mean dally flows from 10/1/1974 to 9/30/1985
Esticmsated
Estimated Estimated Estimated
cs Ca concentrat discharge discharge onin
Meaflsouwr,ed nfolmowa,l fnloomwa,l nfolmonwa,l Estniommaatled RtiovOehriion RlitvoOehriion ROihveiro,
Mo
fdsec Musec mdsec mymo flow. Umo 1996,Ibs 1996.kg ko
Jan 6400079 64001 181E+03 4.69E+09 469EH12
Fen 8800868 88909 2.52403 6.74E409 6.T4EH12
Mar 1112358 111236 3.156403 BAIEH00 BAIEH12
Apr 401667 94017 266E+03 6.906409 6.90E412
May 6710733 67107 1.90403 509E409 S.09E12
Jun 4737891 47379 134E403 34GE409 34BEH12
dul 3098947 30389 8.77E+02 235E409 235E412
Aug 3050191 30502 863402 231E409 231E412
sep 253393 25339 7.47E802 1.73E409 1.73E412
oct 3302062 33030 9.35E+02 2.506409 250E+12
Nov 423207 42330 1.205403 3.1E409 3A1EH12
Dec 7898592 78986 224E+03 5.99E+09 599E+12
Tolal 744E405 7.14E+05 2026404 53IE10 SIE 40500 18416 3456-10
[IEEE
EID082040
Esticmsated cancentral Estimated C8
ohio concentration River, in Ohio River, mon. uglL
34sE.04
0.345
00aB4l
EDos2061
`Ohio River monthly average flows at Huntington, WV' River flow data from <p:/iwww.Ird-we.usacearmy. millMonthly_htm/> Assume: 1 fd=/0.0s283me3/scec; 1 m3 = 1106 cm3; 1 cm3 = 1 mL.
MoYr Jungs Jul98 Aug-98 Sep98 Oct98 Nov-98 Dec98 Jan99 Feb99 Mar99 Apr99 May99
Measured flow, fdsec 97300 68742 28484 17.733 19710 18233 26710 141810 108500 142350 112200 57484
Long. termof noma,
% 172 190 94 78 80 41 36 126 84 86 82 62
Estimated normal flow, Msec
56570 36180 30302 22735 24638 44471 79750 112548 129167 16552 136820 92716
Estimated nomalflow,
mdsec 1.60E+03 1.02E+03 B.SBES02 643Ee02 6.97E402 1.26E+03 2265403 3.19E+03 366E+03 4.68E+03 I87E403 262E+03
Estimated normal Estimated flow, _nomal mimo flow, Umo 4.1SE+09 4.15E+12 274E+09 274E+12 230E+09 230E412 167E+09 167E+12 1.87E+09 1.87E+12 326E+09 326E+12 G.O4E+09 6.04E+12 B.SIEH00 B.SIEH2 B.84E+09 BB4ENIZ 1256410 1.25E413 1.00E+10 1.00E+13 T.03E+09 7.038412
Total flow Jun-98 to May-99, L
6.908413
C8 discharge to Ohio River in 1996, bs
40800
009511
EID082042
Estimated C8
Cdischarge Estimated C8 Estimated cs Concentration
10inO1h9i9o6,Rikvger OchoincoeRnitvreart,iokngiiLn OchoinocReintvreart,imongiinL
in Ohio River,
uglL
18416 267610 2676.04
0.267
089013
EID082043
`Ohio River monthly average flows at Cincinnati, OH River flow data from <ftp:/iwww.Ird-we.usace.army. mi/Monthly_htm/> Assume: 1 fid/sec = 0.0283m3/sec; 1 m3 = 110 cm3; 1 cm3 = 1 mL.
Estimated Estimated Estimated
Measured Longemn nomnal nomnal nommal Estimated
flow, ofnomal, flow, flow, flow, nomal
Mor
fsec % Msec mysec mymo flow Umo
Jungs 131,400 175 75086 2.126403 S.51E409 SS1EH12
JukS8 94452 211 44764 127E403 3.39E+09 3I0E12
Aug98 28,387 80 35484 1.00E+03 2.69E409 269E+12
Sep 21,200 74 20649 8.11E402 2.10E+09 2.10E412
oct9s 21.085 77 27357 7.74E402 207E+09 207E412
Nov-s8 21.400 40 53500 1.51403 3.92E400 3.926412
Dec9s 34,548 35 98700 279E403 TAGE09 7.48E412
Jan-99 178,190 131 136023 3.85E403 1.03E+10 1.038413
Feb99 134,860 81 166404 471E403 1.14E+10 1.14E413
Mar99 180.260 85 212071 6.00E+03 161E+10 161E3
Apr99 118000 65 178788 5.06E+03 1.31E+10 131E13
May-9s 60226 49 122010 348E+03 9.326409 9.32612
Total
1.028408
1185406 3.34E+04 BT4EH10 BT4EHI3
CBdischarge 10 Ohio River
in 1996, Ibs 40600
00001
EID02044
Estimated Co Estimated Cop
C8 discharge concentration ~ concentration
to Ohio River in Ohio River, in Ohio River,
in 1996, kg.
ko
mg
Estimated C8
concentration in
Ohio River, ug/L
18416
2.11E-10
2.11E-04
0.211
00a:
EID0s2045
ROihvieorRliovewrdmatoanirhoyma<vpe:rage flowIsrda-tweP.tussabcuer.ghar,myP.Am,iHluMnotnitnhgltyon,hmWsY>, and Cincinnal, OH
No. 14am Mo 23 FMeabr 45 AMpary 673Judn 895Aeupg
10110Ncovt 12 Dec
PitsPbAurgn, 332M0EEH122 S422EEev1Z2 2T8T6EEcN1Z2 QTOOBSEEVM12 TOA1SSEEMMl1 2T6S6I8E4M1Z2
DBaelmlvWilVe HuntWinVgton, CinciOnHnati, AGSTIAEEMM2Z BBSSIAEEMS22 111L4OEEHN1D3 GBR4IEEMe1Z2 1120504E1H33 1{SMIEEVDI 3SMOEDEEWWiZ2 T4O43SEEeeMi22 SSS2IEEIMZ2 2283(4Ee2f2 22T340EEWe22 233609E4M1122 215T0Ee1r22 11S8T7E4M122 221007E6W411Z2 SSSAEEHWZ2 3B2M6EEeW1Z2 3T9A2IEEwN1Z2
1.8E+13
3ogre
16E+13
1.4E413
eee SEOEOIR sT 1e.0El+13
A
5
dl gl dl
8s6.0eE+12e :| LIA RAS
i 4.0E+12 A |BE| iNH
i ME HR HN
0.0e+00 HEHE] H
!
a
Jan Feb Mar Apr May Jun
HEPitts
Sell
iii
a
:
Jul Aug
0a
EID082046
burgh, PA
olobemw
|
tington, WV CL
innati, OH
I ] Hi | |] oI
Sep Oct Nov Dec
sev
EID082047
101
RTTACH MENT s01
/sTScA CaTx. Den 6 3010000014
No San: tized Version was pro vided.
039515
|
102
0005.19
:
.
OuWffroormee tos
wan
August 31, 1999
M`GrE. PDlaalsltaicssSilverthorne, PlanMt anager P.0. Box 68
Washington, WV 26181
Dear Dallas:
.
As we discussed by telephone on August 30, T have enclosed the lab report on the
`water sample taken perfluorooctancate.
at your Ihave
facility on June 3, 1999, for analysis oflevels ofammonium also enclosed the. DuPont Material Safety Data She
documents refer to the material as FC-143, but itiscommonlyknownasC-8. et. Both
ThreuLpmrVaesnaennhTdte'sadilsaltiihdnkoeetsfhtfeeoerlcestoiaswtmeehrreaarttveahenatgnbhteeaaethnsetohTwbeLhs0aeV.rt5wv5weo2deuluasgdte/lecaoiclnnolcnoeocwnue.rntsIrintaetf'aiscotdn,rdiiten'tkseiacnptgpewdraoixtnieymroawuterelllssyi,t1e'N%soosfatmhplee trations many times this level,
you can}hreoapcehtmhaettahti8s63i-n4f3o0r5m.ation s useful to you. IFyou have any (Further) questions,
Sincerely,
Enclosures
ft H Lite
Plant Manager
irre
e495.
COPY
EID089407
_--
-
i
Analysis Repa
<P Where quality is a science.
pip ia LL sample No.
WW E3i167122 rusts 616s
EcicdRo:viaoxcmato7d0s3r2oss-recoyarl
5.0. tat0.c221
Sm
aR
SE
ater Sue
Ao cashot 1999 aBT wusswe
fesJarss ezmiovnrennonpar TS
Zoe TSfeEcSMsIoEateTr ye advisRory nSly etaldoS]isfeictns acohupsies wn
220 BwrFeeg) to uisateere
an oom aun
aBok6oe `QUALITYCONTROL REPORT
Bows sBsREeE o } Pa A 0m
Ji
\ rr BA SgHnOUymT Sara ROzSE
&s5nore LMTTo8t
224 Fea nace en
JEiye
:5
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foseiniJ
"UGRATORY
CHRONICLmEo n
i
aBuset3A8/0w8S/o59r,0e730 GaB pvarrasnn H. Zimmarnan
22 ENN Mime ater tee FEL HAT
EID089408
TB SE en nm sme ee se co 1C0PY TO Woodward Clyde Diasonds
ATTN: Ms. Sara Seastron
JUN 18 1999
ceptoad ate.
ToT
Check|
Date_
2
EHE5TERshy4 ron i a QrueesytiBoonrsr?nolCoantact your ClientatSer(v7i17c)es6R56e-p2r3e0s0entatib ve i`Hon ldingsTimeChe>ck
DOste.
A
a tics
RSeesapevcetrtul,ly hesSsu.mi0t.e5es
Group Leader Pesticides/pss
MM en rn Tn
ee.
009i
Material SDaufpeotnyt.Data Sheet
Page 1
.
voo03045 FC-143 FLUORAD BRRAeNDvisFeLdUOR1O5C-HJAENM-I1C9A5L7SURFACTPArNiTnt(e3dM) S-AUG-1995
CHEMICAL PRODUCT/COMPANY IDENTIFICATION
:
TT
Tradenames and Synonyms
-
FLUORAD FC-143
Company Identification
HANUPACTURER,/DISTRIBUTOR
R33eHvCGieesnneetdrear2l3-AOUfGf-i1c9e9s:6
~
FsYt. Paul
5u5s1a44-1000
PHONE NUMBERS
TPrraondsupcotrtInEfmoerrmgaetnicoyn :: 860102--472343--31310100
COMPOSITION,INFORMATION ON INGREDIENTS Components
MaAmtmeorniiaulm Perfluorooctancate Ammonium perfluoroheptanocate AAmmmmoonniiuumm ppeerrfflluuocrroohpeexnatnacnactaete
CA3S82N5u-2m6b-e1r
6130-43-4
6281265195--1417--04
933-37
1-3
01-.311
EXPOSURE CONTROLS/PERSONAL PROTECTION
Exposure Guidelines
ApAplmimcoanbiluem PExeprofsluurcerocLicmtiatnscate
ATPLEEVLL + (((OADSCuHGpAIo)Hn)t)
::: 0N0.1o00n11e mmEggs//tmma33b,,lis88heHHrrd.. TTWWAA,, SSkkiinn, A3
i* mpAoELsedisocDcuuPpoantt'isonaAlcceepxtpoasbulree ElxipmoistusrewhLiimciht.areWhleorweergotvheanrnmtehentAaElLly
are in effect, such limits shall take precedence.
EID089409
009:
0003045
Material DSuapfoentty Data Sheet
Page
OTHER INFORMATION
TT
Additional Information
TT
#*EEaInnRdfoErsmhR RaotuAilRodnbeinustehdeRAaaRsbEotvEehRe SRpeRrAcitmiaoArnAys AsaAroAeurcRpeArRoAvfRiodrReAdthRebsyEe bRupEoAnAte.
+AAcaRtegorRiAeAsA. REARR AERARARESAAR RRAR AREAL L885A .
Vendor MSDS Text
3M MATERIAL SAFETY DATA SHEET 33M4 CGeennetrearl offices 6St1.2-7Pa3u3l-,111M0N 55144-1000
1pAC)LouLpryptrhoreisigeghihttno,sfforpr1mre9aos9te6p,rievorenlMdyi.nisnuetCcsiooloppityizaiienndMggininai3nnMdgfp/ulroalorndduwdciMottawshnnlunofiosaadcacitlhnulagroniwgoneefgdstCphorimsopvainidnyefdormthastti.on for the
2)
wNaiegtirhteheemtrehentthienitsecnootpbiytoannionroefdthefearronomirni3gHg,inparalonfdiits
rtheesroelodn.or
tniess otherwise
price distributed
Abbreviations: NN//AD -- NNoott ADpeptleircmaibnleed DIVISION: SPECIALTY CHEMICALS DIVISION TRADE NAME: FC-143 FLUORAD Brand Fluorochemical Surfactant 3M ID NUMBER/U.P.C.: ZF-0002-0378-4 98-0211-0008-0 00-51135-09138-8
0908--501211315--00829914-19-100-51135-09365-8 98-0211-5489-7
0908--501211315--6518017-602-1 00-51135-10405-7
1. INGREDIENT
c.A.s. No.
AAMMMMOONNIIUUMM AMMONIUM
PPEERRFFLLUUOORROOHOECPTTAANNOOAATTEE PERFLUOROPENTANOATE
38812350--2463--14 8289-11-0
AMMONIUM PERFLUOROHEXANOATE 21615-47-4
2. PHYSICAL DATA
98-0211-7394~7
PERCENT 931-- 397 011--13
sv7oaaippolorirnDgPernePssoisitunyrt:e::
NN//AA N/A
009:5B%
Hac89h4 e
v0003045
Material SDaufpeotnyt.Data Sheet
Page 3
:
(Continued)
ESvoalpuobrialtiitoyn iRnatWea:ter: wA/paprec.
PSpe.rceGnrtaviVtoyl:atile:
0N./4A - 0.5 Water=1 (Bulk)
3
VpHi:scosity:
cna/.p 5 (0.5% Aqueous)
AMpepletairnagncPeoinatn:d Odor:
N/A Light colored powder: slight odor
3. FIRE AND EXPLOSION HAZARD DATA
FFllaamsmhabPloeintL:imits - LEL: NN/oAn-flanmable AFultaomimganbilteioLnimTietmspe-raUtEuLr:e:N/A Extinguishing Media: WNa/tAer, carbon dioxide, dry chemical, foam Special Fire Fighting Procedures:
asHrreoeausrnsdufruelalrmospr,roptrweeacsitsstiuvreeanddcleomltaehgnisdn,gb,fraecaietnhcmilanusgdki,nagpapanhrdealtmpuersto,,tecbsutenilkvfee-rcocncotovaaeitrnienadng,dfppoaornstiestx,ipvoebsaendds areas of the head.
Unusual Fire and Explosion Hazards:
See Hazardous Decomposition section for products of combustion. i. REACTIVITY DATA
stability: stable
Incompatibility - Materials to Avoid: Not applicable azardous Polymerization: Will not occur
fazardous Decomposition Products:
iZnamrobnoina.monoxide and carbon dioxide, oxides of nitrogen, hydrogen fluoride,
5. ENVIRONMENTAL INFORMAaTION spill Response:
EID089411
UOPblssaeecrewveetinpsrwaeececapluiotsniegodncscoomnpftorauoinmndeorto.rherwatseecrtitoonsa.voidCodlulsetcitngs.pilClleedanmatuepriraels.idue.
Recommended Disposal:
aInccoimnbeursattieblien maanteirnidauls.triaClomborustcioomnmeprircoadluctfsacwiilliltyiinnclutdhee HpFr.esenDciespoosfal
2
0005
v0003045
Material SDaufpeotnyt:Data Sheet
Page 4
t
(Continued)
aclhteemrincaatlivwea:ste.Dispose of waste product in a facility permitted to accept
Environmental Data:
.
MDCiehnmenamoniwdcal((BPOOiDxm2ye0pg)heanl=eDsNeimlap;rnodmTeh(leCaoOsDr))eti=9c6a-Nlhilr(O.xL0yC0gS00e7n0=Dg7e/4mg0a)n;dmg/2(L0T;h-OdDWa)ayt=eBrio0c.f3hl2eeamgiyc(qaB:lapoyhaxabiyesgeenna mc1aa4gp-nrdaia)cyor4EnC8u5-t0hurm()cEeClS1lO4-=ddrayy46w0EeCi5mg0gh/tL();cel=Glre73ecnoumngAt/l)Lg;ae=Gr4(3eSeenmlge/AnLlagsaterum(Scealporniaccotrrniantim)
B(iPoFOcon=ce1.n8t)ration factor (BCF) for ammonium perfluorcoctancate
Regulatory Information:
VVoOlCatLielses OH2r0gan&icExeCommpptouSnodlsv:entsN:/A N/A
bSienfcoererdeigsuploastailo.ns Hazardous.)
vU.aSr.y, EPcAonHsauzlatrdaopupslicWaabsltee
rNeugmublearti=onNsoneor (aNuotthoUr.Si.tieSsoA
TrheegisctormaptoinoenntsreqoufirtehmiesntpsroodfucTtSCaAr,e EiInNEcCoSm,plCiDaSnLc,e AwIiCtSh, tMhIeTTcheamnidcaKlIccL. EPCRA Hazard Class:
FChirroeniHca:zardY:es No Pressure: No Reactivity: No Acute: Yes
6. SUGGESTED FIRST AID
Eye Contact:
iImmmmeeddiiaatteelmyedfilcuaslh aetyteesntwiiotnh. large amounts of water for at least 15 minutes. Ge
skin Contact:
Faltutsenhtisokni.n with large amounts of water. If irritation persists, get medical
Inhalation:
EID!089412
IZfontsiingunes,/scyamlpltoausphoyccsuirc,ianr.emove person to fresh air. If signs/symptoms
If swallowed:
0 not induce vomiting. Drink two glasses of water. Call a physician. 7. PRECAUTIONARY INFORMATION
006555
v0003045
Material SDaufpeotnytData Sheet
Page 5
(Continued)
Eye Protection:
Avoid eye contact. Wear vented goggles.
Skin Protection:
ABavioridofskignlovceosntamcatd.e rubber. "Use one or
fWreoamrthaepprfooplrloiwaitneggmlaotveersiawlh(esn) haarnedlirencgomtmheinsdemda:teriBault.yl a more of the followig personal protection items as necessary
ttohanpreglvoevnets)skisnhocuolndtabcet:madeheaofd ceoivtehreirngo,f Ctohveerfaollllso.wingPrmoatteecrtiiavles:garments (othe:
Polyethylene/polyvinylidene chloride (Saranex).
Ventilation Protection:
Utosemawiinthtaianppermoipsrsiiaotneslboecallowerxehacuosmtmenvednetdileaxtpioosnu.re Plriomivtisd.e is not adequate, use appropriate respiratory protection.
suIfffeixchiaeunsttvevnetnitlialtaitoino
Respiratory Protection:
-
AaacvpcopoirrdodvabendrceeartewhsiiptinhrgatoOofSrHsAaibrreabgsouerlndaetoimnoanatsei:rribaolrf.nuell-Scfoeanlcceeecntthorinagethi-oeonfffitofhceiecnofcnoytlalmofiwinilantngetrsNrIeOasnSpdHiriantor, full-face supplied air respirator.
Prevention of Accidental Ingestion:
Dtohornooutghealty, widtrhinksoaopr sanmdokewatwehre.n uWsaisnhg thhainsdsparofdtuecrt.handWlaisnhgeaxnpdosbeedfoarreeaseating. Recommended Storage:
Dcoontnaotinesrtordrey.contKaeienpercsontoanintehreirclosisdeeds.whenStonroet aint rusoeo.m temperature. Keep +*PREVENT MOISTURE CONTAMINATION TO KEEP POWDER FREE FLOWING*.* EID09413 FKiereep acnodntaEixnpelrositoinghAtvloyidcalnocsee:d. No smoking while handling this material. ther Precautionary Information:
EMIS HAZARD RATINGS:
HEALTH: PERSONAL
P3ROTEFCLTAIMOMNA:BILIXTY(:See0preRcEauAtCiToInVsI,TY:section
7.)
EXPOSURE LIMITS
Ingredients AAmmmmoonniiuumm PPeerrfflluuoorroohoecpttaannooaattee Ammonium Perfluoropentanoate
Value Unit Type 00..011 nmgg//mm33 TTWWAA 0.1 ng/m3 THA
Auth Skint
A3CHGIH
3H
C0535
v0003045
DuPont
Page
Material safety Data Sheet
:
(Continued)
Ammonium Perfluorohexanoate
0.1
ng/m3 TWA EL
Y
paIuoctSoekunistniaNmloetmabctroianontner:ibauntdLiioesyntee,dtoesituthbhesetroavnecberysalaliirnbedoxirpcnoaestuerdore,wibtmyohtrhe"eY"pcaruuttniadcneuerouSsKINrourteeferinctloudtihmee
contact with the substance.
larly, by direct
Vehicles can alter skin absorption.
S=oAuCrGcIeH:ofAmEexrpioscuarneCLoinfmeirtenDcaeta:of Governmental Industrial Hygienists
=~ AIHA: American Industrial Hygiene Assoc. Workplace Environmental Exposure Level
= 3M: 3M Medical Department Guideline
3. HEALTH HAZARD DATA
EYE CONTACT:
Yoderate eye irritation: signs/symptoms can include redness, swelling, pain,
searing, and hazy vision.
Airborne product may cause eye injury consisting of corneal opacity.
SKIN coNTACT:
Product is not expected to be irritating to the skin. ifnicldludsekinredinrersist,atisownell(ianfgt,eranpdrolitocnhgiendg.or repeated contact): signs/symptoms can
INHALATION: fay be absorbed through the skin and persist in the body for an extended time.
Illness requiring medical attention may result from a single exposure by
inhalation to moderate quantities of this material.
May be absorbed by inhalation and persist in the body for an extended time.
eRincepoeenlametevenaddteeiddnhgoaurligadatenilooifnnleuoscf,riamdiaerybolcreanvueeslesp:roidnucttheabbolovoed.theSeixnpgolseuroevergeuxipdoesluirnee, caanbovreesult
Ianrdritthartoiaotn, (cuopupgehrinrgespainrdatsonreye)z:ings.igns/symptoms can include soreness of the nose
2rolonged or repeated overexposure, above recommended guidelines, may cause:
i>fveurppeErffeacbtdso:mens.igns/symptoms can include yellow skin (jaundice) and tenderness
IF SWALLOWED:
Boots 14
ingestion is not a likely route of exposure to this product.
oon
V0003045
Material SaDfuertanytData Sheet
Page 7
(Continued)
mIaltlenreisasl.may result from a single swallowing of a moderate quantity of this
AcC2MoAnMmNmCOpoENonRIui:UnuMdmApPiemnEridRfxuFlctLueUuodOrrReoOcpOaoeCrfnTctAiaaNnmnoOmogAoaeTntnEieiucm(ia3tpn8yde2r5wfa-a2lms6um-oo1rnf)oioouuwcnmatdsapneionrfafetldteuh,detroosahtameulmdxboyain.nnioouamtTrehap,etersrefthlfawuoteorrrewo2ahsyeepator3asn,cwaotneg.
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a
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s
MtUrTaAnGsEfNoIrCmIaTtYi:on Niont mautmaagmmeanliicaninceilnlvittrroanmsuftodrgmeantiicointyassaasys.ays. Did not cause cell
RSEoPtROtDeUrCaTtIoVgEe,n/iDcEViEnLOrPaMbEbNiTtAsL TbyOXIoNrSa:l 3avage or inhalation exposures.
administration.
Not teratogenic to rats by
AOT3HMERPHrEoAdLuTcHt HToAxZiAcRiDtyINSFuORmMmAaTrIyONS:heet is available.
SECTION CHANGE DATES
4EADING
SFeLcUtOiRoAnD cBrhaanndgedFlsuionrcceheMmiacyal20,Sur1f99a6ctainsstue MSDS: FC-143 August 23, 1996
sITNohCerLrUeiDcnItfNoGar,smatoBifUTontNhOeiTndaLttIheMiIsTiEMsDasuteeTdOr.,ialAN3YSMaMfIAeMKtPEyLSIEDDaNtOaWAWRASRRhAReANeNTtTYI(EOMSFS,DSM)EERXCPiHsRAENSbSTeEAlDBiIeLOvIeRTdYIMtOPoLRIbEeD,
JFsIeTrNESisS FreOsRpoAnsPiAbRlTeICUfLorARdePtUeRrPmOiSEniOnRg particular purpose and suitable for
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No.of Pages including cover sheet:
Message:
000525
EID087238
7 FIE Mh, 610 8 CH 120E IWR GF TLL
02 9 Gz
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C-8 Monkey Study
+ Goal: A) (0 determine toxicologic effects of C-8 in the primate following an extended exposure period
B) to determine potency lor producing change (NOEL-LOEL-EL)
Surprises: - Potency at lower dose (3 mg/kg) - Failure of all animals in group to respond similarly
- Quick plateau of C-8 in blood
A) Quick clearance from blood B) Lack of proportional response
(exposure of x, 3x, 6x did not lead to blood concentrations of x, 3x, 6x)
= Subtle vs major toxicity end points
= Hormones unchanged
+ Pathology unremarkable, especially in severely affected
monkeys
3
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C-8 Monkey Study
Sponsor: APME Ad-Hoc APFO Toxicology Working Group
Testing Facility: Covance Laboratories
Madison, WIT
Study ID: 6329-231
Study
Study
Study
Director: Peter Thomford
Monitor: Paul Lieder- 3M
Representatives: David Farrar - [CL Reinhart Jung - Clariant Gerry Kennedy - DuPont
[Giovanni Costa'- Mitani]
[George Lin - Daikin]|
In Life 9/23/98 - 7/2/99
9g
EID087240
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C-8 Monkey Study
Experimental Details
+ Oral dosing - gelatin capsules
3
+ Diet - primate diet, 1 or 2 x/day - supplemented fruit/vegetables
+ Young adult/adult - 3 >5 kg
S
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Design
Cy-8 Monkey Study .
ky A oH
TMA
Group |
Control - 64 cynomolgus males
4 6 months 2 6 months & 3 months recovery
+5 Sh ar
Group 2
Group 3
3 mg/kg - 4 males - 6 months
(1 monkey - died day 137)
10 mg/kg - 64 m6almeosnths
2 6 months & 2 months recovery
"L1hd
Group 4
20/30 mg/kg - 6 males
30-day I-11
0-day 12-21 20 - day 22 -6 months
3 monkeys - dosing discontinued
(1 monkey - died day29
All sacrificed at 6 months
we Days 43 +81 ~ [de shpJloTMaSie ny
EID0g724;
009:27
FILE Me Sia 0 ET 123 IDENT oF Tr
0 61
"
C-8 Monkey Study
Parameters
L In Vivo
.
Observed 2x/day
Body weight - weekly
Food consumption - estimate daily Ocular exams - pre-test/weeks 27 & 40
II. Clinical Pathology
Timing - Pre-test, days 30, 60, 90, 180
Recovery days 30, 60, 90 Hematology - RBC, Hb, PcV, platelets
WBC & dict, reticulocytes, cell-indices Coagulation - APTT, pro time, fibrinogen Clin Chem - glucose, UN, creatinine, prot. bilirubin,
cholesterol, triglycerides, ALT, AP, AST, GGT, SDH, ions (Ca, etc), amylase, lipase Urine - standard & urobilinogen, bilirubin
00935
EID087243
FILEN:. S84 10 27 1m HOE GF 711
sic we Gz
i
C-8 Monkey Study
IT. Blood Hormones
- Timing - 3x pre-dosing, day 30, 60, 90. 180
Recovery day 30, 60, 90 - Estradiol
Estrone
Estriol
Thyroid stimulate hormone
Total & free iodothyronine (T3)
Total & [ree thyroxin (T4)
c
Testosterone
Cholecystokinin
S
IV. Exposure Indices
- Serum APFO - 7 days & every 2 weeks thereafter - Urine APFO - as serum - Feces APFO - as serum - Liver APKQ - at sacrifice
000085
EID087244
FA te 2 La NRA T
oi ten E125
"
C-8 Monkey Study
V. Pathology
Complete nescropsy
Organ weights
adrenal, brain, epididymis, kidney,
Vz
liver, pancreas, testes, thyroid (parathyroid)
Histopathology (36 tissues)
Additional parameters
- Palmitoyl CoA oxidase
- Cell proliferation
- Bile acid determination
(receptor level determinations)
(bone marrow smear)
9
J--
8g
eed
FILE N, S501 27 10T ITERT OF TI
30 i 1
fo
C-8 Monkey Study - Results
I. Clinical Observations
Control - none
a de
ake
3 mg/kg - 1 monkey - week 18 - ataxic, hypouctive no food consumption, limited use
of hind limbs _ end vewtyoy
week 20 - sacrificed, lost 9.5% bwt
3 monkeys - none
10 mg/kg - 6 monkeys - none
30 mg/kg - week 1 - low [ood consumption
|
lost 3-7.5% bwt
20 mg/kg - week 3 - 3 monkeys - same as above withou marked wt loss, treatment
discontinued week 7, 10, 12
1 monkey died week 4 2 monkeys - no clinical signs
after week 2
000225
EID087246
BIEL S10 ET CEE EET GE TIL
02 se 123
ng
C-8 Monkey Study - Results
SE 11. Ophthalmology - no findings
(ots
lL Body Weight
-
cL TF z pire
0/3/10 mg/kg - no differences
a
Ioss. 4a" 22[030mmgg//kkgg- -lloowweerrFWwwkk7,1]9, 24.( 14.3% wit gain of controls)
wha ie
TV. Food Consumption
0/3/10 mg/kg - no differences
20/30 mg/kg - lower (some no foad consumption)
V. Blood Hormone
No significant effects (0-30 mg/kg)
Unexplained total thyroxin lower 20 mg/kg
tree triiodothyronine lower 20 mg/kg
9
3
VL. Clinical Pathology
0/3/10 mg/kg - no differences
30/20 mg/kg - mild * wiglycerides
mild neutrophil, protein, albumin - 2 distressed -4 marked ALT, AST, SDH, (creatine
Kinase)
4 mild bile acids - recovery in oft-treatment monkeys
000:37
EID087247
FILE ti Sd 16 27 CH LT ISNT UF TL
02 a 12
Fu
C-8 Monkey Study - Results
VIL. Palmitoyl CoA oxidase - expect <4 wks Cell proliferation - expect <2 wks
Bile acid - no differences
VIIT. .
Pathology
go Iost
Gross path-o unrlemo arkgaby le
~ 5a
Organ weight - liver weights elevated
oo"
Lopror 3
GO/82/83/90 gems Mean (all test)
1.5/1.8/1.9/2.4 Organ/bwt (all testTM)
Histopathology - unremarkable Cause of death - --u_n--clear in both moribund animals
2
g
000525
EID087248
C-8 Monkey Study
Urinary C-8 Levels (ppm)
. oe
pEeeT2 TT E wlEww[1Teal1 os
E tL mT
-. f ineSu:n animals
T I T
EID087249
;
000: 2%
FUE the, S54 1 27 1 IER OF TH
0 i E12
-
C-8 Monkey Study
Liver C-8 Levels (ppm)
Group (mg/kg;
0
3
10
20/30
Recovery
Liver 0.04 (0-0.04)
5.9 (4.1-6.8) }
593.6-8.7) 17.2 (8-28)
0.8 (0.03-1.2)
ESde
2 5
065.09
EID087250
IE, Sd TT Te Len TEMEOTF TH
ne i SR
C-8 Monkey Study - Conclusions
Monkeys do not tolerate 20 mg/kg or higher - Non-specific response involves liver
- Recovery complete in oft-dosing monkeys
- Effects include body weight, liver weight
- No specitic histopathological changes
hormonal changes
Effects at 10 mg/kg only liver weights Effects at 3 mg/kg - 1 death (relationship to treatment?)
liver weights
C-8clearedquickly from urine (proportional to exposure
+ C-8 clears quickly from7 blood (not proportional) Se dt
- Reaches plateau quickly
ley
- Leaves system quickly
i" p
+ C-8 in liver proportional to exposure,
recovery quick and complete
* C-8 in feces - will get "matrix information"
g
EIDog7,s,
3
0600.05
Fie a bse AE GAT iF TIL
02 en 8123
or
C-8 Monkey Study - Conclusion
card
=
ee
mel
7 Capt
Thr
S we
+ No observed effect level not attained (<3 mg/kg)
w,
Thee
+ Potential serious effect in [/4 monkeys at low dose
3
(liver effect unexplained currently; best explanation
could be enzyme induction) ~~ unichidyiy odor
At AEL/TLV of 0.01 mg/m?, daily exposure to man
is 0.001 mg/kg
or bodryd ~Ji
MGEi Wagl rt tt*
ve Te
fort pe
.
3g
3
0306.05
EID087252
FOENe S34 10 27 6 105 IHof 711
0 ea e12
fy
C-8 Monkey Study - Issues
. + Livereffect (will answer)
mt er
ors I foo : wt
+ Death of low dose monkey
+ Lack of slow elimination as seen in man (does human data reflect multi-phase clearance)
+ Evaluation of monkey-by-monkey data (in progress)
000803
3
g
EID087253
Thanks for
Hanging in there.....
Trewmah {pet Cluight RN oder po
Una! posure Tris am Aaphier Psgerst
( A) Senate pg fexic Risfinrit
,
fo Ky Talk dz farm K.
p
Fm To
Sh wet Soars =F Py Te
Ly wt Ga 1teser
Nos Lbs [ls = yp8 22
(Ge wi
cS ds PE
[5p fm pig RE
003%
107 009507
s
FFI e roger azote
i
1117799 11:27 Am
Tor Robert F PnchouDEVIAEDuPam@OuPont
cSeutbject: ORes:caCr8TMGoanrkzea/yASEt/uDduyPoanntd@ADlulPoownatble Exposure Limit 2
Rdoube,to| dCon8'texfpulolsyusruep.pTohrtusthIebflrisetvebutrgsehroduoltd arseaidt issimsitlaatredt.o |thdeons'etctohnidnkbuthragterwdeotc.an rule out death Roger. Robert F Pinchat 11/15/89 03:06 PM
RobFPeinrchtot 11/15/99 03:06PM
Br RR RERs
To: Robbin Saneree/AEDUPoR@OuPort, Oscar T Garra/AEDuPorr@OuPort, Anthony J
PMTlaaantyattkhiaes/w/PCCOLI/KDDouuePPnooinnntg@@sDDEuuUPPoRon/ntDt,u,PSNotonertfp@uhrOmeuJinPoOGnhittss,suyAk/arA/EPeJDOu/VPDeourPnmoten@utD@luDePunoPn/otEn,UtRR,DoUBgaPerorbnaJ@rZOaiuJpPtoenlt/,AESDeuiPcohnt@DuPont,
C`aGvaayndaau/gAhE//ADEuPDounPto@DnutP@oDnut,PoBnar,baRroamJaGnayVdaan/AAKEeDnuEPUoRnItD@UDPuoPnotn@tO,uTPhaonmta,sBJarbara J
DADaanvwGisidouMnl/oRA/uEA/rEDaUulPPAooEnnDt@u@DPDUouPnPoo(nn@ttD,,uPMSoaunutsri,acSnMeiAcMhsiatleoelrtigEDaMulcPACoEonDtru@dPO/ouAnPtEo@DnDutuP,PooRnnitct@h,DaruMdPaorJ.inatn,neRoMbaerrtsiDupon@0uPont,
CMaavcaFnaaduagnheDu/PDoPnLtD@UDPu@POoUnPt,, Laas/AEDUPo@OuPont
ACnldarreeancVe
MPaMlhinaoUwAsEkiI/DALEPIDOu@POoUntP@oDnu,PoEnta@W.DUP,
Sharron
ce DKieannneeRdyS/hAoEmDpuePro/rAtE@IOUuPPoonntc@DuPon, Gary W JepsDuaPornt@/DuAponEt, Gerald L
Suect: C-8 Monkey Study and Allowable Exposure Limit
Most of the results of the 6 month monkey study are available. Due to some of the findings of the
snottuidfyi,catthieonswtiuldlybies shorty thereattar.
mSraeipndoceretbaeybmlpFelrtiodoyaetyeh,seNpUooSvteeEnmtPbiAaelrluyn1de9extrphoTasSnedCdAtthoSeeCcl-ta8itoehnrawv8i(elel)3
bbreiycghotthmeteo3akMnpuocbwolamicbpoadunoytc.tuhmTeehnits
ffoirndyiongustoofutshee fsotrudyyo,urDicaonmemuSnhiocmaptieornsa.nd |Thairsecdoemvmeulnoipcinagtiaonnepmapclkoaygeesschoomumludnbiecaatviaoianbflreafmoerwyooruk
10 use by Monday November 22.
To give you a preview of what we will be in the communication, here are the key points:
OOnnee mmoonkneky iinn tthhee lhiogwhedsotsedogsreougproduipeddifeodr rfeoarsroenasstohnasttahraetuanrceleuanrc.lear but may be related eAtlonlzCmy-om8neekxiepnyocssruesrahseeo.sweindtshoemheiglhivdeorseeffgerctosup(vmaornkweeyigshtthaitncwreearsaesinidniasltlrdesoss.agTehegrroeucposv,erlyi.ver
* aNnoimtahlsedricdlninoictasl horowpatthheolsoegeifcfaleccthsasnuggegseswteinrgtohbasetrhveedfovtehreerfftehcatnswthaerederaetvhesrsainblde.the liver * Tafhfoecstts,udy resuits are not complete. We won't have a full analysis of the data until January. * TGuhiedelAiEnLe. (0(3.m0i1cmrgo/gmr3am8s/adnady)12wihr, TfoWrAnowwi,thsatasykitnhenostaamteio.n)TahnedCCoommmmiuttneietywiElxproevsiusritethis
000%e35%
HOY81959
afar the full asus are in and analyzed. hPliesasneotwealist1f0orgitvhee yfooruma3lhceoamdmsuunipctahtaiotnhipsaccokmamguentiocactoimomnunisiccaomtiength.is broadly. The purpose of RReogbards,
.
00062060
i
EID081960
3i
|
C-8 Monkey Study Communication Plan
Communication to Employees
.
DuPont Legal opinion is that communication is required to US employees. No specific time frame is given in the OSHA Hazard Communication Standard.
To be conducted on Thursday, December 9 to all DuPont and employees potentially . * exposed to C-8 (Sites include WW, Parlin, Spruance, CW, DW, Mechelen, Shenzhen, Madurai, and Shimizu). Summaryofstudy made public on November 22 through TSCA 8() filing by 3M.
Messages to be conveyed atal sites
:
1. Current AEL is protectiveof human health
2. Liver effects seen at al doses, effects were reversible after ceasing exposure
3.
Two deaths occurred in the test groups. One at low dose and one at high dose. The causeofthe deaths is unknown.
4. More data will be communicated when analysis is complete (early 2000)
`Some sites adding site specific information on exposure levels at thei site (allofwhich are less than the AEL)
WW communicating that C-8 s in drinking water a the site, at levels less than the Community Exposure Guideline.
WW is communicating the results to GE Plastics management.
CommunitcoaCutstiomoerns
No MSDS changes have been made at this time. No need to communicate to all
dispersion customers. May have to change the MSDS once the final results are analyzed and will need to communicateto customers Chem Fab and Gore have been told about the monkey study. We will share the results with these two customers in the near future. (Gore meeting set up in January).
0006
=
EID083021
S
=
Terman: Fam Herd Health nvesugaion
Cate Team Report
Tennant Farm Herd Health Investigation Cattle Team Report
EP/DuPont Cattle Team DDrr.. LPiesrrayAL. DHaavbise-cHkeelrler DDrr..PReotebreGr.Jt.MMouinssanon DDrr.. GRroebgePr.HtS.ykPeosppenga
Decembe23r. 1999
QUIIn
'
DUP 242
Tena Fam er Hest ncsigaion TABLE OF CONTENTS
Carle Team Repon
[Er Signatures
0 SETHoDs 2.0.
| INTRODUCTION
rr
--
3.1 1 Cattle Team 3.01 T members
523 dissnosi paology epors 32 1 Animal Daia
321. | videotapes
3.23 1 April 1999sitevisit data 324 | miscellaneous data
s 1 6
4
16 6
17
s | 7
18 T1
3 CITTCodueans [ONSE1
S151 Aon 1999 se vie dais
is
1 a._herd history (4/8/99 interview)
115
7 ._physical examination of cattle (3/7/99)
116
T e cimee shus e ime punoloss
--I ]ie
_--_ 1d hay and grain analysis
118
o32se= Miscellaneous Data ] 1 19
[Esl Tvocouges
5}
E-- 5E0 | DISCUSSI-- ON ----1
FT endophveroiey
000s
:
DUP 243
-
`Tennant Farm Herd Health Investigauon
Cattle Team Report
TABLE OF CONTENTS (continued)
1 50. | DISCcUopSpSeIrOdNef(iccoinentciynued) toxicology sues
F 60. r | RECOMMENDATIONS
-
--7
2
7.0
CONCLUSION
8.0
| REFERENCES
-- on
1 Graph I: Individual Prolactin Values
26
26
5]
30
-- Fa re -- i Figure 3: Delayed shedding --
| __ Figures 5and 6: Coronitis | Figures 7and Cale standing in water
--
1.3 134
35
11.0
|| TTAaBbLElSeI Table
Review of Individual
Tennant Animal
Farm Data:
Videotapes ClimcalSig
ns
5 136 T=
| Table 3rd Animal Da: Hematology (ervvon places
35
|
Tabl4e:
Table
TIrnddinviCiddhuueaalmliAAsnntiimmaall
Data:
Data:
Hematology (leukon). andSpecial
Clmeal Chemise
| 48
i%
|TaTbabllee7 TInedninviadnuFalarAmniGmarl Daoatna:diHaSneyr:oloNguyriavnodnaFelcaAlnaElxysaims
[I5S
12.0
1APPAEAppNppDee9I7nnC:ddEMiSBAc. hiDAgibaabngrneAovnsitiaimicaedlPaCHtuehraolrltiohcguyDliRuamegpnVooisrttasieco(OfLhaCiboatD#eep1t7T.9e25Aag7mr1i;Mc.eUnm4i3bs9e77r.s||
33365 35
P#e9n9n0.14L3ab7., of Large Animal Pathol. and Toxicol. UP9902702.
|
AAppppeennddiinx
C: D:
DFirgyurReusn1S2af:ery
Plan Photographs
of
he
43
30a
calle
Figures 43.66 Miscellaneous photographs ofthe
71
`Append E: Ferd Health History ("ATpernina8nt 1F9a9r9miannedrvciaewey.
106
Appendix F: Diet Analysis: Computer Software Simulation
1109
coats
3
DUP 244
|
Teanans Farm Herd Health Investigation
Cate Team Report
10 SUMMARY
Introduction: Earl Tenant's
cTahtteleobhjeercdtiavnedodfettheirsmiinnveesptoisgsaitbiloen
cwaaussteosoefvaalnuyatperotbhleehmesa.lthThsteatus
of
Mr.
wainhnvidecsehtviaogluauttalitioinnoensinsoctfluunddeyewdfidanandtaie.nxgasTmahinnedaitnmivaoenksoetfisgraretleiecovonamtnmeternmhdiiasnttaotireoidcnasilntdotahtieampparsroodwveuelclthieaorsndtohhfeeatclhotilshlercetpoirotn,
vMeettehroidnsar:ianTshweitThencnoallnetctfiovremexhpeerrdiheenaclethininbvoevsitniegadtiisoenasweass, choerndduhcetaeldthbmyaanatgeeammeonft,six
dtiosxciucsoslioognys.. ptahtehoclaouglye.taenadmwviilsdiltiefdetdhiesTeaesnensa.ntInFaadrdmitoinonAtporinlum7-e8r,ou19s9m9eientionrgdseratnod
collect relevant data. diagnostic laboratory
rTephoertcs)ataendtceoanmtreemvpioerwaerdy
historical data (e.. data (e.g. clinical
videotapes, examinations.
blood
tests). Diagnoses and recommendations were based upon the data collected.
Results: The herd revealed
multifaceted disease health problems that
winevreestrieglaattieodnotofetnhdeoapdhuylttecattotxlieciitny,thienfTeecatinoaunst
beef
hKiesrtaotroiccoanljduantcat.ivwiittihs p(rpoilnakcetyien).vamlaulensutorfitsioomn.eaanndimcaolpsp,ewredreeficcoinesnicsy.tenCtliwniitchalenadnodphyte
pcPlrIiSonCiiOocIanOlgNeieCdxOassmieisvn.eateAieonnnzseoxooatfmiipcnrsaeotvfiioofunascloeyfflavyfifd(eeMcouttesadcpaeasdauumlrtaudamenniadmluairlsis)ngdiuntrfheiesntgsauttimhoemnehaernrddmocvnoistnichtosimnaidntidacnatted
pinkese. and grain
rHaasyioannsalfyesdisw.erceatcloensbiosdteyntcownidtihtipornotsceoirni-negn.eragnydmaanlneuvtarliutaitoinonanodf
the
mineral
mactomineralfiruce serum texting ut the
nutrient deficiencies. time of the herd visit
Earlier laboratory were indicative of
sdaetvae,reclcionpicpaelrsdiegfnisc,iaenncdy
in
the cattle.
Conclusion: continues fo
There was conclusive be. suffering from four
evidence that major disease
the Tennant cate herd entities. some of which
was. and were
fmpioantldeninunttgirsai.ltliyoann.idntaheinrsrdieolcraoitpecdap:lerdaetdnae.dfoitcphiheeynstceye.ftoouxAriscciostnuydbi(sttfiaeonsntcsiuaertemeadydcibolytyotaxhiceccoocsluiinnsti)c.faolpraitnnhkdeeyclaehb.roornaitcorhyerd
health problems on the Tennant farm.
inTnuhtieeirthniaoelnr.dpahirenaasalidttehequcianotvneetsrtvoielgtaeptrriioongnarrrayemcvsaeradeli.eddanndodetfliaacpcipekenaocrfieftsloyihncaohvnteerroadl.smuabTnshtaagenetlmiaaeclnktio,mfpiavncacctlcuiodnnianttghiiopsnooarnd relatively isolated herd.
eDveisdpietneceoanfteoxxhiacuisttyivaessroecviiaetwedofwihtishtocrhiecmailcaanldccoonnttaemimnpaotriaornyohfertdhedaetnav,irtohnemreenwta.s no
039cin
:
DUP 245
Tennant Fam Herd Heat Invesigaion
11 Signatures
Cate Team Report
pa Hobecho
Perry L_Habecker, VMD, Dipl. ACVP
(223/45
Date
Lx & Ae LAU,
isa B. Davis-Heller, DVM
12/50/65
Dad'
SM een
Peter G. Moisan, DVM, Dipl. ACVP, ABVP
CAN ve
Robert J. Murison, VMD
DA E --
RobertH. Poppenga, DVM. PhD, Dipl. ABVT
CSrTm lSeS
Greg P. Sykes. VMD, Dipl. ACVP, ABT
ues
Date
13 joc
Date
. el
Date
3.33
Date
06a.
DUP 246
s
Teanan Farm Herd Health nsestigation
Cate Team Report
2.0 INTRODUCTION
`cTahueleobnjeercdtiavnedofdettheisrmiinnveesptoisgsaitbiloen cwaaussteos eovfaalnuaytpertohbelehmesal.thTshteatiunsvoesftMirg.atiEoanrlinTcelnuadnedt'asn edaxtaa.minTahteioinnvoefstrieglaetviaonnt theirstmoirniactaelddaitnathaes pwreoldluacstitohne coofltlheicstiroenpoarn,dwehviacluhaotuitolninoefsnsetwudy findings and makes recommendations to improve herd health
3.0 METHODS
31 Cattle Team
LL Members
`("TehaetiTleennteaanmt")F.arTmheHetredamHewaalsthcoInnsvteisttuitgaetdi1o0n iwnacsluadesseixgpneerdtitsoeaitnebaomvoifnesidxisveeatseersi.nhareiradns hDeuaPlothntmaCnoamgpeamneynt(.DtuoPxoincto)losgeyl.ecptaetdhotlhorgeye.maenmdbewirlsdl(iDfres.diSsyeakseess,. DaRveipsr-eHseelnlteart.ivMeosiosfatnh)e: trherpereesmeentmabteivresso(fDrst.heHUanbietcekderS.taPtoepspEennvgai,ronMmuennstoanl).ProAtbebcrteivoinaAtgedenCcuyrr(iEcPuAl)umseVlietcateeodf the cattie team members are included in this report (Appendix A) Cautle Team
Perry Habeier, VNID Dip ACVP | ChiefT.oLuaircgoeloAgym.mUanlis.PafooflPoegnyn.. LSchaoob! oofrVoeatfetrFiantoahraryiogys snd
Ts Dov Hetier BUNT
| PravaMwteeycp_riancet,ionNeerw.Bio.ltMoanryC'esntVeert,erKienanrnyerClSiqnu.areS.t PMA.ares
PeterANBiVorEan, OVA. Dit Robert Muon VAD
ACVP.
Dipl
|
VeterLiinbaorrystPaotrhsol(osgaitee.IRsobolrlamtsorAv)n,iRmoalelygBhr,scsNsCe. Diagnosis Field Inesigator. Centerfor Animal Health 3nd Producti
| Unsivq.uowfePpesnn ScohfVoeteorinlary Medicine. Kennett
RaberA:BeTppens DVL PRD Dift. | Chit.UnTio.xiocofloPgeyn.n.SLcahoboloofVreotafePrthinooatrryogyMedaicnidneT,oxNiecwol
GregAS5yTkes. VNID. Dipl. ACV. Dipl
|
PatholBoogliisto.n CSearfneetry. AKsesensnsemtentS,quaDrue,PoPnAt. PRarmacearcaly Company. SineResearch Center. Newark.DE.
DDDiiVppMll.AAVCBVAVPD === DDDioipcpltlooomrmaotaefs.:VAAemmeerrriycaannMCBeodlioeoenfaoVfetVreerirndearnyaPrPiacbelo(Fgososd Animal and Beet tleSpcisiss
DDiIpl AABCTVT == DDiipplloommsaitee., AAmmeerriiccaasCBololsegeofofToVentceoriinoatryy Touclogis
ASctietnhteiffiicrstLemaedeetri(n2go.ftchheaicramttalne)taenadm G(rMeagrcShyk9.es19w9a9s),elPeecrtreydHCaoboerdcikneartowra,s Tehlee.cted
0006S
6
DUP 247
Tennant Farm Herd Health Instigation
Cate Team Report
clehaadierrsm,anDras.ndScaoroarhdiCnaastpoarrw(eErPeAi,nsRierguictoend I(I0I)caonmdmuRnailcphatSetawhilth(DtuhPe o"nStteCeorripngorcaotmemitee" RMeimkeediHaotrinoen(GUrSoFuWpS))a,.s MnaeredkedS.preThnigser"s(tEePerAi-nOgEcRoRm)mi,ttaened"RiuncdlyudVealdenDtrsi.neC(aDspuaPro,ntSt-ahl, Specialities Chemicals toxicologis).
3.1.2. Cattle Team Meetings
The cane team met formally on four occasions, including the Tennant Farm site visit Cattle Team Meetings
March 5.795
New Bolion Center. Kenner Square. PA
TireIsting premeen Fare svn LFORESY Inn. Pakersburg. WY
In addition. among Drs.
sHeavbeercakleirn.-pMeurnssonond.isPcoupspsieonngsa.toaonkdpSlayckeesatbNetewweeBnolMtaorncChen1t9e9r9baentdwetehne
and
issuanceofthis report. and US postal systems
foArllpcaiartlaendtegarmoumpemdibsecrusssuitoinlsizaenddthienftoerlmeapthioonne,shianrtienrgn.et
email
32. Animal Data
32.1. Videotapes
Ttawpoesvwiadseoatacpoelslewcetiroensoufppvliideedottaoptehsemcaadttel,e atnedamnabryrattneed.stbeyerMirn.g cEoarmlmiTtetnene.antEaocnhhoifs ftaherm
and the adjacent different seasons.
landfill area. it appeared
thAalttthhoeusgehttahpeestawpeersewaellrepreodidtuecdedanbdetiwnceleunde19m9at5erainadl
from 1997
Tennant Toe |
Farm
Videotapes
Te
FT [| TennianoteFarm: New England. Wood County. WV - January snd Febras FE] 0%wRevn Fs PC. Wood Co OF Nort Fork of as Ceak New Engand.
ANnuimmbaelrsCoxe | 1-15 | 1060
Bothofthese tapes were viewed. in their entirety. by the cattle team members iHsniedcliklvecirdouwnaoslt.lyp.wreesrTeenhtee)v.yalwuAearteteodt.aallslooifre6em0vsiaoennwiemtdhaelattcaaapsceeassu.tlhreaattnegwaienmrgemfneroeottmiannagidmoeanaldJrucelrlyaayt2ef8di"s(he(.Dtgro..,gwrDaoatuveiprss-of theraelatthmednatt)awdeerreivneodtefdrobmutthneosteetvaaplesu.ateTdh.isTatabbllee d|iosesa ncootmpiinlcaltuidoenmoafntyheasrseelretviaonntsaannidmal
:
'
0ODnLT
DUP 248
Tennant Farm Herd Health Investigation
Cate Team Repo
interpretations. be incomplete
made by the or erroneous
narrator
in
the
tapes,
which
the
team
members
considered
to
3.2.2. Diagnostic Pathology Reports
Tcowmomiptaeteh.oloBgoytrhepwoerrtes i(sAspupeednbdyixstBa)tewaenriemaslupdpilaigendosttoitchelacbaotrtalteortieeasmibnyretshpeosntseeertiongthe
submission feviewed by
of dead animals the catle team.
or
tissues
from
the
Tennant
Farm.
These reports were
oAf tohnierdapnaitmhaollo(g+y37r)eoponrtJ(uAnpepe10n,di1x999B.) wTahsecpartotdluecceodmsmuibtsteeqeuednectitdoedt,heatelaemceteivteisnagcroinfice
oMnaeyor25.tw1o9o9l9d,etrhactowist.woMurl.d Tbeeninnafnotrmwaatsivaes(k0edhatvoesealtecotxiocnoeloogrytswcoreoeftnhoen ctaitstslueesthfatrohme
ccoonwsitdheatrehdadtofbreesihnetnheedwaorfsetwmcoonndtihtsione.arliHeer.chTohsiestaonsiamcarlifwicaesceouwth#an3i7z.ead Tb-yvegaurnsohlodtrbedy
prMre.seTnecnenoafntoDrn.
Dtahveisf-aHremlloenr.JTuinsesu1e0.s
1w9e99r.ecoMlrle.ctTeednna(Dnrt.
pDearvfiosr-mHeedlltehre)
dissection for
in
the
histopathology and analytical toxicology.
IPnadiiisoigdsuaRlepoArtni|mal
Pathology Reports Nameof Diagnoste
Liboratory
I Case Mawral
Die | Stores 10. 1997 | Animal Disease Diagnostic Laboratory, OMG
(ase numbers G63 mont3 hold bull si
Nar 12.1997 || AmaDleoHuenamltehnDtioafgnAossrtciucluLraebo.raRtoervyn.olCoslbluergee, oOfH_||*Wocsruie7s-7s:e9a7rold Hoffer soo
To ET]
|| Canerss. Lansing MI Caborsons of Large Amal Paelogs and
su(e1s7992s5e7a1r)-oldHolsiin con sues 7-vear-old con
||_ TPoeunincsoyllovsasn.ia,NeKwenBnoelttoSnouCsermeer.PaUniversitoyf| (+UP9S02702: L#99014371
3.2.3. April 1999 Site Visit Data
Tahnde 8c. at19e99teianmorvdiseirtetdo ctohlelTecetnndaatnataFnadrmbioalnodgiacdajlacseanmtplDersyrReulenvalnatndtfoiltlhesiheeordn hAeparlitlh7
aitnvtehsetiPgaatrikoenr.sbuBregfoHroeliprdoacyeIendnindgutrointghewhsiitcehontheApDrrily TRtuh,naSabfreietfysPalfaenty(mAepepteinndgixwaCs) hwealsd
Hreovrienweeda.ndT2heU6SFcaWuSleetmepalmoymeeemsbewresr,e
2 of the present.
steering
committee
members
(Caspar.
il 7.1999
Tgrhaezincga.tleantdeainmtehravdiepwlaMnrn.edTetnoniannstpeocnt tthhee faafrtmemaonodnaodfjaWceedntnelasnddfaiyll,Apvriielw7.theHhoewredver,
00 25093
5
DUP 249
Tennans Farm Herd Health Investigation
Cate Team Repan
dmuoreni10n3g.miWsuhnednertshteancdatitnlge.tMera.m TaenndnEanPtAh/aUdScForWrSallpeedrshoinsneenltiarrerihveerddaotnapWperdonxeismdataeyly
s5e:v1e5raPlMh.outrhse.heTrhdehtaedabmeethnerceofnotraeineeledctinedatsomcaollndeuncctlotshuerei,ndwiivtihdouault afnoiomdaolrewxaatmeirn,aftoirons
ainnsdtaslpleedcinmeextn tcooltlheecteinocnlsosiumrmeedtoiatfaecliyl.itatAe anneiwmahleahda-ndhloilndg.resMtrrk.inEtardlevTiecnenhaandt baenednhis
brother device
were
very
helpful
in
handling
the
cattle
and
moving
them
into
the
restraint
The 41 halter,
aandduletxacamtitnleedw.ereEaicnhdiavdiudlutal(l3y8
run into cows, 2
the chute, bulls, and
secured 1 steer)
with was
the head hold and given a general
a
cpohnydsiitciaoln.exaanmdineasttiimoantiinocnloufdianggeobbasseerdvaotniotnheofingcriossosrsa.bnBolromaolditwiaess,coglrlaedcitnegd obfybjoudguylar
svaemnpipluensctwuerree
(r2ecrteadll(y0pc.ol|legcrteeedn
top. from
and | each
lavender top adult. Cows
twbes) from were rectally
each cow palpated
and to
fecal
dwiettheramniniedetnthiefiicparteigonnannucmybsetratausn.d
All one
ewxiatmhiannedimapdrueltgnaantiemdalisnsercetcieciivdeed.
two ear tags. one One Hereford
Gpaolwpa(tiico.n..tbhleo3od9coclolwecti4o2n. aandudlte)arestacgagpiendg.the chute prior to examination. aging. uierine
pEhaocthogadrualpthsbo1v-i3n2e) was individually photographed and identified (Appendix D.
Only est.
wI acsoiwnc(iasneidmaalnd#2dr2a1irneecde(ivAepdpetnrdeaitxmeDn.t
p-ho2tmoagsrsa.phmso4s9t-5c1o)n.sistent
with
a
dermoid
Aadndiimtailon"alelspiohnostogorbaspehrsveodf
the on
farm April
7(.Ap1p9e9n9d(iAxppD.enpdhioxtoDg.,rapphhotso4g3:.
54-58), individual .phs 44-48. 52, 53.
p2hpohtootgorgarpahpshsoufppclatiteldettoetahme atnedamsbteyeMrirn.g cToemnmniatnttee(Ampepmebnedirns D(.ApppheontdoigxraDp,hsph60o-t6o5g)r.apahnd
66) are also included in this report
= Adult Cattlee vPraocnedures Teel ample cllecion
seamen
rcechtalmperaesgunraenmceyntexamination.
T [ee araapssseedd:iansnemctailciedenim
shotographed
|
Twelve calves tags: the larger
were five
examined as a received no ear
group. tags as
The Mr.
smaller seven received Tennant indicated that
insecticidal they were (o
ear be
sold in the very near foture.
cAaltteh.outghhe ttheeacmatdtelceitdeeadmthwaatsthperreepawraesd n1o0 daoniamaplosstuf-fmiocritenetmlyexilalmtionjautsitiofnyoenutohnaenaosriamoarned necropsy at the time of the visi.
009521 DUP 250 5
Temas Fem Herd Healt Iesigarion
Cote Team Repors
bAlylDarn.iHmaablebcikoelro.gicBallosoadmpslaemspl(ebslowoedreansdubfjeeccetse)dwteorheetmaakteonlobgayc,k steorNuemwchBeomilsttorny.Ceanntedr
serology. Randomly selected fecal samples were subjected to fecal flotation.
The following clinical pathology parameters were evaluated:
Hematology
[obcleiom eidncceil ddiissrbibuwiioonn wwiadtnh C Thess pm arameterse ers sm ued sp g hen mesear1 edd do-- e A giy me
Serum Chemistry
CcrosmisncSinanem ansieoss Slo ures nein
TcaHcorudme masnesm
oun
lseepnunionzer
]
<T= oBbRaS 5neSarIed froombToEnmdpelaesmra dUeemd fro8moElDTpArWoensvdeandetpr)
[ovSnersolTogey rem vm er
|conooneemoron Gusmeofdeer and
TET
Son[ehevrosnsGarbao anres mor cla 5-11 = rom nen EE
Jlepaiimoieons Gar (TS rope ss: (379) S S50 ET
Immenoditun te
April 8, 1999
(Appendix E. Three membersof the cattle team (Drs. Moisan, Munson, and Davis-Heller) met with Mr.
Earl Tennant and recorded his recollection of the 1998-1999 herd health history
Drs. Caspar and Horne gave allof the cattle team members a driving tour of the property
DbuertiwnegenthtohseeT(en0narnitps.barthneatnedatmhemeDmrbyeRrusnwlearnedfialbll,eionclsueeditnhgeacodrninveectwiintghipnastthuerelasndfill.
009525
"0
DUP 251
Tennan Fain Herd Health Inestigation
Carle Team Reporc
abdejiancgenutticlriezeekds.at tnheeigthibmoeorifntghceastietegvriaszii.ng. and wildlife. The landfill was open and iWnhcilluedionng stihtee,ftlohrea.caftaluena.teaanmdmmaadne-gmeandeeralstroubcsteurrevsa.tioCnosreresgaamrpdilnegs tohfetehnrveierloanrmgeenrto,und hthaeytbeaalmesswoemreerceocleliepcttsed(a(t3essamrpalnegse/dbaflreo)mf2r/o9m8 btaole1s2/i9n8)thferboamrncoymaprdl.eteM,r.miTxeendnafneted,gaavned mineral supplement he had purchased. tAollnuptlrainttiobniaolloagniaclaylsissambypltehse (Fboarialegde hTaeystcionrgeLsaabmoprlaetsoraynodfgtrhaeinNosratmhplCea)rowleirneasubjected pDreopgarrammen(tCoNfCAPgSrivcu3l.t1u)rfero(mTaCbolren7e)l.l TUhnievseersdiattya twoereveaulusaetdeitnhaendiEextcseilnstpwroeacdoshweemtodels under two feeding situations (Appendix F. models 1-4).
Toe following nutritional parameters were evaluated:
HaySnanmdeGrrain Analysis
Tmoencsum
uennidloblreopron
Tpoususlsphiurom
acdiudsdieetdercsreantte ievveran
T croopnoer
oulwdseesinble nirozen
pnmanganese
|
E esttum ySn| umer
Thien
ee ------_|
324. Miscellancous Dawa
DDru.riSnagrathheCasistpeavrisiifttihnerAeprwile.reMra.nyTefnutnuarnetswiganssoafskdeidsetaosneotpirfoybDlre.msLiisnahDisavhiesr-d.HelTlheer otream owfisthheedTeionncaolnltechterwdhatever data might be relevant (0 their assessment of the health status
Between April and December Heller. Subsequent to notifying
23. Dr.
1C9a9s9p.arMro.f TaennenwabnotrcnoncsaullftwehditcwhicweaswibtohrnDr.wiDtahvais-
"Drc.loDuadvyise-yHee"l.lMerr.exTaenmniannetdbtrhoeucgahltf athned cmaalfdetoaDrd.iaDganvoissi-s.HelMlre.r'Tsenclniannict(lAepftriwlit2h1.th1e99ca9l,f.
On May 26. mandible.
1999. Dr.
Davis-Heller examined cow
#30 for a lump under the right
009525 n DUP 252
Tennant Farm Herd Healt Inesigation
Caile Team Report
325. Wildlife
EPA small
and DuPont each mammals in the
sponsored environmental studies that grazing fields of Mr. Tenant's cattle.
included the trapping of These reports were supplied
0reltahteesca(t0tlsematlelammabmymtahle sptaetehroilngogcyo,mmwietrteeeev.alTuhaeteddatbay itnhcelcuadetdeitnetahme.se reports. as it
Small Mammal Studies
Nonvatetmyber. 1997| Dry RViuensCivrae,ekUSWaEsPhiAnEgntvoinr.onWmoeontdaClouRnetsyp,onWseest | F3H5i1st39o:paRtoelogsy aoffor the
December 3.
Team | Smal Mammal Trapping Effor. Dry Kun Landfil.|
TaMbeiaId: oDwaVoSleummary Smal
1998 fevers | WCaistheiagsiuosne,) WY (URS Greiner Woodard Stamml Tnvergon
TDrh.eCcratutmle atnedamaswsoacsiaatlesso omfadthee aWweasrteVoifrgpienriiaodDiecpdaeretrmerenptroodfuNcattiuornalsuRrevseoyusrccoensd(ucWtVe.d by DNRyin the Dry Run arez. however no reports were available.
4.0 RESULTS
41 Cale
411 Videotapes (Tudiz i)
wTiwldolivfiedesocteanpeesswoefresevpersess!eaiheodu.rsdedpuircattiinogn nwuemreerroeuvsielweesdi.ons.ForTthyeciantdeivsidcueanlesscaenneds 2t0i.
cases). along with the catiie team's order in which they were =-esented
diniatghneovsiidse/octaopmemse.nt.ThaerehperredsehneatletdhipnrToabblleems1
in
the
identified in these videos ere summarized as follows:
1. Kerautis: observed in
Cornea! ulcers, scars and opacitieass, many care. These were all considered
wellasblepharospasm. to be manifestations of
were
"bopviinsk.eyTeh".e afnaceifnlfyec(tiMouussckaeraauttocuonnajluincst)ivpirtoibslceamusoebdsebryvebdacitnertihaesseucvhidaesosMoarnedxetlhlea
ainctkhoefseefcfaetclet.iveAfflfyecctoendtryolouwnegreancdonasdiuslttenctatwtilethwethree doibasgenrovseidsotfo sheavveere2-"3pitn0k2ey5e-'50
osercrmeotrioensf.aceFfiligeusrefsee|dianngda2t atrhee pmreidnitaslfcraonmtvhiudsoeoftaepaech#2e,yeillaunsdtroatnintghethleacfraicmefally
cphrroobnliecmkoernataoccoanljfuannctdivhietrisd.am,Firgeusrpeec3ti(vveildye.otBaopteh#2o)f tdheemsoensatnriamtaelss awnereearbllyicnedntfrraolm
corneal ulcer on the left eyeof acalf: aceflies are seen by the lower eyelid.
00:24
[i
DUP 253
Tennar Farm Herd Hesih Inestigation
Cate Team Report
2p.robHlaeimr.losTs,heneaclkopaencida otail:bserTvheedcoenrvitchaeltaaillosopefcisaomweascamtotslet(ce.ogn.silsotsesntofwi"tshwaitlciche) may also have been due to lice. or may have been related to fescue mycotoxicity. 3a. ndPsouormmseherdsdienggmoefnhtsaiorf ctohaetsv:ide`Tohtiaspecsli.nii caclonssigins,temnotswtitphrommuilnteipnlteinnutthietiloantealspring cvaifdiecoiteanpceie#s2atshwatelwlaassdfeessccruiebemdycboytoMxri.coTseinsn.anFtigausrhea4vidnegmodnesltaryaetdesshaedcdoiwngforfomthe winter coat.
+o.fteHnaiarssdoecpiiaetmeedntwaittihona:nutTrhiteiodniaslcodleofriactiieonncoy.fatnhed cisaetstlpeechiaairllcyoactosmimsoanchianncgaesemsosotf copper deficiency.
5f.esCcoureonmiytcios:toviAcloospiesc.iameacnhdaneircyatlhetmraauamba.oveortahse
coronary band 2 non-specific
may be seen with dermatitis. Figures
5
abyndMr6.(vTiednenoatnatpein#2m)aanryeorfephriessecnattaet.iveFoifgtuhreee7sryatnhe8dma(tvoiudseoftoaoptele#s2i)on) sdoembosnesrtvreadte
tFheesccuaetlme'yscoptroexfiecroesnicse (f"orfesstcaunedifnogoti"n) twhaeswcaotnesriwdehreend tthheesemolsetsiloinkselwyerdeiapgrneosseinst.of
this condition
6a.od"oHmuinnaclheodf ufopo opraipn.ainbfuutlhsatsanbcee:enTshpiescifisicaalcllyindiecaslcrsiibgendofastean maasnsiofceisattaetdiownitohf the fescue endophye toxicity complex
c~.aseTshipnrebsoenctecdomndoisttiolni:kelPyoorrepbreosdeyntceodnddiiffifoenrenist aetnioonl-ogsipeesc.ifiTchfeinedmiancgiaatnedd tdheead cdailafrrwhietah osrermoausstiactartoipohnypraopbpleeamrss.toChoanvseidsetrairnvgedthwehiolteheorthfeirnsdianpgpseainr tthoishahveredh(aed.q. lfiekeedlyancaolnytsirsi)b.utniuntgriftaicotnoarl tionspuofofricbioedncsyc(onpdriottieoinn.-energy malnutrition) was also a
Sproombaeslfyindwienrges rdeeaslc.riFboerdeixnatmhpelsee.ttahpeesdewsecrreibdeidff"icluultmptso"evianlauactoewbuyddveidre(ocaalseth#ou5g4h)twhaeys
dwiefrfiecudletsctorisbeeedbaust"whouunlcdhebde-ucopn"siodre"rheudmapnedin-cuipde"nt(aclasfeisn#din1.g5i,n 1a7n)y-catshee.seAmafeywhcavaete
been related to mycotoxicosis.
lameness, hardware or other condition.
disease (traumatic An individual cow
reticulopericarditis), that was slobbering,
fescue losing
cud.
and was
urinating not clear.
(Acnaoseth#er13i)ndmiaviyduaallsochoawve(chaased
#ha4r5d)wwarheicdhisweaasse,paanlttihnogugwhatshecodnisaigsntoenstiswith
wfeasscuGeenmayicnoltyoxnoinc-osspiesci(fi.icc... "summer fescue hyperthermia), although this presentation
069621
DUP 254
ts
Tennars Farm Herd Health Investigation
Cate Team Report
4.1.2. Diagnostic Pathology Reports (Appendix B)
Oofnlsyomfeourtyopef. MrT.heTemnonsatnts'isgnciaftitclaentwefriendsiunbgmiwtatsedmofdoerrpaotset-tomomratrekmeddicaognpopsetricdeefviacliueantciyonin
the three cows analyzed was formally necropsied.
forThhiesav6y-mmoenttalhs.oldKebrualtlictailsfwaapspaorbesnetrlvyeddieind
tfhreoomnlwyinatneirmal
that
sutnatrrveaattieodni(nit.e.s.tinneaglactoicvceideinoesirsg.y bTahleasnecereoproprrtsotaerien-ienncelrugdyedmailnnAutprpietnidoin)xcBo:mpsluimcmaatreidebsy
are presented below:
a. Dead 6-month old bull Laboratory. Ohio Department
calf submitted of Agriculture,
to the Animal Disease Reynoldsburg. OH on
Diagnostic 2/27/97: Laboratory
report dated 3-10-97 (Appendix B)
History
Gross diagnosis: Histopathologic diagnosis:
6-momnotnhtho:ldrebcuellivceadlfn;ounmeddeircwaetiigohnt:; cdoiranrerahleaopfaocriotinees: died
Emaciation with serous atrophy of fat Intestinal parasitism (trichuriasis) Entericcoccidiosis Kezatiis, moderate, chronic. focally extensive
bD.iagnostTiicssLuaebsorfartoomrya.4C-oyleiaersoeldofHoVlestteeriinnacroywMesduibcmiintet.edMtiochtihegaAnniSmtaatle HUenailvterhsity. Lansing MI on 374/97; Laboratory report dated 3-12.97 (Appendix By
History
4-yeoawrnoelrd:Htoilssstueeisnsucobwm;itdeidedby2-E18P-9A7: dissected by
Heavy meta! screen
Copper deficiency in liver (1.9 ppm vs. 25-150 reference range) and kidney (2.37 ppm vs. 4 = 6 opm reference range).
Mangwaasnessleighwtalsy imnacrrgeiansaeldlyinltohwe iknidlniveeyr: cadmium No heavy metals found in urine (urine fluoride was
6.6 ug/mi){reference range: toxic if 2 14 pg/mL]
DiagnosTtiiscsLuaebsorfartoomrya.9C-oylealregoeldofHoVlestteeriinnacroywMesduibcmiintet.edMtiochtihegaAnniSmtaatle HUenailvterhsity. Lansing MI on 3/4/97: Laboratory report dated 3-12-97 (Appendix B)
History
9-year old owner;
Holstein cow; died 3-2:97, tissues submitted by EPA
dissected
by
085:
DUP 255
Tennsns Form Herd Health Insigaion
Care Team Repor
Histopathologic diagnosis: Heavy metal screen:
Clinical pathology
(only hear, liver, and kidneys submitted: autolysis
and freeze/thaw artifact)
Myocardial sarcocysts
Coppreefrerdeenfciecireanncgye)inalnidvekri(d2n.e0y3 (p2p.3m3vps.pm25v-s.1540- 6 Manpgapnmesreefewraesncmearrganignea)l.ly low in liver; iron was,
elevated in the liver: cadmium was slightly
increased inthe kidney. Urine heavy metals were normal (urine fluoride was.
5.55 uglmi){reference range: toxic if = 14 ug/mL] No significant findings
d. `Tissues from a
Tennant) submitied to
t7h-eyeLaarboorladtroerdycoofwLa(reguethAanniizmeadloPnat6h/1o0l/o9g9y
and
and
dTiosxsieccotleodgbyy
Mr.
School of Veterinary Medicine. University of Pennsylvania. Kennett Square. PA on
6/27/99: Laboratory report dated 7-35-99 (Appendix B)
History
Histopathologic disgnosis: Heavy metal screen:
7-year old
owner:
red cow: euthanized 6-10-99; dissected
tissues submitted by Dr. Davis-Heller.
by
Enteric lesions of minimal significance {forestomach,
asbasrcceoscsyessi:s)intestinal coccidiosis: myocardial
Coppreefredreefnicceiernacnyge).inliver (7.71 ppm vs. 25-150
4.1.3. April 1999 Site Visit Data
a Herd History (Appendix E)
The herd history (Appendix E) was based on Mr. Tennant' recollections during the
interview on April 8, 1999. A written record of herd health was conspicuously absent
Muchofthis can be auributed (0 the lack of outside intervention. There is no record of
veterinary care or consultation with an animal nutritionist. Minimal medications have
been used
Excepefor
on these
the few
animals.
animals
and the
noted in
re has been no
this document
use
(se
of vaccines
e Diagnostic
or modern
Pathology
dewormers
Reports.
above), no diagnostic herd management has
laboratory tests were done on dead animals. The not changed since the installation of the landfill
levelofcaule
0095s
DUP 256
BE
Tennant Farm Herd Health Insesigation b. Physical Examination (Table 2)
Cate Team Repon
ObunllsA.prainld7.| a1d9u9l9t,sttheeerca(uTlaebltee2a)m. eExsatmiimnaetded4a1geasnifmoarlst,heinadcullutdicnogw3s8raadnugletdcofwrso,m 23 atdoult gbreeaotledrerthtahnar99yyeeaarrss., TThwiesntiys-asheevrednof(27a/g3e8d)ccaotlwes; w3e2roefptrheegn3a8ntc.ows were estimated to Body Condition Scores aBvoedryagceonsdciotrieownassco3r.e5s((3B=CthSi)n,w4e=rbeorbdaesreldinoen,a5-17-9issccaolnes.iSdceorreedsorptainmguemd)f.rom 2 o 7; the Clinical Signs iHnacilrucsoiaotnscbynso:rmthaaltitwiaess lwaenrceedevainddenetmpitnie9do.f tMeam41macaruyleg.laOnndeluamnpism,alcohnasdisatnenetpiwdietrhmal c(hsrcoanricussmuaest.itiRs.ectwaelreexianmtienraprteitoendoafsaobnsececsoswessourggaestcedcthue pmresuoenfclfeooarfotuinstciroan-onaebcndtoimsvineal fat necrosis Clinical Pathology (Tables 36; Graph 1) Hemstologs Eanriymtahivsonw(eTraeblceon3s:ideRreedd abnleomoidc,cell indices were generally in the low-normal range. No LDiefofkeroesnt(iTaalbcleell21c:ounTthsewteortaelcwohnistiedebrleododincvealllicdoduunetstowetrhee 3w6ithhoiunrthdeelnaoyrmbaeltwreaennge. collection and tesing. Clinica! chemistre (Table $1 Mwiotshtmeilledctdreohlyydteravtailonu.es wSeirnceeinthtehecahtilgeh-wneorremapleatnoesdlidguhrtilnygeltehveadtaeydlirgahntgeh,ocuornssiosfteAnptril 7. wunheixcphecwtaeds.unDseehaysdornaabtliyonwaisraml.soatnhdehmaodstnoliakcecleysesxtpolawnaatteiro,nclfionrictahle deleehvyadtreadticorneawtiansinneotin 40/31 cate. dMioasgtno(s2i7s/o4f1d)eohfydthreatcaitotnle(thoatdaleplreovtaetiend =togtallobpurloitneifn,rawcthiiocnh+alaslobucmorirnelfartacetsiohni)g.hlyInwailltha ctahtetlreef(e41r/e4n1c)etrhanegeg.lobulin fraction was elevated while the albumin fraction was within
[LEE
0
DUP 257
Tennant Farm Herd Heal Inesugsuon
Caule Team Report
Gamma glutamylransferase (GGT). a sensitive indicatorofactive liver disease, was cmounsscilsetennetclryoswiist.hiwnasthealnsoornmoarlmarelfeinreanlcleofratnhgee.catCtlree.atHinoewekvienars,ea(sCpKar)t.ataen indicator of mamiinniomtarlalnysfeelreavsaete(dAiSnT)3,3/a41lecsasusleen.siTthiivse miingdihctatboerforfolmivleeruaknodcymtuesdcilsesodleugteinone,ratthieonr,eswulatsof the 36 hour interval between blood collection and testing.
Specialchemistry.
Prolactin: `According
Plasma prolactin levels to the testing laboratory
(Table 4 and Graph 1) were significantly depressed. (Dr. Neal Schrick, UniversityofTennessee). an
average prolactin level for cattle on fescue-free pasture (for April) was 171.6
micrograms/liter Tennant samples
(ng/mL) (ie.. reference mean = was 110.1 ng/mL and 36/41 of
171.6 ng/mL). The average of the the Tennant cattle were below the
41
reenfdeorpehnyctee-mienafenct(e1d71f.e6sncuge/m(Ls)i.mulIantceodntbryasetr.gaontaamvienreagteartprraotleacatdimninliesvterlaftoironc)atwtlaeson105.8
ng/mL (data from Dr. Schrick). This average was similar to the Tennant herd average
(110.1 ng/mL) and 24/31 of the cattle were below this reference level (105.8 ng/mL).
According to Dr. the Tennant herd.
Schrick.
these
findings
were
highly
supportive
of
endophyte
toxicity
in
Copper: Blood copper copper assay was below
levels were in the deficient the limit of detection.
range
for
26of41
animals:
one
Selenium: Blood seleniurs levels were normal fo4r1 of41 cattle.
Pepsinogen: Pepsinogen. 3 blood enzyme indicator of parasite damage to the
anboormmaasurme.ferweanscemreaansgeu.redThiense10dcaotwas.supopnoertsetederthaencdonocnleusbuilol.n
All that
values were within the sbomasal ostertagiasi
was not 2 problem in adult cae in this herd.
Serologs (Table 6)
BLV(Bovine Leukemia Virus) Johne's (Mucobacierium paratuberculosis antigen) Brucella BBVVDD (MBiocrvoipnleatVeirAusssDaiyar(rvhireeamainatidgeetne)ction) Bluetongue LEeHptDostpyiprea2in(tEeprirzoogoatnisc (H5esmuobrvrahriaegtiicesD)isease of deer)
1/31 positive [1/214 positive 2/41 positive a1 ol 3/41 positive 2/12 positive
NLeopnteoosfptirhaemsiegrholoregfylevcatlureessidsuuaglgevsatcecdinaathieornd-tiwtiedrse
problem. Positive titers in purchased animals or
for BVD natural
and
exposure (0 this disease
these diseases. has been in the
The local
discovery of two deer population
positive
EHD
titers
was
evidence
that
008530
DUP 258
1
Tennant Fasm Herd Health Investigation
Cate Team Report
Parasitology
Routine samples.
fecal The
flotation (Table 4) magnitude of ova
revealed shedding
parasite ova in 11 of could be categorized
14 as
randomly selected rare to moderate
fecal
pPaarsaassiitteisgmrowuapss niontclcuodnesdidceorcecdidtioa,betaapmeawjoorrmsh,eradndprsotbrloengmyline-tthyepeadnueltmactaottdlees..ThIen.testinal
sheddingof small numbers of oocysts and helminth ova is expected of mature cattle,
d. Hayand Grain Analysis (Table 7)
rDeugrairndgintghehecartdtlfeeetdeianmg'sprvaicstiitcteos.thTehTreenenalanrtgefarromun(d4/b8a/l9e9s),oMfrh.ayTeinnntahnetbwaamsyairndt,erviewed (i3d/ebnatlief)iewdearserceoplrleescetnetdatfiovreaonfaltyhseish.erTdh'sisfofroargaeg,ew(eire.e, vhiasyu,alglryasisn/sfpeescctueed) awnadscfoerdeasdamples libitum,
During the hay
tahpepesiatreevdis1i0t,bfeohraiggeh
quality was and forage
asnuabljyescitsiv(eTlaybleeva7l)ualatteedr
as poor. The substantiated
fiber that
level
of
observation. feed can be
Fiber levels of consumed. Dry
forage matter
play an intake
(iDmMpIor)taisntinrvoelreseinlyderetleartmeidntiongfihbeorwlemveulcs.h
oaf
pAocucnorddsipnegrthoeMard.peTrendnaaynto,fmaagtruarien amniixmaclosm,poonsethde oTfendrnyanetarfacromrn,,wseoryebealasno mfeeadl,fivaend omifntehriaslfsee(datweascotualkdennoatnbdeavnaalliydzaetde.d, despite the existence of grain receipts). A sample
eAvnalEuxacteelthseprdeiaetdss.heUestinpgrotghreafmor(aCgeNCaPndSgvra3i.n1)nuftrroitmioCnoarlnealnlalUynsiisvecrosnidtuycwtaesd buysetdheto tFowroamgoedTeelsstifnogr mLaabtourraetcoroywsof(etahrelyNolratchtaCtiaornolainndadDreypparretgmneanntto)fweArgerisceulletcutreed(tToaeblxeam7i),ne the current feeding program (Appendix F).
According to 1999 fed five
tphoeucnodmspouftethrismogdraeilns,anadcforweeicnheoaircley
lactation hay was
(model #1) in the in severe negative
spring energy
of
rbeaqluainrceeme(n7t2)..5%Thoef rleiqmuiitredemneunttr)ieanntsd alveasislsaebvleerweopurlodtehinavdeefaicnieegnactyiv(e90im.p9a%ctofon milk
wprooudludctrieoqnu,irpeer2s.i4stteinmceysotfheprcoodrunctciuornr,enatnlyd bceailfnggrfoewdtht.o bAe icsoocwaluonrdiecr(mthoidsefle#e2d)i.ng system
nSiemgialtairvley.enaedrrgyy pbraelgannacnet(c7o5w.2(%moofderleq#u3i)reimnetnhte)sbaumtenofteeddeifnigcisenytstienmprwootueilnd(a1l2s5o%b)e. inThe
nseagmaetidvreyepnreerggnyanbtalcaonwcem(a8x7i.m7i%z)i.ng dry matter intake (model #4) would still be in
008500
DUP 259
1'
Tennan Farm Herd Health Inestigaton
Cate Team Repose
`tThheedbieotsd.y cTohnediitmipoancstcoofrtehse(BpCoSosrq)uaolfittyhe hfoerradgeweornetchoinssifsatremntanwditshubtsheeqeuneenrtgyendeerfigcyit of
deficits pasture.
were
considered
to
have
chronic
effects
well
after
the
cows
ret
to
adequate
42. Miscellaneous Data
Following suspected
the sick
site visit. animal.
Mr. Mr.
Tennant Tennant
consulted with Dr. broaucaglfhwitth
Davis-Heller regarding 2 2 "cloudy eye" to Dr. Davis-
tHheelrleerw'assclnionitchi(nAgprwirlo2n1g, w1i99t9h).theDre.veD,aevxicse-pHtelfloerraesxlaigmhitnmeudctohiedcaelxfudaantdedoentetrhmeinceodmethaat
which was easily wiped away.
On May 26. 1999. Dr. mandible. The lesion
Davis-Heller was aspirated
examined (pus) and
cow #30 for a lump subsequently lanced.
under
the
right
43. Wildlife
43.1. Videotapes (Table 1)
T(chaese2#0 4w9i)l.dloiffencoadsieasgpnroessteinctveadluien. thTehevisdeeowtearpeesalwlecroensailldedreeaddtaonbde. ienxcciedpetntfaolrdoenaethcsase
sdeiantches.theIrne fdaicdt.ntohtesaeppdeeaarthtso abpepaenayrecdontsoibsetemnocsytincotnhseisstpeecnitesw.itlhoctahteiorna.nodromtiwmiinlgdoef the
c#a4r9c)aswshesicwhhipcrheswenotuelddwbiethfohuenmdorirnhaagheealftrhoym
ecosystem. the nostrils
The may
individual have died
dead from
deer (case epizootic
ohfemtohirsrhdaisgeiacsediisnealsoceal(EdHeDeIr.(pTerhsiosnadliacgonmomsuinsiwcoautlidonc:orDrre. spCornudmwitothDrt.heSkykneosw)naenxdisttheence
finding of some EHD seropositive catle in the Tennant herd.
4.3.2. Small Mammal Data
Tshwroewpsa.thaonldogmiisctes)rceavpiteuwreedd tohne tlhieveTreannndanKtidpnreoypehritsytoilnog1y99f7ro(mUS45EPsmAalElnvriordeonntmsen(tvoalles,
RTaebslpeon3s9)e. TeNaomledsriaofntsrecphoarrta:cteDrriystRicunofCrheepeakt,otWoaxsihciintygtoofn.neWphorootdoxCiocuintytyw,eWreesetviVdierngt.inia;
Although several teratogenesis.
anomalies
were
identified.
none
were
considered
suggestiveof
toxic
The 1998 small 1998) observed
mammal no gross
atbrnaoprpmianlgit(iUeRsSinGrtheeincearptWuoroeddwanairmdalCsly(vdoelesst,udsyh,reDwesc,eamnbdemric3e,).
43.3. Deer Studies
TthheeWceastttleVitregaimniwaasDempaadremeanwtaroefoNfattwhreaplerRieosdoiucrdceeesr(rWepVroDduNcRt)ioninstuhreveDyrsycRoundnuacrteead. by
Although available.
tOhenetetaemamremveiemwbeedrs(oSmyekeosf)
thhaeddaattaeslheepehtosnefrcoomnvtehressaetistoundiweist.hnDor.reCprorutms
were of the
00a 19
DUP 260
Tennant Farm Herd Healt Ins stigaion
Cate Team Repor
WV DNR additional
regarding dees herd information. From
health in the Dry this conversation.
Run area it was the
in order to acquire some catle team's understanding
that
evidence of low fertility overpopulation:
rates
in
young
does
was
probably
attributable
to
deer
epizootic hemorrhagic disease (EHD) has been diagnosed clinically and
serologically in dead and captured deer, respectively:
-
bovine virus diarrhea from Dry Run:
(BVD)
has
been
diagnosed
serologically
in
deer
not
far
Tn addition. the team has learned that outbreaks of EHD in West Virginia deer were rpuebploirctaetdiobn.eeFieenld 1M9a8n0uaalndof1W9i8l9dl(iSfoeutDhiesaesatseersn iCnootpheerSaotuitvheeaWsitledrlnifUe.DSi.se2ansdeeSd.t]u. dy
Since there population
was was
no not
evidence of considered
an EHD or BVD outbreak to be a contributing factor
in in
the Tennant herd. the the cate herd health
deer
problems. for any of
Also. there was no the disease entities
evidence identified
that the deer herd was in the Tennant herd.
a
useful
sentinel
species.
5.0 DISCUSSION
The six veterinarians comprising the caule team agreed that there was conclusive
evidence toxicity.
that the pinkeye.
Tennant herd malnutrition.
was and
suffering from four copper deficiency.
major disease entities: endophyte The clinical. leboratory. and
historical daa substantiate that these herd health problems on the Tennant
ffaorumr.conditions
can
readily
account
for
the
chronic
Endophvte toxicity
According fescue hay
to in
the the
history winter
acquired on and pasture
April 8. 1999. the herd has been fed a die that approaches 100% KY31 fescue during
of KY31 the
summer. There has The clinical signs in
been no supplemental the Tennant herd that
pasture or other forage fed to these animals highly suggest endophyte toxicity (fescue
mycotoxicosis) include:
+
swelling the creek
and pain at during hot
the coronary band (coronitis) weather (Figures 5-8);
and
above.
with
cattle
that
stand
in
+ +
ppaotocrhsyhteadildianlgoopefciwainwtietrhclooastssof(tFaiiglursew4i)t;ch:
+ birthof undersizedcalves:
+ +
poor conception numerous vague
adnidsecasaelsvisnuggrgaetsetsi:ve
of
immune
dysfunction;
060525
DUP 261
0
Tennant Farm Herd Heslh Insestigaion
Cate Team Report
Other clinical signs that are consistent with endophyte toxicity include:
+ +
cfaotncneocmriotsains,t ppresrumpteiovfesc.oapspedeiradngenfoiscceidenebcyy:rectal palpation in cow #15;
+ +
gpeannetrianlg fianilcuorwe o4f5t,hescuagtgleesttiovethroifveh.yperthermia;
eVnadsoopchyotnestrifcutnigounsisassseoecniaatseda rweistuhltfoefsciunegemsytciootnooifcaosniusmbiserAocrfeemrognoit-uinkecoaelnkaolpohidisa.luTmhe
ewthail.c.h 1p9r8o5d)u.ceTshepsereloalliknael,oipdesrlaoclicduimnuel,aNt-eacienttyhlelfoelsinceu,eagnrdasNs-sfeoerdmyd!urlionlgingero(wStthu.edemann.
acquiring the the alkaloids
highest may be
fcoounncednitnrasttioornesd
a the hay.
greatest
maturityof
the
grass.
Additionally.
Tprhoedcuocreodnibtyisepnrdoobplheymteobtsoxeircvietyd iinn tthhee "vfiedsecouteapfeosot("Fisgyunrdersom5ea.ndS6i)gnwsasoftfypeisccauleoffootthat
agnendersaolrleynessisartinwointhe roerdbuoctehdrweeairglhitmbgs.ain.Hyoprelroessmoifaowfetihgeh,corrooungahrhyaibrancdoaot,ccaurrcshebdetbwaecekn,
the al.
d1e98w4c1,lawAsracnhdinhgooofvetsheabnadciks
gweanserraelployrtaecdcboymptahneioewdnebyr sinomtheesvwiedleloitnagpe(sHeamsken.
et
"hunched and "humped" posture in some cattle,
Pdiesrsiipphaetrealhevaatsodcuornisntgrihcottioenatfhreorm. thTehsiesvpahsoeancotmiveenoalnkaislokindsowrensualsts"isnudmemcerreassleudmspbility to s(uOgsgbesotrinveee.otfalt.h.e1s99u2m1.merThselupmapntsiynngdarnodmed.rooling by ared cow (#45) in videotape 2 was
The has
ablisrethbeofenunddoecrusmiezendtecdal(vBeosk.to
dams et al..
i1n98g6e)s.tinTghiasdimeat yhibgeh
in by
eanmdoepchhyatnei-isnmfessitmeildarfetsocue
tbhleoovdasvoecsosnesltsrimcatyionrecsualutseinddbeycrtehaeseerdgocti-rlciukleatailoknaltooidtsh.e gVraoswocionngstfertiucs.tioTnhoefetfhfeecuttehraisne
been pups
dforocmumfeenmtaeledsinfemditchee
that were material
deuxrpionsgegdesttoatthieonewnedorpehaytleigdhtuerrinbgirgtehstwaetiigohnt.,
Mouse were
delayed 19911
in
post-partum development. and
grew
slower than
control
mice
(Varney.
et
al.
oEfvitdheenaciel tshwaittecnhdiosplhayrtgeelytoaxinceictdyotianl,fefsrcuoem gvreatzeirnignacraytplreacmtaityiobneerrsetshpaotnshiabvlee efxopretrhieelnocses
with similarly affected vasoconstriction result
cattle. in dry
gTahnegrmeonseotfstehveeretaifloarnmds
odifgeitnsdo(pRahdyotset-itisn,duetceald.
1994:
Hemken. etal. 1984).
Rinecprreomdeuncttailvley edfefpercetsssferdocmotnhceepitnigoenstriaotnesofinencdatotplheygtrea-ziinnfgesitnefdecfteesdcupeasitnucrleud(ePaterson, et
al. 1995). potentially
In the play a
Tmeajnonranrtolheeridn.tthheeugnraaczcienpgtaobflpeacsotunrceesptwiiotnh
100% KY31 rate. A poor
fescue could conception rate
009527
2
DUP 262
Tena Farm Herd Heal Inesugarion
Cate Team Report
could where
also be secondary 10 a breeding occurs year
lackof round.
intensive breeding management at The advanced age of most animals
the Tennant farm, in the breeding
herd could also be interval. Likely. 2
expected to be a cause for depressed combination of all three factors have
fertility and contributed
an to
extended calving suboptimal
ferility
.
Tofhethpeocoorwgsroowrt2holifmittheednguernseitnigc cpaoltevnetsiaclouilndtbhee hmeurldticfaocutlodrilaeladastoweplolo.rTmhielkapdrvoadnuccetdioange
aanmdonpgootrchealbfrgoroodwtcho.wsSciomuilldardlye,prleascskocfalpfrgorpoewrthn.utrTihteioinnogresatiloancokfoefn2dobpahlyatnec-eidndfieestted
fescue could lead to depressed milk production due to prolactin inhibition (Hurley. et a..
1950; Paterson. etal. 19951. The mechanism is considered to be due to the
dopaminergic effectsofthe endophyte pituitary gland (Schultze. etal. 1999).
ergopeptides
on
prolactin
production
in
the
bovine
Endophye intoxication is also considered to have an immunosuppresive effect by an
ainptpoaxriecnattliyoninidsirreecstpornosuitbel.e Afolrthdoeupgrhesasneedcdiomtmaluneevifduennccteioenx,istthserteo aspupgegaersst ttohabtefensocue
apparent lack etal. 1997).
of immune response Indirectly. however.
to vaccinations of cattle fed diets high in fescue there is a relationship between immune function.
(Rice.
e1n99d8o:phSyatkeer.intetoaxl.i.cat1i9o9n5:a.ndSctoeperpsergrsatzaitnusg oefndcoatpthlyetoe-nianfheisgthedfetsalcluefedsiceute(Dheanvneisl.oweetral
sinerduepmrceosptpeedrmcoonnocceynttrea-tmiaocnzsotphhaangtehofsuencntiootnos.n
a high-endophyte tall This is apparently an
fescue diet. resulting effectof the
decreased uptakeof copper by the infected tall fescue plants. Another source has
recorded 1999)
depressed
globulin
levels
in
animals
grazing
infected
pastures
(Schultze.
et
al
FTahtenneeccrroostiiscifsat3 ahcecrudmpurloatbiloenmosfarceamtoestglryazwiinthgitnaltlhfeeosmcueentwailthanhdigehtceonpdeorpihtyotneeallevfealts.
depots. masses
and consistofhard masses of partly mineralized within the sbdomine! cavity that were identified
fat. Cow during the
#15 had palpable herd exam on April
7.
r1e9a9c9.tionThceasuesimnagsstheesfwaterneecmroossitssiusgugnecslteiavr,e ohfowmeavsesre,s ionfanfefcercotteidcafnati.maTlhsethbaitocarheemoincaaldiet
ohifgchhoilnesNt-efroorlm(ySltuaenddemNa-nanc.esye]tall.olin1e9.85t)h.ereAinsiamaclonssiwsittehntinrcerdeuacsteidondioeftacriyrcluelvaetlisngoflevels
endophyte-infected fescue had decreased body condition and increased fat necrosis.
Pinkeve
FTaecnenfalnitesfwaerrme(Faisgeurrieosus| parnodb2l)e. m Aidndtihteiocnaatltlley,inthtehye hvaivdeeoatlaspoedbereencoardpirnogbslteamkeinn ootnhetrhe
years. according (0 the history interview. Faceflies were seen
provided in small
by Mr. Tennant during numbers at the eyes of
the the
Apri caule
8. 1999 during the
April
7au.t1u9m9n9alhiesr.disvisaitv.ecrteoprrefsoernMtionrgaxaenlelaarlbyovsipsr.inthgeientfeisotlaotgiyono.f Tmhosetfabcoevfilny,e Mpiunskceyae. Control
eannii
DUP 263
Tennar Farm Herd Helin Investigation
Cate Team Repon
of these insects is based on the care. Insecticides and
preventing insecticidal
the ear
ftlaigess,farsomapfpeleideidndguornintghethleacvirsiimta,larseecerfefteicotnisveof
csounstcreopltsi.bleSeccaotntdleardiulryi.ngthoeuitnbsreecatkiscoifdepsintkenedyet.o limit the spreadof M. bovis between
Safefveecrteedfacactetflle.y iSnfoemsteatoifontshecapnoorreswuletigihntpogoarinfdeeedsccroinbsedumipnttihoenhiasntdorcyoonfvtehrseiohneradmaonndgthe
videos may be due to "fly worry" The manic in oneof the videotapes. was likely due to the
sltaargmependiungmofobftfheleicersatle,
that
was
described
Malnutrition
Mhaaldnuiidernittiifoinedwpaosocrognrsiodwetrhedratteosbaenad siingfneritfiilciatnytapsrsopbelceifmicinptrhoeblTeemnsnaanmtohnegrd.hisTchatetloe.wner
Tthheislowwasbocdoynsciodnedrietdioanmascnoirfeess.taDtiieotnaorfy prreoqtueiirne-meennetrsgyofibneseuffficcaitelnecychaanndgweadsrarmeaftliecctaeldlyin
during the life environmental
cycle of the animals and during the year. and physiological stressors as fluctusting
particularly with respect to ambient temperatures and
such
miomipsrteusrseiocnoonfditmiaolnnsu.trliatcitoantitohna.tgfroolwtlho.weadntdhebrveiseidtisnogf(ARpicrei.l
1991). 7 and
8
The clinical were confirmed
by
the
results of the feed analysis of the hay and grain mix rations taken during the visits
Copper deficiency
As indicated by the heavy metal three animals. copper deficiency
analysis performed is a problem in the
by two laboratories. on tissues from Tennant herd (Appendix BY. In
H1o9l9s7teicnopcpoewr dbeyfitchieenAcnyimwaals HdeiaalgtnhosDeidaginnosat4i-cyeLaarboorladtoHorlysotfeMiincchoiwgaanndStaa9te-yUenairvoerlsdity
isnacEraisfticeLdan7s-inyge.arMoilcdhiregdanc.owInby19t9h9e. LcaobpopreratdoerfyicoifeLnacrygewaAsnirmevaelalPeadthinotliosgsyueasnfdrom a
Toxicology of the University Furthermore. serum samples
of Pennsylvania. Kennett Square. taken from 41 adult animals at the
Pennsylvania. farm on April
7.
1999
rexealed that 26 a the reference
of the 41 laboratory
(63%) had (Table 4).
serum
copper
levels
below
that
considered
deficient
cColuinsi.caplosoirgqnusaolfitcyohpapierrodneftihceiceonwcys,seaenndoonvetrhegrToewnnnahnotovfeasr.m Twheirse wlaigshtreenpionrgteodfbtyheMhra.ir Tennant and shown in videotapes made of the herd.
`efTfheecctlsoinficaslucehffdecetfsiocfienccoyppaerre wdeeflilcdioenccuymearnetemdult(iNpRlCe.,a1n9d96t)h.e cTlihneiceaflfeacntds iphnycsliuodleogical
iinmemxutnreemdeefciacsieesn.cieDsu.ripnogordiqsueaalsiet,y choaiprpecroadtse,fiicnicernecaysecdanfrraegsiullittyionfdbeopnreessaendd lseuvdeldsenofdeath
tumor necrosis infections and
dfeapcrteosrs(eadcfyeteodkiinnet)akweit(hGernegseulltbiancgh,abentoarlm..al19t9e7m).perature
responses
to
gant
DUP 264
5
Tennant Fam Herd Hest Instizaion
Conte Team Report
aIcmumteunpehadseefipcrioetneciinesrerseploantsede taoncdolpypmerphdoecfyitceiernecsypaornesimvuelnteispsletoanmditiongcelnudsetdimeuplraetsisoend
(Arthington, et ai.. 1996: Gengelbach. et al., 1997).
efciency i expected fo be present at his ime and to continue. The relationship As there has been no documentation of any copper supplementation of the herd. the
between high endophyte fescue grazing and copper status in the feed has been described
(Dennis. et al., 1998). Copper deficiency is widespread throughout the United States
(Dargatz. et al.. 1999).
Toxicology issues
Based upon the
Response Team
draft report entitled Dry Run
of the US EPA, carnivorous.
Creek. 1997
piscivorous,
from the Environmental
omnivorous, insectivorous
and
`herbivorous mammals in the Dry Run Creek study area are at increased health risk due to
exposure to metals. fluoride and wrichlorofluoromethane. At least with regard to metals.
of concern. diagnostic evaluationoftissue and fluids collected from three animals from
the Ten
Bolton
nant farm (two
Centedro) nots
submitted to Michigan State Universit
uggest elevated concentratoifoannsy
y and o
metal.
ne
In
submitte
addition.
d to N
urine
ew
(two samples submitted 10
Michigan State University
Michigan State University) and
from the cow evaluated ac New
bone (one sample submitted
Bolion Center) samples for
to
fluoride analysis did
The urinary fluoride
not measure
values were
concentrations above expected or "background" values.
6.60 ppm and 5.55 ppm and one bone fluoride value
was 1090 ppm (expressed on a fat free. dry weight basis). Urine and bone fluoride
concentrations in adult cate consistent 3000 ppm or greater (expressed on a fat
with free.
fluorosis are 15 10 dry weight basis).
20 ppm or greater and. respectively (Osweiler
et
al. 1985). In addition. there was no clinical evidenceofchronic fluorosis in theTeanant
herd.
Exposure 10 trichlorofluoromethane
a lackof toxicologic benchmarks fo
was
r this
considered
compound.
10 be a default risk factor
However. available toxic
basedupon
ity data
cdehrliovreodflfuroormocianrhbaalnastisounchstsusditersiucshilnogrocfolumomroomnetlhaabnoerahtaovrey laoniwmaaclusteinadnicdatcehrtohnatic toxicits
(ndMeearvgvedolauo.spmse1yn9st9t9a)el.mtsoSuxiicgchnansatsass.lsedotochianaritgteydaafwnfidetcthinarcceoupotrreodditunoacxttiiicoivntey.paeCrrhefloorerrvomefarlnsucioebrleoacnedafrfabercoetnssnaoatnret4hnenotOcUeOntXrCai
6.0 RECOMMENDATIONS
hTehred mvoissitt simnpdorretvainetwgeonfehrael irnevceostmimgeantdoraytidoatna,frwoomultdhebceatftolre ttheeaom.wnaeftreorfcohmeplTeetninoanontfthe phreordgrtaome.ngage veterinary and nutritional consultants in the designof a herd health
080 ih
DUP 265
Tennant Farm Herd Health Investigation
Cane Team Report
`Endophvietoxicity: With dietary forage that contains nearly 100% KY31 fescue, fed Guring all seasons, the immediate goal would be for the dilution of the endophyte in the Gdiieftfebryentmifxoirnaggethseouhracye.anAd sphaosrttu-rteewrimtghoeailthweorulnodnb-een1d0orpehdyutceeitnhfeesctoendtefnetscoufeeonrdaonpohtyhteerinfested hay and pasture to 50% or less of the diet. primarily by supplementing the diet with higher quality forage. An acceptable long-term plan would be to replace the fescue pasture and hay fields with a non-endophyte-infested forage crop or crops over time. again with the goal of diluting the dietary endophyte consumption. Crop management should be auempted under the supervision of specialists in forage and grazing management. Pinkeve: Prevention of pinkeye (keratoconjunctivits) in the immediate future should be attempred by an approach that limits the spreadofthe infectious organism. Moraxella bovis, from carrier caule to susceptible caule. Effective fly control, through the use of insecticide-impregnated eartags or some other proven method. is perhaps the most effective control method that should be practiced during the warm months. The insecticide-laden eantags should be rotated every year in order to circumvent the development of insecticide resistance by the local facefly population. An additional long-term approach that may be employed is the breeding for cattle that have dark faces, By selecting for dark-faced cate. the comeal damage that is caused by the ultraviolet light of the sun is minimized. However, while minimizing the damage to the corneas of the cattle may prevent overt lesions of keratoconjunctivitis. the loss of condition from severe fly infestations will not be avoided by selecting for face color in cate. Thus regardlessof the type of cattle in the herd. insecticide fl repellants should be used every year Malnutrition: Rations and pasture nutrition should be planned with the assistance ofa Specialist inbeef caule nutrition. In the Tennant herd. there was evidence of gross protein-energy malnutrition. 2s well as concerns about macromineral (calcium. phosphorus. and magnesium) nutrition. Trace mineral and vitamin deficiencies are common 0 many beef herds and should also be addressed. In the development of a cation for this herd. particular attention should be paid by the nutritionist to the local trace mineral and macromineral deficiencies. Copper deficiency: Copper is a trace mineral that is crucial to the healthof cattle vet is missing from the diet of caule in many areasofthe North America. As copper deficiency was suspected clinically and confirmed biochemically in the Tennant herd. the provision of a high copper trace mineral supplement. again under the supervision of abeefcattle nutritionist, should be a priority year round. This is especially eritical considering the. prevalence of endophyte-infested fescue on the Tennant farm.
00052
DUP 266
Tenn Farm Herd Health Investigation
Cate Team Report
7.0 CONCLUSION
`sTuhfefreeriwnagsfrcoonmcflouusrivmeajeovriddeinsceeastehaetnttihteieTse,nsnoamnet coafttwlheihcehrdwewraes.poatnedntcioanlltyiniunetesrrteolbaet,ed: eAnsdospuhybtsetanttioaxtiecditbyy(tfheescculeinmiycaclotaonxdicloasbiosr)a.topriynkfeinydei,nmgsa,lnauntrdihtiisotno.riacnald dcaotpap,etrhedesfeicfioeunrcy. conditions readily account for the chronic herd health problems on the Tennant farm,
`nTuhteithieornd, hienaaldtehquinavteestviegtaetriionnarryevcaerael,edanddefliaccikenocfiefslyincohnterrodl.maTnhageelmaecnkotf,viancccliundaitngiopnooarnd
internal parasite control relatively isolated herd
programs
did
not
appear
to
have
a
substantial
impact
on
this
eDveisdpietneceanofextohxaiucsittyivaesrsoecviiaetweodfwhiitshtocrhiecamlicaanldccoonnttaemimnpaotriaorny
herd data. there was of the environmen.
no
8.0 REFERENCES
Endophite Tovicity References
1.
Boks DI. BonJd: Effects en calfbirth weight.milk
iynieplrd.egannadntcablefgerfohwetifhe.rsJA grazin Sngcifi 6u3n(gsuusm p-piln)f:e2c9t7e.d
tal! fescue 1956
2.
DNeeaonnissphSoBd.iuAnllcenocrViGo.phSiaalkienri_KoEn.
cFoopnpteernotcoJnPc.enAtryaatdioJnYMin. tBalrl ofwenscuCeP.:
Influsnce of J Anim Sci
76:2657-2695. 1995.
3.
Hembken RW. Jackson S3:1011-1016. 1984.
J.
Boling
JA:
Toxic
factors
in
tall
fescJuAnei.m
Sci
+
Hurley WL. Convey EM. soncenteations as affecied
Leung K. Hemken RW: by tall fescue summer
tBooxvicionseispraonladcttine,mpeTrSaHt.ureT.
and T3 Anim
Sci S1:374.379. 1980.
3.
Ofsunbgoursn-einTfGec.teSdchamniddftunSgPu.s-MfarrepelefeDsNcu.e
Rahe CH.Steenstra JR: and ergotamine tartrate
Efoffcoenscumitng on selected
7ph0y:s2i5o0l1o-g2i5c0al9.va1r9i9a2b.les of cattle in environmentally controlled conditions. J Anim Sci
6.
Paterson toxicosis
J. Forcherio onbeef cattle
C. Larson B, productivity. J
Samford M. Kerley M: The Anim Sci 73:889-898, 1995.
effects
of
fescue
7.
cRyaadnoosbtaicttserOiaM..
cBllavoiobdactDeCri.a,GainysecCtCs:,
aDnidseaasneismaclas.usedIn:byVettoxeirnisnariyn
plants. fungi. Medicine: A
009-25
DUP 267
Tennann Farm Herd Health Inestigauon
Cate Team Report
textbook of the
OM. Blood DC.
diseases
Gay CC.
eodfitcoartst.le,Baislhleiepr,e
Tpiingdsa.llg,oaPthsi,laadnedlphhoirase1s5,328-"16e1d.1,,
R1a9d9os4tits.
8. ERxiacleuRatLi.onBloodfgehtutmoDJr.alScihmurmiugneGG,reSswpeocnskeesriWnSc,aFtoentegrnaoztinJPg, eAnldloepnhyVtGe,-iAnkfeecrtsedRMor endophyte-free fescue. Vet Immun Immunopathol 59:285-291, 1997.
9.
Saker KE. Monocyte
iAmllmeunneVGc.ellKalrneistpsoknyseJ. aTnhdatccohperperCD,staStwuseckiner,beJerf.
WS, Fontenot, JP: steers that grazed
endophyte-infected tal fescue. J Anim Sci 76:2694-2700, 1995.
10.
Schultze AE. bovine serum
Rohrbach BW, biochemistry
pFrrofiibloeusrgasHsAoc,iaWtaedllewritIhC,prOolliovenrgeJdW:conAsltuemrpattiioonns
in of
endophyte-infected tall fescue. Vet Human Toxicol 41:133-139, 1999.
11.
Stuedemann JA. AB: Association
Rumsey of blood
TS. Bond J. Wilkinson SR. cholesterol with occurrence
Bush of fat
LP, Williams DJ. necrosis in cows
Caudle and tell
fescue summer toxicosis in steers. Am J Vet Res 46:1990-1995. 1985.
12
Vamey DR. Vamey endophyte: effect on
cLoAng.enZiatvalosdePvMe.lopWmiegnltesawnodrtphupMDg.rowStihegienl
MR: mice.
Tall fescue J Dairy Sci
74:260-366. 1991
Malnutrition References
13. CRliicne NLoE:rtThhAemeerf~fFooeofdncuAtnrtiitmisoPnraocntre7p:r1-o2d6u.ct1i99v1e.performance inbeef cate. Vet
Copper Deficiency References
14. dAenfhiicniegnicoyn oJnD. acCuotrez-hphaLsRe. Bplroetcehian cF:oncTehnetraetfifoencst, ofsupmeorloyxbiddeenudmi-simnudtuasceedacctoivpipteyr bloevukionceyhteerpnesutmibceurs-s1.. aJndAnliymmpSheioc7y4t:e211pr-o2l1i7f,era1t9i9o6n, in beef heifers inoculated with
13.
Dheairfegrast.z DJAA.VGMaArry2F1B5.18Cl2a8r1k83G2B.:
Serum copper concentrations 1999.
inbeef
cows and
16.
NDeeoatnhissphSiBo.diAulnlencoVeGn.opShaikaelrumK_Eo.n
FcoonptpeenrotcoJnPc.enAtyraadtiJonYMi.n
Brown CP: tall fescue.
Influence of J Anim Sci
76:2687-2693. 1998.
009i
DUP 268
=
Tennars Farm Herd Health Investigation
Carle Team Report
17 Gengelbach GP. Ward ID, Spears JW. Brown TT: Effects of copper deficiency and
copper deficiency coupled function and response of
with high calves [0
dietary iron or a respiratory
molybdenum on phagocstic disease challenge. J Anim
cell Sci
TELS 1997.
18.
National National
Research Academy
PCroeusnsc.ilW:ashMiinngetroalns,.D.in:C.N5u4t-r7i4e,nt19R9e6q.uirements
of
Beef.
th ed.
Toxicology Issues References
19.
MagdaS: Fluorocarbons. McClellan R and Welsch
FIn.: edTiocoxrisc.o.lAocgay.deImSi!ecd.P,reMsas.rqSuaanrdDtiHeg,oS,c6h5a9f-e6r6S2G..1999.
20. Osweiler GD. Carson TL. Buck WB, Van Gelder GA, editors: Fluoride. Clinical and Diagnostic Toxicology. Kendall/Hunt Publishing, Dubuque. IA, 183-188. 1985
21 USEPA Environmental Response Team: Dry Run Creek. 1997 (drafo.
=
aan
DUP 269
EY
Tennant Fam Herd Health Insestgation
Cate Team Report
9.0 GRAPHS
Graph
1:
InHdeivpiadruianlizCeadlbeloPoldassammaPprloelsatcatkienn
(April from
7, 41
1999). adult cate
during
the
catle
treesapmo'nssivivseith1o0rmthoeneT,enpnraolnatctfina.rm Gwrearpehainlalluystzreadtefsotrhtehelaebnordaotpohryy'es-
rineffeesrteendce(1m0e5a.n8sngfo/rmeLn)doApprhiyltep-afsrtueree.(17T1h.e6 anvge/rmaLg)e apnldasemnadopprholyarcet-in
evnadloupefhoytre-tihenfTeesntneadnrtefheerrednc(e1.10T.h1ensge/rmeLs)ultwsaswesriemihliagrhltyo tshuepportive of
(tTheesdtiianggnolsaibosoraftoerny:doDprh.yNteeilmySccohtroixcikc,oUsniisveirnstihteyoTfenTneannnteshesrede)
09: DUP 270
"
e
"
:
l|Lag
`
o
:
zi
L oTdE
Ez
i
" i
"
:8:gzzsggzszee-
(lw/u) unoejord
C0dn1
30 DUP 271
Tennan: Fam Herd Health Insesugation
Caute Team Report
10.0 FIGURES
Figure 1: Faceflies on the head ofa calf. Fparcoebflleym(oMnustcheaTaeuntuamnntalfiasr)m.infIenstaadtidoint,iownastoctohnesicdoensrteadnttohbaeraasmsamjeonrt dbiysease cflliiensi,catlhilsy cballifndhaodn stehveerveidbeioltataepreal(pkheortaotowcoansjutnackteinviftriosmanTdenanpapnetarveiddetootbapee 2)
Figure 2: Faceflies on the head oaf cow, b"Tihliastecraolwkewraastotchoenjduancmtiovfittsh.e c(aplhfoitnofwigausreta1k.enLifkreomheTrecnanlfa.ntshveihdaeodtsaepveer#2e).
FigurFeac3:eflLieefst aeryeeaofveactcoalrffwoirtthhefabcaecftleireisalanadgecnetnstroafl pcionrkneeayle opacity (`mkaeycatporcoognrjeusnscrtiovdiitfisf)usseuccohmaesalMourlacxeerlatliaonboavinsd. clCiennitcarlalblcionrdnneeasls.op(acpihtoiteos.was taken from Tennant videotape #2)
Figure 4: The
Delayed sheddingof videotapes presented
the winter coat on a multiple catle with
beef cow. delayed shedding
of
winter
caosatnsu.tciTihoinsailsdaecfliicniienccailess.ig(npohfotteon waasssotcaikateendfwriotmh Teenndnopahnyttevidteooxticaiptey =a2s) well
FigurTehi5:s Allesoipoenciwaasanpdreesreyntthienmsaevaebroavlecatthtelecoinrotnhaervyidbeaontdap(ecso.ronIittiiss)a.common sign ofendophyte toxicity and is generally referred 10 as "fescue foot (photo + 35 taken from Tennant videotape 52)
Figure 6: This
eAxlaompepclieaoafnd"efersyctuehefmoaota"biosvseimtihlearcotrootnhaartyprbeasnednt(ecdoroinnitfiisg)u.re
5.
(photo
was taken from Tennant videotape #2),
Figure 7: Three cate standing in the creek. cAautneusiunatlheprseudimleecrt.ionThfoirssbteahnadviinogriinswkantoerwnwatso bdeesacsrsiobceidatfeodr wtihethTenant efonodto"p)hayntde htyopxiecritthyearsmiitap(r"ovsiudmemsesrofmeescrueel"i)e.ff(oprhobtoothwacsorotnaikteins f(r"ofemscTueennant videotape #2).
FigurAesS:deTsewroibceadtfeorsftiagnudrieng7.instaanpduidndgle.in water provides some clinical relief to cisatatslseowciitahtecdorwointithis".fesAclutehfoouogth".n(opn-hsopteociwfaisc.taakpernedfirloecmtiToennnfaonrtthviisdbeeohtaavpieor 2) 0054.17
31
DUP 272
rer ese Re Ge
PRS alr" Sor iT SEs
4 ==
syHoa PES ESS d
CA J
EN RY
raed voy 0 AN SEN
7a
Re = Es
Figur1e
EL TEA
od GE
Lo Te
NE
Se
Fgus2
ean!
DUP 273
2
pry pi) y
|
FE i ~.
SM =
pm
BeS.Cll0 Crone
en. Ee E22
so .
F
=e
i
(PECTS
2
LEE CR
oT
Te
DUP 274
ei
000515
3
Ee
m= TE.
EEE
=
a
Bay SS
d= aT
= =
-
FE
0 IE
Rt =
- CE =
FZ
|
mooo <
ans
FF
See
Figure 5
Ea
=
pE e =s
Ee
=
ee
aE
= #7
:
Ti
Ea _
--
Zi
Toes
. 009:
DUP 275
2
Ex 3 EE
- E SS lr t
BEE SE
Le NY
R eeA e --
a
een)
=rE a dl
-
2co
= = = = AP 2
EE a =2x =a e oN T Te a T E e e8
EE rEE nT eae a RTA nee LD See
C09
5
DUP 276
?
Tennant Farm Herd Heslh Investigation
Cale Team Report
11.0 TABLES
Table I: Reviewof Tennant Farm Videotapes Table 2: Individual Animal Data: Clinical Signs Table 3: Individual Animal Data: Hematology (erythron, platelets) Table3: Individual Animal Data: Hematology (leukon),and Special Chemistry Table 5: Individual Animal Data: Clinical Chemistry Tabl6e: Individual Animal Data: Serologyand Fecal Exam Tabl7e: Tennant FarmGrain and Hay: Nutritional Analysis
000.
DUP 277
36
Tenant Farm Herd Heath Investigation
Cute Team Report
Table I: Review of Tennant Farm Videotapes
Tape #1 (cases 1-18): Tennant Farm: New England, Wood Co., Wa January &February, 1997
Animals)
T||Cow, Hereford | ++
dnecek:salcopaersci"iah,ubsmcapeleiddng-,| |+.
probable Tee, "humpdifeficudltt-oapuprepcia"te
+_(swnpo,wing)
ontape.
Z|
Cow, Hereford | + +
c_o(Grsnneoawliongp)aciy,
+ cpionmkeeayel.scar, probablysecondary 10
3|| 2black bulls
|+
possible discoloration ofhair (notclear),
| not clFeromatrape
7]
Con.Hereford
|
+ +
|
[1
t(hsinnowing)
+ very thin,probadbule1y0
itraipvooressd, decforodeconasumsptieonadnd
| |
+ (snowing)
`mnaosttisceaetnioonnpvriodbeol,em.althoughteeth
|
[Con
Hereford | +
+
possible hunched back | +
atgeeethuprnoblkemcn uanuksnoeoownw f.ponssi;ble notclear from tape.
|!
(notclear). + snowing)
6] Cowltani i|
| alopewicl siwiath., || tsnowing)
|= wtoaiullhdaiinTcolsusdeGimfeecrheanndiiclald,ialigcen.os fescue toxicosis, and selenium
7| Cow |
+ I
(asnlowoinpg)eiclsiwiatc.h,
| ttaoixlichoasirsl.oss Gifierenial diagnosis would includemechanical, lice,
|
|
tfoexsiccuoesist,oxicosis. and selenium
[CA black |. sdneaodw,(dmed29/97) in | + hoboutvneost uanulsueall,onger thannormal.
|
+ overgrown hooves,
bilaletnseoparciatiels,
|. "cold cataracts" (post mortem),
+ teeth normal,
+ +
blmacuklcooroonwfnuetceesest,h,
|. ffecaelimnucrceoecutsusmn,ormalforstagnant
+ lneescironosp,sy:noother |. naetcrroopphsyy:oflafactk: eomfafcaitatsieorno,us
+ sted: haddiarthea
probably duetostarvation.
00001
Tabl1e: Revie.of TemFanrmVaidenouptes
DUP 278
37
Tennant Farm Herd Heath Inesigaion
Cale Team Report
Table | (continued): Review of Tennant Farm Videotapes
Tape #1 (cases | - 18): Tennant Farm: New England, Wood Co., WVa -
F] sibia
January &February, 1997
Presentation
Diagnosis/Comment
STcar,Animal(s) neck: alopecia,
probable Tice,
fbalcaeck/white +| dleinasmohreac,omeal
+ +
pcraoubsaebolfedicaormrehaelascuanrkn(ohwarnd,to ell).
T0| | Cow, Hereford | +
opacities thin,
+ comealopacityprobably secondary
+ +
acboomveealhooopvaecist:y,alopecia| +
diffpeirneknteiyael,diagnosis of hoof
+ 2dnidahnyeperemia,
dleesrimoanrsitisn,clfuedsecumeecthoaxniciocsails. and
!
+ cmaouissetodferdmiaatrirthiesadaunedttohuinnnkinnogwn
i
i
unknown.
C+|
13 Cond |
||
|
|
{| +
| i|
T4|Cov.red |+
i|
{| +
|
ve sores slobbernglosing eud
(uroinnagtrionugn,d).
il switch alopecia
neck: alopecia, wil swich: short hair
[robes | + sobberingurnadng Geren]
diagnosis includes hardware and
clihkoelliynedsuteertaoisnediinvhiidbiutailonco(lwess + alafofpeectceida)d,ifferential diagnosis
ifnecslcuudeeosrmseeclheanniiucmalt,oxliicceo.siasnd neck: probable lice, | + tianlclhuadiersdimfefcehreanntiicaall,dilaigcen,osainsd fescue or selenium toxicosis.
17 Cow. Hereford| +
possible hunchedback | +
dmioatgcnloesairsfirnocmlutdaepse;hadridffwearreential deitsiecausleop(ewrriacuamradtiitcs).
089.00
Tabl1e: Review of Tennant Farm Videotapes
DUP 279
36
[I ----
Catt Team Repon
Table I (continued): Review of Tennant FarmVideotapes
Tape #1 (cases 1 - 18): Tennant Farm: New England, Wood Co., WVa -
January & February, 1997
# | Subject |
Presentation
|
| Animals)
Diagnosis/Comment
18| Cow, red
+ dead in bam,
(same as #13) | + corneal opacity,
+ necropsy: no other
lesions.
|
|
|
|
|
|
I
|
|
|
|
|
+ (is this the 9-year-old cow
submitted to Michigan?), + comeal opacity may be postmortem
artifact,
+ necropsy: serous atrophy of fat, + noted: normalpostmortem changes
include moderate to severe autolysis, pseudomelanosis of intestines, interlobular emphysema
(agonal),
+ also noted: normal front teeth
+ large gallbladder suggests period of
+ acnaourseexioaf,death unknown |
Table 1: Reviewof Tennant FormFarm VidVeidoetoauppess
06a
DUP 280
37
Tennant Farm Herd Heslh Investigation
Cate Team Repon
Table | (continued): Reviewof Tennant Farm Videotapes
| [Lins Tape #2 (cases 19-60): Dry Run Harris PC. Wood Co. - Off North Fork of
Lee Creek, New England, WVA
.
FSi T Animal(s)
Presentation
Diagnosis/Comments
15 [ Calves, muliple
~ comeal opacities of | + fly problem with secondary varying severity; some| pinkeye,
with exudate and/or blepharospasm,
| + hair coat shedding and coloring probably due to a nutritional
+ fly problem (summen).| problem.
|
| shedded andor light-
|
| colored coats
1 Tr |S
raccoon?) 77 | Cow
| = | car
i
possible
skeleton
~
incidental possible.
death:
no
diagnosis
|= comeal opacity i
[comes searsscandary 0 piney
J+
cpoosmseiablleaphaecadiitsli.(not
* |+
cheoamdeatlilsncoatrcsleecaornodnartyapte.o pinkere,
| clean
Tar |
i
I. fies
|
T+ dead (<1 month-old) {+ comeal opacity.
|+ |
causeof death unknown. comestscaseconduy to pines
i+ (burning carcass)
[GE BERETS)
l
! T|+. cfloymeparlobolpeamcities. [+ dead
!
possible.
I
`Ny problem pinkeye.
withsecondary
I incidental death: no diagnosis
possible.
1
TableI. Review:of TennantFarmVideotapes
DUP 281
eda
#0
Table 1 (continued): Review of Tennant Farm Videotapes
Tape #2 (cases 19-60): Dry Run Harris PC. Wood Co. - Off North Fork of
Lee Creek, New England, WVA
7 Subject I Presentation
Diagnosis/Comments
Animal(s)
31 | ad
+ dead,
+ cause of diarrhea, emaciation and
|
|
!
32 | Crow
34 |! Calves,
multiple
3 [Cow
|
(dehydrated?), serous | + lung emphysema was agonal and
||+ agonal lung
| emphysema
+ dead
ianocivdeinetal death: no diagnosis
T+
|
comeal opacity
T+ comeal opacity.
| + thin
: possible.
+ comeal scar secondary 10 pinkeye.
+ comeal scar secondary 10 pinkeye.
+ diagnosis of the causeofthin condition not possible.
38 !| Salamander
39 Toad
|l . dead
dead
40 | Newborn calf
|
[+ contracted tendons,
+ big hocks
T| + ipnocsisidbelnet.al death: no diagnosis
+ incidental death: no diagnosis
+ difficult to evaluate from tape; may
be congenital contracted tendons.
possible.
Table 1: ReviewofTennant Farm Videotapes
00:00
DUP 282
4
Tema Farm Herd Healt nsesigaion
Carte Team Report
Table 1 (continued): Reviewof Tennant Farm Videotapes
Tape #2 (cases 19-60):LeeDrCyreReku,nNHearwriEsnPglCa.nWd,ooWdVCAo. - Off North Fork of
#1] Subject T | Animals)
Presentation
Diagnosis/Comments
=| Cow
praensptiirnagt:ioinncreased ~ dhifyfpeernehnetarlmidaiadgunoestios siuncmlmuedersfescue
||
+ ditaoxgincoossiiss,uncerain.
37 | Raccoon
|
| 39 f|Deer
|
50 | Revit
ST Tuner
1
|
Hak
!
I Shall
{T+T debaldood(yfrensohs)e.
|
| + dead ad
iTae
+ incidental death: no diagnosis
possible.
possible + hdeeamtohrprhaogicsdidssueaesiteooebfpidzleoeortyic
(EHD)
+ incpoisdseibnltea.ldeath: nodiagnosis incidedathennoGtaganoln
[iponssibdle. en possible
vo
dso
possible.
55 | Cows. multiple I above hooves: alopecia,| + differential diagnosis includes
||
|
i+ ovpeosrsgirbloywneryhtohoevmeas,
|
mtechoanixcaalinddemrcomaitsoittidsse.rmfaietsciutseisd,ue
unknown,
F [Bullcows. || comedopaciies. hcoomoefallensgctahrnsotesicgniofinctaondptiakresy.
| multiple
+ aabolveohoaponvdeeesrcytiheama | + hmoeocfhdainfifcearelntdiearlmadtiiatigsn,osfiessicnuceludes
|
toxicosis, and
to unknown.
moist
dermatitis
due
Table 1: Reviewof Tennan arm Vidseosrpese
cadiin
pup2ss
Teanan: Fam Herd Healt Inesigation
Carle Team Report
`Table 1 (continued): ReviewofTennant Farm Videotapes
Tape #2 (cases 19-60): Dry Run Harris PC. Wood Co. - Off North Fork of
Lee Creek, New England, WVA
FT Subp | Animal(s) |
Presentation
Diagnosis/Comments
38
|Cows. multiple| +
|
above hooves: alopecia,| - hoofdifferential diagnosts inclodes
possibly erythema.
mechanical dermatitis, fescue
i
+ poor shedding of coat in some animals
toxicosis, and to unknown,
moist
dermatitis
due
|i |
+ pnuotorrithiaoinralcopartosbhleedmdoirngfessucgugeests
|
mycotoxicosis.
60
Cmuolwtsi.plheeifers.
[+ +
thin. delayed shedding
i
+ deffrionmittiavpeed-iapgrnoobsaibslyno2tnpuotsristiibolneal deficiency.
sNVgoiiredeeeTishh"s tEhnelarenraaxrtrsaotlrourb'dsuetswsesrmseoneycronnofsittdhherereSbdlIabcyEkethnegedcmatsuelte3h7t8oerapmaphatotclbhoeygimacecaclluacrnaootnsesd.owmeFrsoeraseorxnaomwrpemlraele.,ptrhoAepleeseoeandicmbmiyerBonEvoxs scpleusieidatine tchosmmteabnites regarcing normal organs. durin the dissections Shown in he deotspes. wert nox
Tabl1e: Reviewof TeFnarmaVidnosptes
000"
DUP 284
#3
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DUP 295
Tennant Farm Herd Health Incstigation
Cate Team Repors
12.0 APPENDICES
Appendix A: Abbreviated Curriculum Vitaeof Cattle Team Members
Appendix B: Diagnostic Pathology Reports
Ohio Department of Agriculture: #4977-97
Michigan Animal Health Diagnostic Laboratory: #1792571
University and
oTfoxPiecnonlsoyglyv:an#iUaPL9a9b0o2r7a0to2r,y#o9f9L0a1r4g3e7Animal
Pathology
Appendix C: Dry Run Safety Plan
Appendix D: Figures 1-42: Photographsofthe 42 adult cattle;
Figures
43-66: Miscellaneous and caule
photographs
of
the
Teanant
Farm
Appendix E: Herd Health History (April 8, 1999 interview)
Appendix F: Dies Analysis: Computer Software Modelling
ede
55
DUP 296
Tennant Farm Herd Health Investigation
Cate Team Reporc
Appendix A: Abbreviated Curriculum Vitae of the Cattle Team Members
:
TT CeifhiceaNraiemon-- esn:: DrV.M-- DP.eDrirpyloLm-- atHeabAeCcVkP-- er -------- ----
Employment Chioeff, PLeuang.eSAcnhiomoallofPatVheotleorgiyn.aryLMaedibcioner,ofaNPeatwthoBoolrloigyoyn CnednteTro.xiKcoelnongess. SUqnuia.re
Eaucarion: JunsPtA College (BS. 1972-1976)
GUnniisveerrsstiyt ooffPPeennnnssyyllvvaanniiaa.. SScchhoooollooffVVeetteeriinnaarryy MMeeddiicciinnee ((rVesMidDent1,96199-5199.7139)92)
Adiliaions: PAemnenrsiyclavnaCnoilalVeegteeorifnaVreyteMreidniacryalPAatshsloocgiiastiosn
----------
AAmmeerriicanAAsssoocsiinaiioonnofVVeetterinaryLLaabboorratoryDDiissggnnostiicians
TT beNaemes: Dr. Lisa Davis-Heller
CEemrpnlfcoaynmoennst: DPriVvatePracuioner. St. Mary's Veterinary Clini. St. Mary's, WY.
Educaiion. Atiliancas:
OOhnioo Sisttee UUnniivneerssiityy. College of Veterinary American Veterinary Medical Assocation
Medicine
(DVM,
1979-19551
OWheisot VVeitregriinniaarVyeMteedriicnaals AMsesdoicciaaltiAosnsociation
-- HolsIHi onlrinsatircis oVneatlerViV entaerryinSae orcyirAycue punctun re Socim ety n00S0 een
TT
Name: CenfiDceasuroeness.
DDUr.N.PeDtieprloGm.atMeoAisCaVnP.DiplomateABVE (ood anal specialist
speci
bese
Employment. Education:
VCelteevrLeailbnaoanrrdaytSoPtraayit.heoCNlooogrmitmshtunCaainrtoylFieCnloaldDlIeengpveaers(ttAimSgea.tnot1ro9.7f4RA)oglrlicnusluArnei.maRlalDeiiseeha,seXCD.iagnostic
EEUaanssittveTTreesinntnnyeessossfeeTeeeSSnttnaaetiseeseUUenn.iivCeeorrlssliiteyyge(o(M5fS.,VeMMtiieccrrrioonbbaiirooylloMoggeyyd..ic1i19n97e758)()DVM, 1981)
Aflistions: AMKmaiencrshaiisgcaaSnntaSBtoetaeUrndiUvnoeifrvseViretstyietr(yiRne(asRreeyasriPcdrhes.nctiV,eiVtoeentreeirrnsianrayrPyaPthaotlhooglyo.gy.1919959-51)998
``AAmmeerriiccaann CAoslsloceigaetoifonVeotfeBrionvairnyePPartahcoilotgoinsetrss
``AAmceardiecmayn oAfssVoetceiraiinoanryofCoSnwsiunleiaPnriasctitioners
AmAAemmreeirriicccaaannnAVAsesstoerciinaaattrioynMoefdViecteaerriAinsnasaroycLiLaaatbbiooornatorryyDDisgnnoossiiciaannss
AppendiAx: Abbreviated Curriculum ViotfCaalee Team Members
DUP 297
esses
se
|
|
bee: Andrew Hartten
Rob Pinchot
Sharron Laas
JHLitde
:
HD Ramsey
D.D Jackson
1M Migliore
RBanerjee
RIZipfel
AJPlaytis
11%, 200
:
089-70
EID089382
{
SAeNniDoRr ECoAunsV.elMALINOWSKI, ESQ.
DoaoPouatLegral,Rboom D078
FPVhiaolxcnei(:ag0i()o30n7,T)D7aE74s619484938
:
January 12, 2000
VVIIAA OFVAEXR(NcoIveGrHlTettMeAr oInLly()wi[t4h13a-t4t4a3c-h6m5e5n3t]s)
LDeoguagllas Johns, Esquire OGenneerPlaalstEilcesctArivcePnluaestics Pittsfield, MA 01201 Dear Mr. Johns: D5uP7ontto[tcThoeinmscselert1nt-ie3nrogifsfFMuCrt-.h1e4Dr3atl(oealoVsuoarnrecDfoenervreVeredslatdotei'aossnoJCaf-n8ulaoasrrtyaw5me,em2ko0n0ain0udemmmpoaerireflltsupoerBcoioofbicRalilcychieny of
ctanoate).
pSroemsceenrcmeRienoggfatFrhCde-ip1nrg4e3siteiennmcee1no,vfDirFuoCPn-om1ne4tn3tdaiildn mneenodvtiisrauobwnmamisetnrtaeaTvliSmeCewdeAida.w(iet)ThhnioentiD8f(uiePc)ao-trnietopnoartntoabEiPliAtyofthe
to not be reportable. The reasons for that decision are as follows:
d deformed
* TTTheSeeCrAtoox8uisc)oTlsoSugCbymAoisf8sF(icCo)-n,s1u4db3amtihesadssiNobonesve.enmIrbefeparoxret1de9,dtto1oy9E9o9uPaAlansdbtywbeoetkhaDcuoPpoynotfatnhde3aMteisnt
Psruobgmriassmi.ons were made both before and during the TSCmAad8e(eb)yC3o4mp.liOatnhceer Audit
* Johudenetd,hiescW1h9ea8sr1tgelVoeifrtgeFiCn(i-aa1t4aDc3ihveiidnsooDntohoecfOWuhaimtoee1Rri)nRvteteosrohtuahrescWebsVee(nWrVeDpoWrRt)ed.toFEoPrAexRaengpiloen iIna citoniscesnttarteadtitohnatofFaCb-o1u4t3 0s.1prmegs/eLn.t iOnuutallll000S0Sd(ipsecrhamriDgteWWsVRi0nt0(oc0ot1ph2yet7Oo9h)iEoBiAnRa.i.vReer.gioNnotIe)i,t
EID089383
-
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"
General Electric Plastics
-2-
January 12, 2000
was later were not
determinedthatthe caused by FC-143.
defects
observed
in
the
study
referenced
in
this
letter
:
Thbeeenprreepsoerntceedotfo FECP-A14R3egiinotnheIaTqauinfderthuendWeVrlDyWinRg.thFeoWraesxhaimnpglteo,naWtotarckhsedsite has
SuDrovceumyesnutbm2iisssainonexmcaedrpetifar1o9m8W5atsohEinPgAtoRnegWioornksII"T S(ocloipdyWtaostthee WMaVnDaWgRem)e.ntIUnnit
bseecetniodnetBe-c4t,edpairnatghreapahqueinfteirtlaetdp"pRbelleeavseless., Spill, etc. it is stated that FC-143 has
rTheepoprretsteeodncEePoAf FRCe-g1i4on3 IiInItahnedLtuhbeeWceksptubVliircgisnuipapDleypwaerltlsmeinntpopfbNlaetvuerlaslhRaessboeuernces (WoWrVkDsN'RV)er.ifFicoartieoxnamIpnlvees,taitgattaicohnedWDoorckuPlmaenn(3tVTi)s raenpoerxtcesrupbtmiftrtoemdWiazs1h9i9n0gttoonEPA RpaeggeionnumIbIe(rceodpy18toofWthVeDVNIR, iat nisdstthaeteWdetshtatVtihregiLnuibaePcokllpuutbiloincCsounptprloylwDeilvlissihoan)v.eOn detectable levels (ppt)ofammonium perfluorooctanoate (also called C-8). AdminisBtraasteodruhpaodnktnhoewalbeodvgeeocfortrheesppornedseenncceeso,iftFwCa-s14d3etienrvmairnieodustheantvtihreonEmPenAtal media, both at the plant site and outside the boundaryofthe plant site. 8() repIonrtaidndgitiisovna,gause,youunckerntoawi,n,EaPnAd cguurirdeanntclye(ofnothtehecrpiatsetrisaevfeorraclayveiarrosn)mebnetianlg TSCA r3e7w7r3i5t;teJn.ulyIa13it,s1l9a9st3)N,otEiPcAe osftaCtleadritfhiactation on TSCA 8() reporting criteria (58 FedReg
"With regard to interprets section
non-emergency 8(c) to require
reenpvoirrtoinnmgenotfailnfcoornmtaatmiionnattihoatn
pirnofvoirdmeastieovn,idEenPcAe
ofwhwiicdhesbperceauasde
environmental of the extent,
distribution patter, and
oamafoucnhetmiocfatlhesucbosnttaanmcienaortimoinxtsuerrei,ouasnldy
threatens mutation,
odreamthayorsesreiroiuosulsy
threaten: (1) or prolonged
Humans with incapacitation
.c.a.ncoerr,(2)birntohn-dehfuemctasn,
organisms `Thus, the
with mere
large-scale presence of
or a
cehceomliocgaiclalsluybsstiagnncieficianntanpoepnuvliartoinomnendteasltrumcetdiioan,.
raebpsoernttinsgoumnederotsheecrtiornel8e(vca)n.t" information as noted above, would not trigger
AdotetshneoltevpeolssetFhCe-1th4r3eaistporrepsoetnetnitniaelntvhirreoantmdeenstcarlibmeeddiaab,ovDeu.Pont concludes that FC-143
oben r(ev)IienewnmevadirkaoignnamigenntothnaelcdereeEcpiPosrAitoininsgosnuwea8s(stch)ienrefnpleourwxtaaebnnivdliiirttyow,namDseunPdteoacnlitdgreueditcdhoaangtcnteih.ziesdtdheactitshieongwuoiudalndce
EID089384
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General Electric Plastics
-3-
January 12, 2000
Items 2 and 3: Correspondences to the Town and Test Data on Town Wells (LubeckW)eanhdavteestlodcaattaeodnthtehefotiolwonwiwnegllcso:rrespondences about FC-143 to the town
+ (LJLuPnPSeSDD1)3w,ait1ne9wr8h9tiaclpehsttiietnrsc(oansttctaeatncethdreaodtnDioponacsgueram2noegfin4tnt)gheftrocootmvhe1rL.0luebttoteec2r.kt2hPpautpbblF.iCc-WS1ee4r3vaiwrceaesnDodtievatiemscaitroenedoifn pwaeualrylcswh,rassiaetmdepntlhreeessseopfowuewslhelisctoahnthdhaitsvheeattaeltshroefbLrePoemSnDtthenesotLewPdSbdDyr.aDwusNPoiottsnttdhra(itsnekeDiunngePxowtnattbuelsrluefbtr)s.oeqmudeinftfleyrent
* rMaananarlgcyeshde2fs3rp,oem1r9f09o.2r0m9le]edtXeoprnpabstattmaopc0lh.ee4sdptDpabok.ceunNmofetrneotmth5ta)htrJteoXeothfmeetaLhnePsSnDeeswtpirLmoaPvtiSed.DinwWgeelrleassr,ueltRnseosotuflatwsare ofany writen response to this letter fom the LPSD,
Follow-up
ahpespirteactieaIttfeoycrooeunctenaiecvetidnmgaena.ycIoafdpdGyioEtfiositnh.aolulidnfdoercmiadteiotno sorubfmuirtthaenr c8l(acr)ifnioctaitfiiocna,tpiolne,asweedwoonuoltd
Very truly yours,
Attachments
Andrea V. alll
ce: SGtEevPelaAsutsitcsin [Fax: 413-448-6590] OPinttesfPilealsdt,iMcsasAsve0n1u2e01
MDaanlaegVearn, EDneviVreolndmeen[tFaalx:Pr30o4g-r8a6m3s-7128] 2G.e0n.erBaolxEl6e8ctric Company, Plastics Mfg. Div. Washington, WV 26181
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:
November 19, 1999 CERTIFIEDMAIL
220450 ATER ed ed 8 ech
1% =
E 3 38
(DoAcumeSnetctPiroonce8s(s9i)ngCooCrendtienrat(o7r407) UOfSfiEcePoAfToxic Substances 4W0a1shMingSttroene,t,DSCW20460
=Z as =
Re: ATmSmCoAn8i(cu)mSPUeBrfSlTuoArNooTcItaAnLoaRteISCKASNHOT3I82C5E-2O6N-:1
Dear Sir
S3tMudbyapserrefcoerntmleydcwoimtphlaemtemdoanireuvmiepweorfftluhoerodorcatfatnroeaptoert(PoFnOaA6)-bmyonCtohvparnicmeatLeabfoereadtionrgies,
Madison, Wisconsia. M
capsule deposition of0
ale cynomologus
(2=6), 3 (n=4), 10
monkeys wer
(1=6) and 30
e give daily
(n=6) mg/kg
doses
ammo
by intragastric
nium
S`peevrefrlaulcrwoeoecktsa.noaDteo.sinSiggwniafsicsatnotpipleldnewshsiolcecutrhereadniinmatlhse r3e0comv/erkegd.doDsoesignrgouwpawsitrheisnumed at
a2n0dmhgi/ghgd.osAet tghreouepnsdwoefrteheaslilxomwoenttodhrdeocsoivnegr pfeorr9io0ddatywso. Oanniemhailsghidtohseecaonnirmoall, wmaisd
asraecrfeilftitcoiebndemcoomrpiobuunndd-rceolnaditteido.n Ootnhdearyhi29g.h dTohsiesaanniimmaallssaulfsfoereexdhihbeiptaetdiclilveesritoonxsicwihtyi.ch
The following findings are being reportedby 3M under TSCA 8(c):
- &TSihgemnriyefkiwcgaainsitnaioynccr1oe0rarmseegsdhpgolin/vddeiarny-gt)oa-dtbveoedrrymsiweenpiaaglthhtsolraoatngiyeosi.wnetrhLeeiovtbewrsoewrleoviwegedhsttipndraoleslsedsgoerssoeuwgpersorueps. reversedafter a90dayrecoveryperiod.
35S =: 7& =2:
-
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fluorine or as PFOA, have not been associated with clinical bepatic toxicity.
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(DAomc:umeSnetctPiroonce8s(s)inCgooCrednitnearto(r7)407) UOfSfiEcePoAfToxic Substances PNaogveemNboe.r2 19, 1999
- TcIenovnaeddaidltiitaoisnopneo,cniofsnitecudlcyoawudsadeyoosf1e3m5(o.3rbmAigdn/iktigyn/.ddTeapyhe)entdeeefsnftteacnptiasmboaobllsowegarysversdeiavcnirtiehfwiicosefdaitnhniismmaoclarsiweebrduieaddnnoott
CCoonmspiosutnedn-trweiltahtetdh.e sTihgenirfeicwaenrtehenpoateofxfiecctist,yootbhseerrtvheadnaitntchreeahsiegdhldiovesrewaenidgmhtaiy ntohtebe
remaining three animals testeadt the low dose.
3ThMishcahseamnidcawlililspcroondtuincueedbtoyco3nMduacntdmeisduisceadlbmyoniintdoursitnrigalofciutsstcohmeemriscaasl apprrooduccetsisoanid.
`workers and to reduce potential for worker exposure.
Acopy ofthefinalstudyreportwillbeseattotheEPA whenreceived:
.
Please contact Dr. William Weppner, 651-733-6374, for further information.
Sincerely,
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Dear Gerry, AECseepTodEriotsuscyuisaascndeeddanaoyhndAoptsrhuiell:fonr1ae3tleebdvyanpptheocnfieln,ufoorrEomPcAahtenineoiencdasilnst,oyouwrrietvpihoewsisneicstosimaiplloentfeoorcucscoopniotenrsoPlFofOoAnfinal ESTrpveairrfsointmoernnsetTaoluctgafinanotgiecpSahucaiirtdme)as:cokaiInnhdeetiinrcfesoq)ru,meastetineovdni,cionnafnnoedmnathtauilmoanneffiaenncdctlsuednevsstiurdohineemasel,ntthaleffeexcptossuce iSEVteaugidaliraedbslteoa,npdwreoijnerfcoerqtmueaedtsitcoonmt,phalteitniycoolnuuddicalntagermiofanynidttophrerionvsgit.daetusuIsfoWffiitnahanly troheengpooliranttgsestsarteuadndnioetsmoswtith ee Elen SE i preriminary reports in your possession of controls W2e000r:eq"ueRstethgatayotrhued'upirlovfniodnegatu"esdwiptahcfltuhoezoacbhoevmeicianlfso,rmoautrioniniotniaPlFOAintbyeceMsaty 2i6s, Ehoecuhseodveon{phefrofcimuaotriooonetoynlPRsOuSlfboynicAPFaiclid28(,PF2S0)00and we request Sat you provide pE1eecfyloCuuhoermhoiaccvhaeelnsaincyfaolosaf,lltvhoeew aufsbeoqvuteeosticnofnthofaritmr,amtiboouynrApoirnnitleorteh2s8et,r, 2c0aa0nr0db,oxtyhlyeoanutperdionvioirtdieaslulltyhfeoindaetnetdify pFoerqtuleusocreodchienafiocramlastiobny Mianyyo19u,r 5p0o0s0seasnsdiononofothceorntrcoaltboonxyloattheedr pseurlfflouncartoecdhemicals mBays"t euseekfulllatyerb,e apryovi26d,ed20i0n0.chTehmeicailnfsopremcaitfiiocn oinncrtheemseentsadd43ititohneaylaccehemciocmapllestecda,n Sth completion of the full submissions by the dates requested.
A feu points of clarification regarding his request:
>TdSuCpAon58t(en)e,edan3otFilrse,subumnidtercoFpIEiReAs) ofaltshtouduigehswealdroeadryeqpureosvtidtehdattoyoEuPpAro(vei.dge., aunder cSogmapirneshtenosuirvehobldiibnlgiso.graphy of the studies already submitted so ue can check this c35oipdiieess o2fs daecsucteeibsaydsteimnicchetoDxaitcaityAdsetquudaiceysacnadnrboebusltimistuemdmartyo tghueidaknecyeodrevceriltoipceadl aZo'rBitbhleiogHrPaVphCihcallleinsgteingProagletshso.ughUfnudlelr cthoipsiesappcraonabceh lalilmitsetduditeosswtiuldliesbewhciictehd (i1)n ZSoeuvteescoor'id(e2)ntirfeyporltowecsbtser(vie.d..efBfoescttstworhiicc)h dlieftfhearl dforsoem vtahlouseessbeyendiifnfesrteundties {using che same route) submitted under (1).
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neuzotoxicity.
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mFeetlhaotdisngusGeodthfeorulstaimmpaltinegenavnidroannmaelnytsiasl. faWtee aacned dalissoeriibnutteiroesnteodf tinhessetudciheesmicals.
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PlayisCUDUPoN@OUPont Roger J S96AEuPom DuPont Ostar TCarre uPon@DuPant Sibiect EPASideofPFOSStory NY Times
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From: Bemard JReilyon 05/19/2000 05:32 AM
To: ARRGaombseUerytAAEPIiIDnDcUUhPPooO/nDN@E@OVDuIUPAPaEroDtnU,,POJPnaotu@nlDJSuPBSooinesgts,EeUrMiRAc/EhDIaAeDlPuoPMnoIn@@CDOuuAPPoonSnt,:DHuPDoindt@DuPont, RicharJd
=Sibioct PASideof PFOS Sony -NY Times
May 19, 2000 ELPA. Says It Pressed 3MforAction on Scatchgard Chemical By DAVID 8ARBOZA
CHICAGO. May 18 -- The Environmental Protection Agency said today that it had pressed Minnesota
MhceihanelimtnihgcaaalnndcdotMhmaepneounfuvanicdrtouunrsmieendngtit.noSccoamfcehguaprwditahnad saonluataioyn aofftehrotuhseehcoolmdpapnryod'uscotswncotueisdtsphoasde sahsokwntothhatumaan {TmeahsketsiEns.ghP.otAhw.eedactchhceaomtuitnctahlediucfsheeerdmsificnraoSlmctcohlocamhtpgooafurn3ddMas,nfdwahimilacedhntysoaoidtdehcoernompMrpooondsudecatIysnbtthyhaettehtneehvianrddoonvomfleutnnhtte.aryOieflfayirdciebacelicsdaoeufds3etMotshsteaoyp hey have no evidence tha the chemicals pose a long-term thea to human healt Wmfafhroikmleett,htehaemgaer.nPkc.eAyt..ofTsfahicedilotsffisicdaiiadnlsotthiastdeIefta3hMneyihgmarmdeewdniocatotanecctseeadmfeettdhyeaiybkwoouuftolrpdocthoeanntvsieuamltealrkosennugsstieenrpgsphtreooadrlutechmtsosvknesotwthoeohnpurtmohdaeuncst aantderaaniSmMalsttiusdsyueshaonwdetdhatthhatigthhedocsheemsiwcealr,o pkenrofwlunortoooKcitlanlya!bosrualtfoornyatrea,s.ingered or years in human blood lp"eToshntegircriledeesrsucasonnrdsaietsoqexudiecnascnueubssm.tbaBeunrtcweosfeactdonotchneetmhs.a.Pv".eAs.aeiv"diWdShetnaecpe1hesnu1gsJgouehnsnstsasofnteo,nwuohswoi.swhoartksthienrethaereofpfoitceenotifaplrlyevention, aOrfeflnaolsloonfg-3tMe,rmhocwoenvseerq,uesnacyetshtyo ahruemaabnsohleuattehl.y confident that thelr products are safe, and tht here a"TMh.iswshinchaishebaalstedssinueSt.noPwau,la.nd t won't be a health Issue," said Lamy Zobel, the medical director at Tthootuhsaenqduseosftyieoanrosf,w0hebteheartthriesabtudhse suapdi.n humans, it would havteo be a long time, ike hundredosf Many scientists have praised 3M' decison to stop production of periuorooctanyl and elated chemicals.
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o11iadsd.itioSnartpootSseoatncdhgiasartdheprr,odauncdtsi,ntphaepecrhepmaicckailngi,s usnsaecdka-1s0s0tdabnagresp,elpleatn-toaondd bpargotse,cftiirveeficgohattinigngfoonam and pesticides. eTSnahvmeiprElo.enPsmeAt.natks:eaniftdfariptospmedeaacrrisosuiinnodnwittdhoieipfrweeosrasdn;d3Mahnurdme,satbneadsteiosdnsuofenouatrrhoceuosnntdcuedtmhyseo:wfotlrhalebdo;croattmaoprpoypuernaatrdss,isiitnpheharussmistathneenbptolitoneontdthieal to harm humans. T{CnohanettiEindPuyedA,.tmosaagliedet iart newgdauslfaefrmradstloesaelaestrostfewdaetbrooeutthgei3v.se2tnumddiyollsoifegslraaobmfosrtaphteeorcrkhyierlmaoisgcrasalhmoaornfldybtoahdteyenrwmefiat gtwheatds,.cmWoohnsdetuncoftaetdpherienogf1nf9as8np8rti.fnagItn died within four days. "YWoiuthgoailngthtaotdion?f"orsmaaitdioMnr,.wJeohfinnsaollny attaltkheedEt.oP.3AM. and said tharaises a number of concerns. What are Texhterreemeislsytihligah,dibfufterE.ePnAce.ofofifnitceiraplrsetsaatiidont,hhaofweewveort.heOrffcihceiamliscoafls3wMosualiddhtahveedoassessegvievreenatnoetfhfeecrta.ts were "This i fay toxic stuf in rats," one E.P.A. offical said. "Theres clear evidence it presents a problem in ats `tBhuetc3hMemsiaciadlist hsaodthnaott yeatppdeetaerremdiinnetditsshueecoarubsleooofddseaamtphleins.the ats nor how humans or animals ingested "Thats a very interesting question; Mr. Zobel said. "We can't say how t gets ino anybody's blood." AGso aawraesyulwtitohftthhaetcuhnecmeritsariyntbyy, tahnedetnhed poefrtshiestyeenacre. Tofhtehecocmopmapnoyunsadidinitthneegeontviiartoendmweintth,t3heMEs.aPi.dAi.tbwuotultds Gecision was voluntary and there was never a discussion of recall of the products. 3diniMs,rceowcnhetniitcnhwueeiseuktsshie,ngoanfttlheyer ccthoheemmpia.snPtrAyy.kbnaeoshwkinenddtom3omMsattkooefcpotemsrefSlcuuooptrwociohtcghiaarandyslop,lruhotdaiusocntb,se,tehnwehsciecoahmrpcahacincnyogdufenotcrifdaolretdaebmtaootuitve$s3.00But milion n sales,o less than 2 percentofthe company's $16 bilion in annual revenue. inc ne anuncamenton Monday, he campanys hares Nave gained 31.125, as asta7.0825 today. 3cMo,mpwahniicehsatlhsaotpursoedutcfeosr Pthoesirtp:rondoutcetss.and Scotch tape, will sop supplying the chemical to other
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Siejct SPA and Canada on PFOS and Rlted Peruosiys - BNANews Ci
:
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Economic Cooperation and Development, Auer said
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Inventory Update"ofchemicals in commerce, Auer sai.
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Canada Welcomes 3M Decsion OemnTadTtoAefWs2A,0-0E0TnhtveihrCouansnmeaeodnfitapMneirgtsuotcvereroroacmvieainndty|AwcnehleacromsmsoetnsystianihdsdMoemcaiesio1o6f.niby cMomptanpyh'assesputecbyythe oP(PrrPeoFrhttAueu)cmotcraiaaonnnschaAiaalocnftys(s!,CucbEAhsPnetAdma)einrcc3saeolsnsrdewsqeeaunrdieii1eagdmjfounnnthg1se9rta9hie9eavcmnioedemnewmtreawrtcihipteoatCHleanoctnhaiaeanlmaiMnciraneEslatnsnetriotAgeltamnpneaarFrusovocirkconamleknyt A{wT9geheeeenknCcsatynHywaeadaaisllalsnmasgCnoaounfvsaatecudrtyamuieranenngrtdsaiEatennavdcmiaerisodmnpsiomoreftMnecatrhrsCecamohinfca2ta0dle0as,0cohfhfieahctmisilttshcaeatwiUelamsneu,ndstEegnsahvtaieh.reora1nufmoeonhnrtetamelcasoPtmrmioitnoCeogncnEtiPoAn Canadian sage and toxicological momaton. 536,
8 Pete Menyasz
Copy: 2000 by The Bureauof National Ata, Inc. Washingon D.C.
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EID072415
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EID072415
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ar a DuPont Haskell Laboratory
Ene il ..
o[ceolueaormtaraemyeter
.
. Caf
2) Ar asd Soha
RECEIVED
w
May 25, 2000
JUL 08 70
LEGAL
Mr. Charles M. Auer, Director U. S. Environmental ProtectioAn gency Officeof Pollution Prevention & Toxics Chemical Control Division 401 M Street, N.W. -- Room 403
Washington, D.C. 20460
Dear Mr. Auer:
LAasborreqauteosrtyedw,itehncAlmomseodnairue mthPeesrufmlumoarroioecstaonfosattuediaensd
conducted at DuPont
Perfluorononanoate.
Haskell
If you have questions, please contact me at (302) 366-5259.
GLK:jhh Enclosures
3
a Si ly,
Gerald L. Kennedy
Director ~ Applied Toxicology
and Health
.
4Po 2 NemoursandCompr
Co0can
EID091521
roadon treatin.
SUMMARY OF A STUDYSUCLOFNODNUACTTEE(DPFWOIST) HATPODTUAPSOSNITUM PERFLUOROALKYL
Type:
Species/Strain:
Sex/Number: Exposure: Period: Frequency of Treameat: Exposure: Levels: Method:
Biopersistence Screening Study ~~ RMaatlse//SC/rgrlo:uCpD.SD(IGS)BR
5 or 10 days; 94 daysofrecovery
Ad libitum for5 or 10days
APomtmaossniiuummpeprefrlfulourooraoloycltasnuolaftoen:at2e0(mPgF/OkSg): 10 mg/kg
Speirxflgurooruoposctoafnroaattse,we1regraodumpinriescteeirveedd
ammonium the test substance
for
s5ucbosntsaenccuetfiovre 1d0aydsayasn.d Atpheprootxhimea$rteglryou2pshoruercseiavfetdertthheetfeisrtst dose,
bdolsoeosd. wTahsescoellseacmteedraftrsowmeeraechsarcartiffircoemd othnetgesrtoudapyde$saipgpnartoexdimfaotre5ly
2rehmoauirnsinpgosgtr-odouspisngr,ecaenidvebdltohoedtaesntdsluibvsetrsanwceerfeorco1l0ledcatyeds..
The Five
rats
(w2erheousrascrpiofsitc-eddosaen)d,h1a3d, 2b4l,oo5d2,aonrd9l3i/v9er4s.cTolhleecttoetdalofnlutoesrtindeaycsont1e0nt
of the blood combustion
mweatshodde,tefromlilnoewdedbybyusainnaglyasiWsiwciktbhoaldfltuoorrcihde
ion
stehlreocutgihvoeuetletchterotedset..
Body Liver
weights weights
and clinical signs were were recorded, but not
recorded reported.
sSuilxfgonraotuepsasodfersactrsiwbeerdeabaodvmei.nisFtoeordedapnodtwaastseirumweprereflauvoaroiallakyballde laimbmitounmituhmropuegrhfoluutorthoeoctteastn.oaCteotmesotiglrwoaupss.used as the vehicle for the
are: `Test Substance:
Potassium perfluoroalkyl suspending it in com oil.
sTuhlefornaattieoowfaascedtisosnoelvteodcionmacoeiltownaesbefore
20:80. tested
Negative controls of as described above.
corn
oil
and
corn
oil/acetone
were
also
No
Ammonium perfluorooctanoate, purity 93-97%
Results:
P#2o1t9a5s-s3i9u-m3,pe3rf-l8u%orCoaAlkSyl#3s8u7l1fo-n9a9t-e6,,pu3r-i7ty%8C2A-S86#%29C4A2S049-3, R1a-t3s%dCosAeSd #wi6t0h27a2m.m25o-n1ium perfluorooctanoate exhibited wet perineum and diarrhea during the dosing period. Alopecia was eoqbusievravleedatdsur(ibnlgootdheorrgeacnoovfelruyorpiedreiolde.veTlhs)einnorramtablliozoeddpueMaked after
EID091522
00050
Reference:
T5hdeayCsomafxdowsaisng51a8n.d12the4n4d.e8c9repapsread wtihtrhougtheorumtinthael htaelsft-ilnigfepeorfiod. (8.B3iodaacycs.umuTlhaetiAoIn)(Awcacsum64u9l7a.t5i.onAInndaerxe)a wuansde1r2t.h5eacnudrvtehe(eBsItimated fluionrfiinneitcyo)nt(eAnUt.CITNhFe/DA)UCwIasNFca/lDcuwlaatsedcaalncdulnatoerdmaalsi7z0e,d78f9o.r6.
dRiaatrsrhdeoas,esdalwiivtahtipoon,taaslsoipeucmiap,erbfllaucokrooacluklyalrsduilsfcohnaartgee,exahinbditsetda.ining
wofasvaorbisoeursvpeadrtdsuorifntghethbeordeycdouverriyngpetrhieoddo.sTihneg pneorrimoadl.izAeldopueMcia
equivaleats (blood rise throughout the
odrogsainnogflpueorriioddealnedvemlsa)yinnortathbalvoeordecaocnhteidnued
to
hsatlefa-dlyi-fsetaotfe.40.T5hedaCysm.axThweaAsI98w9a.s8559.01a1n6d.9t0heppBIm wwaitsh5a83t8e2r.m2i.nal
`The AUCINF/D was calculated as 566,479.1.
DuPont Co. No.2922.
(2000).
Unpublished
Data,
Haskell
Laboratory
Report
SUMMARPYEORFFSLTUUODRIOEOSCCTOANNDOUACTTEEADTWDIUTPHOANMTMONIUM
Ecotoxicity Type: Value: Breakdown products: Method:
GLP: Test Substance: Results:
Biodegradation 13%at Day 28
coy wMoadsimfeiaesduSrterduamsTCeOst;(eOvoElCutDio3n0.1 ABc)t.ivIantetdhissltuedstg,ebwioadsegursaeddabaislithtey inoculum. No AAmmmmoinosiiuumm ppeerrfflluuoorrooooccttaannooaattee,(p3u0ri%tysoalsustiuomne)ddi1d0n0o%t demonstrate B"iRoedaedgyraBdiaobdielgirtaydTaebislti"tdyo."esNnootteitmhpaltyfatihlautrethteotpeastsssuab"stRaenacdeywill persist in the environment foran extended periodoftime.
r`Tehfeerteonxciecicthyetmeistc,awlh(iscohdiiuncmlbuednezdobaotteh) tihnettheestsasumbestflaanscke,aynideltdheed
p<e2rf5l%uobriooodcetgarncaadtaetiwoanswcitohnisnid1e4reddayisn;hitbhietroerfyorteo,
ammonium microorganisms
in
the inoculum.
EIDO9I523
2:
Coen
Reference: Type: Method:
DuPont Co. (1997). No. 24-97.
Unpublished Data, AEM Laboratory Report
AAdmsmoorpntiiuonm-pDeersfolrupotriooocntaSncoraeteenaidnsgoSrpttuidoine/sdesorption.screening scltauydsi,esawwearsehepedrsfaonrdm,epdeaotn msoesvser,alantdesatnmaatgerriicaullst,urianlcslouidlinfgrotmwo aDlesloawpaerref,orUmSeAd.usTinhgetawdososruprtfiaocne/dseosilosrpatnidontwscoreseendiinmgensttsudfireosmwetrhee WOhoiroksRipvlearntconlelaerctPeadrkienrtshbeurvgi,ciWneitsytoVfitrhgeinDiua.Pont Washington
`aTdhaeptaeddsofrrpotimoan/mdeetshoropdtdioenveplroopceeddurbey uthseedOfifnitcheisofstPurdeyvewnatsion, PEensvtiircoindemsenatnadlTPorxoitcecStuiobnstAagnecenscy(OfPorPTuSs)e,inUntihetetdesSttiantgeosf p(eUsStiEciPdAes(a1n9d98t)o.xiFcatse,ubsttraannscpeosr,taannddtthreadnesfvoerlmoaptmieonntteosft tgeusitddealitnaes: `isOoPthTeSrm,83U5n.i1t2e2d0SsteadtiemEennvtiraonndmesoniltaaldsPorroptteicotni/odneAsgoerpntciyo,nOffice of Prevention, Pesticides, and Toxic Substances, EPAT12-C.98-048).
mEexschep)tfstoaritnhleessclsatyeesl, salilevseaminplpersepwaerrateisoncrfeoerntehdethrough a 2-mm (10
awbassohrepdtiuosni/ndgesDoIrp(tdieoinosncirzeede)niwnagtteerstt.hrFouurgthhe2r-momrme,atnhdeSs0a-nudmwas
sutsaeidnlienssthsetesetlusdiye.veTsh. eMsaatnedr,iasloirlse,taainndedsoenditmheentSsO uusmedsiinevtehewas
swteurdeiebsasweedreonaior-vderni-eddrpyriwoeritgo htussoe.ftDhaetasacmapllceusla.tiOonvse,n-hdorweyvweeri,ghts
were determined after drying a subsample 105C for a minimumof 24 hours.
of
material
in
aa
oven
at
`sTuhbesptaHnoceftthoewastaemr)p.lePsewrcaesntdeotregranmiicnemdatitnearrwaatisodoeft1e:r1mi(tneesdt using the loss on ignition method.
Screening Test: Adsorption Studies
bTlhaenkadcsoonrtpatiinoinngte0st.w0a1sM pCearCflo;rsmoeldutiinodnuwpliitchatteestonmaetaercihalmsatearnidaln.o A
`ammonium ammonium
perfluocooctanoate perfluorooctanoate
and a single control at each concentration but no material
were
pahlsaoseioncfluadseodl.utEiaocnohfmtahteertieasltwsaubssetqaunicleiabtra5t0e,d 5w0i0t,hatnhde 5aq0u0e0oupgs/L.
EID091524 3
concn
GLP: Test Substance: Results:
prepared in 0.01M CaCl,
vSteesrsielles.50OnmeLppaortlyapirr-odpryileednmeacteeartirailf(u4g.e0tgu)bewsaswewreeiugsheeddaasndthe test e5xpcaesptts ttheestcsoonlturtoilontu(b2e.0 mTLh)e cweenrteridfeucgaenttuebdeisnwtoerceenstercifuurgeedtounbeasn, e2n4dh-oouvresr.-Snadmmpilxeesrwaenrdeacgeiattartiefdugatedapfporro2x0immaitneultyes30atc4p0m00foxr g, caenndtrtihfeungefitlutbeer.ed Tthhreouvgohluam0e.2ofuamquneyoluosn ssuypreirnngaetfainltterwainstomeaanseuwred caondmproefurnidgeursaitnegd aatnapLpCr-oMxSim.atTehley b5laCnukntainldatnhaelyczoendtrfoolrttuhbeespawreernte subjected to the same steps as the test systems, including filtering. Screening Test: Desorption Studies
sAubfsrteasnhcveowlausmeadodfe2d0tmo Leoacfh so0l.i0d1MphCaasCel;(peslolleutt)i.onThwietshaoumtpltehewtaesst
mthiexeadd,socrepnttiroinfusgteuddi,esf.iltTerheids, sdteosroerdp.taionndsatneaplwyzaesdraespewaatseddoanseecinond
time, No
resulting
in
two
washings
that
were
analyzed
separately.
FAimvmeoonfiummatepreirafllsuotreosotcetdafnooratteh,e paudrsiotryptniootna/pdpelsiocrapbltei:on
cUhpasrtacrteearmissteicdsimoefnta,mEmaosntiWuomopdersfoliul,orGoaorcdteannoAarteea(pseoailt,maonsds,Kaolin
cplearyf)lueoxrhoiobcittaendosaitgeniafdidceadnt) aadtsoonreptoironmo(r>e2o5f%tohfeaamdmdeodnium
concentrations of ammonium perfluorooctanoate. Montmorillonite clay, Downstream sediment, and
Sand, Sassafras
soil
did
natotanaydscoornbceanstirgantiifoinc.ant amount of ammonium perfluorooctanoate
Othnrleye cpoenactemnotsrsat,ihoonwseovfeard,daeddsoarmbmeodnasiiugmnipfeircfalnutoraomoocutnantoaattea.ll pKearoflliundrloaoycatadnsooartbeeadt a50s0igannidfic5a0n0t0ampgo/uLn.t oTfheamGmarodneinuAmreasoil ocoflalemcmtoednaituWmaspherifnlgutcornooWcotarnkosataelsato Sa0ds0oprgb/eLd.siUgpnsiftirceaantmamounts ssiegdniimfeiacatnst farmoomunthteoOfhaimomRoivneiruamnpdeErafsltucWroooocdtasnooialtaedasto5rb0eudga/L only.
Once adsorbed on peat moss, most of the ammonium apesroflluutoiroonoocfta0n.c0at1eM(C>a7C6l%.)Fdoirdtnhoet dKeasoolribn calfateyr, tmwoostwaosfhtihnegs with
a
EID091525
eden
+ Reference:
daemsmoorbneiduwmitpherwfalsuhorionogct(a>n6o0at%e).adsAotrabemdmwohneinumadpdeerdflautor0o0oc0tagn/gaLte
`afwrdhodimecdhthaaetds5Ko0aro0blepidgn/4cLl,6a%hyoaowffetvetrheert,waomanmwaoasvnheiirnuaggmse.poefrTfh9le8uo%EraodsoitcdtWanonoootaddteessooairdl,bded at
t5h0euagm/mL odnesiourmbepderofnlluyoraoboocuttan2c%a.te FdoersotrhbeeGdawrdheenn Aardesaorsboeild $f7ro%mof
pteherfSl0u0orpogoc/tLansoolautteiofnr.omNothemeUapssutrraebalme sdeesdoirmpetnitonaoftferatmwmoownaisuhimngs
was observed at 50 pg/L.
when
the
ammonium
perfluorooctanoate
was
added
DuPont Co. (2000). Unpublished Data, Report No. EMSE-053-00.
Acute Toxicity to Fish
Type: Species: Value: Method:
96-hour LCs L63e4pommgi/sLma(c9r5o%chfiirduucsia(lbliunetgeirlvlals,un5f6i7s-h7)25 mg/L) cAonrcaenngterfaitnidoinnsgosft0u,dy0.w1,as1,co10n,du1c0t0e,danudsin1g00n0ommign/aLl. test F3o2r8,t4h1e0d,e5fi1n2i,ti6v4e0s,tu8d0y0,, naonmdin1a0l00temstg/cLo.nceGnltarsastiaoqnusarwiear(e200,L2)62, ccohnatmabienrisngin10thLeowfatteesrt bsaotlhutuisoendwteormeaeimnptalionyecdo.nstPaonstittieomnpseroafttuerset wreeprleicaatsesiugsniendg ursainndgormanaduommbenrusmb(e2rrse.pliTceantesfipsehrwceorneceandtdraetdioton;cach t1o.t2a:l2.280cfmishstpaenrdcaorndcelnetnrgatthi(onm)e.anCo2n.t1rcolm)fiasnhdra0n.g0e4d51f-r0o.m524 g wet wcoenicglhutsi(omne.anFi0s.h2w28erge).noCtonfterdoalplporaodxiinmgatwealsy02.423hogu/rL.saptrtieosrtto and dveurrsiunsg 8thheotuersts.dAarkpnheostsopwearsioedmpoflo1y6ehdouwristhli2g5htm(i3n1u2t-e3s4o4fLux) alingshittiinotenravlall.ighOtbs(e<r2v.a1t5iLounxs)foprremcoretdailnigtyanadndfoblelhoawviinogratlheef1f6ec-thsour were inade daily.
rDeipslsiocaltveedbeofxoyrgeenad,dpitHi,onanodf tfiesmhpaetrattesutrestwaretr, edamileya,sautrteodtailnfeiashch cmoonrtdaulcittiyv,itaynodf/torheat ctoensttreonld.waTtoetrawlearlekamlienaistyu,reEdDbTeAforhearfdinsehssw,eraend awadtdeerd-actotnetsrtolstraerptl.icAatecownatsinuusoeudsltyo rcehceocrkditnegmptehreatrumroemveartiieartnioans dcounrcienngttrhaeti9o6n-shionurwattesetr. wCehreemnioctalpearnfaolrymseeds.of the te_st substance
EID091526
:
00062
GLP: Test Substance: Results:
`The Yes
LCso
value
and
its
95%
fiducial
interval
were
calculated.
Ammonium perfluorooctanoate, purity 99%
aMnodra8l0it%yaitn0t,h0e.1r,an1g,e1f0i,nd1i0n0g, satnuddy10af0t0ermg96/Lh,ourersspewcatsiv0e,l0y,. 0,0, 0,
Total mortality was 328, 410, 512, 640,
0, 5, 800,
10, and
15, 30, 40, 1000 mg/L
65, and 95% in the concentrations,
0,
262,
respectively. exception of
All deaths occurred within 1 death at 48 hours at 1000
24 hours, mg/L. No
with the behavioral
.
effects were noted at < 640 1000 mg/L were lethargic.
mg/L.
Surviving
fish
at
800
and
Reference:
TAoltlaclhaelmkiaclianlitayn,dEpDhyTsAicahlarpdanreasms,etaenrds cwoenrdeucwtiitvhiitnyoefxtpehceteddilruatniognes.
water control were 79 mg/L CaCOs, 76 mg/L CaCO, and
165 umbos/em, respectively. During the test, dissolved oxygen
aconndcetnetmrpaetriaotnusrerarnagnegdedfrformom6.271-.84.-52m2.g1/LC,.pH ranged from 6.9-7.4,
DuPoa Co. No. 61-94.
(1994).
Unpublished
Data,
Haskell
Laboratory
Report
Type: Species: Value: Method:
96-hour LCs O40n0c1ormhgy/nLch(u9s5m%ykciosnsfi(dreanicneboinwtetrrvoault,) 3327-4932 mg/L) cAonstdautcitcerdanugseifnigndaidniglusttiuodnywwaittehr5cofnitsrhoplearncdonncoemnitnraaltion was concentrations of 50, 100, 500, 1000, and 5000 mg/L.
Nominal concentrationsof625, 1250, 2500, 5000, and
w1a0t,e0r0)0 wmegr/eLc(ho2s0e%n sfoolrutthieondeoffianimtmivoentiesutmbapseerfdlounortohoectraensuolattseoifnthe
preliminary rangefinding study.
.
Test chambers were stainless steel aquaria that held approximately 9 Lof est solution. Two replicate test chambers were used per test concentration with 10 fish in each chamber (total of 20 fish per concentration). Each chamber was covered with a glass plate to prevent fish from escaping. Random numbers were used to assign test concentrations to the test chambers and position of test concentrations in the water bath.
Rainbow trout used ia this study were not fed approximately 29 hours prior to and during the test, and were assigned to the test chambers using random oumbers. Addition of fish to the test solutions was initiated approximately 41 minutes after mixing of
5
EID091527
e09:25
the test solutions was completed. Mortality and behavioral Oatbtseesrtvaetndi.onsAwtetreestmcaondceluastitoens,t saltlarsturevvievriyng24fihshouwresrtehesraecraiffiiccre,d.and
iAn rtehceitrecsutlacthianmgbweartserdubraitnhgwtahse 9us6e-dhotuormtaeistn.taIinnamdediatniotne,maperature ctoenmtpienruaotuusrleyvraericaotridoinnginth1erremploimceatteerofwathseudsieludtitooncwhaetcekrfcoorntrol. A photoperiod of 16 hours light (approximately 199450 Lux) and. t8rahnosuirtsiodnaarlklniegshts(w1a1s-1e5m7plLouyxe)dp,rwehciedcihnignacnldudfeodll3o0wmiinngutthees1o6f-hour + light interval.
Dissolved oxygen, pH, and temperature were micasured in all replicate chambers of the control and test substance concentrations. `These measurements were taken before fish were added at test star, every 24 hours thereafter, and at test end or at total mortality ina concentration. Total alkalinity, EDTA hardness, and conductivityofthe water were measured before fish were added at the beginning of the test. Test solutions were not aerated during the test.
Concentrations of ammonium perfluorooctanoate were measured directly by high performance liquid chromatography/tandem mass spectrometry (LC/MS/MS).
At test conclusion, fish from the water control ranged from 2.53.2 cm in standard length (mean 2.8 cm) and 0.15-0.30 g in wet weight, blotted dry (mean 0.21 g). Standard lengthofthe longest fish was not more than twice the length of the shortest fish in the: control. Loading in the water control was 0.23 g/L at test conclusion.
GLP: Test Substance: Results:
`The LCso value was calculated using the moving average-angle method. Yes Ammonium perfluorooctanoate, purity 99.4% Atthe ead of 96 hours in the rangefinding study, the mortality was 0re,s0p,e0ct,i0v,e0ly,.2nTdes6t0s%ubastta0n,c5e0,so1l0u0t,io5n0s0w,e1r0e00c,leaanrdanSd00c0olmorgl/eLs,s with 0 insoluble test substance present during the study.
In the definitive study, mean measured concentrations of ammonium perfluorooctanoate were 554, 1090, 2280, 4560, and 9360 forthe 625, 1250, 2500, 5000, and 10,000 mg/L dose levels, respectively. Control solutions showed no detectable
5
EID09152!8
00a: 2
Reference: Mammalian Toxicity
Acute Toxicity Type:
Species/strain:
Value:
Method:
csounbcsetnatnrcaetisoolnustioofnas mwmeorenicluemarpearnfdlucoorlooorclteasnsowaitet.h
All test no insoluble
test
substance preseat during the test.
Awlilthcihneemxipceacltaedndrapnhgyessi.caTloptaarlaamlektaelirnsiftoyr, tEhDeTdeAfihnairtdinveestse,stawnedre c1o2n2dumcgt/ivLiCtyaoCfOt,headnidlu2t4io0nuwmahtoesr/ceomnt,rorleswpeecrteiv4e9lym.gD/uLrCinagCOtshe, pteHst,rdainsgseodlvferdomox7y.g1-e7n.2c,onacnedntmreaatniontsemrpaenrgaetdurferwoams7.151-.181.C2 m(rga/nLg,e 1L6-12.1C).
Ncoontmoolrtfailsiht.y Norosmuobrlteatlhiatlyeoffresctusblweethraelseefefenctisn twheerediolubtsieornvweadtaetr c1o1n72c0e,ntr14a1t2i0o,nsan<d25150/020mga/tL2.4,A4t8,57020,0amngd/9L6, mhoourrtsa,lirteyspweacsti8v/e2l0y,. At10,000 mg/L all fish were dead by 24 hours.
sSuucrvhiavsinsgwifimsmh ienxgpoastetdhetosu5r0f0ac0e,mgl/abLoerxehdirbeistpeidrastuibolne,tdhaalrkeffects
coloration, and erratic
slewtihmamrgiyn,gp.artial
lossofequilibrium,
rapid
respiration,
DuPont Co. (1999). No. Dupont-3381
Unpublished
Data,
Haskell
Laboratory
Report
Oral LDss
Male rats/Crl:CD
4M7a8lemgra/tksgre(c9e5iv%incgonafmimdeonncieulmimiptesr,fllouowreoro3c6ta1nomagt/ekga,lounep:per S71 mg/kg, slope 7.9)
Male rats receiving ammonium perfluorooctanoate and pcornef-iudeedntcmeenltimoitfsp,hleonwoebrar5b1i7tamlgs/okdgi,umu:pp5e4r75m8g2/mkgg/k(g9,5%slope 22.1)
Male rats receiving ammonium perfluorooctanoate and pre-treatmentofproadifen hydrochloride: 520 mg/kg (95% cAomnmfiodneincuemlipmeirtfsl,uloorwooecrt4a5no0amtge/wkags, audpmpienris6t1e8remdg/bkyg,instrlaogpaest9r.i8c) intubation as a suspeasionincorn oil in single doses to 1300rraattss,/g1r0o/ugparotupc,onwceernetrtarteaitoendsobfy4s0i0ng,l5e0i0n,troarpe6r5i0tomngea/lkgi.njeAcntiootnhser
EID091529 8
00on 2"
GLP: ReTseustltSsu:bstance:
wfoirth3 adqayuse.ouOsnseoldutaiyoanfsteorftphheenfoibnaalrbtirteaaltmseontd,iuthmearta8ts0wmegr/ekg/day aindtmuibnaitsitoenreudsianmg mthoensiaummepterrefaltumoernotocatsadneosactreibbyediantbroavgea.strAinc aindtdriatpieorniatlongeraolupionjfe3ct0ionraotsf, a1q0u/egoruousps,olwuetrieontsreoaftepdrowaidtihfeann `hyadmrmoocnhilourmidpeeraftl5uo0rmogo/cktga.noaOtenewahsouardamftienristtheirsedtrbeyatimnetnrta,gastric isnutruvbiavtiinogn,rautssifnrgotmhealslatmreeattrmeenattsmewnetraes wdeesicgrhiebdedanadboovbes.erTvheed dvaulruiesnagwe1r4e-cdaalycurleactoevderfyropmertihoedmaonrdtatlhietny sdaactrai.ficed. The LDs
`aTthse fprheonmobboartbhipthaalsseosdeirumepchoamsbeionfetdheansdtutdhye wLaDssorevpaelauteedw.asThbeased oNnoall 60 rats. `ATmhemroe nwieruemnpoersfilgunoifriocoacnttandoiaftfee,repnucreistyinatphperoLxiDmatveallyue1s0o0f% `foalmlmoowninigumprpee-rtfrleuaotrmoeoncttawnictahtee,itehietrhpehrewnhobeanrbtietsatledsaoldoinuemoror proadifen hydrochloride.
tMroerattaeldiwtyitrhat4i0os0,of5020/,10a,n7d/6105,0amngd/8k/g10amwemroenoibusmerved for the rats paenrdflwueoirgohotctlaonsosawtee,rereosbpseectrivveedlya.t lWletlevaenlds/oterssttead.ineOdthpeerricnleianlicaarlea swiegaaksnoebssse(r5v0e0d ianncdlu6d5e0dmsgt/akign)ed, faancde (cSh0r0omaondda6c5r0yomrg/hkega), (500 mg/kg). All deaths occurred within 6 days after dosing.
Mproertarleiatteydowfi0t/h20p,he4n/o2b0a,rbaintdal19s/o2d0iwuamsanodbstehrevnedtrfeoartetdhewirtahts400, 5`W0e0t, aanndd/o6r50stmaign/ekdgpearminmeoanliaruema,psetrafilnueodrofoacctea,ndoiaatrer,herae,spaenctdiwveeliyg.ht loss wiefe observed at all levels tested. Other clinical signs observed included weakness (500 and 650 mg/kg) and lethargy (650 mg/kg). All deaths occurred within 4 days after dosing.
Mproerttraelaitteydowfit1h/1p0r,o5a/d1i0f,enanhdyd8r/o1c0hlwoarsidoebsaenrdvtehdefnortrtehaeterdatwsith 400, 500, and 650 mg/kg ammonium perfluorooctanoate, respectively. Swteaaiknneedsfsacwee,rweeotbasnedr/voerdasttaailnledlepveerlisnteeaslteadr.ea,Otwheeirghcltinloiscsa,l asingdns o(b40s0ermvge/dkgi)n,clduidaerdrhteraem(o5r0s0(a4n0d06m5g0/kmgg)/,kgc)h,roamnoddalcacrryiomrarthieona
EIDO091530
000435
Reference:
D(6u5P0onmtg/Ckog.).(1A9l8l1)d.eaUtnhspuobclciusrhreedd Dwaittah,inHasdkaeylsl Lafatbeorrdaotsoirngy,Report No. 567-81.
Type: VSpaelcuiee:s/strain:
Oral LDso MMaallee raantds:f4e7m0almegr/aktgs/(C9r5l:%CcDonfidence limits, lower 403 mg/kg, upper 536 mg/kg, slope 8.6)
Method: GL: Test Substance: Results:
Female rats: 482 mg/kg (95% confidence limits, lower 438 mg/kg,
`uTphpeetres5t41submsgt/akngc,e,slaospae
12.3)
suspeasion
in
corn
oil,
was
administered
by
6ingtrraoguapsstorficfienmtaublaetiyoonuinngsiandgullet draotsse.sTteon6mgarloeupasndoffmeamlaeleand
rats/group were administered 200, 400, 450, 500, 670, or
a1n0d00obmsge/rkvgeodfdtuhreintgesat 1su4b-sdtaayncree.covTehreyspuerrviiovdinagndrattshewnesraecrwiefiicgehde.d
`The No
LDsp
values
were
calculated
from
the
mortality
data.
MAomrmtaolnitiyurmatpioesroffl2u/or1o0o,ct3a/n1o0a,te4,/1p0u,ri6t/y10a,pp9r/1o0x,imaantdel1y0/1100 0w%ere
rfeosupnedctiinvetlhye.20M0o,rt4a0l0i,ty45r0at,io5s00o,f 06/7100,,a0n/d101,050/010m,g7//k1g0,m9a/l1e0,graonudps,
10/10 were found in the 200, 400, 450, 500, 670, and 1000 mg/kg
female groups, respectively.
Clinical signs observed in male rats included stained and/or wet
cpleirniinceaallsairgenas, owbesaekrnveesds,inatnhdewmeailgehtraltossisnactlauldleldevsetlasinteedstfeadc.e Other
(450 mg/kg and above), chromodacryorrhea (500 and 1000 mg/kg),
hunched posture (S00 mg/kg), morbundity (670 meg), eyes half
closed within
(670 mg/kg), and 4 daysofdosing.
gasping
(670
mg/kg).
All
deaths
occurred
Reference:
Clinical signs observed in female rats included stained and/or wet
perinealarca and weight loss at all levels tested. Stained face was
observed at all levels except 200 mg/kg. Other clinical signs noted
6in70f,emaanlde1r0at0s0imngc/lkugd)e,d haluonpcehceida p(o4s0t0urmeg/(k4g5)0,awnedak6n7e0smsg(/4k0g0),,450,
chromodacryorthea (670 mg/kg), eyeshalfclosed (670 mg/kg), and
atDauxPioant(6C7o0.m(g1/9k8g1)).. AUlnlpudbealtihssheodccDuartrae,dHwaistkheilnl3LadbaoyrsaafttoreyrdRoespionrgt.
No. 295-81.
:
EIDO9IS3L
Ld
00:20
Type: SVpaelcuiee:s/strain:
+
Method:
GL: Test Substance: Results:
Oral LDso
Male
Male
nanedwbfeommalreatsr:at2s4/3Cemlg:/CkDg
(95%
confidence
limits,
undefined,
slope 55.7)
2F4e4mamlgeknge,wbuoprpnerra2t7s:62m5g8/kmgg,/sklgop(e9519%.9c)onfidence limits, lower
M51a4lemgw/ekagn,liunpgperarts6:6547m3g/mkgg/,kgsl(o9pe5%8.c0o)nfidence limits, lower
Female weanling 470 mg/kg, upper
r2at2s5:858m0g/mkgg/,ksglo(p9e54%.7c)onfidence
limits,
lower
4M0a3lemgy/okugn,guapdpueltr r5a3t6s:m4g7/0kgm,g/slkogpe(98.56%) confidence limits, lower
4F1e3mamlge/kygo,unugppaedrul5t0r3atms:g/4k5g3,
mg/kg
slope
(95%
15.0)
confidence
limits,
lower
Male older rats: 336 mg/kg (95% confidence limits, undefined)
Female older rats: 285 mg/kg, upper
343 390
mg/kg mg/kg,
(95% slope
confidence 8.0)
limi,
lower
`iTnhteratgeassttrsiucbsitnatnucbeat,iaosn ainssuisnpgelaesidoonseisn tcoorgnroouilp,sowfasraatdsm.inTihsetegrreodupbsy
(m1a0leraatnsd/gfroeumpa)lewewreeanmlailneg arnatds f(e2m1adlaeynseowlbd)o,rnmarlaetsa(n<d2fdeamyalseold),
y(aoguenugndadeuflitnsed()-.8-M1a0lweeenkeswbooldr)n,raantsd wmearlee aadnmdinfiesmtaelreeodld1e3r0r,a2t0s0,
2a4d0m,in2i8s0t,er3e3d0,13o0r,317600,mg2/0k0g,.22F0e,m2a4l0e, n2e80w,boGrrn32ra0tsmgw/ekrge. Male
weanling rats were administered 350, 400, 450, 525, 670, or
710
450,
mg/kg.
6670
Female
mg/kg.
Yweoaunnlginagdurlattsrawtesrweeraedmaidnmiisntiesrteedr3e5d03,5400,04,25,
D50u0P,o6nrt6R7e0pomrgt/kNgo.. 2Y9o5u-8n1g.adOulldtermamlaelreatrdaatstawearree ardempionritsetdeirned
200, 240, 300, 350, 400, 500, or 720 mg/kg. Older female rats
wsuerrveivaidnmginriatsstewreerde2w2e5i,g3h5e0d, a4n00d,o4b5s0e,rvoerd6d7u0rimngg/kag.14-Tdhaey
recovery period and then sacrificed. The LDso values were
calculatedfromthe No
mortality
data.
MAomrtmaolnitiyurmatpioesrfflouromroaolcetanneowabteo,rnpurraittsywaeprpero0x/i1m0a,t0e/l1y0,100/010%, 10/10,
n EIDO091532 009400
References:
g1r0o/u1p0s,,arnedsp1e0c/t1iv0efloyr. tNheo1c3l0i,ni2c0a0l,si2g4n0s, w2e8r0,e 3r3ep0o,ratendd. 3D7e0amthgs/kg occurred up to 6 days after dosing.
0M/o1r0t,al5i/t1y0,ra6t/i1o0s,faorndfe1m0a/l1e0fnoerwtbhoern13r0a,ts1w6e0,re2000/,102,200,/1204,00,/1208,0, and 320 mg/kg groups, respectively. No clinical signs were. reported. Deaths occurred up to 4 days after dosing,
Mortality
7/10, and
ratio
8/10
s fo
for
r
t
hmea3l5e0w,e4a0n0l,in45g0r,at5s2w5,er6e700,/1a0n,d27/1100,
m2g/1/0k,3g/10,
`groups, respectively. Stained and wet perineal area, weakness, and
weight loss were observed. Deaths occurred up to 3 days fier
dosing.
Mortalit
6/10 for
y ratios for female
the 350, 400, 450,
weanling rats w
and 670 mg/kg
ere
grou
1/10,
ps, r
3/10,
espect
3/10,
ively.
and
Stained and wet perineal area, stained face, weakness, and weight
loss were observed. Deaths occurred up to 3 days after dosing.
Mortality ratio data for the young adult males are covered in
DuPont Report No. 295-81.
Mortality ratios for female young adult rats were 1/10, 2/10, 3/10, and 10/10 for the 350, 425, 500, and 670 mg/kg groups, respectively. Stained and wet perineal area, stained face, nasal discharge, diarrhea, and weight loss were observed. Deaths
occurred up to 4 days after dosing.
Mortality ratios for the older male rats were 0/10, 0/10, 0/10, 9/10, 10/10, 10/10, and 10/10 for the 200, 240, 300, 350, 400, 500, and
720 mg/kg groups, respectively. Stained face, stained and wet
perineal area, weakness, tremors, lethargy, chromodacryorrhea, diarrhea, and weight loss were observed. Deaths occurred up to 9 days after dosing:
Mortality ratios for the older female rats were 1/10, 5/10, 6/10, 9/10, and 10/10 for the 225, 350, 400, 450, and 670 mg/kg groups,
respectively. Stained face, stained and wet perineal area, `weakness, tremors, lethargy, and weigh loss were observed.
Deaths occurred up to 5 days after dosing. DuPont Co. (1982). Unpublished Data, Haskell Laboratory Report
No. 788-82.
DuPont Co. (1981). Unpublished Data, Haskell Laboratory Report No. 295-81.
EID091533
"
coves
Type:
Species/strain:
Value: Method: GL: Test Substance: Results:
Oral LD; Rangefinder and Liver Weight Comparison Test
Male and female rats/Crl:CD
Male rats: 439 mg/kg 554 mg/kg, slope 6.1)
(confidence
limits,
lower
294
mg/kg,
upper
Castrated male rats: 491 me/kg (confidence limits, lower 276 mg/kg,upper 619 mg/kg, slope 6.7)
Female rats: 459 mg/kg (confidence limits, lower 315 mg/ks, upper 607 mg/kg, slope 5.2)
Overiectomized female rats: 400 mg/kg (confidence limits, lower 259 mg/kg, upper 494 mg/kg, slope 7.2) In an LD rangefinder test, the test substance, as a suspeasion in com oil, was administered by intragastric intubation in single doses 0 normal male rats, castrated male rats, normal female rats, and. ovariectomized female rats. Dose levels of 200, 480, and 670 mg/kg were tested in each of the test systems meationed above (10 rats/group).
In the liver weight comparison test, rats/group were administered the test substance, as a suspension in com ol, as a single dose. Male groups were defined as male control, male 100 mg/kg, male 200 mg/kg, male castrated control, and male castrated 200 mg/k. Female groups were defined as female control, female 100 mg/kg, female 200 mg/kg, female ovariectomized control, and female ovariectomized 200 mg/kg. All rats were weighed and observed during a 14-day recovery period. The rats were then sacrificed and the livers were weighed. No Ammonium perfluocooctancate, purity approximately 100% In the LD study, mortality in the male rats occurred in 0/10, 7/10, and 8/10 rats in the 200, 480,and 670 mg/kg groups, respectively. Morality in the castrated male rats occurred in 0/10, 5/10, and 8/10 ats in the 200, 430, and 670 mg/kg groups, respectively. Morality of the female rats occurredin0/10, 7/10, and 7/10 ras in the 200, 480, and 670 mg/kg groups, respectively. Mortality in the ovariectomized female rats occurred in 0/10, 8/10, and 9/10 mg/kg at 200, 480, and 670 mg/kg, respectively.
In the liver weight comparison study tested at dose levels of 0, 100, and 200 mg/kg, no changes in liver weight or in liver to body weight ratios were seen in the female rats given single doses of up t0 200 mg/kg (ovariectomized or normal).A single oral dose of either 100 or 200 mg/kg produced an increase in liver weight of
EIDO091534
" conv
Reference: Type:
Species/strain:
Method: GLP: `Test Substance: Results:
Reference: Type: VSapelcuiee:s/strain: Method:
imnaclreearsaet,s.buCtasrattrsatciaosntrraetdeducaenddtghievmeang2n0i0tumdge/ofktghheadlihveearvwieeirglhitvers
ptehrafnludoirdotohcetacnoonattreol-sw.reaCtleidnircaatlssiingcalsudseedenstianitnheed afamcmeoannidupmerineal
area, and sporadic the experiment.
weight
loss.
No
deaths
occurred
in
this
phase
of
DuPoat Co. No. 600-81.
(1981).
Unpublished
Data,
Haskell
Laboratory
Report
Acute Oral Toxicity
Male rats/Cri:CD
`aTmhmeotensitusumbsptearnfcleu,oraomocmtoannoiautme (pRerifmlaurorCooo.)c,taansoastuesp(e3nMs)ioannsdia corn
oil, were administered young adult male rats.
bRyatisnt(r1a0g/asgtrroiucp)inwtuebraetiaodnmiinnissitnegrleeddo20s0e,s
to
w48e0i,ghoerd67an0dmogb/skegrvoefdtdheurtienstgsaub1s4t-adnacey.reTchoveesruyrpveirviiondg arantds wtheerne
sacrificed.
No
Ammonium perfluorooctanoate (3M), purity approximately 100%
MAomrmtaolnitiyurmatpioesrofflu0o/r1o0o,ct6a/n1o0a,taen(dRi1m0a/1r0Cow.e)r,epfuroiutnyd9i5n %thmei2n00i,mum
r4e8s0p,ecatnidve6l7y.0 mMogr/tkagliatmymraotnioisoumf0p/e1r0f,lu1o0r/o1o0c,taannodat1e0(/130M)wegrreoufposu,nd
(inRitmhear20C0o,.)48g0r,ouapnsd,
670 mg/kg ammonium respectively.
perfluorooctanoate.
iClnicnliucdaeldssitganisneodbsaenrdv/eodr winetampemroinneiaulmarpeea,rfsltuaoirnoeodcftaacneo,aatend(3wMe)igrhatts `lwosesakanteaslsl l(e4v8e0lsantedst6e7d.0 mOgt/hkegr),clidniiacrarlhesaig(n4s3o0bmsge/rkvge)d,iancnldudaelodpecia (200 mg/kg). All deaths occurred within 4 days after dosing.
CCloi.nircaatlssiingcnlsuodbesdesrtvaeidneidn aanmd/moornwieutmpepreirnfelauloraoreoac,tasntoaaitneed(fRaicmea,r ianncdluwdeeidghwtealoksnseastsa(l48le0vaelnsdt6es7t0edm.g/Oktgh)eracnldinliectahlaSriggyn(s6n7o0temdg./kg). ADlulPdoenatthCso.oc(c1u9r8r1e)d. wUinthpiunbl4isdahyesd Dafattear,dHoassinkge.ll Laboratory Report No. 565-81.
OMraalle AraLtDs/(CAhpR-pCrDoximate Lethal Dose) 670 mg/kg The test substance, as an aqueous solution (pH ~6), was
EID091535
14
009,07
Le: Test Substance: Results:
Reference: Type: Species/strain: Value: Method: GLP: Test Substance: Results:
administered by intragastric intubation (0 young adult male rats
(1 rav/group) in single doses. Concentrations tested were 1, 1.5, 2.3,
23.245,05.m1g,/2k6g,.40S,ur6v0i,v7o7r,s 9w0e,r1e2s0a,cr1i3f0i,ce1d701,42d0a0y,s3l0a0t,er4, 5a0n,d6b7o0,dyand
weights and liver weights were recorded.
.
No
.
Ammonium perfluorooctanoate, purity not specified
Dwietahth6s7d0imdgn/oktgodciceudr a2tddaoyssealfetveerldsoosfin1g-,4a5n0dmgth/ekgr.at Tdohseedrawtidtohsed
2250 mg/kg died 1 day after dosing.
S1l-i2ghdatysi.nitiAaltw9e0igmhgt/klogssaensdoacbcouvrer,edthaet 2fe6cemsg/wekrgeasnmdaallboavnedfor irregularly-shaped for 1-6 days after dosing, and the rats were uncomfortable for 1-5%ays after dosing. The compound caused. liver enlargement in rats with single doses as low as 60-90 mg/kg. Based on clinical signs, it also acted as a gastrointestinal irritant. `Additional toxic sigasa the lethal doses (670 and 2250 mg/kg) included chewing motions, polyuria, increased respiration rate, and face-pawing on the dayofdosing. Shovel-nosing was observed at 2250 mg/kg and slight salivation after dosing occurred at 670 mg/kg. DuPont Co. (1968). Unpublished Data, Haskell Laboratory Report No. 128-68.
Oral ALD Male rats/ChR-CD 670 mg/kg `The test substance was administered by intragastric intubation to male rats (1 ravgroup) in single doses. Concentrations tested were 1.5, 12,40, 120,200, 300, 450, 670, 1000, 1500, and 2250 mg/kg. Survivors were sacrificed 14-15 days later, and body weights and liver weights were recorded. No Ammonium perfluotooctancate, purity 99% Mortality occurred at 670 mg/kg and above. Clinical signs of toxicity included inactivity (120, 1000, 1500, and 2250 mg/kg), red ddiissccohlaorrgaetiaorno(un3d00thaendno4s5e0(m6g7/0,kg1)5,00ru,faflnedd2f2ur50(3m0g0/kagn)d, perineal
450 mg/kg), irritability (670 mg/kg), and weight loss (40, 200, 300,
450,670, and 1000 mg/kg). Animals sacrificed 14-15 days after having received doses down to and including 200 mg/kg bad enlarged livers when compared to control rats weighing between 500-550 g with liver weights of 22.6, 20.7, 19.1, and 21.7 g and liver weight/body weight percentages of 4.2, 3.8, 3.6, and 3.8, respectively. Liver weightsat 200, 300, and 450 mg/kg were 30.6,
EID091536 1s 0090:
Reference: Type:
Species/strain:
Method:
GLP: Test Substance: Results:
Reference: Type: Species/strain: Value: Method:
52.53.,2a,nadnd6.228,.r2esg,pewcittihvelliyv.erLwievierghetnlbaordgyemweenitghwtapseraclseontpaogsessibolefin5.6, rwaotuslddosheadvebetloobwe 2c0o0mpmagr/ekdg,inbuotrdaedrdittoioensatalbtleissthatnhids.control ras NDou.Po5n5t-6C1o.. (1961). Unpublished Data, Haskell Laboratory Report
tAocxuitceityOroaflaEmfmfeocntsi,uDmoepserpfrleutorreoaotcmteanntoawtiet?h ethanol modify the
Male rats/Cel:CD
p`eYrofulnugoraodouclttamnaolateeraatssa(66/0g%rouapq)uewoeursesaodlmuitniiosnatetrdeodsaemlmeovenlis uofm200,
w48i0t,h eatnhda6no7l0(m1g5/k%g.v/vA)didnitdiroinnaklinggrowuaptserofforrat1s4wdearyesparned-ttrheeanted
cdoonsceedntwriatthioanmsmaosnliisutmedpaebrofvleuoornoodcatyan1o5a.teTahtrteheeostahmeer groups of
rats were pretreated with a single 6000 mg/kg dose of ethanol via
pientrrfalguaosrtroiocctianntouabtaetitornefatomlelnotwaetdh2e4 hloeuvrelssllaitsetredwiatbhovteh.e aAmnmonium
additional group of untreated rats served as controls. Groups of
rats were also treated with ethanol alone at either 6000 mg/kg or
15% v/v in drinking water for 14 days. Clinical signs and body
weights were recorded. Liver weights were recorded at the 14-day
sacrifice.
No
Ammonium perfluorooctanoate, purity approximately 100%
pAelrlfrlautosrdoioecdtawnictahtienat8 6da7y0samfgt/ekrgd.osLiinvgerwwitehigahmtmboondyiuwmeight ratios
showed an increase in all rats that received ammonium
tpheerfalnuiomraoloscttahnactarteecweihveend ocnolmypaertheadnotlo.thTeheunrterweaetreedncoonstirgonlisfiacnadnt
differences between the untreated controls and the animals that
received only ethanol. There were no siguificant differences
between rats that received ethanol and ammonium
perfluorooctancateandthe rats that received only ammonium
perfliofooctanoate.
DuPont Co. (1984). Unpublished Data, Haskell Laboratory Report
No. 79-84.
Oral LDsy
EID091S37
Male and female mice/CD-1
Male and female mice: 457 mg/kg (95% confidence limits, lower
344 `The
mtegs/tksgu,bsutpapnecre,5a6s0
amgs/ukspge,asslioopne
i6n.c6)om
oil,
was
administer: ed
by
intragastric intubation in single doses to 6 groups of male and
6 groups of female young adult mice. Ten male and female
16
000s
GLP: Test Substance: Results:
4m0ic0e0/mgrgo/ukpgowfetrheeadtmesitnissutbestraendc2e5.0,Th5e00s,u7r5v0i,vi1n0g0r0a,ts20w0e0r,eowreighed
`aTnhde oLbDsseorvveadludeusriwnegreac1a4l-cdualyatreedcforvoermytpheermioordtaalnidtythdeantas.acTrihfeicmead.le
and the
LfDesmoaldeat4a00du0eatnod
l2i0mi0t0atmigon/skgofdtohseecloemvpeulstewre.re
not
calculated
in
No
MAomrtmaolnitiyurmatpioesrfolfuo1r/o1o0,ct4a/n1o0a,te1,0/p1u0r,it1y0a/1p0p,ro1x0i/m1a0t,ealnyd11000/1%0 were
ffeomuanldeignrtohueps2,50r,es5p0e0c,ti7v5e0l,y.1000, 2000, and 4000 mg/kg male and
Reference:
Clinical perineal
sigas area,
woebaskenrevsesd,inanmdalweeimgihcteloisnscliundaeldl
stained and/or wet surviving mice.
Other signs included eyeshalfclosed (250 and 1000 mg/kg),
r1u0f0f0lemdfgu/krg()2,5a0nadntdrSem0o0rsmg(/5k0g0),anadta7x5ia0(m2g5/0k,g)5.00,Alalndd.eaths in male:
mice occurred within 6 days after dosing.
Clinical perineal
signs area,
woebaskenrevsesd,ian nfdemwaelieghmticleossinicnlauldlesdusrtvaiivniendg
and/or mice.
wet
(O1t5h0ermgs/igkngs),intcrleumdoerdse(y7e5s0hamlgf/cklgo)s,eadta(x7i5a0(mSg0/0kmgg)/,ksgt)a,inaenddfraucfefled
fur (250 within 7
and 750 mg/kg). All days after dosing.
deaths
in
female
mice
occurred
DuPont Co. (1981). No. 329-81.
Unpublished
Data,
Haskell
Laboratory
Report
Type: Species/strain: Value:
Oral LDso
Male Male
and female guinea pigs/Duncan Hartley guinea pigs: 178 mg/kg (95% confidence
limits,
lower
144 mg/kg, upper 202 mg/kg, slope 8.9)
Method: GLP: `Test Substance: Results:
Female guinea pigs: 217 mg/kg (95% confidecce limits, lower
T1h87etmegs/tkssu,bsutpapnecre,24as6 amgs/uksgp,ensslioopnei8n.6c)orn oil, was administered by
intragastric intubation in single doses to 6 groups of male and
g6ugirnoeuappsiogfs/fgermoaulpewyeoruenagdmaidunlitstgeuriendea15p0i,gs2.00T,e2a50m,al3e00a,nd40f0e,moarle
w6e7i0gmhge/dkagnodftohbseertevsetdsudbusrtianngcea.14T-hdeaysurrevciovvienrgygpueirnieoadpaingds twheerne
sacrificed. data.
The
LDso
values
were
calculated
from
the
mortality
No Ammonium
perfluorooctanoate,
purity
a.pproximately
100%
Morality ratiosof3/10, 6/10, 9/10, 10/10, 10/10, and 10/10 were:
EIDO091538 7
009.05
Reference: Type: MSeptehcioeds:/suain:
GLP: Test Substance: Results:
found in the respectively.
1M5o0,rt2a0l0i,ty25r0at,io3s00o,f24/0100,,a1n/d106,780/1m0g,/9k/g10m.al10e/1g0r,ouapgsg,
f1e0m/a1l0ewgerroeupfso,unredspiencttihveel1y5.0, 200, 250, 300, 400, and 670 mg/kg
sCwilegitansipceoarblisnseeiraglvuesadroeibansaetnrhedvemwdaelianekmngaeulsiesnegaatuipanilgesaleipvniecgllssuitdenescdtlesudtd.aeidOntsehtdaefirancceledin(ai1nc5da0/l,or 2la0c0r,iamnatdi6on70(1m5g0/kagn)d,2e0y0esmgha/lkfgc)l,osaetadxi(a20(607a0nmde3k0e0)m,gt/rkeem)o,rs o(c1c5u0rrmegd/kagt),allanledvehlusntcehsetdedpeoxscteuprte 4(02000amngd/k6g7)0. mgW/ekigg,htAlllosdseaths occurred within 4 days after dosing.
Calnidn/iocralwestigpnesrionbesaelrvareedaiannfdemwaelaekngeusisneaat palilgsleivnecllsutdeesdtesdtaeixnceedpt
4pi0g0s ainndcl6u7de0dmcgo/nkvgu.lsOitohnser(c6l7i0nimcgal/ksgi)g,nsatnaoxtiead (i6n7f0emmga/lkeg)g,uinea
gasping
tremors
(670
(400
mg/kg),
mg/kg),
eyes half closed
lacrimation (250
(150 and
mg/kg),
250 mg/kg),
stained face
l(e2v0e0lsmgt/esktge)d,eaxncdeplteftohrar6g7y0(1mg5/0kmgg./kAgl)l. 6 days after dosing.
dWeaetihgshotclcousrsreodccwuirtrheidn
at
all
DNou.Po2n9t1-C8o1.. (1981). Unpublished Data, HaskellLaboratoryReport
AMcaulteedoTgosx/ibceiatgyle
Dsuobgssta(ncger.ouTph)e rfeocleliovweidngcibtihoerch2e0m0icoarl4m5e0asmugr/ekmgenotfsthweetreestmade
pohnostphheabtlaosoed.:
sugar, When
utrheea4n5i0trmogg/enk,g
tdootaslecwhoalsesatdemrionl,isatnedreadl,katlhiene
ldeevheyldorfogacetniavsietyo(fIlCaDcHt)i,c adledholyadsreo,ggelnuatsaemi(cLDoHxa)l,aciestoicicttrircansaminase
(meGaOsTu)readn.dAglruotuatmiincephyermuavtioclotgriacnaslameixnaamsien(atGiPoTn)awnedraenalasnaolysis of
T2h2e4-lheovuelrofuvrianreisopuescciommenpownaesntmsaodfetahteibnltoerovdalfsololnowthiensgedaonsiimnaglsw.as
cwiotmhpaarseidmiwliatrhmaenasauvreermageentvamlaudeeobatsetrhveesdapmreiotritmoeeoxnposspuerceimnedns
fwraosmessttaobclkicsoheldonfyrodomgmse.asFuorretmheenetnszmyamdeeacotnivsittioecsk, daongosr.maTlherange
aNcotivity was also measured at least once prior to treatment.
TAhmemGoPnTiuamndpeGrOflTuolreovoecltsanwoeartee,elpeuvriattyed9w9i%thin 48 hours in both
EID091539 18
cava
Reference:
dnoorgmsathlartranegcee.ivWehde2n0045m0g/mkgg./kgOnweaswaedemkinliastetre,retdh,eyalwloerfethine the `eTnhzeygmreeastemsetacshuarnegdewoecrceurmraerdkeindltyheelGePvaTteadnd24ICtoDH48. hBooutrsh alantierm.als tDhuaPtoraetceCiov.ed(1495605)m. UgnpudbileidswhietdhiDnat4a8,hHoausrkselalftLerabdoorsaitnogr.y Report No. 123-65.
Type: Species/strain: EVaxlpuoes:ure Time: Method:
RInahtasl/aCthioRn-CADLC (Acute Lethal Concentration)
4 hours
0.8 mg/L
eMxaploeseradtsto(6d/uesxtspoosfuarme mleovenli),uwmeipgerhfilnugor2o5o0c-t2a7n0cagtreaamtsexwpeorseure
lheevaedl-soonfly0,.e38x,c0e.p81f,or0.t8h3e,22..22,mg4./8L,.oexrpo5.s7 umrge/Ll.eveElxwphoesruerersatwsehraed
wwehroeleu-sbeoddtyoegxepnoesruartee.aTmwmoondiifufmerpeentrfmleutohrooodcstoafnodautsetageernoesrolast.ionIn
atpheprfoirxsitmmaettehloyd3,0ahLe/maivnyuctleooufadiwratshrgouegnheraatehdigbhy vbellooscviitnyg
Cteus-ttsuubbisntganjceet.suTbhmeeraigrecdarirniaedmetchehadnuisctaplalrytisctliersreidntroeasn e8 rLvooftihre
ethxepogseunrereacthoarmabnedr.theSucihtaabmlbeerdiltoutaicnhgiaeivrewlaoswienrtcroondcuecnetdrabteitownse.en
Tlahregegaennedrsamtaolrld,iwdenroetdferlaicvtieorneadteintthoetdhueset,xpaonsduralel cpahratmibceler.sizIens,the
csoenccoenadtrmaettihonosd., aAgfeanlelriangtosrtrweaasmuosfeddufsotrplaortwicaltemsofsrpohmeraicstdirursetd.
craersreirevdoitrheimpparitnigceledsotno aa pcnyeculomnaetihcejaedt.whTehreeaitrhestlarregaemrfornoesm wtheirsejet
rsiezteurfnreadcttioontahteiorne.serTvhoeir.genTehriastogrenwearsatrournauchnideevrecdosnsotmaentpacrotnidcilteions
aainrdbdeutswt ecoenctehentgreanteiroantsorwearned
lowered by diluting the the exposure chamber.
stream with The airbome:
ecxopnocseinutfrea.tiAotnsthweermiedd-eptoeirnmtionfeedac$htiemxepsosduurrei,ngaepaacrthi4cl-ehosiuzre
distribution measurement was made.
GL: Test Substance: Results:
`Cwliitnhicfalluosriogsncseiwneriemmreedcioartdeedl.y aTfhteereeyxepsoosfurteh.e Rraattsswweerreesstaacirniefdiced fpoorsth-iesxtpoopsautrheo.loTgiicsseuxeasmfirnaotmitownoatra1t,s7d,yi14n,g2d7u,roirng42exdpaoyssure were aNloso examined microscopically. TAhmemmoonritaulmityperraftliousorfooorctthaeno0a.t3e8,,p0u.r8i1t,y0a.p8p3,ro2x.i2m,a4t.e8l,yan1d005.%7 mg/L
19 EID091540 coon e
References: Type: Species/strain: EVaxlpuoes:ure Time: Method:
e6/x6p,oasnudre6/g6r,ourepsspewcetrievel1y/.6 (Anlolt dteesatthssubosctcanucrer-erdeleaittehde)r,du2r6i,ng1/6, 6/6, exposure or within 4 hours after exposure.
eCxlipnoiscuarlesilegvneslso)b,sierrrveegduldaurrbirnegatehxipnogsu(arlel einxcplousduerdeglaesveplisn)g, r(aeldl
sdailsicvhaatrigoen a(2r.o2u,n4d.8t,heanedye5s.7anmdg/nLo)s.e C(allilniecxaplossiugrnesloevbeslesr),veadnd
p(o2s2t-aenxdpo4.s8urmeg/inLc)l,uadendd s>o8m0e%rurpattusrheaovfinegyeosp,aaqllueotahnerdeyes opaque
ocfotrhmeodeeyde-sapwpaesarcionngfeiyremsed(0w.i8t1hafalduo0r.e8s3cemign/sLt)a.inE(x0t.e8r1n,a0l.8d3a,maangde
22 mg/L), with 081mg).
the
eyes
appearing
normal
after
20
days
rIenhaaclhaetdioan moafxtihemtuemst (s2ubtsitmaenscneocramuasle)d7l-i1v4erdeanylsaarfgteemeenxtpowshuirec.h
NLiovecrhawnegieghstisarleitvuerrmceedlltomotrhephnoolromgayl wreanrgeeo4b2sedravyesd.afMtiercreoxspocsoupriec.
perxoammpiinlayt,iobnutinddiiscaaptpeedatrheadtiancautpeprpouxlimmoantaerlyy e1 dweemeak,dleevaevlionpged70
`rmeiscirdousacloipnijcuarlyl.y.NTohedursetwpaarstiicrlreitsatwieornoefsteheen
in the lungs stomach that
cleared
in
o2pawceietkys.anAdmumlcoenraituiomn ptheartflwueorreooscttilalnmoiactreoaslcsoopiccaaulsleydecvoimdeenatl
42 days after exposure.
DuPont Co. (1969). No. 160-69.
Unpublished Data, Haskell Laboratory Report
Keanedy, G. L., Jr. etal. (1983). The Toxicologist, 3:22.
Kennedy, G. L. Jr. 24:1325-1329.
etal. (1986).
Food Chem.Toxicol,
DMaelremarlasL/DCshyR-CD
24 houss
6Ra9t5s9wmegr/ekcgli(p9p5e%d fcroenefoifdheanicre olivmeirtsthuendbeafcikneadn)d trunk area.
Five 7500
mmagl/ekrgatasm/dmoosenileuvmelpewrefrleuodroosoecdtawniotahte3.00T0h,e5t0e0s0t,suabnsdtance,
as
2u.n5d0/e5ar0 asqquuaeroeusofsuaslpuemnisinounm,fwoialsaanpdplhieelddtion tphleacbeacwkiotfh cclaacsthicrat
sbpanodnaggeeds.offAfwtietrh2a4mhioludrdsoetferegxepnots,urrien,setdh,edrraitesd,wearned urnewtruampepdetdo,
their cages for 13 days observation or until death. During the
20
EID091541
39. 0Yy
orp: Test Substance: Results: References:
osibgsnesr.vaGtrioosnspepraitohdo,lothgey
rats were was done
weighed and observed on all survivors and 1
for clinical animal that
rwaatssefxocuenpdtd1e.aTdhaet 7L5D0s0p mvga/lukeg.waLsivcearlcwueliagthedtsfwreormethreecmoorrdaelditinyall
data. No
.
MAomrmaolintiyurmatpioesrfwleuroero0o/c5t;an0o/5a,tea,npdu4r/it5yaatp3p0r0o0x,i5m0a0t0e,lyan1d00%
7A5L0r0atmsg/dkogs,edreastp3ec0t0i0v,el5y0.00D,eaantdh 7o5cc0u0rrmegd/kwigthhiand 2inditaiyalsowfeidgohsting.
loss. 7500
Clinical mg/kg),
wseitgnpseoribnseearlveadreian(cl5u0d0e0dalnedth7a0r0g0y
(5000 and. mg/kg), stained
pcehrrionmeoadlaacrreyaor(r7h5i0e0am(g7/3k0g0),mgs/tkagi)n.edGnroosses(p3a5t0h0olmogg/ykgs)h,oawnedd an
pionsctr-etarseeaitnmelnitv.er weighs in all surviving rats examined at14 days
DuPont Co. (1979). No. 659-79.
Unpublished Data,
Haskell
Laboratory Report
Kennedy, G. 81:348-355.
L.,
Jr.
(1985).
ToxApipl.cPhoarmlaco.l,,
Type: Species/strain: Exposure Time: Value: Method:
GLP: Test Substance: Results: References:
Dermal LD
Female rats/ChR-CD
24 hours
>Ra7t5s0w0ermeg/clkigpp(etdhefrmeae xofimhauimr ofveeasribtlhee dboascek)and trunk area.
Faimvmeofneimaulme preartfsl/udoorsoeoclteavneolawtee.re TdhoesetdeswtistuhbsSt0a0n0ceo,ra7s5a0050m/g5/0kg.
asqquuaeroeusofsauslpuemnisniounm, fwoialsaanpdplhieeldd tion tphleacbeacwkitohfeelaascthicrabtaunnddageersa.
Awfittehra2m4ihlodudresteorfgeenxtp,osruirnsee,d,thderireadts, waenrdereutnuwrrnaepdpteodt,hesiprocnaggeedsoffofr
t1h3edraaytss woebrseerwveatiigohnedoraunndtiolbdseeartvhe.dDfuorricnlignitchaelosbisgeurs.vatSiuornvipveirniogd,
rats
No
were
sacrificed.
`ATmhemmoonritaulmitypewrafslu0o/r5ooacntadno1a/5tea,t p5u0r0i0tyaanpdpr7o5x0i0mamtge/lkyg,100%
rpeesrpfelcutoirvoeolcy.tanDoeaattehcoacucsuerdrmeidl3ddsakyins iamfietrattiroenatamnedntw.eiAghmtmolonssiautm
pbeortihnedaolsearleeavewles.reIonbasdedrivtieodn,ats7t5ai0n0edmgf/ackeg.and wet and stained
DuPont Co. No. 682-80.
(1980).
Unpublished Data, Haskell Laboratory Report
EID091542
2
eed in
8K1e:n34n8e.3d5yG5,..L., Ir. (1985). ToxApipl.cPhoarmlaco.l,
TSpyepceie:s/strain: MDaelremarlabLbitDs/New Zealand White
EVaxlpuoes:ure Time: 24247h8oumrgs/kg (95% confidence limits, lower 2369 mg/kg, upper
Method:
R9wae8br1be4itfmisgtt/wekedgrw,eitsclhloippplepaes6dt.i2fc5r0ceoe4l)olfarhsa.irFiovvee,r 5th5e, baancdk2anmdalterurnakbbaictesa,wearned
adpeosrslfeulrduroywriwotiohctth1a5wn0ao0ta,etre3,,0w0re0as,spe5ac0pt0ip0vle,ileyad.ntdoT7th5hee00tbeamsctgks/uokbfgsetaaamcnmhcoernawibabusimt,,maadnde tihneto
etleassttsiictebawnadsagoecsc)l.udAefdte(rwr2a4phpoeudrswoitfhepxlpaosstiucrew,ratph,e aganuizmea,lsanwdere
ufonrwr1a4popred1,5 wdaayssheodbsweirtvhatwiaotnero,rdurniteidl,adenadthr.evDuurrmeidngttohteheir cages
colbisneircvalatsiiognasp.erGirood,ssthpeatahnoilmoaglys wwearsedwoeniegohnedalalnsdurovbisveorrvseadndfor
c1alacnuilmaatledthfartowmasthefomuonrdtadleiatyd daatta3.000 mg/kg. The LDsy value was
Lp: ReTseuslttSsu:bstance:
NAmomonium perfluorooctanoate, purity approximately 100% Mortality ratiosofrabbits were 0/5, 1/5, 3/5, and 272 a 1500, 3000,
o5f00d0o,sianngd. 7G5r0o0ssmgp/aktgho,loregsipceacltievxealmyi.naDteiaotnhsohcocwurerdednowithi4n days
codmospeoulenvdel:s.relCaltineidccalhasniggenss;ihnocwluedveedr,wetihgehret wloasss saknidnliarbriotraetidon at all
bnarseaalthdiinsgchataraglled(oSs0e00lemvegl/sk.g)I,nsahdadiltlioown,brleeatthhairnggy ((53000000 mmgg//kkgg)),,
p(a5l0l0o0r (mg5/0k0g0),mgw/ektg)u,nddiearrnrehaetah(t5h0e0b0omdgy/k(g5)0,00weaankdn7e5s0s0 mg/kg).
References: DaundPocnytanCoos.is(1(977590)0.mUgn/pkugb)lwieshreedobDsaear,veHda.skell Laboratory Report
No. 659-79.
TSpyepceie:s/strain: Method:
:
K81e:a3n4c8d.y3,55G.. L., Jr. (1985). ToxAipplc.Phoarmlacol..,
MDaelremarlabIbrirtist/aNtieownZealand White aSriexasm,aalnedrapblbaictesdwienrFeDcAl-itppyepdefsrteoecokfsh.aiDroosensothfe 0t.r5ungksaonldidlateral athmemiontnaictusmkipnerufnldueorrogoacutzaenosaqtuearweesr,eaanpdpltiheedteasstasnitaeqwuaesous paste (0 semi-occluded (rubber sheeting was loosely wrapped around the
EIDO91543
=
0G
GLP: Test Substance: Results:
+ Reference:
wterurnekraenmdosveecdurferdowmitthheasdthoecsksi,vethteappea)t.cAhfetserre2mo4vheodu,rsa,ndthether.abbits
reactions No
observed.
Observations
were
also
made
at
48
hours,
AAmmmmoonniiuumm ppeerrfflluuoorrooooccttaannooaattee,cpauursietyd ampiplrdotxoimmaotdeelryat1e0s0k%in
irritation in when tested
24 on
htohuerss,haavneddsilnitgahctt
tsokmiondoefrraatbebiitrsriutnatdieorn
in
48
hours
semi-occluded conditions.
DuPont Co. No. 636-79.
(1979).
Unpublished
Data,
Haskell
Laboratory
Report
Type: Species/swain: Method:
GL:
`Test Substance:
Dermal Irritation
Male rabbits/New Zealand White
`aTnwdetnrtuyn-konaeremasa,leanrdabfbiirtesdwweirtehcplliapsptiecd cforleleaorfs.haAimromvoenriutmhe.back
perfluorooctanoate impregnated Teflon strips or ammonium
bpearcfklouforeoaocchtarnaobabtiet.imTphrreegenraatbebditKsesvelravredsatsricposnwtreorlesapapnldiewdetreo the
`wTrhaeptpreudnkionfneoanc-harmambobintiwuamsptehrefnluoccrcolocutdaendoa(twer-atprpeaetdedwimtahtearliaaly,er
Afoifeplra4s-t,ic8w-,raopr,2g4a-uhzoeursterxeptochsubraendpaegrieo,dsa,ndthaedwhersaipvpeinsgtsretwcehretape).
wreermeovseodakaendditnhae 5e0x:p5o0seetdhaanreoals:wwaetreer wsiopluetdiowni.thThgeauazneipmaaldss wthearte
observed No
afier
unwrapping
for
skin
imitation.
Afimbemrso,n3i8u%mTpeefrlfolnuorroeoscitnatnhoaatteinicmlpurdeegdn2a.te9d% TTerfiltoonn X(-4180%0Taenfdl.on
0.061% oil)
ammonium
perfluorooctanoate,
and
14%
dimethylsilicone
Results: Reference: Type: Species/strain: Method:
KAemvmloarnifuibmerpse,r4fl2u%crKoeovctiaanroatreesiinmptrheatgniantceldudKeedv3l.a2r% (T4r0it.o5n%
X-100 and 0.067% ammonium dimethysilicone oil)
perfluorooctanoate,
and
17.5%
NDuoPsoknitn Ciomi.ta(t1i9o8n1)w.asUnopbusbelrivsehdeddurDiantga,thHeasskteuldly.Laboratory Report
No. 736-81.
Eye Irritation ROnaeb-btietnst/hNemwLZ(e3a8l.a3nmdeW)hoiftseolid test substance was placed ino the 2ri0ghsteccoonndjsu,nc|titvraelatseadceoyfeeawcahs owaf2shreadbbwiittsh(steaxp wnoattesrpefcoirfi1edm)i.nuAtfet.er The treated eye of the other rabbit was not washed. Observations
EID091544 2
cgenin
GLP: ReTseuslttSsu:bstance: Reference:
loafmtpheacto|maenad, 4ihrios,urasn,dacnodnjautn1c,t2i,v3a,we7r,e14m,a2d1e, waintdh2a8hdaanyds-,slit
aFfltueorr-tIh-estdraiypofsttarienaatnmednta.biomicroscope were used at`examinations
No
cAAommmmmeooalnniiopuuammcippteeycrfwfliluutoohrraoooosccmttaaalnnlooaaartteee,acopaufursisetedyveg1re0en0eor%paalciizteyd, minotdeerrmaitteent
emyoedetrhaattewairstiusn,waansdhmeoddeafrtaetretrceoantjmunecntti.viTthisewohcuelnarteesftfeedctisn a rabbit
hpgeerraasldiiusnatgle)ld.y, Aarenncdeedayteed2;d1o-hs2oe8wdedvaweiyrts,hwttahhese smtemisaltldlswuabirstethaavnoacfscecouamlnaedraiplzraotomippoantcli(tysyign of
`mwnoaodsrehmraealdtwebiattdohisanlsi7mghadtlalcyosan,rjeeuaxnccotefipvtsiltfiigoshrtwmtiiotlhdmoncdooenrijrauintticectiecfvofamelcetar.eldTnohepseasc,eitywyehaiwncadhs
was normal DuPont Co.
within (1979).
14 days. Unpublished
Data,
Haskell
Laboratory
Report
No. 635-79.
Repeat Dose Toxicity
Type: Species/Strain: ESxepxo/sNuurmeber: Period: TFrreeaqtumeenncty: of
LeEvxepolssu:re: Method:
GLP: Test Substance: Results:
RMeipceea/tCeDd-1Dose Oral Toxicity Study MRaatlse/aCnld:fCeDmale/S/group
9 doses (3/week)
3 weeks
0T,h0e.1t,est1.s0u,b1s0tamncgek,gas aqueous solutions, was administered by
rientcreaigvaesdtrwiactienrtuobnaltyi.onBtoodryatwseaingdhtmsicaen.d cCloinntircaollsriagtnssawnedrmeice
recorded. the livers
Animals were were removed
sacrificed 3 days and weighed.
after
the
final
dose
and
No
AAmsmigonnifiiucamntpleirvfelruwoeroiogchttanionactree,aspeurwiatsy naoptperdoxiinmbaottehlyma1l0e0a%nd
female mice Liver weights
at the were
| and noted
10 in
mg/kg levels. male rats, but
oSnilgyniatfi1c0anmtgl/ykign.creTahseerde
were no significant any dose.
changes
in
the
liver
weightsof
female
razs
at
EID091545
2
eeoLsy
: Reference:
oMcocrutralrietdyioncmcaulreremdiicne,2/m5alfeemraaltse, moircfeeamtal1e0 rmagt/skagt.anNyodomsoeralleivetly tfeesmtaeld.eraStpsoarnaddiicnwtehieg0h.t1,los1s.0,ocacnudrr1e0dmign /tkheg0m.a1,le1a.0n,danfdem1a0lmeg/kg DmiucPeo.ntWeCaok.n(e1s9s83)w.asUonbpsuebrlviesdheidn tDhaeta1,0Hmagsk/eklglfLeambaolreatmoircye.Report No. 138-83.
Type: Species/Strain:
RReaptesa/tCeeld:CDDose Oral Toxicity Study
SExepxo/sNuurme:ber: ~~ Male/12
Period: Frequency of
12 days; 14 days of recovery
Treatment: Exposure
10 daily doses (5 doses, 2 non-dose days, doses)
Levels: Method:
0,67 mg/kg Each of 6 rats received 10 daily doses of ammonium
psoelruftliuoonr.ooBcotadnyoawteeigbhytsinwtreargeasrtericcoridnetdu.baTtihorneeasraatns awqeureeokuislled
414hoduaryss alfatteerr. reOcregiavinnwgetihgeht1s0"wedorsee,reacnorddtehde. rSeimxaiunnddeorsweedrretksilled
GLP:
Nseorved as controls.
Test Substance: Results:
`ATmhemmoonsitupmropmeirnfelnuotreofofcetcatnoofatthe,eptuersittsyu9bs9t%ance was enlargement of
4th5e%lihveera,viwehricthh,anatthtahteoefntdheofcotnhterdolosraagtse. rTehgiismecnh,anwgaespaebrosiustted.
asfotmerewcehsastatlieosnsosfindcoesa1g4ed,abyustltahteerwtehieghlitvedrisscwreerpeanocnylywa2s0% heavier
than thoseofcontrol rats.
`cTohnetrroelnarlasw,eiagnhdtsthiwserinecr2e0a%sehpeearvsiiesrtetdhaafntetrhocseessoafticoonrorfesdpoosnadgien,g bweeiingght2c2h%anagbeosvewetrheatonfott haecccoomnptaronlieradtsby14modrapyhsollaotgeir.caTlhcehsaenges.
Reference:
`lTohweerptahncarneatthiocsweeoifghcotnstrwoelrseatslhieghtelnyddoefptrhesesetde,stbaenidngre8c%ovaenrdy 12% pihnacsreesa,serdesipnewcteiivgehlty.afTehrethaedrleanstaldsosaen,d+t1es4t%es awnedre+1sl1i%g,htly rDeusPpeocnttivCeol.y,(bnu.dt)r.etUunrpnuebdltiosnhoerdmDaalta1.4days later.
EID091546
x
LS
Type: SSpeexcNieusm/bSterra:in: Exposure: PeFrrieoqdu:ency of Treaunent: Exposure Levels: Method:
14-Day Feeding Study ~~ RMaatl/eC/r20l/:gCrDoupBR
14 days; 56 days of recovery ad libitum for 14 days 0,30, 300 ppm abRnoadtdsywwewerereiegfhaetdpspfrrooaoxndigmeaadntdferlwoym6a1wa9etde6lk0iseb2io4tlr0udma5,.t aDRmuairtvisalnw.getrAhetehstoteuussdeypedsrtsiaiornd,gltyhe tceascthsugbrsotuapncwee.reDifeetdsdwieetrethpatrecpoanrteadinoendce0,f3o0r,toher 23-0w0epepkmfoefedtihneg wpeeriigohdeadnadnwdeorbesesrtvoreeddfroerfrcliigneircaatledsiugnntsiloufsteodx.iciAtlyl.raRsatwsenroet osbacsreirfviecedddautritnheg etnhed roefctohveerfyeepdeirnigodp.erCiaogdewseirdee wexeaimgihneadtiaonnds to rdeattesc/tgrmooupriwbeurnedsoarcrdiefiacdedraatts twheereencdoonfdtuhcete1d4t-wdiacyefdeaeidliy.ngFpievreiod, wanedigohnedraectoevaecrhy sdaacyrsif7i,ce28p,erainodd.56B.loLoidvesrasmwpelrees rweermeovteadkeanndfor eenrgdoanfotfhlueorfiedeedicnogncpeenrtiroadtaionnd aonnalryesciosvefrryomdaryat7s.sacrificed at the.
GLP: ReTseuslttSsu:bstance:
Appropriate body weight
sgtaaitnisst,icaanldmoertghaondswewiegrhet
used data.
to
analyze
body
weights,
No
ADimemtsowneiruemnopterafnlauloyrzoeodc.tanoate, purity approximately 100%
tNooxicmiotrytanloitteiedsiwnetrhee o3b0saernvde3d0d0urpipnmg tghreousptusddy.uriCnligntihcealfesiegdnisngof dpiesrcihoadrgien,claunddedhuirnrcehgeuldarporsetsuprier.atiSotna,tirsatpiicadlblryesaitghniinfgi,carnetddneacsraelases rinomuea0nabdoadyys w7eiagnhdts14weofrtehoebsfeeerdviendgipnerraitosdfarnodmotnher3e0co0vperpymddaoyse s7i.gnMiefiacnanbtloyddyewpereisgshetdgdauirnsinfgrtohmetfhiirsstswaemeekogfrofuepedwienrge.
iSnigrnaitfsficraonmttihncere3a0seasnidn3m0e0apnpambsdoolsueteglriovueprswesiacgrhitfsicweedraet othbeseeravded Oifntchreeasfeededmienagnperreiloatdiavendliovenrrweeciogvhetrsywdearyes o7basnedrv2e8d.inSirgaatisfifcraonmtly the 30 and 300 ppm dose groups sacrificed at the end of the feeding
EIDO91547
x
coon
spaecrriiofdicaenddoonnrreeccoovveerryyddaayy287,. and in the 300 ppm dose group rats
Reference:
rMeecaonvebrlyodoadyo0rgwaenrofel0u.o3ripdpemcoinncecnonttrraotlioantsso,fr33a.t2s pspamcr'iifnictehde.on
m30eapnpbmloraotds,oarngadn7o1f.l5uopripdme icnontcheen3t0ra0tpiopnms wraetrs.e 0O.n9 prepcmovfeorr.y day 7,
controls, 300 pra
19.3 ppm group.
for
the
30
ppm
group,
and
22.2
ppm
for
the
DuPont Co. No. 326.95.
(1995).
Unpublished
Data,
Haskell
Laboratory Report
Type:
Species/Strain:
ESxepxo/sNuurme:ber: Period: Frequency of ETxrpeoastumreen:t: Levels: Method: GLP: Test Substance: Results: References:
14-Day Feeding Study
"
~~ MMailcee/aCnrdf%eCmDa-l1e/S/group
14 days
ad libitum for 14 days
0,30, 300, 3000 ppm
wMearleefaendddfieetmsalceonmtiaicnei(naggaem4m3oannidu4m4pdearyfsl,uowreoiogchtianngca2t1e tfoor38 g)
c1o4nccuornrseenctultyivaenddafyesd. oMnallyegarnodunfdemcahloew.conItnrdoilvsidwuearleboobdsyerwveeidghts,
wfoeorde croencsourdmepdtiaotnt,hean1d4-cdlianyicsaalcrsiifginces.were recorded. Liver weights
No
AAlmlmmoanleiuanmdpfeermflauloeromoiccteandoiaetde,afptuerridtoysaipnpgrowixtihma3t0e0l0y p1p0m0.% One.
afnedma3l0e0m0opupsme.diLeidveatr 3w0ei0gphptm/.bodByodweyiwgehitgrhattiloosssshoocwcuerdreaddoatse3-00
sriegsnpsonosbeseirnvcerdeaisnecaltud2e3d0upnkpemmpintmhaelaedaanrdeaf(e3ma0l0eanmidce3.00C0limngi/ckagl)
aDnudPownetakCnoe.s(s19(8320)0.
mg/kg). Unpublished
Data,
Haskell
Laboratory
Report
No. 12:82.
Kennedy, G. L., Jr. (1987). Toxicol. Lett, 39:295-300.
Type:
14-Day Feeding Study
Species/Strain:
Sex/Number:
~~
Mice/Cri.CD-1
Male and female/S/group/gender
Exposure:
Period:
14 days
EID091543
2
0ooy iy
Frequency of
TrEexapotsmuernet:
Levels:
Method:
GLP: `Test Substance: Results:
adlibitum for 14 days
0, 10, 30,
Male and
100, 300, 1000, 3000, 10,000 ppm
female mice (age 41 and 42 das, weighing
19
t0
30
g)
w1e4rceonfseedcduiteitvsecdoanytsa.inMinagleamamndonfiemuamlepecrofnlturoorlosowctearneooatbesefrovred
concurready and fed only ground chow. Individual body weights,
food
were
consumption, and clinical signs were
recorded at the 14-day sacrifice.
recorded.
Liverweights
No
Ammonium perfluorooctanoate, purity approximately 100%
Death occurred at 1000, 3000, and 10,000 ppm. All female mice at
3000 ppm and all male
2-week time point. All
mice at
10,000
10,000 ppm
ppm female
were
mice
dead at the
and 3000 ppm
male mice were dead at the 1-week time point. Although death
owcacsurnrotedreipnotrhteed1.000 ppm mice, details on the number of deaths
Reference:
Body
3000,
weight loss
and 10,000
occurred at the endof
ppm male and female
each
mice.
week at 300,1000,
Liver weighubody
`weight ratios showed a dose-response increase a>t 10 ppm in male
=a13n00d000f,0eamnpadplme3)0m,i0c0ter.pepmmoCl)ris,np(iac3lal0lo0rsai(ng1dn0s,1o00b00s00erppvppemmd)),,inpscitllauoidenereeddcwpteeiroainknn(e1ea0ls0sa,r(e1a00
(100- 1000 ppm), weight loss (100, 1000, 3000, and 10,000 ppm),
and unkempt appearances (30--0 10,000 ppm).
DuPoat Co. (1981). Unpublished Data, Haskell LaboratoryReport
No. 560-81.
Type: Species/Strain:
ESxepxo/sNuurmeber:
Period: Frequency of Treatment:
Exposure Levels:
Method:
14-Day Feeding Study ~~ Mice/Cr:CD-1
Male and female/S/group
14 days oh
ad libitum for 14 days.
Ammonium perfluorooctancate: 0, 30 ppm Nonadecafluorodecanoic acid: 3, 10, 30, 300, 3000 ppm
pMeirxftluuroersooocftannoonaatdee:ca1f5/l1u5o,ro5d/2e5c,an2o5i/c5 apcpimd/ammonium
Male and female mice (age 44 days, weighing 24 to 35 g) were fed. diets containing either ammonium perflucrooctanoate, : snuobnsatdaenccaefslufoorro1d4eccaonnosieccuatciivde, doarymsi.xtMuarleesoafntdhefetmwaoletecsotntrols were observed concurrently and fed only ground chow. Individual body
EID091549
=
cays
rweeciogrhdtesdaantdtchlein1i4c-aldasyigsaascriwfeircee.recorded. Liver weights were
-
GLP: Test Substance: Results:
No LAimvemrowneiiugmhtpbeorfdlyuowreoiogchttanroaattieo,sphuorwietydaapnprionxcriemaasteelaty a1ll0l0e%vels
etensltaerd.gemMeinxtinagpptehaer2edtetsot bseubdsotsaen-creesladtieddnwoitthalter the effects. Liver
* snuobnsatdaenccaefsl.uorodecanoic acid appearing the more potentofthe two
Reference: NDou.Po5n3t7-C8o2.. (1982). Unpublished Data, Haskell Laboratory Report
Type: SSpeexc/iNeus/mSbterra:in: Exposure: Period: Frequency of TrEexaptosmuernet: Levels: Method: GLP: Test Substance: Results: References:
21-Day Feeding Study ~~ MMiaclee/aCnrdlf:eCmDa-le1/S/group.
21 days awidtlhiobuittucmomfporou21ndd,ayfsor(2Midcaeysw)ere mistakealy fed ground chow,
M0a,l0e01a,n0d0f3e,m0a.le1,m0i3c,e
1,3, (age
10,30 ppm 41 and 42 days,
weighing
21
t0
33
g)
(wseursepefenddeddieitns c1o%ntcaoinminogilabmemfoorneibueminpgemrfilxueodroionctgarnoouantdechow) for
c2o1nccuornrseenctultyivaenddafyesd. oMnalylegraonudnfdecmhaolwe.coInntdriovlisdwuealreboodbsyewreviegdhts
atnhedc2l1i-ndiacaylsascirginfsicwee.re recorded. Liver weights were recorded at
No
LAimvmerosnwieuremspiegrnfilfuiocraonotclytahnecaavtiee,rpautri3t0ypappmpr,osxliimgahttleylyhe1a0v0i%e.r at
N3oppcmh,anagnedsaipnpleiavreredweniogrhmtalwearte10sepepnmait nfemeadlinegalnedveflesmoafle1 mpipcem. or
lliogwhetro,fnaond dtihfefseirgennicfeiscaatnc1e0ofptphme, cishqaunegsetioobnsaebrlvee.dTahte3 opnplmy,cliinnical
sDiugPnoonbtsCerov.e(d1w98a2s).spUonrapduibcliwsehiegdhtDaltosas,. Haskell Laboratory Report
No.323-82.
Type:
Species/Strain:
ESxepxo/sNuurmeber: Period:
Keanedy, G. L., Jr. (1987). Toxicol.Lett., 39:295-300.
2-Year Feeding Study MRaalve//C1r5l6:/CgDrouBpR
2 years
EID5185
2
CooL IY
TFrreeaqtumeenncty: of LeEvxeplossu:re Method: oe
ad libitum for 2 years
(M0ca,ol0net(rproaalit)rs,-efOesd()ec,o3nat0drm0oilpnippsamtier-rfeeddetiotthheer0a(mamdoinpiiurammpceornftlruoolragsrcotuappoate dgeirreootuupfposr(eCaaPpc-phCr3ro)ax)t,iwmaoarst3ed0el20syipgypneaamrtsea.dmfAmofortnierithuaesmrspihegornrfmmleouanctartloooectvtraaelanutoamtteienotinn ae p(o1i0n/tg)r,oourp/etviamleuaptoiionn)o,fcpeelroprxoilsiofemreatpiroonliefvearlautaitoino(n8/(gr/ogurpo/uipm/ei.me Sptoaibnit)l.ityAolflarmatms ownerieupmropverifdleudofroooocdtaannodattaepwwas acoantfdirbemeidr.by Tahnraoluygsheoautsttthheebsetguidnyn,incgo,ncmeindtdrlaet,ioannodftehned otfestthceosmupdo.und ia the diet and the homogeacity of the test diets were determined.
sAtlaln.ratBsowdeyreweaipgphrtosx,imfaotoedlcyon4s9udmapytsioonf,aagnedocnlitnhiecadlasyigonfsstwuedrye monitored throughout the study.
6B,l9o,o1d2,wa1s5,co1l3l,ecatnedd 2f1ormhoonrtmhosnaalfearnailniytsieastiaotnoafptphreoxsimwaatye.lySe1r, u3r,a wfoalslicalneasltyizmeudlaftoirntgeshtoorsmteornoene,(FeSsHtr)a,diaonld, lpurtoeliancitziinngcohnocernmtoranteio(nLsE.D,
R1a2t,s15w,er1e8,saancrdif2i1cemdonattthhse ffoorlcleolwlipnrgoliinfteerraitmiotnimaendpopienrtos:xi1s,o3m,e6,9,
ptersotleisf,ecraptiidoindeyvmaildueast,ioancsc.esTshoeryfsoelxlogwlianngdo(rAgaSnGs)wuenriet wwietihghfeldui:d,
lciovaegr.ulaItmimnegdigalatnedl/ysaefmtienrawleviegshiicnlge,wtihtehlfilvueirdarnedmotevsetdes, fprroosmtate, and
palnaicmeadlsinisecleec<toelddfohropmeorgoenriizsaotmieopnrobluifffeerratfioornpeevraolxuiastoiomnalwere
psreelpeacrtaetdifoonr. cTehllepfrooliilfoewriantgiotnisesvuaelsuawteiroen:croilglhetctaenddflreoftmttehsteesr,ts
gerpoisdsidlyemsiiodness., AAlSlGr,atlsisveurr,vdivuiondgetnhuem2,4p-imtuointtarhy,teastodpearllioodrgwaenrsewith
usnaictr,ifciocaegdualnatdinnegcgrloapnsdi/csde.miBnraalinv,eshiecalre,s
liver, with
fslpuliedern,emkoivdeaedy,s,
ASG
plirvoesrt,attees,teesp,ideipdiydmiiddyemsi,deasn,dptaensctreesawse,raendweoirgghaends watitnhecgrroopsssy.lesTihoens
were examined microscopically.
Data were analyzed by appropriate statistical methods.
EIDO91SS 1
coo
ReTseuslttSsu:bstance: Reference:
AInmcmreoanseidurmelpaetirvfeluloirvoeorcwteaingohattes,wpeurreitoyb9se8r-v1e0d0i%n the ammonium palesrofliunocrroeoacsteadnoiantteh-etraematmeodnraitus.m HpeepraftliucoBr-oooxcitdaantoioantea-cttirveiatyrtaewtdsasat salilgntiifmiecapnotilnytsa.lteArmthmeornaiteuofmLpeeyrfdliugorcoelolctBa-nooxaitdeatdiiodnnoort Leydig cell parpoplriofxeriamtaitoen.lyM2o0r-etoivmeers,letshsertahtaen otfheBr-aotiedoaftihoepnatinicLeB-yodxiigdacteilolsn.was uSnecrhuamngteeds.tosTthereornee,weFrSeH,,hporwoelvacetri,n,siagnndifLicHanlteivenlcsrewaesresein serum e1s,t3r,ad6i,o9l,l1e5v,els18i,nanthde2a1mmmoonntihus.m pAetrf1l2uomroonotchtsan,otahtee-atmremaotnediuatms at pwehrefnlucooromopcatraenodatteo-tthreeaptaeidr-rfaetds choandtreolle.vaHtiesdtospeartuhmoleosgtircaadliol levels ecevlall,uaantdiopnarnecvreeaatliecd accoimnpaorucnedl-lrteulmaotresd. iBnacrseeadseosninthleisveedra,tLae,ytdhieg Lesetyrdaidigolcellelvtelusmoarnsdarpepdeuacretdoprboeladcuteintoletvheelsc.ombination of elevated `DuPont Co. (2000). Unpublished Data (Draft Manuscript)
Type: SSpeexc/iNesu/mSbterrai:n: Exposure: PeFrrieoqude:ncy of Treament: Exposure: LMeevtehlosd::
RReaptesa/tCehdR-ECxDposure Inhalation Study Male/20/group
2 weeks; 42 days of recovery
6 hours/day, 5 days/week
0,8, 80 mg/m'
Houseline air eyclone-head
d(uasptprgoexniemraatteolryc2on0nLeicmtiend)towaaspapratiscslee.d
through
a
`aTghietaretsourl-teisnegravioribtohrantecpoanrttaiciunleadteawmamsonpaisusmedpeirntfoluaor3o0ocLtabnaotaetre.y jar
exposure chamber. The atmospheric concentration of ammonium
perfluorooctanoate in the exposure chamber was monitored at
30-mimite intervals.
Rats were exposed, head only, for consecutive days, 6 hours per day. After 5 days, the rats were given a 2-day recovery (weekend), `which was followed by $ daily, consecutive 6-hour exposures. All rats were weighed and observed daily (except weekends) during the elixbpiotsuumraetaanlldtriemceosovetrhyerpetrhiaondsd.urFionogdtahnedacwtautaelrexwpeorseuraev.ailable ad
eClaicnhicgarloulapbaorta,to1r4y,eaxanmdi2n8atdiaoynsspwoesrte-cpxeprosfuorrem.edAfotner10a rtaottsalforfom EID091552
3
000 1h
a100 ,ex1p4o,su3r2e,sa,n5d r4a2tsdfaryosmpoesatc-hexgproosuuprew.erOerpgaatnhsolwoegriecawlelyigehveadl,uaatnedd absolute and relative organ weights were calculated.
GLP: Test Substance: Results:
gOrnoutphefo5r%eaynede9x*amdianyastioofnse.xposure, 10 rats were selected from cach No AOvmemraolnlimuemanpecrofnlcueoartoroacttiaonnosatwee,rpeu0r,it1y1a%pp5r,o8x3im=at1e7lfyor1t0h0e%0, 5,
and 80 mg/m' exposure levels, respectively.
Rats exposed to ammonium perfluorooctanoate showed a
ogsfruoprpuerpceoswvsaeirsoyn.mooDrfuebrosidenvygewereealicyghhaetfxftpehocrstuoerudegd,huosrupitonrgtahedexitcpeoscsta.usreTeshoaefnb8dl3ifnomkrgi/1n4mg,days
pawing, groups.
chewing,
and
red
eye
and
nasal
discharge
were
seen
ip
all
`elSeovmaeterdataslekxalpionseepdhtoospahmamtaosneiaucmtivpietryf.luEofrfoeoccttsawnoearteesdeuesnt idnisplayed gtlruatnasmaimci-npaysreuavfitcert0r,an1s4a,mainndas2e8arnedcogvleutraymdiacy-so.xaTlahceetiinccidence was related to dose; higher activities were found at the higher exposure dlievfefle.renHtowfervoemrc,onotnrlolys.the latter activity at 83 mg/m' was statistically
dPeagtehnoelroagtiicoenvaolfuhaetpiaotnoscsyhteosweind tchleoluidvyerssoweflrlaitnsg eoxrpgorsaenudltaor
aefmfemcotnwiausmnoptersfeleunoraofotcetaarno1a4t-edafyoror10lodnagyesr
with no recovery. recovery period.
This No
oretlhaetredcoimnpcoruenadi-snreelliaveerdwheiisgthotlosgwicaschoabnsgeersvewde.re noted. Exposure-
References:
Nexoamciomneeadla,ftreirc5,oorr9coenxjpuonscutrievadlayesf.fects were seen in any of the rats
DuPour Co. No.253-79.
(1979).
Unpublished
Data,
Haskell
Laboratory
Report
Keanedy, G.L., Jr. et al. (1983). TThoexicologist, 3:22.
Type: Species/Strain:
RReaptesa/Ctreld:CEDxposure Inhalation Study
SExepxo/sNuurmeber: ~~ Male/24/group
Period:
2 weeks; 84 days of recovery
EIDO9ISS3
32
009y
Frequency of Treatment: Exposure: LMeevtehlosd:: GLP: Test Substance: Results:
6 hours/day, $ days/week
bD0,yusp1t,a8a,st8smo0isanmpighgre/rtmeh"srooufghamamgolansis ugemnepreartfolru.orFooocrtathneoahtieghwecroencgeennterraattieodn d(e8t0emrgm/imn'e)d,bcyhgarmabveirmeattrmiocsapnhaleyrseisc.onFcoenrttrhaetiionntserwmeerdeiaptreimaanrdillyow wcoenrceendtertaetrimoinnse(d8baynda c|hmegm/imca'l, arneaslpyescetsiv.ely), chamber atmospheres hMeaalde-ornatlsy(taogdeu7s-t8awtemeokssp,hewreeisgfhoirng6 2ho4u0r-s2/7d9ayg,)5wedraeyse/xwpeoeskedfor 2 weeks (weekends excluded). During exposure, rats were observed oabnsdecrlviendicdaalisliygnfsorwe1r4r'encootveedr.y Pdoasyts-,etxhpeonsuwreeigrahtesdwearned wobesiegrhveedd and s2atcriimfeisc/edweaetk0,th1r4o,u2g8h, 8442,daaynsd o8f4rdeacyosveorfy.recFoivveeryr,atfso/rgraotuoptawleorfe96 test days.
cCalicnhicgarloulpabaotr0a,tor1y4,e2x8a,mi4n2,atainodns84wedraeyspeprofsto-remxepdosounre$.raAtfstferroamtotal eovfa1l0uaetxepdosatur0e,s,14, 2r8at,s4f2r,oamneda8c4h dgaryosuppowsetr-eexppoastuhroel.ogiTcahlelyrats were eevxaalmuiatnieodn.grIonssaldydiatnidont,islsuunegss,anhedarotr,gatnhsymwuesr,essplaeveend, floirvemr,ictreostsecso,pic and kidneys were weighed. At necropsy, blood was collected for analysis of organofluoride wleevreelsainnalryatzebdloaotde.acBhloroedcosvaemrpylpeesriford.omBtlhoeo0dasnadmp8l0emsgf/rmo'm gtrheoups dLaayns.d 8 mg/m' groups were analyzed only at 0 and 28 recovery No AOvmemraolnlimuemanpecrofnlcueonrtoroacttiaonnosatwee,rpeur1i.t0y0a.p5pr,o7x.i6mate2.l5y, 1a0nd0%
83.9.2 12.8 mg/m'forthe 1, 8, and 80 mg/m' groups, respectively.
Body weight analysis demonstrated no significant differences
between controls and 1 mg/m'. Body weights from animals exposed
t1o7-833m.g/Bmo'dywewreeigshigtnsiffriocamnatnlyihmiaglhesretxhpaonsecdonttoro8l0sfmrgo/mmt'eswetrdea.ys.
osfigcnliifniiccaanltlsyiglnoswedrutrhinagnecxopnotsruorlessfsrhomowteesdtodnalyyss2l-i1g6h.t sOibgsnesrovfatniaosanls a3-n4d doacyuslaornditessctha1rgreat. diHeodweduvreirn,gaetxtphoesuhirgehacnodnc1enrattrawtaisons,acarfiiefriced
EID091554 2
00a
References:
Type:
Species/Strain: Sex/Number:
winasexptrreombiasb.lyBeoxtphosoufret-hreesleartaetds,haaldthsoeuvgehrepawtehioglhotgilocses.valMuoartailointy c8o0umldg/nmot' deextpeorsmuirneegtrhoeucpaeuxskeiobiftdeedatlhu.ngTnhoeisee odfur2i4ngrattshein12th-eday exposure period.
Oinrcgraenasteoibnolduyngw,eliigvehrt, raantdiostedsetemsonwsetirgahttesdafatesrig0nirfeiccaonvte,rdyodsaey-sr.elaTtheed liver/body weight ratios were siguificandly higher in animal eLtihxvrpeooruswgeehdi2gt8hotd8sa0ywsmergoe/fmsr'iegcntoihvfreiorcuyag,nhtbl2uy8thtdihgaihysesmorfairnyetcbhoeeva8enrmyagr./timMf?aecatannciaamubassleosdlubtye ainncruenaesxeplianilniavbelreweiincgrhetasseati8n bmogd/ym'w.eight accompanied by 3 normal
aCllkianliicnael plhaobosrpahtaotraysemeiansaullregmreonutpss deexmpoonssetdratoteadmamnoinnicruemase in
.
perfluorooctanoate after 10 exposures, but this finding was
si88g40nidmfagiy/csmaon'ftaroneniclmyoavlaestry8thnaronodudgi8fh0fe1mr4ged/nacmey'ss.owfeTrhreiecsofvoinuecnrrdye..aseAfpteerrsi2s8t,ed42i,n athned
``pCaonmlpoobuunladr-rheelpaattoecdelplautlhaorlohgyipcerftirnodpihngys, icnecntlruodleodbhuelaarvyhelpiavteorcs,ellular hypertrophy, and hepatocellular necrosis in animals exposed to
r8elaantdio8n0shmipg,/mb'ut. wTehreesreevfeirnsdiibnlgesbsyho2w8eddayasn oefxproescuorvee-rryes(8pomngs/em')
or 42 days of recovery (80 mg/m').
eBxlpooosduroer-graenloaftleudoprrideeseanncaelyisnisallclgeraorulypsde(mionnclsutdriantgedthaencontrols, this dfeincdrienagserdemwaiitnhstuinmee,xpbluatinweads).deBtlecotoadbloergafatneorfl8u4ordiadyes loefverlescovery in DboutPhouthteCcoo.nt(r1o9l81a)n.d 8U0npmugb/lmi'sheexdpDoastuar,eHlaesveklesl.l Laboratory Report No. 205-81.
Kennedy, G. L., Jr. et al. (1983).TThoexicologist, 3:22.
Kenaedy,G.L., 24:1325-1329,
J.
etal.
(1986).
Food
Chem.
Toxicol,
RReaptesa/tCehdR-DCoDse Dermal Study Male/1S/group
EID091s:55
34
eed
Exposure Period: Frequency of
ETxrpeoastmuernet:
Levels:
Method:
.
+
2 weeks; 42 days of recovery
- 6 hours/day, 5 days/week
0, 20, 200, 2000 mg/kg
pdMruaerlvienegartatthisen(g2ea-sgwteieo8enkwoeefexktpsho,esucwroeeimgppheoiruinnogdd.21wA0h-me2nm4o5prngei)eunwimenrgeacnodlglraroeodmtiong
perfluorooctanoate, as
each rat that had been
an
aqueous
paste,
was
applied
to
the
backs
of
eganudzeed pwahde.nCtohlelacrosmwpeorsuehnardveewmdaofsvreewdeiopaffehtdaerifrer.xopmoDstahuierleyra6dt-sa'hyobu1a0rc`,kesxpwoistuhreas.
`Throughout the test period, food and water were available
adlibitum. Body weights and clinical signs were recorded.
After taken
exposure day 10 from S rats from
aenadchognrroeucpovfeorryhedmaaytsol14ogayndme4a2s,ubrleomoedntwsa,s
MoGnreoa$snscaantbessc/orglrouoptusepyaaanfndtedrrheelixaspttioovspeautorhreogl1ao0ng,itacoanbldoeodxnyamrwieenciaogtvhietornysdawyesre1p4erafnodr4m2e.d
bpleorfoodrwmaeds.coAlflteecrteedxfporsoumr5e r1a0tsa/ngdroounp rfeocroovregraynodfal`uyaosnrai1ln4yes.aensd.we42r,e
determinations. exposure 9,and
oEnyereecxoavmeirnyadtaiyosns1w3earnedp4e1r.foTrhmeedproonceedaucrherat
after
sienmcliumdiecdrogsrcoosspiocbsoebrsveartviaotnioonftuhseinegyaehsaunsginmgaagnbriifgyhitnlgiglhat,mpanadnd a
slit-lamp biomicroscope.
GLP:
Test Substance: Results:
Data were analyzed by appropriate statistical methods,
No
RAamtmsotrneiatuemd wpietrhfl2u0ormoogc/tkagnoaatmem,opnuiriutmy appeprfrlouxcirmoaotcetlayno1a0te0%showed
normal body
experiment.
weights and no
During the 10-d
auynuesxupaolsuclrienipcearlisoidg,nrsa
du
ts
ring the
treated with
either 200 or 2000 mg/kg after the exposure period.
lost weight, followed Slight redness of the
by a skin
normalgrowth was observed in
these 2 groups, along with salivation in the 2000 `mg/kg group only.
recovery days 14 and 42. Clinical enzyme determinations `monitoring liver function (alkaline
phosphatase, GPT,
treated groupsafter
and GOT)
exposure
1s0h. oTwheedsdeosvea-lrueelsarteedtuirnncerdeatsoensoirnmaalll
at
Liver damage characterized all treated groups following
by the
coagulativenecrosis.was 10% dose. The incidence
observed and
in
EID091556
by
ogo
sinevtehreit2y0ofmlgi/vkegr gdraomuapge14wdaasysdofseo-lrleolwaitnegd.theRe1c0ovedorsye,waasndcowmapslete iernsescteohnvetei2ra0yl0ldy0acymogm4/2p,klgertegevreoirunspat.lheoTf2w0loi0vemrragtd/sakemgxapggoresoeuwdpastaote2tsh0see0a0staimamglel/yktcigmoehm.apdlOetne bc1oo0adegxyuplwoaestiuigrvheetsn.beacsLriiosvs,iessrohwfoetwihgehedtsead,poibsdoeet-rhrmeiolsnaataendtahiebnsdcorolesuaetseesatonendfeorxelpllaootswiuivreneg30day i11n04c,rdweaiaytsshedaaaldriveietnrutwmhee(i0g2hn0to0rpmmeagrls/ikswgteeigdgrhfotourpsa4e2etnd4ai2nysdtahiyens2to0hfemr2ge0/c0ko0vgemrggyr./okuTpghaet gdraoyup1.0,atlhtehomuegahna kriednndeytwoewiagrhdtnsoorfmtahle w2a0smogb/skergvgerd.oupOnweexsposure skiigdaniefyicwaenitlgyhtgsrefarteorm tthhaen2c0o0nt0romlgs/, kagndgrtohuepmweearneasbisgonliuftiecasnptlleyclaesasnd 2th0a0n0cmongt/rkolgs.grTouhpe smheoawnedrelaasttiavteistteisctailcluylasrigwneiifgichatnstfirnocrmeathsee on esixgpnoisfuicraentdaiyncr1e0.aseOninrtehceomveerayndraeylat1i4,vethkeirdenewyasanadsttaetsitsetsicwaelilyghts of the 200 and 2000 mg/kg groups.
References:
eBxlpooosduroergdaanyof1l0u,orfiodlelolweveedlsbyshaodweecdredaossee-irnetlhaeteldeveellesvaattiroencoovnery
days 14 and 42. These values after the 10" exposure ranged from
45a22n.,d88A1t,appanmbdl(o12o01d,8o2pr0gp0a,mnao(fn2ld0u,2o2r00i00d0,e maceon/ndckes2n,0t0rr0aetsmpigeo/cntkiogvf,ealrype)psrpaoetcxrtieimvcaeotlveyel)ryytoda1y,.4, s1e0rpupmme,ntzhyermeewaectrievintoy,rmaanldlniovecrlwineiicgahltsitogabsoodrybwoediyghwteirgahtitos and dleivfefle.reAncteas bflrooomdcoorngtraonlosf.luOorniederaltevsehloowfedaplpirvoexricmhaatnegleys5a0t pthpims, tmheearenwaebrsoelumtaerkanedd rleilvaetricvhealnigveerswaenidghstisg.niNfiocaontthienrcrtoeraiscesefifnetchtse DwuerPeoaetviCdoe.at(1a9t8t0h)i.s bUlnopoudbolrigsahneodflDuaotrai,deHacsokneclelntLraabtoiorna.tory Report No. 589-80.
Keanedy, G. L., Jr. (1985). ToxAippl.cPhoarmlaco.l, 81:348-355. Developmental Toxicity
.
Type:
Developmental Toxicity in Rats
SSpeexc/iNeus/mSbterrai:n: ~~ RFaetmsa/lCers/l6:-C1D5/(grSoDu)pBR
Route of
Administration: Inhalation
EID091557
36 009
Exposure Period: Frequency of Treatment: Exposure
Levels:
Method:
Days 6-15 of Gestation 6 hours/day
0,0.1,
Female
1.0,
rats
10.0, 25.0 mg/m'
were mated to males,
and
mating
was
verified
by
dfeotlelcotwiionngoofvserpneirgmhattcoozboaabiitnatthieonv.agTihnaeldlaayvatghaetesapcehrmmoartnozionag were
detected was designated as Day 1 of gestation (Day 1G).
F24ormEaxtpeedrifemmeanltesI (wfeermealteoshsaavceribfeiceendabsesfiogrneedpatrotucraitcihong)r,oauptotal of
(12 females/group/Run). However, due to the degree of maternal
ctooxnicceinttyraintieovnidweanscereidnutcheed2t5o.010m.g0/mmg'/mgr?ofuopr
in Run
Run II,
I, this
and 15
mated
cfoenmtarloelsgwreoruepsas(s6imgantededtofethmiaslense/wgrgoruopu)p.weFruertahdedremdorteo,RtuwnoITm;oornee:
wthaes1p0aimrg-f/emd'togrtohuep.25.0 mg/m' group, and the other was pair fed to
F1o2rmEaxtpeedrfiemmeanlteIIra(tfsewmearleesdiasltlroiwbeudtetdotgoievaecbhirgtrho),upi.n RWuinthIthe
addition of the 10.0 mg/m' group in Run II, 6 mated females were added to both the control and the 10.0 mg/m" groups.
pReactfslwuoerroeocetxapnoosaetde winho1l5e0L-bogdlyastso aantdmosstapihnelreesssosfteaelmmRoocnheisutmerwtiypree-cmheasmhbemrosduwlietsh.inCwhhaimcbhetrhecornactsenwterraetihoonsusweedrienddievtiedrumailnleydinby
gravimetric analysis either each % hour (1.0 mg/m', and 10 or 25 mg/m') or each hour (0.1 mg/m'), and by a spectrophotometric
teexcphonsiuqrueed(aoynfoeratchhe0.o1thmegr/lme'veslasmtpelset,eda).nd on 5-6 samples per `Dcaomnssumvipetrieonwewiagshemdeaasnudreodbsdeurrviendgfgoerstclaitniiocnal(2sifgenmsa.leFse/ecadge). The ddaatmaswewrereecocloldeectdedf,roamndbeufatoirleaslalcsrtirfuiccteuurnatliallatlelramtaitonesmnaoltaenddafmeotanlg `tehexafmeitnuesdesfworergerocslsaspsaitfhioedl.ogiAcftcehrasnagcersif,iclei,vetrhweediagmhts wwaesrerecorded, aluntdeareapnrdodiumcptliavnetasttiaotnusswitaess wdeerteercmoiunnetde.d,Tahnedutmhebenurmobfecrorapndora positionofall live, dead, and resorbed fetuses were recorded. All live and dead fetuses wereweighedand sexed externally and
EID09 558 2]
e053
Lp: ReTseuslttSsu:bstance:
aaillnittveereranwtailholenys,n. arnAedpmpotrhvoeexdliimvfeartfoeemltuytshbee%sodwfaetmrheeweefrxeeatmuesixenasoemdfinfeeoardcehfxotlreirvtniesarcltehraatl were swailemtrieelraaatrlilosyno.s,eTxahanemdifanelteludsstefsuonrtthheaedtaowdreamrlaetelerfaxtoairommnisen.dedfSeeftcoutrsieovsnisswc,eercraoelnetaaxliatnemirianntgietodnhse h22iyfsetesotoluosfgeis3cfaflreltoyumsfeeosarcfehrxoalmmiicnaatcothfietolhnir.tetecrIoonfntRtruhonel Ig2Ir,5o.ou0npem,gfw/eetmra'le hgperraoodcuepfsrsaoenmdd coafch oex4familintetder.s fIrnoamddtihteio1n0;.0thmegh/ema'dsgrforuopm aanldftehteusceosntirnotlhgergoruopupwepraeir ffeetdutsoesthweer2e5 emxga/mmi'negdrofuopr swkeerleetpalroacletsersaetdiofnosr, examination. All
FsoarmeExapsefroirmEexnpteIrLimtehentprI,oceexdcuerpetsthuastetdhuendtialmDsawye2re1Gwewiegrheedthleess
afnredqutehnetildyendtuirtiynofgegaescthatioofnf,spfreiendgcwointshuimnpltiiteorns wwaass nnoottmreetaasiunreedd.,
pwBoaelfsyocrnaeortebexodpnaeanctdetecwdaagpsaerttteuhrraitmtecidoonnD,taaeyiance1hdPdPba.emddTwihnaegs.dhaTomuhsseewddeartinee aowfeipagrhteudritainodn
egexsatmaitinoendifnodrecxliwneircaelcsailgcnusl.atFedo,r aenadchfotresetagcrholuiptefrervtiialbitiyliitnydienxdaenxd
and lactation Day 22 Pp.
index
were
calculated.
All
dams
were
sacrificed
on
`The pups examined
ffroromexetaecmhaldaamltewrearteioncsoutnotweadr,dstehxeede,ndwoeifghDeady,
and 1 PP.
cTlhienriecaafltesri,gnesaocnh Dpuapyw4,as7,w1e4i,gahnedd2a2ndPPi.nspTehceteedyefosorfatdvheerspeups in
aolplhgtrhoaulpmsoolofgiRsutnonI (DEaxypser1i5m,e1n6t,IoT)r w1e7rPePe,xsahmoirtnleydafbtyeranthe eyes
coopdeende.d.OTnhiDsaeyx3a5miPnPa,ticoanchwapsupcownadsucsatcerdifwiictehd tahnedetxhpeoseuyrees wleevreels
fixed for possible future evaluation.
Datawere Yes
analyzed
by
appropiate
statistical
methods.
TAhmemaocntuiaulmmepearnflcuoonrcoeoncttraantoiaotnes,apcuhriietvye>d9w5er%e 0 and
a10p.p0r,oaxinmda2t5e.l0y m0.g1/4m,?1.e2x,p9o.s9u,raengdro2u1p.s0.mg/m'forthe 0, 0.1, 1.0,
N21odeaffmesctesxwpeorseedobtsoearmvmedonati0u.m1 operr1f.l0uomrgo/omc't.anoNaotneeaotft10h.e0 mg/m'
died, but they showed similar clinical signs to a lesser degree than EID091559
is
econ
sptueharrtvfilsvueeoertnoooactttetarhnme,oa2mt5oe.s0wtmaosgft/ohmv'eerlsleuvyrevlti.ovxoiArctst2ho5ardamtgws/eimtn'at,hbaadtom5mm/eo2n4nsi;diurdmedndoitshedbxerpcoorwesnausrdeeidspceforelieoodrdac;toianonsnduamarpnotuuinnodknetahmnepdetybaeopsd,pyenaowrsaeeni,cgeha.tndgamionudthu;nlgethtahregy, bMaasties miandlicliavteerd wtehiatghetxpcohsaunrgeestoaammomnogngiruoumppseorfnlauorreoloacttivaenowaetieghatt bi1no0cd.r0yeamwsgeei/gimnhl'tiovgrearigrnweeiaintgethrhterseoescugclrutoreurdpeisdn,dsweishgpiniictfheicstaihngetnlisyfigilncaiarfngiteclraynlrtivededreusc.creeTdahstiehsein relative liver weights of the pair-fed contrct groups.
liNemovpelldaintftefsset,reedm.necaesn fnruommbcehrotrfolcowreproeraolbusteera,veodr ifnettalhedmeaetahninnuamnbyedrosoe.f
dDaevmesloopnmDeantya2l1tooxfigceistytawtaiosnnaottadneymcoonnscternattreadtiuopnoonfsaacmrmifoinceioufmthe
tpoexrifcliutyo,roeoxcptraensosaetde atsesdteedc.reCaosnecdenftetraaltwioeni-grhetl,aotcecduermrberdyoon-lfyeatatl
-
25.0 body
mg/m', weight
wpehriscihstwedastooDvearytl1y
toxic to PP, but
the oot
tdoaDmsa. y4ThPiPs.
decreased
vOinvoDfaryosm
15, 16, Run I
or did
1n7otPPre,vceoaldecdonecxeanmtriantaitoino-nreolfattehde
pups'
eyes
in
emxaalmfoirnmaattiioonnosf.thIen evyieesw oofftthheespeupnesgfatriovmeRruesnulItTs,wasisminloatr in vivo
conducted.
Reference:
hAamzmarodnti0utmhepceornfcleupotruoso.ctanoate did not demonstrate a uique
DuPont Co. No. 881-81.
(1981).
Unpublished
Data,
Haskell
Laboratory Report
Staples, R. E. et al. (1984).Fundam.Appl.Toxicol, 4:429-440.
Type:
Developmental Toxicity in Rats
SSpeexc/iNeus/mSbterrai:n: Route of
~~
RFaetmsa/lCe/r2l5:/CgDrYo(upSD()EBxRperiment
I,
12/group
(Experiment
I)
Administration: Exposure
Gavage
Period:
Days 6-15 of Gestation
EID091560
3%
oo
Exposure: Levels: Method:
0,100 mgrkg aI1n0m0amopmrgne/itkeusgtm/,d2paeyrnfotlonu-doperrtoeoegcrntmaainnntoeaftteehmeabmlyeagxraaivtamsguwemeardteo1as5de0mtimhngait/sktthgee/redddaamyso.r could tolerate for the planned exposure period of 10 days, dFaoyr tthhaetdsepfienrimtaivteozsotuadwy,erfeemdaelteecrtaetds iwnervaegminaatledltaovamgaelweas,s and the designated as Day 1 of gestation (Day 1G).
cFoonrsEuxmppetriiomnendturIi,nbgogdeystwaetiigohntsw,ercelirnieccaolrdseidg.ns,Tahneddfaemesd were wceordeedcoflrloecmtjeuds,tabnedfournetislacarlifsitcreucutnutriallaailltmeartateironnaslnaontdedfeatamlodnagtathe fetuses were classified.
Awfetreeresxaacrmiifniecdeo,ftlihveer dwaeimgshtonwaDsayre2c1oGrd,edg,roasnsdpartehporloodguiccticvheasntgaetsus swiatsesdweetreermcionuendt.edT,haendnutmhebearumobfecroarpnodrapolsuitteiaoanozdfailmlpllainvet,atdieoand, awnedigrheesdorabnedd sfeetxuesdesexwteermealrleycoarnddedi.ntAerlnlallliyv,e aanndd dtheeadlifveetfuesteusswesere fweetrueseesoxafmeiancehdfloirteerxttheamtawleraeltaelriatvieownsh.enAprpermooxviemdatferloymtoheftdhaem. m`waelrfeoerxmaemdinfeetdusfeosrwveisrceersailmiallaterrlayteioxnasm.inIenda.ddTithieonh,eaaldlssotfuanltled or tfheeturseesmaeixnadmeirnteodtoftoarlv2i/s3ceorfaleaacltherliatttieornwsearnedfaixseudffaincidenetxanmuimnbeedr of fwoerrheeafidxeadl,tewreartieonesx.amAillnefdetfuosress,keelxecteapltatltheerahteiaodnss.of those that
sFoarmeExapsefroirmEexnpteIrIi, mtehentprI,oceexdcuerpetsthuastebdoudnytilweDiagyht2s1wGerweerceoltlheected aonnddtihfefeirdeennttgietsytofateiaonchdayosf,fsfpereidngcowintshuimnpltiitoenrswwaassnnoottmreeatsauinreedd., Ahtoluesaesdtitnwaopodlayycsabrebfoonraeteexcpaegcetewditpharbteurdidtiinogn., cTahceh ddaatme owfas `pawretiugrhietdioannwdaesxanomtiende,danfodrwcalisnitcealrmseidgnDs.ayFo|rPcPa.chThteestdgarmosupwere lfietrtteirlivtiyabiinldietxy ainnddegxeastnadtiloanctiantidoenxiwnedreex cwaelrceulcaatlecdu,laantedd.foArlelacdhams were sacrificed on Day 23 PP, without pathological examination.
`Tehxeampiunpesdffroromexetaecrhnadlaamltewrearteiocnsoutnotweadr,dsethxeede,nwdeoifghDeady, 1anPdP.
EIDo91s61
"0
000r an
`Thereafter, each clinical signs on
pup Day
was weighed 4, 7, 14, and
2a2ndPPi.nspTehceteedyefsoor fadtvheerspe.ups
in
Dboatyhsg2r7ouapnsdw3e1rePPe.xaTmhiisneedxabmyinanatoipohnthwaalsmocloongdiuscttbedetwwietehnthe
ethxepoesyuersewleerveelfsicxoeddefdo.r hOinstoDlaogyic35evPaPl,uaetaiconh.pup was sacrificed and
GLP: * ReTseuslttSsu:bstance:
Data Yes
were
analyzed
by
appropriate
statistical
methods,
AInmtmhoe nprietuemst,peornfeluroarto(owcetaingohaitneg,
purity 278 g)
> 95% dosed at
150
mg/kg
showed
soenvethreemcloimniicnalgsoifgtnhseof5tTMoxdiacyi,tybybywhtihech4%tidmaeyitanhdadwalosstfound dead
approximately 40 g body weight. Another rat (weighing 260 g)
d5noodtsaeeyddsiaontf11d5ro0astimtnghga/tkatlgo1slt0o0satpmapgpr/pokrxgoi,xmiaatmdeavlteyerls6ye gc1,l1iangnidcbaylwetsrihegen3msi%wndeiarmyea.lnoAitfnttehre
o1t0h0ermgra/tktgh/adtaoysdtoaspapgreolxeivmealtwelays j1u4dgg.edOntotbheistbhaesimsa, xthiemum that
the dams could tolerate for the planned exposure period of 10 days.
pIenrEfxlpuecrroiomcetnatnsoa[taenwdeIr,e 5fooufntdhede3a7ddaanmds1gwivaesnsaacmrmifoinceiduimn a th`meodroisbuinndgspteartie,oda,saclombpuatr|eodfttohe0 dofamthset3h7atcsounbtsroelquaennitmlaylsd.ieDduhraidng wcehtropmeoridnaecarlyaorrchaseaanadndwecrherolmeotrhharigniocr.thTewa.o aAlmsoonhagdthe remaining dInamtsh,e c4ondtervoellgorpoeudpa,ltohpeecoinal,yIclhiandiclaulnsgignnoinsoet,eadnwda|shfaodcadliaarlrohpeeac.ia that developed in 1 dam.
FaprpormoxDiamyaste6l-y151/G3,ltehses ttrheaantetdhegrcoonutproiln gErxopuepr,imaenndtdIurgianignetdhe apomsmto-tnrieautmmepnetrpfeluroiroodo(cDtaanyosat1e6--t2r1eGa)te,dtghreobuopdsyigwneiifgihcatntglayin of the ebxocdeyewdeeidgthhtatwoafsthneotctoankterno,ltghreoruepf.oreI,nDEaxypser6i-m1e5nbtoIId,ytwheeiDgahyt g1a6iGns were not calculated.
Ftheeeddocsoinnsgupmeprtiiodo,ntwhaestrmeeaatesdurgerdouopnlcyonfsoruEmxepdesriigmneinfitcaI.ntlDyulreissn.g cfoenetdrotlhavnaltuhee cionntthreolpogsrto-uepx.poFseuerde cpeornisoudm.ption was similar to the
Mtheeadnifmfaetreenrcnealwlaisvenrowt esiatgihsftiocratlhlye stirgneiaftiecdagntr.ouAptwsaascriifniccree,as1eodf,tbhuet EID091562
41
0001 3N
Reference:
Miscellaneous Type: MeSptehcioeds/:strain:
ldsieavvemre.sraglirveednaaremamsoonnituhme vpiesrcfelruaolrsouorcftaacneoaotfetwheasmeodbisaenrvleodbetoohfatvhee
aIensmoEmrxopptneiiorunismm,epnaetnrdf1,leutthoaerlomobacoitdnatyneowanetaiengcahedtmoiwfneiprsretergnanotationancd.yv,eSrtishmeeilliyanrcalfiyfd,eecintnceedobfy `EpxuppevriiambielnittyILo,r0g0raodwvtehrwseasefdfeecmtonosntrraetperdo.ductive performance or on
cTohmepoounnldy-ermebleaytoe-dfewtaals taonxiicnictryefaisneddiinngcniodteeadcethoaftfceotuulsdesbweith soiinsgstnihifefiicccaoatnnittornoosnlilgtyerisofuoapnn.atlhTyehzifesirdsdtibflyfueamrboeannecr-evtiaenirltienedcbitredasetn.vceerItsswuaspsrtehsseteanitnciscetiiwdcaeasal.lcye pofrotbhaebdlaymsa.reTsphoenspeosttopgaernteurmalviizabeidlisttyr,esgsreovwotkherdatbe,yatnhed toxic state daemvmeolnoipmuemntpeorftflhueoroofofcstparnionagtferwoemreadndoittiaofnfaelctdead.ms given
rIenvveiavloedexnaomicnoamtpioounndo-frpeulpast'edeyaelstebraettiwoenseninDathyesp2u7psa.nd 31 PP
Ahamzmarodntioutmhepceornfcleupotruoso.etanoate did not demonstrate a unique
DuPont Co. No. 1-82.
(1982).
Unpublished Data,
Haskell .
Laboratory Report
Metabolism 2FF0ee0mmgaa)ll;eepaarlnebdginnmoaanlrtaetpsrra(it7ms-i/8gCrweaelve:iCkdDasfoledmaalneds w(ewiegihgihinnggaapppprrooxxiimmaatteellyy 2ap0p0rgo)x;imaantdemlayl2e5r0atgs)(waeprperouxsiemda.tTehley rawtesewkesreolhdoaunsdedweciaghgiengand allowed food and water ad libinum.
GlervoeulspsinAfEemarlatesrwatesreastaesftuendcttoiomneaosfuproestb-leoxopdosourrgeantoifmleuofroildleowing oGrarl aodAmui(ni2ps1tfreatmiaolnearnadtts)owiansvedsotsiegadtewimtuhlt2i5plmegv/ekrgsousraslilnyglaenddoses. G3rroautspsweBreansdacCrif(i1c2edfeatma4l,e 4r,at1s,/2g,ro4u,p)8,waenrde 2o4rahlloyurdsosafetderwidtohsing. a2.n5d o2r41h5o0urmsga/fktge,rdroessipencgt.iveGlryo,uapndD3(2r1atsfewmearlee sraactrsi)fwicaesd datos1e,d2, 8,
EID09 563
2
000v 22
GLP: Test Substance: Results:
11
4,
days
14,2,
with
4, 8,
25 mg/kg orally each day and 3
24, and 168 hoursafterthe 11
rats were sacrificed
dose. Group E
at
s(a1c2rimfailceedraatts),wa8,s2d4o,saenddat16285hmogu/rksgafotrearlldyosainndg,3 rats wege
iGnrofeumpaslFeIratrsatfsowlelroewitnegstiendhatloamtieoansuexrpeobsulroeo.d oGrrgoaunopfFlu(o2r4idfeelmeavleels
e3faxtrpsao)tsswuwraees.reexGspraoocsruiepfdsicG(ae0adnsaidtn1g4H,le%(,162-1hf,o2eu,mrp4l,eex8p,roa2st4us,rgaernoodufp1)160w8emhrgoe/umres'xpaaofnstdeerd to
Gaanrsdoinu3gplreIat6(s1-w2heomruaerlesexacrparotissf)uircweeadosafte|x%p,mog2s/,em8d,'taoonrad0s.2i14ngmhlgoe/u6mr-s'h,aofurteresrepeexcxptpoiosvsueurlreye,.of
10 mg/m' exposure.
and
3
rats
were
sacrificed
at
%,
2,
8,
and
24
hours
after
pGrreoguapasntJ-vNerwseursenotnes-tperdegtno acnotmrpaatrs eanbdlotoodcoormgpaanroeflouroarlideexploesvuelrse in
avdemrsiunsisitnehraeldat2i5onmegx/pkogsuorrea.llyGornoguepsJta(t1i2opnrdeagyna1n5t afnedma3lerartastsw)ewraes
(s6acprriefigcneadntatf4e4m, a2l,e8,raatsn)d w2a4shaodumrisnaifstteerrdeodsi2n5g.mgG/rkogourpalKlyon
gestation days 6-11 and 3 rats were sacrificed at and 2 hours
aadftmeirntihsete6r"eddo2s5e.mgG/rkoguopraLll(y12onprgeegsntaantitonfedmaaglse 6r-at1s5) awnads3 ras
Mwer(e6 sparcerginfainctedfaetmaV4l,e2r,at8,s)awnads24exhpoousresdafvtieartahseing1l0e d6o-sheo.urGroup
wienhraelastaicornifeixcpeodsautre taond102mhgo/umrs" aofntegreesxtpaotisounred.ayGr15ouapndN3 rats
(3
10
pregnant female rats) was exposed
mg/m' on gestation days 6-15 and
via inhalation, 6 hours/day,
3 rats were sacrificed at
to
% hour after the 10 exposure.
Blood No
samples
were
obtained
from
each
rat.
`ATmhemuopntiakuemapnedrfcllueoarroaonccteaonofaatem,mpounriituymappperrfolxuiomraotoecltyan1o0at0e%from
tthhee pbeloaokdroefafcehmedal1e-2rahtosufroslplooswti-ntgreasatimnegnlteaonradlwdiotshevwiratsualratpoitdalwith
aclpepaarraennctecbhyan2g4eshoiunrsb.loAoddoorsgea-nroefslpuoonrsiedewlaesvedlesmfoonlsltorwaitnegdmwuiltthipnloe
foroalllodwoisningga.
A slower single oral
clearance dose.
rate
in
male
rats
was
demonstrated
wAitshiinngl1e 6ho-uhroaufrteirnchealsastaitoinoneoxpfoesxuproesurerseu.lteTdheintpeestaskubblsotoadncleevels
EID091564
0002s
Reference: Type:
Species/strain:
Method:
GLP: Test Substance: Results:
nroatpiadflfyecctlebalroeoddflreovemlst.heMballooed,ratasndcltehaerendutmhbeecroomfpeoxupnodsumrueschdid more slowly.
bPlroeogndalnetvealnsdfonlolno-wpirneggneainthterratosraslhoorwiendhasliamtiiloanreoxrpgoasnuorfelsu.oride
`stTrhaeigahmtocuhnationfiasmommeorniincurmeapseersfrleuloartoiovcettaontohaeteonp-ressternatigahsttchheain
aidsmoimneirsstraasttihoen tinicmreeafsoels.lowTihnigsasmumggoensiteudmtpheartftlhueoraooonc-tstarnaoiagthet chain
cihsaoimnerissoamreerc,loerartehdatframoemtathbeolbiltoeodismporreseearta.pidly than the straight
DuPont Co. (1981). No. 593-81.
Unpublished Data, Haskell Laboratory Report
Metabolism
Male
Male
rmaitcse/Crl:CD
s1oClu-tAiomnmwoansiaudmmipneirsftleuroerdoobcytainnctaratgeas(t0r.i5cuiCnitfubmagt)ioans taon8ayquoeuonugs
caodnutlrtomlaglreourapts(2anradts6aanddul2t mmiaclee)mwiacse astacaridfoisceedoaft1204mhgo/ukrgs.anOdne
t1rceoatnetdroglrgoruopu(p3(r3atrsatasnadn2d m2imciec)ew)awsadsossaecdriwfiitchedcahtol9e6sthoyurrasm.inTehe
(sa1c0r0i0fimcegd/katg)9624hohuorusr.sAfaftteerrddoossiinngg,wriatths tahnedtmesitcseuwbsetraencpleazcnedd tihnen
iantd2i4v,id4u8a,l7g2l,asasndme9t6ahbooulsiss.m Fcehcaemsbearnsd.urEixnheawleedre'c*oClwleacstesda.mpAlted
asapcprriofxiciemattiemel,y 18-m2 LmLofobflboloodowdawsasrermeomvoevdedfrformomthtehreatmsi.ceLiavnerds
owxeirdeizreedmoavneddc,ouhnotmeodg.enized, weighed, and 0.5 g samples were
No
AAlmthmooinugihuamppreervfilouuosfosotcutdayno(aDtueP,opnutriRteypaoprptrNoox.im8a2te8l-y11~00de%scribed
lbeetlhoalw)efifnedcitcsaotfedatmhmatocnhioulemspteyrrfalmuionreoorcestiannocaotueldinrtehdiuscsetutdhye,atchuetree
`pwearsflnuoorsoiogcntoafnoeantheavnicaefdeceelsi,miunraintei,onorofex'hCa-leadmamior.niTuhem differences
babestowrepetniotnhoef2thsetudteisetssaurbestmaonscte.likIenlythbeepcraeuvsieouosf dstiufdfye,remncuecshinof the
dchoosleewstaysrapmrionbeabwlayssialdlmiinnitshteergeads.troTihnteesntoinn-alabtsraocrtbwedheanmmonium
preermfolvueodroboecftoarneoaatbesotrhpentiaosnscocoiualtdedocwciutrh, cahnodletshutsyrparmeivneea,tweadsthe.
EID091565
#
[LDERE
Reference:
acute lethal effects of ammonium perfluorooctanoate.
For both followed
rats and by fecal
maincde,extphierperdiamiar.ry
route
of
excretion
was
urinary,
`After 96 hours, fecal elimination was nearly the same for both
asiprectiheasn; thhoewreavt.erM,otshte mnootuasbley,extphiermedoussigeniefxiccraenttelyd mleosrsein"tCheiunrtihnee
gtrheaantethrecorantc.enTthriastidoinffienremnocuesien
urinary Liver.
excretion
was
reflected
as
a
DuPont Co. (1982). No. 405-82.
Unpublished Data,
Haskell Laboratory Report
Pastoor, T. P. etal. (1983). The Toxicologis\t, 3:82.
Type: Species/strain: Method:
GLP:
Metabolism Male and female rats Male and female mice Male and female hamsters Male and female rabbits A male and female of each species receiveda single 10 mg/kg dose `oTfhe""raCt-s,ammimcoen,iaunmdphearmfsltueorrosowcetarneoahtoeusviead iinntdriavgiadsutrailclyinitnugblaatsison. a`mnedtfaebcoelsiswmeuraeitcsolilmemcetdediaatte1l2y, a2f4t,er48d,os7i2n,g.96,Exapnidre1d20COhso,urusrianfet,er sdtoasiinnlge.ssTshteeelmmaelteaabnodlifsemmaclaegersabibmimtsedwiearteeliyndaifvtiedrudaolsliyngh.ousUerdinien aafntderfdeocessinwge.reExcpoilrleecdtCedO;24w,a4s8,no7t2,co9l6l,ec1t2e0d,. 1B44l,ooadndwa1s68drhaouwrns from the rabbits 168 hours after dosing.
Tdohseinragtsa,nmdibcel,ooadnwdahsamdsrtaewrns.weAlrleaanllimsaalcrsiwfiecreed d1i2s0shcocuterdswaiftther kfiodlalcoywsi,ngsptliesesnu,esteesxtceisseodr,owvaeriigehse,db,raainnd, fGr.ozI.ent:rahcte,aratn,dlumnugssc,leli,ver, fskrionz,ena.ndMefattasbaomlpilsems.uniTthsewcearrecawsassehsewderaendthtehne wcaegieghweadshaensd were collected and refrigerated.
rUardiinoea,ctCiOvi;tysaumspilnegsa, lainqduicdasgceinwtailslhaetisonwecoruentaenra.lyBzleododdi,refcetcleys,for
tissues, organs, and homogenized carcass samples were analyzed
lfioqru'idCsccionnttielnlattiboyn tciosusntueorx.idRaatbibointucsairncgaassetsiswsueereoxniodtizaenraalnyzded for
HC
No
content.
EIDO91s66
as
00043
Test Substance: Results: Reference:
SAumbsmtoanntiiaulmsepexrdfilfufoerroeonccteasnoiantrea,tspuarnidtyh7am0s%ters were observed in
ftheemaelxecrreattiaonndofth"e"mCaalcetivhiatmysftoelrleoxwcirnegtaedsionvgelre 9or9a%l doofset.he Tohrieginal
tVhCe faecmtiavlietyhbayms1t2e0r hexocurrestaefdte3r9daosnidng6,0c%onovfetrhseeloryitghienamla"leCrarand
raacbtibviittsy,exrcersepetcetdivtehley,'*bCyac1t2i0vihtyouarssrpaopsitd-ldyoasnindgc.omBpoltehtesleyxeassotfhe
efxecmraelteedraotnalnyd2t1he%omfatlheehaomrsitgeirn.alT'h"eC amcatliveitaynbdyfe1m2a0lehomuircse
mpoaslte-daonsdinfge.maTlheerarbabpiitds)exccornettaoirnse(dfneemgalliegirabtl,emaamloeunhtamssotfe"r*,Canidn
organs and tissues at sacrifice. The slow excretors exhibited the
lheivgehlesstin"t"hCeckoindcneenytsr,atliuonngss,inanthdesbkilno.od and liver with substantial
DuPont Co. No. 62-82.
(1982).
Unpublished Data,
Haskell
Laboratory Report
Type: Species/strain:
PPrleagcennatnatlraTtrsa/sntsrfaienrnot specified
Sex/Number: ~~ Females/6
Method:
`Cc-alrbaobneyllepdosaitmimononaindumhapderafslpueocriofoicctaanctoiavtietywoafs0l.a5beulCeid/mong.thWeater
was used as the dosing vehicle. The pregnant female rats received
asingle 10 mg/kg dose of "C-labeled ammonium
``wpeerrefliunodriovoicdtuaanlolayteplbaycegdavianggelaosns tmheeta1b9o%ldiasym ounfigtessitamtmieodni.atTehleyrats
after dosing.
Tafwtoerrdaotssinwge.reBslaocordifwicaesd datraewanchattismaceriifnitceervaanldofre2f,ri4g,earantded. bTohures
dpliascseeacttaesd,furmobmileiaccahl octohredrs,,aannddwfeeitgusheesd.weTrheethuemnbirleimcoavlecdo,rds and
apnladcefnettausseswewreereinfdriovziednu.alOlyrgpalnacsedanidnttoispsaupeesrwceormebaulsstoieoxncicsoende,s
Uwreiingeheadn,dafnedcaflrsozaemnp.leTsheexccarrectaesdsbesetwweereenadlossoiwnegiagnhdedsaacrnidfifcreozen.
swuecrceescsoilvleelcytewdiatnhddiflruotzeend.eteTrhgeenmte,twaabtoelri,stanndunaictestwoneer.e
washed The washes
were collected and stored.
eTnhteireptlya.cenStaamsp,luemsboiflitchael mcaotrdesr,naalndtifsseuteuss,escawrecrases,oxainddizfeedceisnwteherier calosuontoixnigd.izTehdeaunrdinaenaalnydzecdagfeorw'asCheacstiwveirtey baynalliyqzueidd sdciirnetcitlllyatbiyon liquid scintillation counting.
EIDO091567
PP
009%!
GLP: Test Substance:
Results:
+
Reference:
No
Ammonium perfluorooctanoate, purity approximately 70%
P`wlaascesnhtaolwntrtaonsofcecruorfa"fCte-rlaabdemilneidstarmamtioonniouafm pseirnfgllueoorroaolctdaonsoeaotfe
fCe-tallalbeevleelsdoafmammomnoinuimupmerpfelrufolruooorcotoacntoaantoea.teTahte2caonmdpa4rhiosuornsof
rpellaacteinvtea,toatnhdeoctohnecreontrrgaatnisornesvoebasleerdveevdidinentchee mofatreesmiasltabnlcoeotdo,
pfletaaclenctoanlcetnrtarnastfieroonfstohfeamtemsot ncoimupmoupnedrf.luHoorwooecvtearn,oabtye 4inhcoruerass,edthe
csounbtsrtaasnttitoalloythmeorrteistshuaens aelxlaomtihneerdo,rgaamnmsoannidutmisspueersfleuxoarmoioncetda.noaItae
`inamthmeonfeituumsepsedrifdlunoortodocetcarneoaasteebceotnwceeentnr4a-t8iohnosuwrse.reTshiemipleaarkinfetal
`Simganginfiitcuadnettqouatnhteitlieevselosfoabmsmerovneiduimn tpheersfpllueoerno,ochteaarnto,atleuncgasn,,and fat.
ptlhaecreefnotrael,bbaerrwiaernsoffefrerreindgfmrionmitmhaelprleasciesnttaancteottohetrfaenrsufserw.ith the
DuPont Co. No. 61-82.
(1982).
Unpublished Data,
Haskell Laboratory Report
Type:
Species/strain:
Method:
EPfefrefcltusoorfooDcotwaneoxa"teIoinn
Exchange
Rats
on
the
Toxicity
of
Ammonium
Male rats/Crl:CD
A range-finding study was conducted prior to the tes to find the
tolerated doseof
study, rats were
Ddoosewdefxrom1-2X020--Cl1.00(0chmogl/eksgt,yra1mriantei)d.oseInletvhealt,
and
6 rats dosed at 1000 mg/kg. noted in this study.
No clinical signs of toxicity were
Aadmmminoinsiteurmedpbeyrfilnutorraogoacsttraincoaitnet,ubaastiaosnutsopeynosuinogn aidnucltommaoliel,rwatass. _
Four groups, 6 rats/group, were used dosed with 500 mg/kg of ammonium
in the study. Group perfluorcoctanoate,
[ was Group
II
`was dosed with 500 mg/kgofammonium perfluorooctanoate and
immediately dosed with 1000 mg/kg of Dowex 1-X2-C1, Group
dIosweadswidtohse5d00wimtgh/1k0g0o0fmagm/mkognDiouwmexperf1l-uXor2o-oCc1taannodat2e,hoaunrds later
GroupIV was dosed with 500 mg/kg of ammonium
perfluorooctanoateand 2 hourslaterdosed with 1000 mg/kg of
D14owdeayxrec1o-vXe2r-yC1p.eriAoldl
rats
and
were weighedand
the sacrificed.
observed
over
a
GLP:
No
Test Substance: Ammonium perfluorooctanoate, purity approximately 100%
Results:
RPrees-idnoastin1g00or0 pmogs/tk-gdocshiannggweisththDeotwoxeixcef1f-ecXt2s-oCf1almomnoEnxicuhamnge
a
EID091568
009725
perfluorooctanoate in rats. All rats dosed with the pDeorwtleuxooc1ta-nXo2a-tCel,haeditrheerdubceefdormeorotralaifttieresthceomapmamroedmitoutmhe rats wdoesreed5/w6i,th0/a6,mm1/o6,mainudm0/p6erffolruGoorcotuapnscaIt,eI,alIoInLe,.anMdorItVa,lity ratios respectively.
Reference:
wAafsoplelrowf-ourpmesdtutdoyd(etDeurPmoinnteRwehpeotrhteNroc.ho4l0e5s-t8y2ra~midneescwroibuelddabove)
enhance from the
the elimination body.
of
absorbed
ammonium
perfluorooctanoate
DuPont Co. No. 828-81.
(1981).
Unpublished
Data,
Haskell
Laboratory
Report
Type: Method: GLP: Test Substance: Results: Reference:
Respirator Evaluation
r`TehsepipruatroproscaertwraisdtgeoseavgaaliunastteaMm.mSo.An.iuCommpbeirnfaltuiooronoTctyapneoaGteMAdu-stHfor
breakthrough. The cartridge pairs were tested against an average
gcoennceernattreadtiinon2 odfus0t.5g6enmegra/tmo'r,aamnmdoinnitruomdupceerdfliunotrooaonctaainrobaltoew of
t6e0mpLe/rmainnurmea.inBtoatihneudpsattr5e0a%m arenldatdiovewnhsutmriediatmyaiarnbdoarnmebient room
dcuosntcebnytrfaitltieornpsawpeerrecamsosneittteosrebdacfkoredamupmownitihuamnpiemrpfilnuogreoroscatamnpolaitneg
`tAaliinqutootsabosfotrhbepaoqsuseiobluesaemxtmroacntisoufmthpeerffillutoerropoacptearnaonatde avlaipqourost.s of
the aqueous ammonium
piemrpfilnuogreoroscatamnpolaetse.were
analyzed
colorimetrically
for
No
AfAtmemro4n0ihuomurpserofflucoornotoicntuaonuosateex,popsuurritey,
not no
specified detectable
amount
of
daomwmnosntireuammpoenrftlhueorboroecattahzionagtseidduesotfotrhevacpaorrtrwidagsefpoaiurnsdtested. The
pmeirnfliumoruomocdteatneocattaeb."leBlaimsietdwoansa1.452p0gLoafirasmammoplnei,utmhis would
calculate to be 0.004 mg/m'. The mean upstream airborne
5co4ncheounrtsr,atrieosnpsecwteirveel0y..6T7he0.re3s3ulatnsdde0m.o4n8s+t0r.at1e5dmtgha/tmt'heatM4S0.San.d.
pceormfbliunoartoioocntatnyopaeteGdMusAt-aHndcavratproidrgceosnecfefnetcrtaitvieolnysfialttetrhae mtemsot nium
cDounPdointitoCnso.fo(r19a8m0)i.niUmnupumbofli4s0hehdoDuartsa., Haskell Laboratory Report
No. 664-80.
EID091569
00043
Type: Method:
GLP: Test Substance: Results:
Reference: Type:
Glove Permeation Testing lFiinveed;tylpateesx;ofnagtluorvaelsl(anteexo;prneenoep;renneeo-rsuybnbtehre)tiwcelraeteexvarluubabetre,d ffloorctheir ppeerrfmleuaotriooonctraensciasttaenacendtoaamm3o0n%iauqmuepoeursflsuoolruotoicotnanoofaatme mdorynpiouwmder. `Spaemrpmleaetsioonf ctehlelsglwoivtehswwaetreer tuessetdedasinacdoulpllieccattieoninm1e0dimuLmgolnastshe `inmseiddieusmurwfaasceanoafltyhzeegdlofvoresa.mAmo1n0imumLpaelrifqluuootorfootchteancooaltleecbtying dsepteecrtmrionpehodtwohmeetnryaadfetteercatanb8le-haomuoruenxtpoosfuraem.moBnreiaukmthrough was perfluorooctanoate was found in thecollection medium. The `1mpign/immLuimndettheectcioolnlelcitmiiotnfmoerdaimummo.nium perfluorooctanoate was No Ammonium perfluorooctanoate, purity not specified Results of the evaluation show that 3 of the glove samples (neoprene; neo-synthetic later rubber, floc lined; and natural latex) do have a measurable breakthrough time and permeation rate afier 8 hours of continuous expose to a 30% solutionofammonium perfluorooctanoate. However, the permeation rates are very low indicating that the materials do offer some resistance to the test substance.
Results of the tests performed with ammonium perfluorooctanoate: powder show that in 4 of the samples (acoprene; neo-synthetic latex rubber, floc lined; latex; and neoprene rubber) no abrnedaoktnhlrayougvherwyassmaolblsearmvoeudnatfpteerrmehaotuerds othfecloantteixnsuaomupsleex.posure, DuPont Co. (1981). Unpublished Data, Haskell Laboratory Report No.612:81. Biopersistence Screening Study Summarized in the PFOS section, see DuPont (2000). Haskell Laboratory Report No. 2022.
EIDO91570
-
000435
SUMMARY OF STUDIES CONDUCTED WITH AMMONIUM PERFLUORONONANOATE AT DUPONT
Mammalian Toxicity
Acute Toxicity
Type: - Oral ALD
Species/strain: Male rats/ChR-CD
Value:
187 mg/kg
Method:
The test substance, as a solution in water, was administered by
intragastric intubation to youag adult male rats (1/group) in single
doses. Concentrations tested were 10, 15,2.3,34,5.1,7.7, 12,
17,26, 40, 60, 90, 130, 187, 300, 450, 670, 1000, 1500, and
2250 mg/kg. Survivors were sacrificed 14 days later, and body
weights and liver weights were recorded.
GLP:
No
Test Substance: Ammonium perfluorononanoate, purity not specified
Results:
Morality was observed at concentrations of 187 mg/kg and above.
Deaths occurred within 6 days after dosing. Slight initial weight
losses occurred at 26 and 40 mg/kg. Weight loss occurred for 9,
12,and 15 days at 60, 90, and 130 mg/kg, respectively. No clinical
signs were observed below 26 mg/kg. Clinical signs observed at
26 mg/kg and above included pallor, salivation, polyuria, and
chewingmotions. Additional clinical signs observed at 187 mg/kg
and above included belly-crawling, half-closed eyes,
incoordination, ruffled fur, diarrhea, and emanciation. Increased
liver weights and increased liver/body weight ratios occurred at
3.4 mg/kg and above.
Reference: DuPont Co. (1968). Unpublished Data, Haskell Laboratory Report
No. 129-68.
Type:
Species/strain:
VMaeltuheo:d:
Inhalation ALC
Male rats/Cri:CD(SD)BR
5Ma9l0emrga/tsm*(6/group), 8 weeks old and weighing between 234 and
298 g, were exposed via nose-only inhalationfora single, 4-hour
period to a dust atmosphere of ammonium perfluorononanoate ia
aDiur.stCaotnmcoenstprhaetrieosnswetreestgeednweerraete6d2w0i,t9h10ab,i1n60f0e,eadenrd4re6g0ul0atmegd/wmi't.h a
volumetric feed controller. The bin feeder metered test substance
into a glass transfer tube. Air introduced at the tube swept the test
substance through asize reducing cyclone and into the exposure
chamber. For the lowest exposure conceatration, the atmosphere
was generated by passing pressurizaeird through a glass generator.
A flask at the bottomofthe generator served as a dust reservoir. A
EIDO91571
%
009%:
. ore: Test Substance: Results:
sctyicrlroinngereoldutargiiattoartewdadsusitnsienrttehde agebnoevreattohre.reAsierrvionirt.rodAucmeodtaotrtihzeed
pbaorttticolmeosftinhtoetrheeseerxvpooisruarnedcahtamthbeerc.yclTohneeaetlmutorsipahteorriscwept dust
ticnohtnrecoreuvngathlrsafibtliytoerdnsrs.awwTaihsnegdaectatmleoirsbmrpiahnteeerddicvatoclaoupnpcmerenostoxrifamtacithoeanlmyobf3ep0rarmatitinmcuuotlsaeptheewraes
sdaemtpelrimnign.edCfhraommbtehre tfeilmtpeerrwaetiugrhet, drieflfaetrievnethiaulmibdeiftoyr,eaannddcahftaemrber
woaxtyegrewnecroentaevnatilwaebrlee
measured. ad libitum.
Except during Body weights
exposure, food and and clinical signs
were recorded. Survivors were sacrificed 14 days later.
Tlioverm,on2igtroorutphseeofffe1c0trsaptsf, a8mwmeoeknsiuolmdpaenrdflwueoirgohnionnganboeattweeoennt2he3.7
Tanwdo2g7r7oug,psweorfe1e0xrpatoss,e8d were exposed toaironly.
wtoee6k7saonldd5a9n0d Each control
mwge/img'h,inrges2p3e1ctaivnedly2.67 group was exposed
,
scaocnrciufrirceeaddSlyorwi1t2h doanyesoafftehreetxepstosgruoruepsf.or pFaitvheolraotgsi/cgeroxuapmiwnearteion of
the liver.
Yes
CAhmammobneirutmemppeerrfaltuuorreosnroananngoeadtbee,tpwuerietny293-92%7C, relative
wheumriedi2t1i%e.s ranged from 19-45%, and chamber oxygen contents
MOonreaolfitthyerartaitossionft0h/e6,5940/6,mg6//6m,'andide6d1o6nwtehree 1o2b%sedravyedofinextphoes6u2r0e,. i9m1m0,ed1i6a0t0e,lyanpdos4t6-0e0xpmogs/umr'e.inCclliundiecdalresdigonrsborboswernvfeadcidaulrdiinsgcohrarge (67-1600 mg/m'), test substance on the head (620, 1600, and
4600 mg/m'), labored breathing (4600 mg/m'), profuse clear nasal and oral discharges (4600 mg/m'), and diminished startle response
ce(l4xi6np0ico0aslmegst/idogmn'6s)7.atmgNh/iogmha'edrvtehcrrosonecuegcnhltoirunaitctatilhoenssirgeincnsocvlweuerdryeedpoehbrusinoecdr.hveeCdd opionmsmrtauotrsne, srtuaffilneeddopredriisnceoulmo,repadllfourr,, lreudngornobirsoewonr flaacbioarleddisbcrheaartgheisn,g,weletthoarrgy, limpness, and hair loss.
pRoastts-eexxppoossuerde,tofo6l7lomwge/dmb'ylnosotrm1a-l9%weoifgihntitgiaalinb.odAyt wceoingchenttr1adtaiyons bgroedaytewretihgahnt 617dmagy/pmo's,t-rcaxtspolsoustrea,pparnodxciomnattienluye6d-t1o5l%oosfeiwneiitigahlt either throughout the recovery period or until they died. Most
51 009% EID091s72
s5u4r-v7i1vi%nogfriantistieaxlpboosdeyd twoei5g9h0t, w62h0e,aotrh9e1y0wmegre/ms'acrwiefiigcehded12ondlayys post-exposure or at the endofthe recovery period.
References:
Rweaitgshetxspaonsdedlitvoe6r-7tmo-gb/omdy"wheaidghsitgrnaitfiiocsanotnlytheele5vataenddm1e2a%ndlaiyvesr after exposure. Rats exposed to 590 mg/m' had significantly
eLlievveartweedilgihvtesr-ftoor-tbhoedsyewreaitgshwterraetinoostosnigtnhiefi1ca2ntdlyaydiafffteerreentxpforsoumre, twthheeerseceossnitegrenomilifsincoganlnyttlhiyendc5oenpsrdiesastyseoenfdtreochncaotnvhgeeers1y2,weardneadydmuoeefarnteoclsoivevevereryrw.eeibHgoohdtwysever,
weight loss in rats exposed to 590 mg/m'. Gross pathologic
elixvaemrsinwaittihonproofmriantsenetxlpoobsueldartopa5t9te0rnmsgi/nm4'/5rervaetaslseadcrdiifsiccoeldoroendthe
5 day of recovery, and similar gross liver lesions in 2/5 rats
DsaucProifnitceCdoo.n(1th9e851).2UdnapyubolfirsehceodveDrayt.a, Haskell Laboratory Report No. 293-85.
Kinney, L. A. etal. (1989). Food Chem. Toxicol,, 27:465-468. . Repeat Dose Toxicity
Type:
Species/Strain:
Sex/Number: Exposure: Period: Frequency of TExrpeoasuuernet: Levels: Method: GLP: Test Substance:
Repeated Dose Oral Toxicity Study ~~ MMailcee/aCnrdl:fCeDmal-e1/(SI/CgRro)uBpR
14days
Ad libitum for 14 days.
0M.al1e,3a,n1d0,fe30m,al1e00m,ic3e00(,5-1600w0e,e3k0s0o0l,d)10w,e0r0e0fmegd/dkigets containing
Vaemrmifoincaituiomnopfertfhleuocroonncoennatnroataitoenfoofrth14ectoensstescuubtsitvaendcaeyisa. the
pwreerpearreedcodrideetsd wtherroeupgehrofuotrtmheed.tesBt.odAyftwereisagchrisfiacned, lcilvienricwaelisgihgtnss
wapeprreoprreicaotredesdt.atisBtoicdayl wmeetihgohdtss.anSdaclriivfeircweesiogchctusrrweedreonantaesltyzdeady w6itath
ccoonncceennttrraattiioonnss ooff 1100000anpdpm30a0npdpgmr,eataenrd, oonn tteesstt ddaayy 184atfor the
Nreomaining test groups.
Ammonium perflucrononanoate, purity 99%
EIDO91S73
52
069.0%
Results: *
Reference:
Mortality ratios of 0/5, 0/5, 0/5, 3/5, and 1/S were observed for the `male mice fed 100, 300, 1000, 3000, and 10,000 ppm, respectively. Mfoermtaalleitmyicreatifoesdo1f000/,5,3030/,5,140/050,,53/05,00a,ndan3d/51w0,e0r0e0opbpsmer,ved for the respectively. Mice fed concentrations of 100 ppm or less exhibited slight to severe sporadic weight loss. Mice fed concentrations of 3le0t0haprgpym, alnodwhpiogshteurree,xhainbditleidmpsneevsesr.e weight loss, ruffled fur, Male and female mice fed dietsof 3 ppm or higher had significantly increased mean absolute and mean relative liver weights. The mean relative liver weights of male mice fed the 1 ppm diet were also significantly heavier than the controls. Comparisonsofmean body and liver weights of mice fed diets above 30ppm were got possible because there were no concurrent control groups. DuPont Co. (1985). Unpublished Data, Haskell Laboratory Report No. 401-85.
EID091574
5
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nota|tcihone,ckwehidcthhemeAaCnGsI:H TLV listing for ammonium perfluorooctanoate, and they do indeed give tt an A3 a"CnoinmfailrsmaetdaAnrielmaatilveClayrhciignhogdeosnew,itbhyUfnouktne(osw)nofRealdmeivnainsctreattoioHnu,maatnssit:e(Ts)h,eoafgheisnttoilosgciacrtcypien(so)g,eonribcny `mCeocnhfairnmisamn(isn)ctrheaatsemdaryisnkootfcbaenrceelrevIanntextpoowsoerdkehrumexapnoss.urAev.aiAlvaabilleabelveideepnicdeemdiooelsongioctsstuudigesgdtoheantsottthe e`axgpeonstuirse.li"kely to cause cancer in humans except under uncommon or unlikely routes or levels of
009%
E
3
EIDO76894
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TSou:bjReEcLtLZARSE: Mr GrahamofDry Run e L Torroouind STaElHlcty"ou tIhiaotntIcce eT'idnkthatthatmatihils Lmielzlsadeakete ofSorereEcnomrpClamiscpaeetriroonfs,thSeutTP EClTenvtelriSConEsautitahtaidonssgrewnicena.thLeongWVtilmoecaalgso hat we vould notify het of S--Fereno-tn-::OrBTiuegetisandaaasyld,M3edsuRsneeaiglel1-y3,--(-2s-0a0i0it1o::5S2ernacd.d.ReillyAUSA. duNpont.con] TiSoEihgeGbchet.k:o'FpRa.acseybiMxeH.EaSb:aGcekaRenaraipnhoGf SDteyanRya3nc sors, hank you for following up.
---semnte
gg 2 EIDOg6147 000417
.
June 23,2000
DUr..S.ChEanrvliersonMm.enAtuaelr,PrDoitreeccttioorn Agency OfficeofPollution Prevention and Toxics 4C0h1emMicaStlreCeotntNrWol,DRivoiosmio4n03 Washington, D.C. 20460 Dear Dr. Auer: As you requested in your April 19, 2000 letter and during our subsequent meeting on MPearyflu1,or2o0o0c0t,anaotattaech(eAdPiFsOa,sCumAmSa#ry38o2f5-D2u6P-o1n)t'ass aU.fS.luoursoepsoolfyAmemrmroenacitiuomn aid including sreulmeamsaersyfroofminDduusPtorniatl shiytegiaenndetdhaetafactoelolfecAtPedFaOt oiunrfUl.uSo.rofplouloyrmoeproldiysmpeerrsmiaonnufparcodtuucrtisn,ga Stiotxei,caonldogaysauvamimlaabrlyeoftto hDeuPeomnptlwoyaesesebnltooudnddeartasefpraormaatescioteveirn othneMUa.Sy.26A, s20u0m0m.aryof the Its important toemphasizethe following points:
> DuPont does not manufacture APFO. All APFO used in our processes asa reaction aid is purchased from an outside supplier.
> tMhoesytoarfetshoeldAtPoFoOutsuisdeedciussrteommeorvse.dAfrroelmattihveelfylusomraollpoalmyomuerntproofduAcPtsFObefore (worldwide, in the U.S.) leaves DuPont facilities in fluoropolymer dispersion products.
> Ofthe APFO in the products sold, most (>97%) is destroyed during customer processing to a non-carboxylated hydrofluorocarbon.
> ApoltleonfttiahleaUr.eSc.onDcuePnotnrattoepdeartatoinoenslotchaattiouns;e WAaPsFhiOngwtitohn sWiogrnikfsicianntWeaxsphoisnugrteon. WV. Therefore, most of the industrial hygiene data and blood serum data presented in this document are from that location.
calm
EID070482
Dr. Charles M. Auer, Director U.S. Environmental Protection Agency
Pagei
> Extensive industrial hygiene data collected on workers potentially exposed to APFO show airbomne exposures (0 be significantly below the ACGIH TLV of s0i.g0n1ifmigc/amnt'ly8 shir.ncTeWtAhe.coEnvxeprossiuorne tloevaenlsAofPpFlOanstolwuotrikonerfsrohmav2eddrryoppopwedder
> Aspartof the ongoing surveillanceofworkers potentially exposed to APFO, in March and Aprilofthis yeaar seriesofblood samples were taken from workers in the U.S., The Netherlands and Japan to be analyzed for serum APFO concentration. DuPont has not received the results from our contract laboratory at this time. DuPont will submit a summary of the results when they become available.
The formatofthe information in the attached is a modified UEIP format.If you wish to discuss the information contained in the attachment, please contact Robert F. Pinchot at
(302) 999-4074 or e-mail atRPoibenrctFhot@usa.dupont.coomr me at (302) 366-5259.
Very truly yours,
Gerald L. Kennedy Director, Applied Toxicology
and Health
0007" 56
EIDO070483
Voluntary UEIP, Ammonium Perfluorooctanoste
Voluntary Use and Exposure Information Profile Ammonium Perfluorooctanoate (APFO)
I CHEMICAL IDENTIFICATION
Chemical Name: Ammonium Perfluorooctanoate CAS Number: 3825-26-1
IL COMPANY IDENTIFICATION
Company Name: E. I. du Pont de Nemours and Company
Site Locations:
Site where APFO is usedas a reaction aid:
Washington Works Route 892 Washington, WV 26181
Sites where APFO containing products made at Washington Works are processed:
Parlin Plant Cheesequake Road Parlin, NJ 08859
Spruance Plant 5401 Jefferson Davis Hwy. Richmond, VA 23234
Site which disposes of waste containing APFO:
Chambers Works Ree. 130 Deepwater, NJ 08023
Technical Contact:
Robert F. Pinchot (D3u0P2o)n9t9F9l-u4o0r7o4products Chestnut Run Plaza Bldg. 71172210 Centre Boulevard Wilmington, DE 19805-0711
cours EIDO70484
Voluniary UEIP, Ammonium Peruoroocianoate
[IL DUPONT AND CUSTOMER ACTIVITIES
:
Narrative Description of APFO Use
pTrhoecebslsoecskddiisacgursasemdobneltohwe.back page titled "DuPont US APFO Balance" describes the
DanudPotnettraufsleusorAoPetFhOyleansea (reTaFcEt)iocnoa-ipdoliynmtehres.proTdhuectpiroonceosfspuotliyltiezterdaaftluDourPooentthy'lsene (PTFE) Washington Works for making PTFE and co-polymers consists of polymerizing TFE (and other co-monomersif desired) in an aqueous media with a small amount of APFO to aid in the reaction.
Following the polymerization step, the polymer dispersion is either dried to remove water and APFO or concentrated (removing some of the APFO), stabilized and sold as an aqueous dispersion. The dried polymer contains very lite,ifany, APFO.
`The APFO removed from the polymer is recovered for recycle, captured and destroyed offsite in an incinerator, captured and sent to an offsite industrial landfill, and/or emitted
aif or water at the Washington Works.
`The stabilized polymer dispersions are sold by DuPont to industrial customers (both in the US and outside the US) for avariety of uses, intemally transferred to the DuPont Spruance Plant for the productionofTeflon fibers and PTFE coated synthetic fibers, or internally transferred to the DuPont Parlin Plant for the productionofTeflon Finishes.
A small amountofnon-hazardous waste polymer, water, APFO and other additives `generated at Washington Works is treated in a wastewater treatment facility at DuPont's Chambers Works. This material is either emitted in the Chambers Works water discharge or captured on carbon and landfilled in a secure landfill
The intemal process at the DuPont Spurance Plant to produce Teflon fibers involves, for most of the product, a "sintering" step in which the APFO contained in the product is
destroyed by the following reaction:"
CF(CF2)COONH," > CFy(CF2)sCFaH + CO; +NH;
This reaction goes to completion at 350C and 0.2s residence time. A small amount of product processed at DuPont's Spruance plant does not get sintered and thus contains a small amountofresidual APFO. These products are used for industrial pump, valve and compressor packing materials.
b77y.h1igKhrtuesmep,erD.aCt.ureRogea.s-"pThhaesrema"lFdNeMcoRm.posAitnieown oAfCl8ifclumortaintattehidervsmuaerflagctraanvtismneddicraenlaileydsimsa,teDruiPaolsntstudied Internal Report.
EIDO70485 000s
Voluntary UEP. Ammonium Perfluoroocianoate
The process for making Teflon finishes at the DuPont Parlin Plant involves a blending operation of fluoropolymer dispersions with other additives including solvents. binders. and pigments. The small amount of APFO emissions to water from this facility is due to waste generated during product changeover. Someofthe fluoropolymer dispersion is processed at contract facilities where the material is dried at temperatures >350C thus destroying the APFO according to the reaction above. This dried material is then incorporated into finishes products. The final product produced is then sold to applicators that apply the product to a substrate (such as cookware) via automated spraying or rollercoating. Emissions of APFO from these operations consistofoverspray that is either captured on filters and landfilled or absorbed into water resulting in a water emission. Product that is applied to the substrate is then typically "sintered" at temperatures approaching 800 resulting in the removal of the APFO from the substrate and subsequent destruction according to the reaction above. C`muossttoampeprlsicoaftidoinsspeirnsvioolnveprao"dsuicnttseruisneg"thsetempatwehreiarleftohreaAvPaFriOetyios fdesatprpolyiecda.tioTnsh.erHeoawreevaer, small numberofapplications where the customer heats the dispersion products to temperatures thatallowthe APFO to sublime resulting in air emissions. There are also a small numberofapplications where the customer's product is not heated resulting in the APFO staying with the product. These applications include industrial packings, and industrial filter fabrics.
IV. SITE RELEASE AND TRANSFER INFORMATION FOR TRI CHEMICALS Not applicable- APFO is not listed on the TR V. SITE RELEASE AND TRANSFER INFORMATION FOR NON-TRI CHEMICALS
A. Onsite Ai Releases.
Stimated Tol Annual Releases (165.1999)
[Fugitiv| e Negigble |0 T 0 7]
0
24000 [oT07]
0
J
Comments
Air emissions are estimated using engineering calculations andjudgements and limited measurements of specific point sources conducted in the past.
000755
EIDO70486
Voluntary UEIP, Ammonium Perfluorooetanoste
B. Onsite Water Releases
[ | WashingtoEnstWmoartkesd |T1 oPwarlliAnn|nuaSlpRreulaenacsee|s(IbCsh1a9m9b9e)rs Works |
[Pomt Source 1 55000
9500
Comments Water emissions are estimated using engineering calculations and judgements and limited measurements of specific sources conducted in the past.
oWtahsehrisnigtetso'nemWiosrskisonesmoicscsiuornfsoroc1c0u-r10f0ordaapyps/ryorx.imRaetleelayse3s50ofdaAyPs/FyOr wthoitlheetOhheio
River from the DuPont Washington Probabilistic Dilution Model (PDM
Works Plant Beta Version
were modeled 4.0 Beta June
using the 11, 1999,
US
EExPcAelOsfpfriecaeodsfhePeotllmuotdieoln. PrAevPeFntOiornelaenasdeTdoaxtiacsf)ora1n9d9a6cwoenrsetruuscetdediMn ibcortohsoft
SmIoLdewloiunlgdebxeerecixsceese.'deTdhaeboPuDt M50i%nodfitcahteedttihmaet AduPrFinOg ctohnecyeenatrr.atAiPonFsOof 1.0 ug C-
concentrations of in the river would exceed 0.1 ug APFOL 90% of the time
during the year and 10 ug APFO/L about 2.2%ofthe time during the year.
Average annual APFO concentrations in the Ohio River calculated by using a
Microsoft Excel spreadsheet was 0.423 ig APFO/L. Modeled AFPO
concentrations in the river ranged from a low of0.199 ug APFO/L in March to a
rhiivgehrofflo0w.s9,65rejspgecAtiPvFelOyC.-A8v/eLraingeSeOphtieombReirv,erwhfilcohwscaornrdevsoplonudmetohdaitgahcaanlcdullaotwed
from the US Geological Survey was collected the spreadsheet model. The Belleville Dam is
at on
the the
Belleville Dam Ohio River 13
and used miles
in
dloocwantsiotnredaomwonfsttrheeaWmafsrhoimngtthoenplWaontrkwshePrlaentt.hisThtiysperiovferinffloorwmdaattiaonisisthaevacilloasbeles.t
In 1999 a drinking water sample obtained fom GE plastics, Washington WV, immediately downstream on the Ohio River from DuPont Washington Works showed 0.552ug/l APFO.
LInubaeddciktiPounblsiacmpSlerevsiocbetDaiisnterdicti,n dJaonwunasrtyr2e0a0m0offrWoamshtihrnegetdoinffWeorernktsweolnlsthaetOthheio River, showed 0.8g/l, 0.44ug/l and 0.313 ug/l. APFO.
W R Bert, Modeling releases ofammonium perflurooetanoat ito the Ohio River, DuPont tema! Report EMSE-054.00.
Coan
EIDO70487
Voluntary UEP, Ammonium Perflaoroocianaate
C. On-Site Land Releases
*
CEnhgaimnbeeerrsinWgocraklcsultarteiatosnsAaPnFdOmecaonstuarienmienngtwsasitndeiciant2e wthaastteawpaptreorxitmraetaetlmyen3t0s%ysotefm.
the APFO landfilled
oinntshitee.waTshteesweatlearndtrreealteeadseiss
absorbed on to a are estimated to
carbon media that be 3900lb in 1999.
is
Prior operations have resulted in measurable APFO concentrations in three lsaunrdffaiclelswoapteerramteedasbuyrethmeenWtasshiinn1g9t9o9naWnodr2k0s00inytWdesrtanVgiergfirnoiam.2.A2t3gLe/tlartto' landfill 3th2e40suagm/elwtiimtehapneriaovderaatgLeetoafrt13l9a2ndvfgi/lll.raGnrgoeunfrdowmat6e0r.3muega/s1utroem1e7n4t0s0gt/aklenwidtuhrianng afvreormag0e.0o4f612g5/3L7tuogl3.9gA/tl twhiet"hlaocnaalvlearnadgfiello"ft8h.e83gurg/olu.ndwSaurtfearcceonwcaetnetrrastaimopnlsesraantge tDhrey"Rloucnallalnadnfdiflilllt"herraengaereflriommit0e.d54muega/slutroem8e7ungt/slowfigtrhoaunndawvaetreargeaonfd 1s8u.rf5agc/el. At Water with maximum concentrations in groundwater of 15ug/l and the maximum concentration in the permitted outfall has been 33g
In 1999 a RCRA Facility Investigation was completed for Washington Works and w`garsousnudbwmaittetredcotnoceEnPtrAatRieognisoonfIAIIPiFnOJuanteWa19s9h9i".ngtTohne Wroerpkosr.t contains data on
D. Transfers to Off-site Locations
Washington Works:
EE [WasntdeewragrtoeurnwdeIantjemcetniotn
Hazardous Waste Landfill Other landAll
mated Total Annual Releases or
Transfers (1b. 1999!
|
16000
1
|
13400
1i
2600
0
]
IV. ON-SITE WORKPLACE EXPOSURE
A. Informatioonn the Number of Employees Potentially Exposed
7+ MReapposrotfwathsestuabndmfiitleldoctaotMiaorntsiann.dT.spKeoctifsicch,moRneimteodriianlg lPorcoagtrioanmsMaanndargeesru,ltsEaPeA aRveagiiloabnlellu,pPohnilraedqeuiespthi. # This i the same material that was described above in paragraph | ofsection V.D.
000455 EIDO070488
Voluntary UEP, Ammonium Pefuarosianons
The tables below describe the number of workers that may be exposed to APEO during
their normal work activities for eachof the three sites where APFO is used or APFO
containing product is processed.
Washingion Works
or Imw Hours/Day
1
Too DaTys1/yr030 [5-- 30
vas mT]
22
-- --
BT1]
Routine worker activities that have potential for exposure:
>
>
Handling
Handling
raw
raw
material APFO
dispersions containing
APFO
> Maintenance of polymerization reaction systems
>
>
PPaoclkyomuetrodfrPyeTrFoEpearnadticoon-apnodlymmaeirntdeinspaenrcseion products
> Operation and maintenanceof APFO recovery systems
Coan
EID070489
Voluntary UEP. Ammonium Perfluoroocunoite
Hours/Day
J1 ess
<10
0385-1
1
>8
I
Parlin Plant
.
Days/ye
1710-100
100-250
1>250
{]
1
[7
Routine worker activities that have potential for exposure:
> >
OHpaenrdaltiinognofanPdTmFaEinatnednaCnoc-epoofblylmeenrdidnisgpefracsiilointiepsroducts
> Packoutoffinished product
NwohteerethtahteaAtPnoFOticmoeuilsdtsheubmlaitmeer.iaTlhhearnedfloerde tathetrheeiPsarliltilnePploatnetntaitalanfoerleevxaptoesdurteemtpoerature ahiarnbdolrinnegoAfPFthOe patolthyimsefracdiilistpye.rsAiloln emxatpeorsiuarlespaoltleonftiwahliicshthcroonutagihns<ki1n%coAnPtaFcOt dwuirtihngmost containing <0.25% APFO.
Spruance Plant,
Hours/Day
Daysiyr
10-100
[100T5-252 0 50|
pr ms --T |
1
rr
1 0 |
[ET 1 eT
rr 7]
Routine worker activities that have potential for exposure:
> Handlingof PTFE and Co-polymer dispersion products > Operation and maintenance of fiber coating facilities > Operation and maintenance of sintering rolls > Packagingofnon-sintered product.
Note that the PTFE and co-polymer dispersion products used at the Spruance site contain <0.9% APFO with most containing approximately 0.3% APFO.
B. Information on the Exposure Levels of Washington Works Employees
Since mostofthe processing done in the US with APFO and APFO containing ihnytgeiremneedidaatteasias ncdonpcreondturcattsedisadtotnhaetastitWe.asThhiengltiomnitWedormkesa,suDruePmoenntt'ssoafiafibrobmoerniendAusPtrFiOal cmounccehntlroawteironlsevaetlsth(emoostthleyr sniotne-sdwehteecrteabAlPe)FlOevceolnstoafinAiPngFOp.rodTuhcetsdaartea uinsetdhehatavbeleshboelwonw
oY EY
EID070490
Voluntary UEIP, Ammonium Pecfluoroecianosie
arrefeleactcommobniintaotriionng odfonceheomviecralthoepelarsattoryaenardsmaatiWnatsenhainncgetownorWkoerrksp.ersTohnealssaammpplleesr.esults
Year | Sample | 7ol Minimam Maximum | Mean| Sundar
| Type | Samples Concentration | Concentration | (mpb)| Deviation |
(mpb')
(mpb)
|
1999 | Partial
100
0ST |
(Shmioftst[ y [ 85 T | 000 1 [|20 0s78 0 TTo0m0a3s5]]7 0031745||
199] 6-8
0069 |
1995 |hows) [7327 | ND | 016 J0067] 0.063
tPhaarttihalasshbieftenaiprrseatrmepalteesd awriethtaskoedniautmthheydrraotexiodfe'2e0t0hymlLe/nmeignlyucsoilnigmeathTaennaalx. cTohlleecAtPioFnOtuibse ddeersiovrabteidzifnrgormeatgheentt,ubceosnvuesritnignmgetthheaAnoPlFicOhtyodirtos gmeenthcyhlloersitdeer,. wAhfitcehr awlosroksuepr,vetsheasmeathyl eTshteemiestqhuyalnteisftieerodfuspienrgflauograosdcehcraonmoaitcoagcriadpihs euqsueidpapsedanwiitnhtearnnalelsetcatnrdoanrdc,apatnudreatdelteeascttor tPhrreeceisciaolnibirsaetsitonimsaatmepdlteosbaere+/p-re1p0ar%edreltaoticvoev.er the concentration rangeofinterest.
"oTnhleydaatvaearbyofveew sshaompwlaevsearbagoevse ctohnesiTsLtVe.ntlyWhbeerleowretshueltAsGaCreHaIboTvLeVoorfne0a.r01tomgth/em'TLwVi,ththe eenvgeinntieeriinnvgecsotnitgraotlesd)atnodrecdourrceecttihveeeaxcptoiosnur(eadldeivteilosnails upnedresrotnaaklepnr.otOelctdievredeaqtuaifprmoemntthoer f1r9o8m 0rescehiovwinhgitghheerAlPeFveOlsaosfaexppoowsduerre.toIrnetcheeivcianrglyit 129s9a0'nsaWqausehoiusngstooluntiWoonr. kTshsiwsicthcahnegde swhaosulddonbee tnoorteeddutcheatthine tphoete1nt9i9a7l tfiormeexppeorisoudr,etdhuersiintge hwaansdlsitanrgtoifngthuep ndreywpAowPdFerO.reIctovery ffaacciilliittiieess.mOapyerhaatviengcoanntdrimbauitendtetnoatnhceehdiigfhfeicrullteiveeslsasosfoAciPaFteOd winitthhethpeersstoanrat-lupsoafmpthleesse: during that year.
Tnoatskinsdpieccaitfiivce moofneimtporlionygedeatexapaonsdurweiapendmaorneitnoortipnrgedsaetnateedxihsetr.e.HoTwheevseersathmepsleesdaatraeatraeken 10 identify areas where additional exposure controls may be necessary.
Engineering controls to reduce exposure consist ofthe following:
>
Reaction systems are closed systems with continuous ambient monitoring for monomer concentrations
> >
VTehnetiploaltiyomnersydsrtyeemrss oapreeriantsetaulnldederwhneegraetaiivfebporrensescuornetceontcroanttiaoinnsAaPreFsOigannifdicant
> oRtehceorvmeartyersiyaslst.ems are in place to reduce airborne emissions.
Tempe molespe illon, 056mpb is equivalent tothe ACGIH TLV of 001mg'
OBES
EID070491
Voluntary UEIP. Ammonium Perfluorooctanoste
Personal protective equipment that workers regularly wear consist of the following:
>> SIamfpeetryvisohuosesglaonvdessiwdeh-esnhihealdndslaifnegtyAgPlaFsOsessoilnutaillonasreoars.aqueous dispersion
> pCrhoedmuictcsa.l protective coveralls and goggles or face shields when the possibility
>
oAfirslpilnaesrheesspoifratAoPrsFoOr
containing solutions carridge respirators
is present. where monitoring
has
shown
to
have high exposure potential.
APrtioWrasmheiansgutreomneWnotrskosf,bbllooooddfsleuroruimdelelveevleslsofhaAvPeFbOeehnatvaekbeenepnrimoeratsou1r9e8d1sibnuctear1e98o1f.
limited value in assessing exposure to APFO. identified APFO exposure potential the 1995,
A summary of resultsof employees 1989-90, 1985,and 1984 volunteer
with
dsuarmipnlgintghiesvpeenrtisodios finttihmee,taabnlaelybseilsoowf. tDreunedstoofsidgantiafaircaentdijfofbicaulsts.igTnhmeendtatmaoivnetmheenttable:
cboemlpoawrpirsioonrsotof1r9e9la5tairvee floevreelmspolfoAyePeFsOinicnlbuldoeoddinsetrheum19c9a5n sbaemcpolmipnagrdeadt.a sTohetheanttire data.
set of blood concentrations is available upon request.
Year
Minimum Concentration|_ Maximum
Mean
[oes 7
ol
[oss 23 [oa
[ross| or | eee
(ose| 0[oor
(ppm)
as Rs
eT
Ta
(ppm)
LST | An aa
58 |
7* TThhiissiinnddiivviidduuaallcwoanssiswtoernktilynghaisn hajdobthtehhaighhaesstA: PblFoOodecxopnocseunrteraptoitoenntoifaAlPatFtOhe tsiincmeofAtPFeOsasmpepclief.ic semapmlpolyeese'wserleotaakdens.erTuhmisleevmepllwoyaese l44epman. APFO exposure potential assignment n 1991. In 1995 tis
06075 EIDO70492
|
8/15/00 LPSD Water Sample Analytical Rests (Letter, R. L. Ritchey to Mr. James C. Cox, LPSD dated 10/4/00)
BCC: A.V. Malinowski, Legal, D7078 M. A. Bradley, Spilman, Thomas, &Battle P. J. Bossert /H. D. Ramsey/D. D. Jackson 1.1. Zanikos/A. S. Hartten RF. Pinchot R. Banerjee/R. J. Zipfel
dow /2:817.2
ECEIVE
oct 13 200
Caan
EID090036
sv See wn
October 4, 2000
Mr. Jamas C. Cox
PL.u0b.ecBkoxPu7b0li0c Service District
`Washington, WV 26181
RE: LPSD Water Sample Analytical Results
Dear Mr. Cox:
Attached are copies of the analytical results for water samples taken
oon August 15, 2000 from three LPSD wells and the LPSD Building 1 main water line.
If you have any questions or need additional information, please contact
me at 304-863-4271
Sincerely,
R. L. Ritchey Sr. Environmental Control Consultant Washington Works
RLR/gw:dsw
Attachments cc: William J. Gibbs
Lubeck Public Service District P.O. Box 700 `Washington, WV 26181
EID090037
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Faget Account. umber: 07032 rSRoi6um-ti5ee.sy7.H4biu1iraonFti4a8scee, Neimeo.urs25& Co Wilmington D2 E 1980
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EFFECTIRVEEVIPDSAITAOEN.3GNowoFi:E1se32 EeEXmPARATTOIONNADTATEE:asavriur
TEFLON NON-SALABLE PROCESS WASTE DISPOSAL.
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e Federal Register Vol. 65. No. 202 Wedney sday.T Octobb er 18. 2000 Prpopoorseesd Ruullees 5S2231
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TABLE 1.--ENTITIES POTENTIALLY AFFECTED BY THe SNUR REQUREMENTS
- Coors WaGieom Garcesclean secesoes
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TABLE 2.--CHEMICALS REQUIRG A SGNIFICANT NEW USE NOTICE ON OR AFTER JANUARY 1, 2001
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TABLE 2.--CHEMCALS RECURIG A SIGNFICANT NEw USE NOTICE On 0% AFTER January 1, 2001--Contnued
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Federal Register Vol 63 No 202 Wednesday Ociobor 18. 2000 Proposed Rules 62323
TreLE 3 --CHEMICASLcSaSuUPBiIaEnCtT NTe0wVOULsUeMENOCTIpCEROENSTROIRCTAIFOTNESROJNANOURARAYFT1.ER20J0A3NUACRoYnt1.in2u0e0d1 a0 REGURNG A
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5olHeucSurlaied hers. somewhere i he DhWihliocgihirceaiapartoscbedsrseeesgsk.aadTotwrnoenmbyoprcrshodeFumcRitcOaSflAoomr otIfMh.ethEeSnuMplaofomrnmcaet1hnet,d.2P0e0S0go,lurowcohecsehDaipmsacppeaerrlssiboyinn.
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inTthheemnoulmebcer aorficsarfboonmaettooms10prxes=ent gesutiamlatioofndmtodeplus tis alitmoitheed rby the aAsgseenssemyeactasn.onWliythsptheelsprieeseonnt data. the
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Su(altFcana(siYi=dhOanHsdd)e.ssmhe1otra=dlosXcailvtssatu(ilYvoen=sa)Om'TihdMee+,)s. Cspaomrmppleoiunsngordeefscneoinnrctfltiyeshdsinspdcooicvtneurhoeerdhoetnhelen.ting per1s01iesatlent EaenEdfectmay bioaccumulate.
pliosl"tTyehmdeecrcshleamsicoaflchseumbistcaanlcseusbasltsaonciensclude bSlioorcudatsthiaocPnaescoisifshicCtha[nRaUdlnai,1t1.eSdTwhSetedaetwenisdaaennddt1h8e SPlRToOhmSoeniAigso5ernricenyvg'isedwahaoizfa(hrRedaelatn1ha.lbyTasoixrsiacfooralaodgy
includingth perfuoroslil slfonyl diibution of he chemicals in high Studies show hat PFOS fa well absorbed
0001 dx
52526 Federal Register ol 65. No. 202/Wednesdas October 18. 2000 Proposed Russ
ry deeispm he Short wl ge 30%iosonpn.PL oowmnni pmori Trnee
formed 15 2 metabolite of other
Eiot withdiayne ale bith, AS3 biosccumulatuve potential snd the |
oE S peprfelruiortionbaeteBfdurrsetuE hlefronmaetAetsa.boalItiS nzdeeode.suaraotped Frr{oepeedsoEonusfeltrsghtreouoppEsuy,pSsomnolrcytaatlahietbsmytaaiwaootanhlerorwt,ewsot. tpE irheeporocohdeeue mscitciaavle aanrnadiscesnsubcScsohnuerc2doen0rhinpecsoectoohfxporeirlcreiytnydof :J
ES EE R e ean eEn oReta Soinoe]nOAdBEoe)tadndbTSloreFenOiALTs,r oa 3 tnotmaosnaoaus82 rode
{dapproTximateElyLoaumTso)aaAmSnumssTaedooAoamnth),e ESEpouhvpisesirweopsrnecT0aao1soemcpgb/ododbyanywdaaoondkg0phomsac!al [of aa5nipi e sriankd1wiUiplid he1ie.igPciEhOeSehsla
eae ASSESS SSoyv:epamenc actomndtoe sShoewnaos oSfhwerdisSeueest,a ipxpooarvs tSotons dcehnemn
Parmates wars ote.
potential for davelopmental
PEGS hat been 1a commercial use since
IATL A erE rJT PFOS bas shown moderate acute F`EneturootpoxmiceitnyafollleofwciI ntgsewxpaoT srueresto tnbpheie1ee9a50'pts,ioprecndoaomadinnoaanptglsey idanasooiloannd
BEEniibemalis6nhamegoathrsebe BSamoe udaovgedaoshhpehmaabotSSaTyvoehoew,rle. SeFaapnospeoamede)aeeedianosnnagdoef croeat
eisduaca e asmce taooieh atnds bheabvoeen SdomesesoafSeudtoysPHeOSanGdo,iln?g FCSaoobliunamnnfoPsEtOcTopoeonvdonineotndshpcdeet
bnoUeialionaeOpEsmpeasBrednAopbeesoonrodCOoARiEBAeS!| SvB SepAeealenAmaebd tasalosnartedbsmoesnrSoeysafdv fSSLoohbdueBenoe1dAipABeOsSntuntpeeenoysrtsomPEorOSp.oeeatl
CoBoymaaobithrvO ed a 3 R ko. tatttoed Gheoaperle sowpoehtTonEoeTdoAndotvebse SSSiocomneikseTx nheomle70sswehbicpisomeomadla
B Dlorrsp.ecsoenrovthuiyiopnse e.maonoditdseaetnh TwfEoheaehcWsse.R CSboooapvesn.TtAdIisRyoeCrAnsSoidrfdSudcHmiyvncshyur ma ahi.dHiSpr nhcdiluudpeinndgLhDAipaoarnyaLavakie ofooelm tihe
eCoeO oSr hiardedsisAmosweesentmsao?yr SaaStboriveoesdnaoeohnendwFaOeStmerge.d tn oceommsnitnotEEoEpOledetooemnsaouTPtHOeaSt.bn
neo sgenmi gEsvvepn anotnoroPh prmoshreuoioduna.sd ebheonfSniNeoeSmtn oaeolldhneesnuem(epplueesSooSPfpRapOiSouanstr1. faeCeblrseitiietnpeinSetFdsoOnoSpreaeieneds
[E PEE r ss Stecga pore. be ona ond ent, et FFGk Coe
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hoWeetiksaeLiltyoodtanCryeahltomdeidnetornastmdpsmosioensonnat,se"low0735+ IEbaalnIeikbsoStanenLddemEcedonRmesmeProrcoOiaSnloBsaodkuorecresehSau0v%eg pDapriooetdrsuicimtmsaln.nwchcSctihphcahetsrcsaoineebnfa(decnivfidS3we1dgoTnotoeo
"Haetusoltiezeastailoinvaabatnid:oenh.ejnpaabtoorrceeeedlddli`ubtlraoerarthsin0g. i SfroomE saaivnasemeh.tL yaIonnfdosniftese1,aFciERroesnsftoUhnspiatceasd DvvaooprlrliuaiomcunseieostanuforPsfpaEceOoeSetortpermaohtdameuecngnttiaoatnmneudenBEdepid roe ns
dE ienavioepb lumoepnmni eednssfeivccassendwwearraeedsfdaoeponrn"eed dthsSBekpEolptouopmestaocfesFhedRviORee.omMboebeecspepheotpfnaaemlebnsle,ess. eoPtFOwOinSRdecSshgpecemiaidpntoomppernneedosudntsPlEfoOorSicreir
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nFneesnrertoionn m tspriawg 1 pauhps) he"Altfoulghthee PseOnSorlavPelsodetpecteaad 6in AUpEhBoLlsCtMeroyi.s4adtwcaarpret.rTehness
eaIvern
Federal Register/Vol 65. No. 202 Wednesday October 18. 2000. Proposed Rules 62927
ldushtrimaillssotonvgserbyncnusetorm.ersSsauschhe1s3
O out produE cers. and carom lsae ate
ipoEzaaiptnsgealargsesntwwsah1dorumnaednesuJrfiotaaocmkteeuenrRnemoatimnbaagls.pyebry
aoq fpprAoNxiYm.a1te0lya 210.10300millolwoinnpgounds (Ref
niSeoddmlaionabtaihfeet.eirunmptaherorkleistotrewrbesy.sttcmhaeeropgteetnoefraaanpldparel cdahnodemmpieacspalepcfrodotodhudict(siReoufnsev4c1a.ot1e2glo2ro0yu0f0ismFhOeeSS coomrersimaelnevteheanpncrouohnsceienigbnsSh=,aatiwsoouuld
Su1bai2c0o00.prtohfeesdsoiomneasltiScppplriocdiuocrtsio(Rnef.
<simated tbs appro mates 3.7 milionpounds (Ref 6).
ail Fr wuts Lridiant products tn 1s semen. 3
vSiegorloSufOPmUFOeTSiHch0emi0ca0ls for his(uRseef COprROBSoAcfhseCpmhiececaglisaeidwnetdhUuescpkearilfno,armiandcse cpSrooomdmluictettierodn'tobyT"hsuoebsotasandtioealflcy ephnatsesoeutse
FrOScchheemmiiccaallssprporodduuccededCfXorPpUapRer Scoommnerncieala.pplacndaioCnosnsiumnecrhsapphlriscations. cproomveisdpeodndaesncchendwuilhs dtohecuAgmemnciyn.s31Ms
B FeErsootE aornd.ssSeppuaetncao inssespdpfvsliipcoipsienassealand msRueactfabalucnapnlatftsoia.nmagsc,aindmdimneiisltoegcstuaapnnpdirceosrslsiacwnhetilsnlgor rmCeaolnmauptfleaedctctehueprmeliaocffaoslpefdcoiirsficmcoonPtsFinOsuuSirnfaagncadel
hinnioCnoprlatee s ooo d contcionma Ophyoetogarapihinc Ailm.udesaturTeoocrlepaonleirss,hes. (ientcluumdainngn{5d08paCpoenrtapcrtosteecstiroenguulsated
End Ddrug wArdampism)iseugautliuoined(FbDYAt]heunFdoeord cthoummipnagosad.dicthiveemsi.caclaripaettosrpmootdiclneeasn.ers. dbyishcoonFtiDuAi)nbgytlhlemaenufnoafc2e0du0r0,fo3rasday
ZCoanCtcaPikRneaErps7p5lci1ac7sa0bt,oi2no0insewssefloflod5rimnangsocanan-rdtooonds,|
sapnurnsoddu(4Rc3et4fim.on4r)mva1sacoh2c0li00do,euftaPhmeFbdOeuoStmescsthatetmiiicocn|aslosr
sucsheesdbulye,tahaadneIonfs3a0n0t3ic(iRpafa.te5)d. This productionvolumes. are summariziedn
asking papers) The spphicationof lor this ae category s esumated tobe Table'.
TABLE 5.--ANTICIPATED ANNUAL U.S. PRODUCTION VOLUME (POUNDS) FOR PFOS USE CATEGORIES
Gre cares
20
2000
ES
wa
EaSSraiarararcmeapnavcocsarrmoanartmes
m2pame0)
o:Torso
TYoSar
i5o
fo
sa
191%
"8%
5
cuAmceoctolrydianvgaitolbtlhee tionfEoPrAm,atMionis the SflesctmeadgubfyachtiusrepsroopfoPsRedOSSNchUeRmi(cRaelfs 1. 3`TaMsupailaacnis2buotrofedoClifostctaoeen3tci.hneu(mei1tcghaoelassrield.attfhioesed sPe0op5ce0iraapaerodtteowcidttiihsoncsouwnrtoaicaeueesetshtehtecawheatmdiaocfanl|ds SdeenanrialedboisnsTaabslseac3ionfedUnwiitthLA (is
Berraromanrceachemical plsiocpatlicoanso]nbbyy
VP.rOobpjoescetdivReuslaend Rationaleforthis
aIn mdetaercminringiwnhatewoBunclhdecmonisctaitlute
substancesthatare the subjects of this
stsshlseeosvciuaibaetrdainncfeoswirh .mlaitpkoietoelnnytoeinaxlpthouessuetrsoexsicity of
{sionufrocremsa.tiaonnd prothve ifdoeurdbfayctionrsdulsitsrteyd in TSuCsAedsecotniohneSss42co)ns1id2edraUtniiotnsL.8.EPA. wObajnetcstitvoesacwhiitehveretghardfotlolhoweinsgignificant Rew ses hat areCosignated in his
phraotposed rule. EPA wants 0 easure elxlitmafnruofmatchteurmearokfeth,oEsePAchboemliiceavless that
per1s.onE'sPAiwnoteunltdtoremcaemiuvfancottuicceeoofraimyport lciokneclyerwnieldctahaste.maHmouwfeavcetru,seEcPoAul1d2 be
B3RgOniSficchuentmiScealws0forbaedfeosrigtnhaatteSdVity iOnpiPtOiRaAtYeiYd10thsevarluuaet,e aanaddcwoanntotls.h1e
beg5insE.PA would have an opportunity to raview and avaluate dats submited 12a
hthot apcye. pThoe nnotsiceohatc would d be _foquirod by the SNUR would provide
SbeNgUiaNs bmeafnourfeacthteurnionigcoersiumbmpiotRtienrg th+e EacPuAviwtitehs atshseocOipaptoerdtuwniittyhatosiegvnailfuicaatnet
SuSEbgjReIcfntcacahitameidcwalbuseseua.bbslteantcoersefguol3rae naunpespweowrusstoeuns4ai5bylpetroosppkorsos.teedfctahaeagr.iensFsotamad4a
pmrposoprecatsivoefmtahnufsuabcjteucrtecrhseamaidcal Soxnpotsirs to the substances which could
socicubras.sceproavifderd ssuchfregutlatioonwis| se IMGiavreencuhrartenntglycompapnroiduceinsg tthbe an
r JAnEECT 0 TER secon ci hemicalselieedsc an Tabele 3or f Unit sLaAd
as concernsregarding the
tory smvronment associated wi
BCnlhotaucmsci,ccpthrsaolipbobsaedagSpeoNstUehnRtaitaIliMo.sfttihhneeclsouldsed tlnhaiwkGemolasyntutsfhaeacvtocucortmiepnadgncwiaiepsahcwisoteuylafdolriihnencsugre
MTiaintuefdacSttautrese,ofnasecsheoscehn avomluiatcaiarnilltyhseto discontinue their manufacture and sale
CEhpPeuAmrsiwucaianlltsu[0isnetha(eafnorvrtemaoadtatotiroeoynrsUupribdmsaittmeiaeRrdukleet
omarnsauulbfsatucatsnutoriaeblylfoyDrretechdieurcmembhoe3esr1i.wi30d0e3s.prnedad 4p[8r0otdhCueFcvRtpeionantrvto7hl1au0t1mhetesoprhofaacstkehe-hsoeeucthoefmihceasles
use byDacomba3r1. 2000. Wh nfs checaicalsdoesno progress as
[LL
02028 Federal Register/Vol. 65. No_ 202 Wadoesdsy, October 18. 3000, 2roposed Salas
odESeiyscprbpiruboerdpursiseGhSiuHnLdooprmro)TpoSTsCeAdAEcsAinoarcCPiscAi4.on shphsoatwsoeuc-saosuetodfowfBnahssossaemnyoCwhaAamRnieceldss Bfsoiunsmaiotan aftohrleslsoccwninihstemsptvossuiublirsanhecipecr aodce
pVe 1 Aloraatives
SCEeiodnarsrdmhipiisdiodocyioSanhcsaodnpurse RLmoiupoerninycSiaimdyise.amdmdueto viisnpmyooraseas
roy propBosSsUiRaEgA prope
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STCoaSSnH EmoiomcafUauclnahioniv1ct8t4.es CUstovvmoniecdgaiTldTSaMpaCabAecalsiroaSccsrito2n
anhinarsrohlf.ahLef vfprsopbGooosgalfdeaatceotrofPtdUheaSLSEoUAfEtRhO.eR oftheproposed SwNareU considRered.
oEmerusmhnaet,donavaoncsanoevrirhoelmamsaunatdlgFotearnd pti content (log Pr. log of ton
3{i0on)wphloerh.teEyfPolrAamtaceotduilo1d9nSrtoeHhnwAAaBnGVyRpEYose b31oo0cnHcuthlemirf,oeraaEebPaeAtrtbthsoanncusaebws4, 0wSoNrUuoRlnd Kaaoci)s:gebiinsoecnnonocsedbnsoteiirnopgniPiocmor,nr(VhABcpCeeRnF.t 10g
E ai{dpooSiroo tftehGdyaistnuo[tbisAsanaTprociorsptoshteedesdgGia1fmrcTaoa1nbt3tlseee2sw
cphorluolpdbosodecadufngtsaAthielnStN5UdaRtwbhyeusLs1i5ua0ftoBanbtoe Daur omoly"
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oScaeeilrvslbuypsionrestseaas:.mbnpefcofaruomsamnttiThoSonsCehAoAsrmcmhson eSLxcottwovnia1ieosnBsdo.oetnfego,arntepnoo4gdr5usgoAinaGdwRhaIoCaAbaByoaao SwiNEtUhPNthoeonArcgoyvuaracogyfebsheypfeoPrrsRoOFnSsubtboircEaoSncsguelts
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h{SaiRrrlboTerSmiCioen SSdhoeuLdcnoenoABgStt)GoUucRlyCIbfAeoLrtooeivsee Caonqndamredetoohraveiaetathcrifisna.l SNR. smiuoabmlvissebreoTndoonvtooegpesadelanecctcimoonrudofitsnegstoto ltho
SCEhPioAc'anadinnhteocChbeiwmeoicucilavdesausbostmanceesa VseIcLoATner,otcpDogeeierzasensodanOstthathae0r eunbqdaruoismdeTno . dSFot30aE mnaydiraaeo4srDtCdriPnsRyEpaArsRt7nr9d2i?nFagiltuhraetto
unlSidesetgerdue3TSwTCaaAdbleesrseTc2St3CinoAd8nsSeCocPfAoUnNmuL6sLftA|h.ere dsreavueeblodip dmoan3iylySipNA0nUriNSgc,uubaRasatttoees.4dp4arstbo5enashrasreee sr42su4sbopnmuaibbtslydas htealathmamaphslfebiicchaiueeionintso1oaffotcosse
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mGpaiortsersaseloon"ifpbrnesceihnnatksmoiofcrmlwiarllbtsparteonscoennutomre4aa h3e5aH0lo4twh)e:vaen4rd0.eCinaFvivRrio7en2w1moef2n9t)hael apoktseapioasled wsSoomduclisdpqravreresodnttmooerncteollupdEoronemiateshosenstaiabgtblmRyecant
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F5iinapgpareboaapebonlstyedsncoStiNonUneRucnwdieelrsaTlaSoChwAioscntcmieo.n CCinuhtremanadlemyd ssbugebnessvthaecnsacnettsawtwhtwhenuksuensoeEdwPnAo.rora CpSuoobsmseptdaargbecyedshtedosakedcsnhieopmroimscaeatdlibosyunbposotnsaanscikebsse |
Ageaty 10 addres he potoail rks essondble asconaiaable results of he subsite.
069d
|
FederalRegister Vol 65. No_ 202 Wednesday. October 19. 2000 Proposed Rules 52320
SE EconAomieCorse tens ecoyns S rHnIsTpSrS ocecopa peTde tmilbeansapasy aselm mned
Hsbimobilsteio2snaopfdSoTaNbtla O3stofhNeaUansitpsdoLrAe
mmcene], woul o ceauired forthe fst export to.
$333 for she est rn Ltan exporter
SE Serena aren information les maintained in the
abined as dascibed imCon183
srecitioonni12(bb).sanndd thed. vdelvpemleonptsooff S TTytan den Ppe omtaacesSulfhoenaEtend ver
UFsnoluefsscal tihaotncroEa emqpuiaArneymednetesc.idaethsoetsnoencpouern,ssue oJmuu"brimEeyq1bu+Noe4aTtT9SGCexAS4p0oCsret0nsIismSo1aiftIice9aotih)an A|L 3Mo. StFhrr Pyauil MN.e oMTr ahc0eh s1,Se20r0v 0.o,
aEesvuss
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TABLE 1, --CHEMICALS HEQUIRING A SGNFICANT NEW USE NOTICE ON OR AFTER JANUARY 1, 2001--Continued
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(i)Any manufacture or import for [38485 1. 00142dbefor A3uAry1. (7 Oo. 00-2671 Filed 10-17-00.0454
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(028 On VUALI bEIEC ML 00/60/10
Public Service District
--_-- es M. Cox, Manager
Jarses M, Gx, Mariage
TeFlaecpehmolnee ((330044)) 886633-33739411 Dear Lubeck PSD Customers
P.0. Box 700, Washington, West Virginia 26181-0700
October 31, 2000
CouMiSSIONERS:
JamesE. Smith, Chairman
LDoavsi"d0D%. SJtoehenlsea,nS,ecTrreetaasruyrer
In compliancewiththe Safe Drinking Water Act Amendments and the West Virginia Bureau for
Public Health, Lubeck Public Service District (LPSD) must provide our customers with an annual water quality report, which was done in an advertisement in The Parkersburg News and The Parkersburg. Sentinel on July 1, 2000.
In order to insure that tap water is safe to drink, the U. S. Environmental Protection Agency (EPA)
prescribes regulations which limit the amount of certain contaminants in water provided by public water
systems The presenceof those contaminants
LPSD routinely monitors your drinking water
does not necessarily
according to Federal
indicate that water poses a health
and State laws. The July 1, 2000
risk.
advertisement provided the results of monitoring for regulated contaminants.
`manufacturer, the 3M Company. An unregulated chemical for which LPSD has monitoring data is ammonium perfluorooctanoate
(also knownasPFOA, APFO, FC-143, and C-8), which is used at DuPont Washington Works. Amention has recently been focused on PFOA because it is one of several products being phased out by its
have bePenFOexApoisseadpetrosiit.steDnutPcohnetmirceaplortthsatthiastsilt ohwastotobxeiceolliomgiincaatleadnfdreopmitdheemibollooogdicsatlrdeaatmaotfopseuoppploerwtho confidence that exposure guidelines established by DuPont are protective of human health.
Although PFOA is unregulatedfor
regulatory agency), the DuPont Company
drinking water
has established
purposes (that is, it has
its own drinking water
no limit established by
guideline of | part per
a
dbirlilnikoni.ngTwhaeteDruaPoWnatsChoinmgptaonnyWhoarskasdv(i0.s2edptahrtesDipsetrrbiicltlitohna,tolropwpbc,onacsenotfrAautigoinssth2a0v0e0)beaenndfionutnhde iLnPSD
wells (0.2, 0.5, and 0.1 ppb, also asof August 2000). These levels are below the DuPont. guideline and
DuPont hasadvised the District that it is confident these levels are safe.
LPSD is committed to providing safe water to our customers. If you have any questions, you can
reach the District at 863-3341 or Dawn Jackson at DuPont at 863-2513.
cerely, m. Ga
JameasgeMr. Cox.
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SbMinadgr-Hoorscghos(01145.6190.807-354 o(SCo01io1m-ne35n.:0a V44eA5.sr0a6na3-847) oGleinnnnaDisayki-AnDuTp$eo1nT4t.Y(6350625.13506).5207)
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SsTC N YftG ucteSnt ADDLe .meeDIE STT .----
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TOX FILE
CLI 0304
'
Covance Laboratories MadisonW,I
009.2% MAY 19 1999
Receiv#e1d5
WLS I OE NEDA CU cE uC .
wow nw
May 19, 1999
To: APFO Sub-committee: APME From: Paul H. Lieder
Anached is the preliminary analytical results for the animals at the end of the
dosing phase of the study. One animal in the low dose group died during the
dosing phaseofthe study as did one high dose animal.
In summary, the low dose and mid dose animals had similar serum and liver values. Three high dose animals became very sick during dosing and
consequently dosing was terminated mid-study. The serum and liver PFOA levels from these animals appear to be much lower than the high dose animals still receiving compound, indicating a relatively (vs. humans) short half-life(?)
The resultsofthe histopathology and hormone analysis will be sent by Peter "Thomford shortly.
Regards,
PHL
ee.
CLI 0305
Caan ey Se NAL CU GE UC
won
.
6 Month Capsule Toxicity Study wit APFO in Cynomolgus Monkeys
Sera and Liver Analysis at Study Termination Preliminary Results: 18/5/99
Part 1: Serum Analysis
Control Group
0mg/kg/da
.D. Conc (ug/ml)
nous
5709 0.393 5714 0.229 5715 0.099 5718 0.215 5719 0.322 5725 0.142
Average=0.233
Low Dose
3me/ke/da
Conc (ug/ml)
5702 49.7 5706 66.9 5716 45.7 5721 41.7 5723 62.2
Average=54.5
Mid-high Dose
1Lm0De./kCeo/ndea(ug/ml)
55770078 3837..30
5709 49.4 5712 104 5717 81.0 5718 67.6
Average= 70.5
cones
CLI 0306
:
MAY. 19. 1999 8:44AM MEULLAL 2U Ce Ue
MwOYILL fd
High Dose 2010 30 mg/kg/da On dosing (receiving compound at end of 6 months) LD. Conc (ug/ml)
5703 60.8
5713 192 Average= 125 High Dose--Moribund-sacrificed mid-stady LD. Conc (ug/ml) 5724 403 High Dose-Recovery-removed from dosing mid-study due to toxicity 1D. Conc (ug/ml)
5703 7.76
5711 0.909 5722 6.90 Average=5.19
Part 2: Liver Analysis Control Group
LD. CoOnmcg/(kugg/gd)a 5709 <MDL 5714 <MDL 5715 0.0474 5725 <MDL Average=0.0474
Low Dose 0 mg/ke/da
1D. Conc (ug/g)
5702 5.77
eet CLI 0307
ual inv Dea EVLA CCU CB UC
[RITE
5706 6.81 5716 4.12 5723 6.80 Average=5.88
Mid-high Dose 0 me/kg/da
1D. Conc (ug/ml) 5707 8.7 5708 3.61 5709 5.64 5719 5.50 Average=536 High Dose 30--20mg/kg/da On Compound--receiving compound at endofstudy LD. Conc (ug/ml) 5704 8.03 A57v1e3ra2g8e3=172 High Dose-Recovery-removed from dosing mid-study due to toxicity LD. Conc (ug/ml) 5703 1.05 5711 0.0278 5722 1218 Average=0.766 5724 30.3 Moribund-sacrificed mid-study
eu CLI 0308
126
000735
John L. Butenhof, al.
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mTitle: ToxicitMyoonfkAemysmmafotneriTuwmenPteyr-fSliuxorWoeoectkasnooaftOer(alAPDFoOs)inign Cynomolgus
Authors in sequence to be determined
c:
DRAFT July 28,2000
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Abstract: `The purposeofthis study was to identify the earliest clinically measurable biological response from repeated daily exposure to ammonium perfluorooctancate (APFO) and to comelate this response to serum concentrations for purposesof isk assessment and medical monitoringofexposed populations. Groupsofmale Cypomolgus monkeys received daily doses of 0 (six per sex), 3 (four per sex), 10 (six per sex), or 30/20 (six per sex) mg/kg/day ammonium perfluorooctanoate for 26 weeks by gelatin capsule via gastric intubation. The high-dose group received 30 mg/kg for 11 days, afer which dosing was discontinued for ten days (through study dosing day 21) due to signsoffew feces, low food consumption and weight loss. Beginning on study dosing day 22, the high-dose group was given 20 mg/kg and remained on this dose through termination of the dosing phase with the exceptionofthree animals for which dosing was discontinued between days 43 and 81 due to emaciated appearance, weight loss, few or no feces and low or no food consumption. Two males in the control and mid-dose (10 mg/kg) group `were followed for ninety days after cessationofdosing and observed for reversibility, persistence,or delayed occurrence of toxic effects. One high-dose male was sacrificed in `moribund condition on day 29 ater exhibiting hypoactivity, body cold to the touch, few feces, lowor no food consumption and weight loss. One low-dose male was sacrificed in `moribund condition on day 137afterexhibiting limited use and paralysisofthe hind limbs, ataxic and hypoactive behavior, few feces and no food consumption. There were no effects on estrone, estradiol, estriol, testosterone, cholecystokinin, thyroid stimulating hormone, or thyroxin. Triiodothyronine tremded dow in three high-dose monkeys who were taken off compound for the remainder of the study. T3 values for these monkeys trended up after cessationofdosing... Atall dose groups, significant increases in mean absolute liver weight and mean liver-to-body weight percentages were observed. The. liver weight increase in the low dose animals occurred at a mean serum concentration of approximately 50 ppm. Mean liver-to-brain weight ratios were increased in the mid-dose group. Organ weight and body weight effects were not evidenta the end of the recovery period. No test material related macroscopic or microscopic changes were observed in any organs, including liver, adrenal, spleen, pancreas and testis. The liver weight increase at the low dose occurred at serum concentrations which overlap those which have been observed in some workers with high exposure; therfore, the liver enlargement was considered a significant effect and the low dose of3 mg/kg/day is characterized as the lowest observed effect level (LOEL).
< Z
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John L. Butenhoff, etal.
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INTRODUCTION
Ammonium perfluorooctanate (C,F,COONH,; C.A.S. Registry number 3825-26-1; `ammonium perfluorocaprylate, ammonium pentadecafluorooctancate; FLUORAD TM Brand FC-143 Fluorochemical Surfactant; C-8; APFO'; PFOA'; Mol. Wat. 431.1 g) is used as a surfactant in the aqueous polymerization of fluorinated monomers such as tetrafluoroethylene. `The assumed presence of PFOA in general population blood and in exposed worker blood, coupled with the observed persistence in workers, has led to extensive research into the potential health riskofexposure to APFO (Guy, 1972; Venkateswarlu, 1975; Guy and Taves, 1976; Guy et al, 1976; Belisle and Hagen, 1978; Belisle and Hagen, 1980; Singer, 1979; Paez, 1980; Ubel, 1980; Belisle, 1981; Yamamoto, 1989)
APFO has been produced since the early 1950's. Medical monitoring of employees involved in PFOA production began in 1976, by measuring serum levels of organic fluorine (OF) and performing medical assessments. Serum PFOA levels in production `workers have been measured ashighas 114 ppm. Eighty percentofthe workers had serum PFOA levels less than 10 ppm. Average serum concentrations have been approximately 2 ppm and individual values have range from 0 to 114 ppm.
Past studies have demonstrated that the primary target organ for APFO-induced toxicity is the liver (refs). The hepatotoxicity manifests as increased liver weights, hepatocellular hypertrophy, liver degeneration, increases in liver enzymes, necrosisofthe liver, and proliferationofendoplasmic reticulum, microsomes, and peroxisomes (rats and mice only) yet does not result in hypolipidemia (Pastoert a, 1987). Manyofthese effects `were demonstrated to be reversible when animals were provided with a recovery period.
APFO has been demonstrated to be aperoxisome proliferator in the rat. APFO exposure in the rat was found to be associated with tumors in the liver, Leydig cell, and pancreatic acinar cell. Peroxisome proliferation is associated with: increases in number and volume of peroxisomes; an increase in DNA synthesis and liver growth; and liver, Leydig cell, and pancreatic acinar cell tumors. Several known peroxisome proliferators (clofibrate, HCFC-123, methylclofenapate, and Wyeth-14,643) are reported to induce this triad of tumors in rats. The phenomenonofperoxisome proliferation is not uniform across all
species. While rats and
cats, dogs and primates
(miincceluadriengpamratnic)u,laarrley
psreendsiotmiivneatnotltyhisnopnh-reensopmoensniovne,.
guinea
pigs.
i
As noted above, chronic dietary studies in rats have produced hepatocellular adenoma, * : pancreatic acinar cell adenoma and Leydig cell adenomas (refs). The mechanisms of tumor formation have been studied. Hepatocellular tumors in the rat may arise from the proliferationofperoxisomes (refs). In investigating the role of increased cholecystokinin (CCK) or CCK, receptor binding as possible mechanism for pancreatic tumors, APFO
DRAFT July 28, 2000
EID101455
Page 3
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John L. Butenhof. tal.
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failed to bind directly to the CCK, receptor and it failed to inhibit trypsin, 2 common mechanism for increasing plasma CCK levels (ref). Jn vivo studies with Wyeth-14, 643, model peroxisome proliferator, suggest that these peroxisome proliferators produce `pancreatic tumors by cholestasis, which may be responsible for the decrease in bile acid output which contributes to the increase in plasma CCK levels (Obourn et al, 1997). Therefore, the pancreatic tumors produced by APFO may be secondary to hepatic cholestasis. The Leydig-cell tumors appear to arise from an inductionof aromatase with a consequent increased conversion of testoterone to estradiol an
As
iheotweohsotrtmaorutasltitybsotlutdyv:onf.wdoarndkieerpsdensogeaIgeadiniAPGAglroogdluiogtrioosnftotuend ao
asi
eea: Sli
; Hepatic toxicity and hypolipidemia have not been associated with the PFOA
levels measured in APFO production workers (Gilliland and Mandel, 1993; Gilliland,
1992; Gilliland and Mandel, Am J Ind Med 129:560-568; Olsen et al, 2000). Based on
toxicological findings that suggested PFOA may increase estradiol du to an induction of
hepatic aromatase activity, Gilliland examined and found a positive association between
serum total organic fluorine levels, used as an approximate measurement for PFOA, and
estradiol (Gilliland, 1992). Gilliland and Mandel also observed thatserumtotal organic
fluorine negatively modulated the effect alcohol has on high-density lipoprotein (HDL)
levels and exacerbated theeffectthat obesity has on hepatic enzyme tests among these
workers (Gilliland and Mandel, AmslndMed129:560:568). However,ananalysis of
two subsequent medical surveillance examinations on this APFO production workforce,
which specifically assayed for PFOA, did not confirm these associations (Olsen etal,
1998 and Olsen et al, 2000). Neither didOlsenct l find an association between plasma
cholecystokinin and measured serum PFOA levels (Olsen et al, 2000).
The occupational exposure limit in current use is the American Conference of Gmogv/emr'n,maenatnal8-Inhdouus,trtiialmeH-ywgeiiegnhitsetds (avAeCrGaIgeH)wiTthhreasnhootladtiLoinmfiotrVsaklinueex(pToLsuVre)aondfa0n.01A3 designation for animal carcinogen with questionable relevance to humans (13, 45
The purposeofthis study was to assess the effect ofAPEO on critical enzyme levels,
hormones, and other selected biochemical parameters when administered daily by oral
pcearpssiuslteentcoe,cyonrodmeollagyueds omcocnukrereynscefoofrtaot xlieacstef2f6ecwtesefkosr a13ndwetoekasssaefstserretvheers2ib6i-lwiteye,k
treatment period
L
:
MATERIALS AND METHODS EIDI01456
5
Aobntiamianlesd farnodmhCuosvbaanndcrey.ResYeoaurncgh ParduoldtucttosadInucl.t(mDaelneveCry,nPoAm)olognuAsumgounskte2y5s, w1e99r8e, and
DRAFT July 28, 2000
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John L. Butea, al.
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weighed 3.2 to 4.5 Kg at initiationoftreatment. Animals were acclimated for 35 days before initiation of treatment. Each animal was assigned a permanent number upon asrursipvaelndaendd sitdaeinntliefsise-dstweietlhcaacgoesl.laTrhteaga. nTihmaelarnoimoamlswawsereenvhioruosnemdenitnadlilvyidcuoanltlryolilned to `maintain 18 to 29C, a relative humidity of 30 to 70%, and a 12+hr light/dark cycle. Certified primate diet, (#8726C,Harlan Teklad) was provided once or twice daily along `wwaittehrfrwueirtseoarnaadldyizteidonfaolr ssupepcpilfeimcemntisc.roWoartgearniwsamssapnrodvciodnetdaamidnlainbtist.um.DuSraimnpgltehseo:fsttuhdey, severalanimalsexperiencing low food consumption inthe high-dosegroupwereoffered supplements to rehydrate and stimulate food consumption. Adnesiimganlesdwteoraechaisesviegnbeoddtyowteriegahtmtebnatlgarnocuepwsituhsiinngeaacchotmrpeuattemreinztegdrboluopc.king procedure
M3a3t2e)riwaalss,obdtoasienepdrefpraormat3ioMn(aSnaidnttrPeaautlmeMnNt.; Apumrmitoyn0i0u)m.peGrefllatuionrocoacpastunloeaste(T(oArPpaFcO,,Ilnoct., uFasierdfifeolrd,dNoJs,e aSdimzienNisot.ra2t,iLoon.t NCoo.nt1r2o2l9a3n2i)mcaolnstraeicneiinvgetdheemapptpryogperliaattiendcoaspesuolfesA.PCFaOpswuelrees were prepared at least weekly. Individual daily doses were calculated based on the most recently recorded body weights. The dose preparations were stored at room temperature. Since the APFO wasaddeddirectly to capsules as supplied without the useof avehicle, no dose analysis was performed. Dose levels were 0 (control group, n = 6), 3 mg/kg (low-dose group, n = 4), 10 mg/kg (mid-dose group, n = 6) or 30reducedto 20 (30/20) mg/kg (high-dose group, n = 6). The c(a1p8s3udleasysw)eerxecaedpmtiansisntoetreeddboerlaolwl.y oOnncee afedmaayl,esienvetnhedlaoyws-pdeorsewegerko,upfonreaetdleedastto2b6eweeks irneiptliaalceddosfeoronnond-atyre1a7.tmHenitg-hr-edloasteedainsismuaels.s wTehreerienpiltiaacteemdeonnt 3a0nimmga/lk(g1;0h5o72w1e)verre,cediuveedtohis t2o0ximcgi/tky,g.dosAilnsgowdause dtiostcooxnitciitnyu,eddofsreoamddmainyis1t2ratthiroonugwha2s1alasnoddriseccoonmtmineunecdedforonthdraeye h2i2gha-t dinosbeotahnitmhaelcsonotnroelitahnedr dmaiyd-4d3os(e10g5r71o1u)p,s dwaeyre66de(s1i0g5n7a2t2e)doars draeyco8v1er(y10g5r7o03u)p.aTniwmoalasnainmadls were observed for reversibility, persistence, or delayed occurrence of toxic effects for 13 weeks after the 26-weck treatment period.
DRAFT July 28, 2000
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John L. Butenhoetfa,l.
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Observations. The animals were observed twice daily for general health, behavior and qualitative food consumption. Ophthalmic examinations were conducted on each animal before treatment and on weeks 27 and 40 (recovery animals). Body weights were rfoercodrodseedcwaelceukllaytiboen,foorne tinhietifairtsitondoafyotfretartemaetnmte,nto,natnhde dwaeyekbleyfotrheerienaifttieart.ion of treatment Dfaestteerdmainniamtailosno1f8,b8l,oaonddh4ordmaoynsepsr.iBotlorooinditwiaatsiocnololfecttreedatfmreontmatnhed foenmodraaylsv3e5i,no66f,n9o4n-and 183oftreatment. Blood collection from recovery animals occurred on days 220, 248 and 276 after initiationoftreatment prior to collection. Blood samples were split into serum and plasma samples for further analysis for various hormones. Plasma samples were analyzed for cholecystokininandtestosterone (with the exception of recovery animals in which case serum samples were used for testosterone). Serum was analyzed for estradiol, estrone, estriol, thyroid stimulating hormone, total and free triiodothyronine, total and free thyroxin.
Clinicalpathology observations. A clinical laboratory evaluation was conducted before initiationoftreatment, on days 31, 63, 91 and 182oftreatment and during recovery on sdaamypsl2e1s7,we2r4e5,coalnldec2t7e5d affrtoemr ianniitmiaatlisonthoaftdhoasdinbge.enAtfaesatcehd osvaemrpnliignhtg.tUimrei,neblwoaosd caonldleucrtiende overnight on wet ice before blood sampling; water was provided ad libitum. Blood was collected from the femoral vein. Sodium citrate was used as the anticoagulant for cAonatgiucloaatgiuolnanttesstsw,earnednpoottuassesdifuomrtEhDeTcAlinwiacsaltchheeamnitsitcroyagtuesltanstamupsleed cfoolrlhecetmiaont.oloBglyootdests. was collected from animals with unscheduled sacrifices. Otherwise, animals with scheduled collections were bled in random order. `The following hematological parameters were measured or calculated: erythrocyte (RBC) count, leukocytes (WBC) and platelets (PLAT); hemoglobin concentration (Hb) and h(eMmCatHo)cr;itm(eHaent)c;omrpeuasncucloarrpuhsecmuolgalrovboilnucmoenc(eMnCtrVa)t;iomnea(nMCcHoCrp)u;scudlifafrerheenmtioaglloblboiond cell count of segmented neutrophils (N-SEG), lymphocytes (), eosinophils () basophils (; and blood cell morphology and reticulocyte count. BdeltoeordmicenleldcoounntasA,bhbeomtotgCleolbli-nDyconn3ce5n0t0r0athieomnahteomlaotgoycraintalMyzCeVr.,DMifCfHer,enMtiCalHcYe,ll wceorunets were determined on an Abbott Cell-Dyn 3500 and reticulocyte counts were obtained using a Miller Disk microscopy technique. Bone marrow smears were prepared at euthanization
EIDI01458
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John L. Butenhof, etal.
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Coagulation parameters measured were prothrombin time, activated partial thromboplastin time, and fibrinogen.
Clinical chemistry measurements were made for glucose,urea nitrogen, creatinine, total protein, albumin, globulin, total bilirubin, cholesterol, triglycerides, aspartate aminotransferase, alanine aminotransferase, alkaline phosphatase, gamma glutamyl transferase, sorbitol dehydrogenase, creatine kinase, calcium, inorganic phosphorus, Sodium, potassium, chloride, bile acids, amylase, lipase, and pancreatic-specific amylase. Clinical chemical analytes were measuredon aHitachi Model 704 Chemistry Analyzer. Serum globulin concentration was calculated from the total protein and albumin concentrations. Urine was analyzed for volume (approximately 16 hours ovemight), specific gravity, pH, protein, glucose, ketones, bilirubin, blood, urobilinogen, microscopic examination of sediment, and general appearance. Determination of serum and liver PFOA content. Approximately 2 ml of whole blood (for serum) were collected from the femoral veinof non-fasted animals during week 2 and every two weeks thereafter. A sectionofliverwascollected at sacrifice from each animal, weighed, flash frozen in liquid nitrogen, and stored at 60to~80 degrees C until shipped on dry ice to 3M for analysis. Sera and liver samples were anlalyzed for PFOA content by 3M methodology (refs). Concurrent with blood collections for PFOA determination, at least 2 ml of urine was collected on wet ice and at least 5 goffeces (overnight) were collected from each animal. Results of urine and fecal analysis will be discussed in a future paper.
Anatomic pathology. After 26 weeksoftreatment, four animals in the control, low and. `mid-dose groups, and the five surviving animals in the high-dose group were fasted overnight, anesthetized with ketamine and xylazine, weighed, exsanguinated, necropsied. Similarily the two animals in the control and mid-dose recovery groups were sacrified 13 weeks following the last dose. Necropsies were also performed on the low-dose and high-dose animals that had unscheduled sacrifices on treatment days 137 and 29. respectively. The adrenals, brain, epididymides, kidneys, liver, pancreas, testes and thyroids with parathyroid were collected and weighed. Organto body weight and organ to brain weight ratios were calculated. The following tissues were collected for microscopic evaluation: adrenal; aorta; brain; cecum; colon; duodenum; epididymus; esophagus; eyes; femur; gall bladder; heart; ileum; jejunum; kidney; lesions; lung; mammary gland; mesenteric lymph node; pancreas; pituitary; prostate; rectum; salivary gland (mandibular); sciatic nerve: seminal
DRAFT July 28.2000
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vesicles; skeletal muscle (thigh); skin; spinal cord; spleen; sternum with bone marrow; stomach; testes; and thyroid; trachea; and, urinary bladder. Tissues were embedded in paraffin, stained with hematoxylin and eosin and examined by light microscopy. Palmitoyl CoA oxidase determinations. `Samples of the right lateral lobe of the livers from each animal at scheduled and unscheduled sacrifices were flash-frozen in liquid nitrogen at necropsy and analyzed for palmitoyl CoA oxidase activity (need Cliff's method here). Cellproliferation determinations. Representative samples of the left lateral lobeofthe liver, left and right testes and `pancreaswerecollected from each animal. Afterfixation (formalin or zinc formalin), samples were embedded in paraffin,and sections stained with hemotoxylaindn eosin were prepared. Previously described methods were used tostaintissues for PCNA (Eldridge er al, 1993). Bileacid determination. Bile (up to 5 ml) was collected at sacrifice of each animal, flash frozen in liquid nitrogen and analyzed for specific bile acids (insert Cliff's methods) Statistics. Levene's test (Levene, 1960) was used for variance homogeneity. In the case of heterogeneity of variance atp 0.05, transformations were used to stabilize the variance. One-way analysisofvariance (ANOVA, Winer 19712) was used to analyze initial body weights, body weight changes, continuous clinical pathology values, and organ weight data. ANOVA was done on the homogeneous or transformed data. Ifthe ANOVAwas significant, Dunnett t-test (Dunnett, 1964) was used for control versus treated group comparisons One-way analysisofvariance (ANCOVA, Winer, 1971b) was used to analyze body weights, with initial body weights as the covariate. Although Levene's test for variance homogeneity was done, no transformations were used because covariance adjustment removed extraneous heterogeneity. Ifthe ANCOVA was significant, covariate-adjusted `means were used for control versus treated group comparisons. Dosed groups were compared to the controls at the 5% two-tailed probability level. Blood hormone levels were compared by ANCOVA with significance at the p=0.05 level For CCK, all data were analyzed using Jonckheere's test for trend (p < 0.05).
RESULTS Clinical observations. During the first week of dosing, all animals in the 30 mg/kg dose: group had qualitatively low food consumption and and lost from 3.1 to 7.5 percent of
DRAFT July 26.2000 EICDI010014E60
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John L. Butenhoff etal.
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body weight. Fourofthe six animals also had few or no feces. Dosing was suspended on Day 12 and recommenced at 20 mg/kg/day on day 22.
Only two animals were continuously treatedatthe 20 mg/kg/day dose for the remainder ofthe dosing period. Dosingoftheother three high-dose animals was discontinued on Days 43, 66 and 81. These animals exhibited low or no food consumption, few or no feces, and dramatic body-weight losses prior to being suspended from dosing. Bodyweight losses were 17.5, 23.1 and 18.7 percent prior to suspensionof dosing on days 43, 66 and 81, respectively. The remaining high-dose animal was sacrified in moribund condition on day 29.Thisanimal had lost 12.5 percentofbody weight, was hypoactive, cold to the touch, exhibited low or no food consumption, andfewor no feces.
There was a lackof opthalmic effects in all animals.
Overall, body-weight losses in the 30/20 mg/kg dose group were significantly lower than controls (14.3 percentoverthe 27 week period). Dosing at 30 mg/kg during the first two d`waeyek2s2,cawuesiegdhtcolnosssidwearsabsliegnwiefiigchanttlcosos.mpaArfteedrtcoocmomnternoclisndgurtihneg2w0emegk/sk7g,/d9aaynddo2s4in(gTaobnle 1.
Clinical signs and body-weights were normal in monkeys receiving 10 mg/kg and all but omnreoimbounnkdecyonrdeicteiiovninogn3dmagy/1k3g7e.. IHnotwheisveorn,e oanniemlalo,w-pdaorsaleyasinsiomfatlhweashisnadcrliifmibcsedainnd ataxia occurred as well as few feces and low or no food consumption and loss of 9.5 percent of body weight in the week prior to sacrifice.
`Blood homone determinations. No effects on estrone, estradiol, estriol or testosterone were noted. Mean group estradiol values in all groups including the controls tended to be considerably lower dutring the treatment period than the corresponding pretreament values. In the high-dose animals these values appeared to be lower than the other groups. N`Toheseisgtnriafdiicoalntvaclhuaensgeisn tihnetreestcoosvteerryonaenivmaalluesstwenedreedsteoenbedusriimniglatrhteottrheeatpmreendtospeerviaoldu.esI.n the last recovery sampling, mean values (9 and 15 ng/ml) tended to be higher than means during the rest of the study (1-8 ng/ml).
Taken collectively, values for the thyroid hormones in APFO-treated monkeys appeared
0endboefutnhafefescttueddy. reWmiatihnetdotraellaatnidveflryeecoTn3s,tamnet;analvtahlouuegsh,frmoomnkteesytsdaiyn--the thhirgohu-gdhosteo gthreoup
eprxehtiebsittdedaygsen-e8raalnldy ~l1o8wewregrreocuopnmsiedaenravballyuehs.ighIetrsthhoaunldthboesepodiunrtiendgotuhtetrheasttovfatluhees sotnudy.
;
Group
period,
mean total T3 values are shown in Figure 1, page
the three high-dose animals that were eventually
56). During the treatment
takenoffcompound for to
xic
it
y
:
tteennddeedd ttoo ihnacvreeadseecrteoawsairndg pTr3e-vsatluudeysvparliuoerstaoftreermcoevsaslatfiroonmotfrteraetamtemnetn.t.ThFeisgeurveaslu2e(spage
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57) and 3 (page 60) represent the individual trends in Total T3 for the control and highdose groups, respectively.
No statistically significant or biologically significant alterations in plasma CCK.
.
concentrations were observed.
Clinicalpathology. Administration of APFO at 3 or 10 mg/kg produced no apparent effects on measured clinical parameters including hematology, coagulation, clinical chemistry, and urinanalysis. The 3 mg/kg dose group animal that was sacrifeed in `moribund condition on day 137 showed marked hyperfibrogenemia, moderate: Iymphopenia, moderate hypoalbuminemia and mild hypocholesterolemia.
Findings inthe 30/20 mg/kg dose group were complicated by the unscheduled sacrifice of one animal on day 29 and the cessation of treatment for three others by day 80. Only two animals remained on treatment during clinical pathology tesing intervals on days 91 and 182. In this group, mild increases in triglycerides and mild to marked decreases in absolute neutrophil count, total protein concentration, and albumin concentration occurred. The differences in triglycerides were statistically significant on days 31 and 91, The other differences were not statistically significant but were consistent over time. Absolute neutrophile count and albumin concentration were mildly decreased prior to cessation of treatment for the three animals for which treatment was stopped early. One `monkey at this dose had moderate increases in serum activitiesofaspartate `aminotransferase, alanine aminotransferase and creatine kinase when dosing was stopped `on day 66 and moderate increases in serum bile acids on day 63. The high-dose dose group animal which was sacrificed in moribund condition on day 29 had numerous nonspecific clinical pathology findings commonly observed in animals that are very ill along with marked serum activitiesof aspartate aminotransferase , alanine aminotransferase, sorbitol dehydrogenase and creatine kinase as well as unusually low cholesterol (14 mg/dL)
Eleven days prior to initiationoftreatment (day ~1 1), the animal in the low-dose group `which was sacrificed in moribund condition had a high hematocrit (49.7%) and albumin concentration (5.6 g/dL), possibly indicativeofmild dehydration, and it had the lowest neutrophil count (1,600/L)ofall animals.
PFOA levels in Serum andLiver.
g
Steady-state values for PFOA in the serum were attained within 4 to 6 weeksof dosing.
z
In the 3 mg/kg group, this value was approximately 110ppm and in the 10 mg/kg group
it was 100ppm. Although difficult to determine becauseofdiscontinuous treatment, peak
g
values were highly variable and averages of around 150 to 1000ppm were seen in
animals receiving 30/20 mg/kg. It is apparent that the relationship between APFO
administered and APFO in the serum is not linear (Table X)
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Amounts of APFO in monkey liver averaged 14 10 16 ppm in the 2 lower dose groups (Table Y).In the higher group the values for the 2 monkeys which continued through the entice treatment period were 17and 87 ppm. In animals from this group that were rmiedm-odvoesdefrreocmovdeorsyinmgo,nklievyesr ,coAncPeFntOractoinocnenotfraftrioomns0.i2n ttohe1.li5vpepr mwewnetrefroobtmaianmede.anInotfhe142 ppm to 0.1 and 0.3 ppm respectively.
Preliminary data from urine analysis for PFOA suggests that most PFOA is excreted in theurine. Thiswilbepresentedin afuturemanuscript.
Palmitoyl Cod determinations. Theewereincreasesover coinnpetlmirtoyolGolA. oxidase activity.
Cellproliferation results. There were no significant differences in cell proliferation observed in liver, pancreas or testes as measured by PCNA.
Anatomic Pathology. Increases occurred in mean absolute liver weights and mean liverto-body weight percentagesinall dose groups at terminal sacrifice after 26 weeks of dosing (Table Z). Liver weight increases showed a positive dose-response tread. The silmoiw-ldaorasendansdigmniidf-icdaonstelyaenliemvaaltsedgroovuepr mcoenatnroalbvsaolluuetse.aTnhderetlwatoivheiglhiv-edrowseeainghitmsalwsetrheat wwehriechtrweearteedsuingtniilfitchaenetlnydoefltevhaeteddoosvienrg tpheeroitohdehratdreaabtsmoelnuttegaronudprselaantdivceonltirvoelr.weights
Nthoe AtePrFmOi-nraellsaatceridfimcaec.roTshicsopiincclourdemsickreoyscoorpgiacnschsaunchgaesswtehreeliovbesre,ravderdenianl,asnpyleoerng,ans at pancreas and testis. At the recovery sacrificeofthe 10 mg/kg animals, there were no effects on terminal body weight, there were no macroscopic or microscopic findings, and liver weights were normal.
ili "Table Z: Absolute and relative liver and body weights at scheduled dosing termination.
mgkg(m) | (8)
5)
0Control (4) | 3947 591 | 60.16693 [100| 1.530.07 | 100
30)
348630 | 81.79281 [[1315 .822005 [119
020) [3025 58 [895.01379294.2662 [[1520 402T08730106
:
dTuwroinagntihmealdsoswienrgepferoiuondd. iAn m3o0/r2i0bumngd/kcogndaintiimoanlawnadsssaaccrriiffiicceeddaotnundsacyhe2d9ualnedd tfiomuensd to Thhaivse aendiemmaal aalnsdoihnafdlalmivmeartlieosnioofnts,hiencelsuodpihnaggmuisd-aznodnsatloamnadchceinntdriiclaotbiuvleaorfhdeopsationcgelilnujluarry.
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degeneration and necrosis, diffuse hepatocellular vacuolation, and hepatocyte basophilia in centrilobular areas indicativeofliver regeneration. Involution of the thymus, a common stress response, and degeneration and necrosisofthe heart, probably agonal changes, were also observed in this animal. Although the esophageal and gastric lesions are complicating factors, the contributionofAPFO to this animals moribund condition `cannot be dismissed due to findings in the liver, which were likely due to APFO exposure. A3 mg/kg animal was found in moribund condition with hind-limb paralysis and ataxia and sacrificed on day 137. The blood supply tothisanimals hind limbs was severely compromised, as indicated by the cool temperatureof thehind limbs on final medical `examination and the fact that ketamine injected into the thigh muscle failed toreachthe systemic circulation. The microscopic and macroscopic findings did not reveal evidence: ofspinal cord injury or impaired blood circulation.
DISCUSSION
Qualityofthe study (GK) Dose-level selection (PL)
+HiHgihg-h-ddoossee ucenssscahteidounolfeddossacirnifgic(eB()JB)
Liver findings (/B)
Sex hormones (GK)
Thyroid hormones (JB)
Recovery story (PL)
Mechanistic endpoints (PcoAO, PCNA, CCK, bile acids) (GK)
Pharmacokinetics (PL)
+ LOEL/NOEL (GK)
Low-dose death (GK)
Relate to thesus study (JB)
+ Relate
Relate
to
to
rhoudmeantnssttoorryy
((PULB))
CONCLUSIONS <5
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Resource material for discussion follows:
`These findings were non-specific and, with the exceptionof low albumin concentration,
`wweerree nwoitthcdonrsaiwsntefnrtowmitthretahtmeefnti.ndiTnhgesroebfsoreer,vetdhefocrlianniicamlalpsatihnotlhoegyhirgehsu-ldtossefogrrtohuispltohawt-
dose animal were not assumed to be due to APFO exposure.
"There are no known metabolic processes that degrade PFOA. The urinary elimination of PFOA in rats appears to be hormonally regulated (refs). Female rats and castrated male
rats rapidly clear PFOA in the urine; whereas, male rats have a significantly longer
urinary clearance half-life (refs). Sex differencesinurinary clearance have not been
found in [species] (ref). PFOA is excretedinthe bile and enters enterohepatic circulation
(Johnson, J.D. et al. 1980; Johnson, J.D., et al., 1984). Follow-up on blood levels in retired workers indicated that, althoughtheconcentrations detected wereinthe few ppm range, the chemical was present in some individuals well after the possibilityofexposure
had ceased, suggestianng elimination half-life on the order of 18 months (bel, 1980). A
reelciemnitnasttiuodnyhoaflf3lMiferiestiarpepdrcohxeimmiactaellypl3a0nt0 wdoarykse(rBsursruigsgeesttasl,th2a0t0t0h)e mean serum
Liver tumors
`Th finding of liver enlargement in male cynomolgous monkeys at all dosesin this study
is significant in ligtofprior information available from a 90-day oral gavage study in
`male and female rhesus monkeys. The rhesus study was conducted with APFO (FC-143,
Lot 340) in male and female rhesus monkeysat doses of 0 (control), 3, 10, 30 and 100
mg/kg/day in 0.5% Methocel.. Unfortunately, all animals in the 100 mg/kg/d group and 3
of4 animals in the 30 mg/kg/d group died. No treatment related gross pathological
.
lesions or alterations in urinalysis values were seen. Significant effects (and LOELSs in
mg/kg/day) included: weight loss (30); anorexia (10); emesis (30); black stools (10); pale.
swollen face (10), swollen eyes(30); decreased activity (30); prostration and trembling
(t1i0m0e)s;(a30n)e,mdieac(r3e0a)s,esdlisgehrtluym ianlckraelaisneedpphroospthhartoamsbeinacatnidvitayct(i3v0a)t;edinpcarrteiaasledthsreormubmopalsapsatritnate
aminotransferase (SGOT) activity (30); increased serum creatinine phosphokinase (CPK)
activity (30); diffuse lipid depletionofthe adrenals (30), bone marrow hypocellularity
(30), splenic and lymph node follicular atrophy (30). The NOAEL for this study was 3
mg/kg/d (ref). Subsequent analysis of serum and liver samples showed dose-related FC-
143 concentrations. There was no apparent difference in serum or liver FC-143 levels
between males and females (ref).
o
Testosterone inhibits urinary elimination of PFOA in male rats. It has been suggested
Z
that the gender difference in elimination may be due to a testosterone inducible serum or
5
tissue protein which binds PFOA [48].
=
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John L. Buteahoff, etal.
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No changes in liver weight to body weight ratios were seen in female rats given single
oral dosesof upto 200 mg PFOA/kg. In male rats, single oral dosesofeither 100 or 200 `mg PFOA/Kg produced an increase in relative liver weight. Castration reduced the
magnitudeofthe liver weight increase [13].
Estradiol treatmentofcastrated or intact male rats produced PFOA excretion rates similar
teoxctrheotsieoninbuftenmaolteas.s eCfafsetcrtaitvieolny wasitehsoturatdeisotlrtardieoaltmternetat[m5e1]n.t also enhanced PFOA
PFOA induced hepatomegaly, peroxisomal B-oxidation, microsomal 1acylglycerophosphocoline acyltransferase and cytosolic long-chain acyl CoA hydrolase in male rats to a much greaterextentthan in female rats. Testosterone was shown to be
necessary for these effects and estradiol blocked these effectsin male rats [53].
Activitiesofliver microsomal 1-acylglycerophosphocholine acyltransferase (AGA),
cmoimcproossiotmiaolnostfeairvoeyrlm-iCcorAodseosmaatlurpahsoes(phSaDt)idaynldchpoelrionxeis(oPmCa)lweB-roeximdeaatsiuornaendditn hraetsacfyeld a
diet containing 0.01 % PFOA for 2, 22 or 26 weeks. Females showed only slight changes.
in these parameters. Inmales, activitiesforall three enzymeswereelevated by two
weeks. Activities of AGA and B-oxidation remained unchanged throughout 26 weeks. `The activityof SD declined but was stillhigherthan contraotl2s6 weeks. The acyl `compositionofmicrosomal PC was significantly altered in males. All ofthese
parameters retumed to control levels within 4 weeks after PFOA was withdrawn from the diet [72].
hPeFpaOtAicipnetrhoexdiiseotmoafl mfiatctey aatciadcoBn-coexnitdartaitoino,nodfe0c.re0a2s-e0d.h0e5pa%tifcorm5i-t1o0chdoanydsricaalussiezdeianncdreased
increases in the following hepatic enzyme activities: @-hydroxylation of lauric acid and
cytosolic epoxide hydrolase, glutathione transferase and DT-diaphorase. There were no significant differences between males and females [85].
PFOA has been shown to induce hepatic peroxisomal proliferation in rats and mice There
was a marked sex difference in rats (38, 53, 54, 58, 83]. PFOA-induced hepatic
peroxisomal proliferation in male rats is most prevalent in the centrilobular region and is
associated with increased peroxisomal palmitoyl-CoA oxidation, marked hypolipidemia,
an almost 10-fold increase in hepatic free acid soluble CoA, and altered peroxisomal
polypeptides [83].
c5
Perfluorooctane, CF, did not induce peroxisomal proliferation in rats, indicating the
importanceof the carboxylic acid group in causing this effect [54].
PFOA caused peroxisomal proliferation in primary culturesofrat hepatocytes. PFOA-
mediated increases in the peroxisomal enzyme fatty acyl-CoA B-oxidase (FACO) were inhibited by cycloheximide and correlated with elevations in FACO mRNA levels. Thus,
EID101466
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John L. Butenhof. etal.
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PFOA appears transcriptional
atondintdrauncselapteiroonxalispormoaclespsreosli[f6e9]r.ation
through
the
regulationof
gene
pPrFoOliAf-eirnatdiuocnoefd shempoaottohmeengdaolpyliassdmuiec prerteidcoumliunma,nmtiltyotcohocneldlrihaypaenrdtrpoeprhoyxiressoumletsing[38f]r,om
pPrFiOmAar-iilnydiuncethde DpeNriAposrytnatlhreesgiison(.hypIenrcprleaassiead)DhaNsAalssyonbtheeesnisshococwunrrteodoicneutrheinabrsatenlciveero,f
hneepcarotsoicse,llsuulgagresintjiunrgy.thPatertohexiceslolmperoplriofleirfaetriavteioanctoicvciutryriesdnportiamarreigleyneirnatthievecernetsrpiolnosbueltaor
region suggesting that PFOA-induced independent processes(73].
hyperplasia
and
peroxisomal
proliferation
are
dPeFcOreAasiendtbheoddyietweoifgmhatlaendmitchee aftolcloonwcienntgrhaetpiaotnisoc feff0e.c0t2s:thoe0p.a1t%omefgoral2y-,10dedcaryesasceadused imnictroecahsoenddrciyatlossoilziec, eipnocrxeiadseedhymdircorloassoemaanldPD4T5-0d,iaPp4h5o0rarseed,ucatnadsedeacnrdeaespeodximdietohcyhdornodlraisael, glilpuitdatpheiroonxeidpaetriooxni.daHseepaatnidcsmuipcerroosxoimdaeld,ibs,mauntdasceytwoesorleicnogtlustiagtnhifiiocnaenttlryanasfffeercatseed, [84].
bHeepdaetpoemnedgeanltyo,nbuctorntoitcopsetrerooxnies,otmhee pprroilmifaerryataidorne,ncaalugsleudcobcyorPtFicOoAidiinnrraotdsewnatss [s7h3]o,wn to
hUynploilkiepimdaenmyiah.epRaattohcearr,cPinFoOgeAniccaupseerdoxaimsaormekepdroilnifcerreaatsoersi,n PheFpOatAicdilidpnidotsycnatuhseesis [38].
cDhioelteasrtyertorleaatnmdenttroiafcmyalglleycreartoslswiatnhd PinFcOreAas(e0d.l0i2v%erfforree7-c1h4oldeasytesr)ocl.ausHeedpadteoccryetaessedissoelartuemd hfyrdormoxtryemaettehdyrlagtlsustahroawteed bruetdnuoctedfrsoynmtmheesviasloofnactheo,leisntcerreoalsefdroomxiadcaettiaotneo, fppyarulvmaitteataenadnd rreedduuccteadsefaatntydaaccyidl-syCnotAhecshiosl.esAtcetriovlitaiceysoltfrlainvsefrerhaysedrwoexryemertehdyuclegdlu[t8a2r]i.c acid-CoA
hPeFpaOtAicimnitthoechdioentdorfiamlicperotfeoirn,uphetpoat1i0c dpaeyrsoxciasuosmeadlgpraealtmeirtionyclr-eCaoseAsoixnidlaitvieronw,eilgahutr,oy
a`cCiodsA.oxPiFdaOsAe aicntcirveitayseadnpdecraotxailsasoemaalctfiavtittyyatchiadnfd-iodxipdeartfilounor(owahciectih,p-rboudtuycreics oHr,0d,e)catnooaic
c
DmiuectharygrelaevteelrseoxtfePnFtOtAhanascaltaolwasaes (0w.0h0i1ch%recdauucseesdHsyig,nitfoicwaanttecrhaanngdesm[o6l1e]c.ular oxygen).
:
tPrFipOhAospchaautseed(IeTnPh)arnecceedptaofrfsiniintymaanlde rraetdsu.ceIdTPmaisxiamsaelcobnidndmiensgsceanpgaecritiynvooflhveepdatiinctihneositol
`mobilizationofcalcium from intracellular peroxisomal proliferation [74].
stores
and
may
be
involved
in
the
process
of
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John L. Butenhoft, eal
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Valproate (2-propylpentanoic acid), a non-fluorinated analog of PFOA, is a hepatotoxin `which impairs mitochondrial function and fatty acid metabolism [97],
Induction ofperoxisomes by treatment with PFOA did not increase rates of hydrogen peroxide production in rat or mouse liver [12]. Oxidative stress resulting from the
increased production of hydrogen peroxide has been postulated as a mechanism by which
peroxisome proliferators cause liver damage and cancer.
PFOA induced hepatic microsomal carboxylesterase isozymes in male rats 106).
PFOA. displaced efluorescentlylabeledfaty.acid from iverfatty-aciddlingarotsin
ie oe raBammiteas`seperiunmaR lbuT tiinim n:vifro-(YDc9]o:mpe gTiotesvtihbedIiuyplpoettEQsmAeEdnoid
`(5m-deimaetshyularmilnoniapnthvalientesrulloofsp-shooafniysnli)at-iuapnldfeeicbrarnceosieccennaccteid. (10DJAVUADPAF)OfRrcoamuLs-eFAB4P8w%as reductiatofinital fidorescencewhenadded:to solutions containing 1 MAFABPand W1MMofDhAeUkDnAo.wTnhoerLsOusEpLectfeodrpPeFrOoAxiisnomtehpirsoalsisfaeyrawtaorss0:.p5e-rf1l.u0ouroMo.ctBaynecsoumlpfaorniiscoanc,id10 * E(tPhFyOlSp)r,lWuyoertohg,tNa-nEetshuyllfpoenrafmliudcereotohcatannoelsu(lNf-oEnaFmOiSdeE)(cFaXu-1s2e)da6n6d%,N4- 8%,a4nd539%% reductidaofinitalflnorescence; respectively. Results for BSAvierevery4itilirtohose
seen with L-FABP [109, 122].
`The serum concentration at which this liver enlargement occurred (approx. 50 ppm) is
`within the range experienced by workers with higher exposures. Studiesin exposed workers have not indicated liver toxicity. However, the enlargement at the low dose in the cynomolgus monkey was not associated with any clinical manisfestations of liver toxicity; therefore, it is not possible to knowif workers with similar body burdens, as
represented by serum concentration, experience similar liver enlargement.
Pancreatic tumors
The absenceofan increase in cholecystokinin is also also significant in lightof Cook et
al.'s findings in rats (ref). This may indicate a decreased risk ofpancreatic tumors in primates. It is also important to point out that CCK, receptors are distributed differently in the rodent as oppsed to humans and primates (ref). [comment on CCK, receptor
agonism] PFOA has been asssociated with elevated CCK levels and pancreatic tumors. PFOA did not bind directly to the CCK, receptor in a competition binding assay, and did
not inhibit trypsin in vitro, thus two possible contributing mechanisms for pancreatic
carcinogeneis were ruled out [111].
Leydig cell tumors
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aIbnstehnecmeaofltehriats, eefsftercatdiionltihseeplreevsaetnetdsatnuddyteasntdotienrosnteuddieecsroefasweodrokenrrsepseuagtgeedstesxpthoasturteh.e The primate is not responsive to the hormonal changes seen in the rat. Since these changes are thought to occur in the ratviainductionofaromatase and are related to the formation of Leydig cell tumors in the rat, the risk of testicular tumors in primates from exposure to APFO is assumed to be much lower than that in the rat. In fact, the spontaneous incidence of Leydig cell tumors in rats is ordersofmagnitude higher than in the humans (insert detail and ref).
`The historical incidenceofLeydig cell tumors in Sprague-Dawley rats ranges from 1.4 to 10% with a meanof 4.7% [60]. The incidenceofLeydig cell tumors in man is estimated to be less than 0.0003%. A numberofchemical agents, nutritional and hormonal factors have been showntocause Leydig cell tumors in rodents. However, wherethere have been studies on the same chemicals in man, there appears to be no evidence of Leydig cell tumor formation in man [0].
Elevated estrogen levels havebeenassociated with Leydig cell tumors in mice,ratsand humans [91,9596]. Serum estradiol levels were significantly elevated in rats treated with PFOA at dosesofmorethan 10 mg/kg/d and accessory sex organ relative weights were significantly reduced in rats fed 50 mg/kg/d PFOA for 14 days. In addition, serum testosterone levels showed a dose-dependent decrease which was, however, not statistically significant. This decrease in testosterone levels was shown, by human chorionic gonadotropin (HG) challenge, to be associated with inhibition of steroidogenesis in Leydig cells [10]
The increase in serum estrogen caused by PFOA appears to be due to inductionofthe enzyme aromatase (Cytochrome P450 XIX) which metabolizes testosterone to estradiol. A two-fold increase in serum estradiol showed a linear correlation with a 16-fold increase in total hepatic aromatase activity (57, 118).
PFOA caused a dose-dependent decrease in hCG stimulated testosterone secretion and.
also reduced the basal release of estradiol by rat Leydig cells exposed in vitro, suggesting
that PFOA may have a direct effect on the ability of Leydig cells to produce testosterone
parnoddeuscttriaodnioiln [h5C5G,-s1t1i9muInlactoentdraLsety,deixg-vcievllos sftrudoimesradtesmtornesatterdatweitahn 2i5ncmrge/askeg/idn atyesAtoPsFteOrone
for 14 days, indicating that the direct inhibitionof testosterone synthesis seen in-vitro is
reversible in-vivo. Furthermore, in the in vivo studies serum estradiol and testicular
interstitial fluid estradiol and transforming growth factor alpha (TGF alpha) levels were
also increased, consistent with the hypothesis that estradiol may modulate growth factor
expression within the testis. APFO produced a 4.5 fold increase in hepatic aromatase invivo, suggested as the primary cause of increased serum estradiol (120).
;
PleFveOlsA, aitnc3r0e0aspepdmheipnattihce pd-ieotxifdoart|ioynea(rpeirnomxailseomreatpsrcolaiufseerdatiinonc)reaansdedinscerreuamseedstrrealdaitoilve
DRAFTJuly 26,2000
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COOLEY
John L. Butenbof, es.
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olxiviedratwieoing,htosr.sePrFuOmAtehsatodstneoroenfef,ecFtSoHn,hperpoaltaicctionroLrelyudtieginciezlilngprholoirfmeroanteiocno,nLceenytdriagticoenlls.pThus, PFOA did not induce peroxisome proliferation in Leydig cell at dietary levels which did induce hepatic peroxisome proliferation 56].
The lackofperoxisome proliferation seen in this study in not unexpected. Primates are plaerstsiraellsypodnuseivteo ttohepefarcotxtihsaotmperipmraoltiefserhaatvieonmfurcohm fxeewnoebriPotPiAcRcGomrpeoceupntdosrstthhaannrrooddeenntts,s. Since the hepatocelluar tumors observed in ras with APFO ere thought to derive from rpiesrkooxfistohemseeptruomliofresraotcicounrainndg tihnepprliemaitoemsoripshciocnsriedseproendselofwr.om activation of PPAR, the Waxman et al 1999) have studied the effectsofPFOA on transactivation ofPPARG and PHPuAmRayn PinPCAORS:-1wcaesllsletsrasnesnfseicttievdewtiotPhFmOouAstehaanndmohuusmeanPPPPAARR.aHaundmaPnPAaRndYmroecuespetors PPARy were non-responsive to PFOA. Thyroid hormones
AfLorTma4lveasl,uaensdwe1.r3e 7wi.t6hiungt/hme Lrafnogr efpeumballeissh(eDdefPoaroRlhoeasnudsMmaosnakreoy.s19o8f90)..8T-ak6.e6nutgo/gemtlher, thedatasuggestthatthechangesin T4values observedappear tobesystemic trendsthat are not compound related and not biologically significant. A1IgL/1T030vmalluaensdw6e5r-e2w9i5th0i/n1t0h0ermeflfeorernmcaelreasngaenfdofremmaalleesa,nrdefspeemcatilveeMlayc(aDqeuPaeosl(o5a4n-d115. Masaro 1989). Cell proliferation discussion
Membrane secretionof
EIfgfMecftsr:omAtcuslutbulreetdhhalumcaonnceonrtmraotuisones,B
PFOA cells.
did At
not alte the expression lethal concentrations (>
or 0.8
mM), PFOA caused have suggested that
a detergent-like solubilization of someofthe biochemical changes
membrane and target
proteins. The authors organ effects observed
in
vivo with PFOA may be secondary to cel ysis [92]
PFOA caused lipid peroxidation in vitro [80].
Z
PorFgaOnAizaantidoontahenrdpfelrufildiutoyroinfacteeldlsmuerfmabcrtaanntessca[u6s2e.9a2l.t9er3a9t4i]o.ns in the fatty acid composition.
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John L. Buteahof, etal.
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At sub-lethal concentrations, PFOA did not affect migration or cappingofcell surface
immunoglobulins after antigen recognition in lymphoblastoid cells in vitro. However, PFOA (0.9 mM for 15 min) did cause changes in membrane lipid architecture. It was.
suggested that direct, physical disruptionofcell surface membranes is the likely
`mechanismofacute PFOA toxicity [93].
Sodium perfluorooctanoate had a much higher affinity for
dipalmatoylphosphatidylcholine vesicle membranes than did the corresponding nonfluorinated compound, sodium octanoate. This difference was attributed to the greater
hydrophobicityofthe fluorinated acid [compound [94].
PFOA did not inhibit cell-to-cell communication in cultures offreshly isolated or established (ARL) rat liver cells as did PFDA [76].
mPiFtoOcAhounndcroiualploexdid(aEtDiyv,e =ph0o.s1p8homrMyl)atainodn aitn hviitgrho.er cTohneceanuttrhaotrisonhsypionthhibeistiezdedratthat
uncouplingof mitochondrial oxidative phosphorylation by PFOA in vivo would lead to
reduced cellular ATP levels and elevated intracellular unsaturated fatty acids which would activateprotein kinase leading to increased cell turnover which is believed to be
involved in the carcinogenic process for nongenotoxic carcinogens [67].
PFOA (100 uM) exhibited a general detergent-like effect on mitochondrial membranes as
reelected by a decrease in respiratory control without uncoupling oxidative
phosphorylation
phosphorylation
in-vitro. FC-143 slightly increased the activityof enzymes
and respiratory chain, the most probable mechanism being
of oxidative.
the
fluidisationofthe inner mitochondrial membrane [121].
PFOA at concentrations up to 500 pg/ml did not impair clone-forming ability in L5178Y
mouse lymphoma cells in vitro [77].
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:
CONCLUSIONS
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5
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103. Vbeonuknadtefslwuaorrliune, Pi.n 1o9r8g2a.niScodcioummpobuinpdhesnyalndmetbhiooldogfiocraldetmaetremriinaalst.ion oAnfacl.ovalCehnetlmy 54,1132:37.
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Olsen G.W., Gilliland An epidemiological
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Burris J.M., Mendel J.S., reproductive hormones
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Mandel men
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111. OefbfoecutrsnofJ.WDy,etFhra1m4e,64S3R.,(AbEslltiroatctG.1S1.8,1)anTdoxCicooolokgiJs.tC..361,99273.2-P2a3n3c.reatic oncogenic 2
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Repon-
T-6075 in
Analytical study.
rabbits. 1995 (in
Single-dose
vivo reference
dermal
number:
z
8
HWIH6329-153, Study number: AMDT-011795.1) 3M Environmental Laboratory
113. CMuhrilnieseH.haMmusttaegrenoivcairtyy(CteHsOt )oncellTs-.61395986.mCeaHsVuriSntgudychNroo.:mo1s7o3m8a8l-0-a4b3er7r.atCioomnsinign Hazelton Inc. Vienna, VA.
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114. Murli H. Mouse micronucleus test on T-6358 in an in-vivo mouse micronucleus assay. 1996. CHV Study No.:17388-0-455. Coming Hazelton Inc. Vienna, VA.
115. Maller W. Perfluorooctanoic acid ammonium salt, solution 30% Chromosome abberations in vitro in V79 Chinese hamster cells. 1996. Study number 96.0003. Hoechst Aktiengesellschaft Pharma Development Corporate Toxicology. Frankfurt
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116. M`umlulteagreniWc.potPeenrtifalluoirnosotcrtaainnsssoufreSaamlmmoonnieulslaaztlypshuingmur(i3u0m%(AiMg)ESSTtuEdSyT).of199t6h.e SCotrupdoyratneuTmobxeircol9o6g.y0.00F2r.ankfHuoretcahsmtMaAiknt.iengesellschaft Pharma Development
117. Murli H. Mutagenicity test on T-6342 measuring chromosome aberrations in human lymphocytes with a confirmatory assay `with multiple harvests. 1996. CHV study No.: 17073-0-449CO. Coming Hazelton Inc. (CHV), Vienna ,VA.
118.
L`ipue,roRxiCsoMme,proHluifretratMorE, ,ammCoonoikumJ.Cp.erfalnudoroBoicetgaenloaLt.eB(.CB1)99o6n.
Effects of the
hepatic aromatase
activity in adult male Crl:CD BR (CD) rats. Fund. Appl. Toxicol. 30, 220-228
119. Liu R.C.M., Hahn C., and Hurtt M.E. 1996. The direct effectof hepatic peroxisome proliferators onratLeydig cell function in vitro. Fund. Appl. Toxicol. 30,102-108.
120. BpieergfelluorLoBo.c,tanLoiauteRoCn Mle,ydiHgucretll MfEunEc,tioann:dInC-voiotrko,J.iCn.-vivoE,ffaecntds eox-fviavmomsotundiieusm. 1995. Toxicol. Appl. Pharmacol. 134, 18-25.
121. Wallace K. B. and Starkov A. 1998. The effectofperfluorinated arylalkylsulfonamides on bioenergetics of rat liver mitochondria. Dept of
DBuiloucthhe,miMstNry5a58n1d2M,oUleScAu.laSrupBpioorltogeyd,bUynivgerrasnittyfroofmM3NMSCcohmopolanoyf.Medicine.
122.
Nabbe
Fatty
fAeclidd-DB.in1d9i9n8g
APnrotIenivne.
stMiagsatteirons
oTfhetshies,EfUfneicvtesrosfitFyluoofrMoicnhneemsioctaal.s
TohnesLiisver
research performed at and supported by 3M.
2
Jams 1/26/98, replaces: fscg 9/14/94
z
DRAFT Jlyva 28,2000
EID101492
005:.7L% ea
John L. Buteahoff, tal.
DRAFT
12000
DRAFT July 26,2000
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:
EID101493 CEEIT puget
John L. Butenhoff etl.
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References:
Astdaatumss,anMdRa.th,erKoaspcllaenr,osIisR.i,nCClyanrokmsoonlgTu.sB.maonndkeKyosr.itAnxitkerDi.oRs.cl1e9r8o5s.isO5v:a1r9i2e-c2t0o0m.y, social Baselet R.C. and Carvey, R.H. 1995. Dispositionof f Toxic Drugsand Chemicals in man, Fourth edition. Chemical Toxicology Institute, Foster City, CA. PCaotptpleJyAR,CR,obDienLsuocnaDJE, ,ElSccohmwbetezC,B,FTenungewro-CordisJ,p WP,ahLlaikeW.BGD,oMpaerrsoxmiasnomDeS,prPoalsitfeoroartiTnAg, compounds pose a hepatocarcinogenic hazard to humans? Regul Toxicol Pharmacol. 1998 Feb;27(1 Pt 1):47-60. iCnoclrveians,ePc.hLo.l,eWstaegrnoler7 Ja.-DH.y, dArdoaxmysl,asMe Rm,RNanAd iSnonrcoin-hTuhmomaans,prMim.aGt.es1.9M98e.taSbeolxisstme:roids Clinical and Experimental. 47:391-395. C`aomomkoJnCi,umMuprerraflyuSorMo,ocFtranaomaeteS:Ra,pHoussstitblMeEe.nd1o9c9r2i.ne-IrnedluactteidonmoefcLhaenyidsimg. cTelolxiacdoelnoAmpapsl by Pharmacol. Apr;113(2):209-17. TDehPeaCollioniLc.aVl.ChaenmdiMsatsryaorfoLaE.bJ.or1a9t8o9ryEAnndiomcarlisn.e EHdosrmWo.nLeoscIbn aLnadboFr.atQouriymbAnyi.maNles.w YIonrk :Parmagon Press. (Note: These are secondary references.
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SEludlrfiodngiec,ASc.iR.d PFoetbarsusairuym25Sa2lt00(0P.FO2A6;-Twe-e6k29C5a)psiunlCeyTnooxmiociltgyusStMuodnykweiytsh.PeDrrfalftuoCreololctane
Proliferation report. Client Number 6329-223, 3M T-6295.7. Pathology Associates International, Frederick, MD.
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Gdoalydesnutbhaaclu,teErLat sJteusdsyu.p,SDt.uCd.y,NGoe.il,13R7G-.0,8J5e,ffInetresmoant,iNon.aDl. RaensdeaArrccheoa,nRdJD.ev1e97l8o0p.meNnitnety & Corporation, Mattawan, M1.
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Goldenthal, ELL, Jessup, D.C., Geil, RG. and Mehring, J.5. 1978b. Ninety-day subacute rhesus monkey toxicity study. Study No. 137-092, Intemational Research and Development Corporation, Matawan, MI.
Gpluays,maW:Sp,rTeavavleesn,caenadnDdRc,haBrraectye,rJirz.a,tWioSn. (1(I9n7)6)B.ioOcrhgeamniisctrfyluIonrvooclvoimnpgouCnadrsbionn-hFluumoarnine Bond, pages 117-134.
Hefafuecgthoofmp,erBf.luaonrdooScptyadneoviocldac,iOd.(P1F99O2A.),Tpheerfmleucohraooncitsamneunsduelrplhyoinnigc tahceidhy(pPoFlOiApeAm)icand clofibric acid. Biochim. Biophys. Acta. 1128, 65-72.
Jdooshen.sonPr,oJj.ecDt.Naon.d8O9b0e0r3,1R02F0.0,1 R9i7k9e.rALbabsoorrapttoiroineos,fIFncC.-,9S5t.-1P4auCl,inMraNt.s after single oral
Johnson, J.D. and Behr, F.E- 1979. Synthesis and Characterizationof FC-95-C. Project No. 8900310200, Riker Laboratories, Inc. St. Paul, MN.
tJioshsnues.ond,isJt.rDi.b,utGiiobnsoofnt,otSa.Jl.caanrdboOnb-e1r4, iRnEr.ats19a7ft9e.r aExstiennglteanidv.roduotseeooffexFcCr-e9t5i-o1nC.andProject No. 8900310200, Riker Laboratories, Inc., St. Paul, MN.
J`aonhdnFsoCn-,1J4.D3.,-CGiibnsorant,s Sw.iJt.hacnhdoOlbesetry,rRamEi.ne19tr8e0a.tmEennth.anPcreodjeecltiNmoi.nat8i9o0n0o3f10F2C0.0-,9R5i-kCer Laboratories, Inc., St. Paul, MN.
Johnson, 1.D., Gibson, S.J. and Ober, R.E. 1984. Cholestramine-enhanced fecal eliminationofcarbon-14 in rats after administrationofammonium
["Clperfluorooctanoate or potassium [""Clperfluorooctanesulfonate. Fund. Appl.
Toxicol. 4, 972-976.
JBuisotchWe.miWc.a,lGeofrfgecatssKa.n,dHazrotnlalF-hUe.t,erHoegeinneeimtayonfnpPe.,roSxalizseormMe.praonldifSecrahtiimoansisncdkucHe. d 1b9y89. perfluorocarboxylic acids in at liver. Hepatology 9:570-581 et al. 1989
Kennedy toxicityu
G.L.Jr., Keller D. A., of fluorinated acids in
Biegel LB. and Brock W.J. 1998. Repeated rats. Toxicologist Volume 42. Abstract No.
dose 1829
p.
371.
LEnadroscorninP.oRl.ogayn,d8Ingedb.arEdSs..H.J. 1D9.9W2iTlhseonThaynrdoiDd. GW.lanFods.teIrn,Wpipll3i5a7m-s48T7e,xtPbhoiolkadoeflphia:
i
:
W.B. Saunders Co).
NlaabbebleefdefladttDy., acBiud taennahloogfufe J.,fBraosmsfNa.ttyanadciSdecaacrartieAr.pr1o9t9e8.insDibsypwlyaectehm-e1n4t,o64af3,falumomreosncienutmly
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perfluorooctanoate, potassium perfluorooctane sulfonate and other known peroxisome proliferators. Toxicologist 41. 1998.
NolJd.B.July 13 1999. 26-1
af
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with Perfl
e Sulfonic
Acid Potassium Salt (PFOA;T-6295) in Cynomologus Monkeys - Draft Pathological
Report (Ancilliary Study) Electron Microscopic Evaluation of Liver in Cynomologus
Monkeys.Client Number 6329-223 PAI Study Number EM 99.76. Pathology Associates
International, Durham NC.
Nold, J.B. May 30, 2000. 26-weekCapsuleToxicityStudywithPerfluorooctaneSulfonic
Aci
i
A;T-6295) is
=
Pathologic
Re; (Ancilliz tud
n Micros i
ive
le
Monkeys (Recover Animals). Client Number 6329-223 PAI Study Number EM 99.76.
Pathology Associates International, Durham NC.
Osc'rCeoennniengr bJa.tCt.,erFyracmoem, pS.aCr.,etBdoicagnelinL-.uBt.erCooeoxpkoJs.uCr.eafnodr DdaevteicstiLn.gG.thSeenessittriovgietny roecfaepTtioerr 1
agonist 17 B-estradiol. Tox. Sci. 44, 16--9 184, 1998.
Olsen G.W., Burris J.M., Mandel J.H., Zobel L.R. Serum perfluorooctane sulfonate and
hepatic and lipid clinical chemistry tests in fluorochemical production employees. JOEM
41:799-805.
Reimers J.R. 1999. Hormones. In: The Clinical Chemistry ofLaboratory Animals. Second edition. Eds.: Loeb W.F and Quimby F. W. pp 455-499, Philadelphia PA. Taylor and
Frances.
Smith, D.R. 1998. Animal models: Nutrition and lipoprotein metabolism. Current
Opinion in Lipidology. 9:3-6.
Turley, S.D., Spady D.K., and Dietschy JM. 1995. Roleofliver in the synthesis of
cholesterol and the clearance of low density lipoproteins in the Cynomolgus monkey Journal of Lipid Research. 36:67-79.
`Wagner, J.D., Zhang, L., and Adams, M.R. 1997. Effect ofestrogens on arterial LDL
a
metabolism. In Hormonal, metabolic, and cellular influences on cardiovascular disease
=
in women. Ed. T.L. Forte, pp 153-174. New York: Futura Publishing Co.
g
Wallace K. B. and Starkov A. 1998. The effectofperfluorinated arylalkylsulfonamides
$
on bioenergetics ofrat liver mitochondria. Dept of Biochemistry and Molecular Biology,
University of MN School of Medicine. Duluth, MN 55812, USA. Supported by a grant
from 3M Company.
EID101496
DRAFT July 28,2000 0005.17
Page a4
[
121
0005.15
PaatthoollooggyyAAssssoocciiaatteessiInnteemrantatiioonnaal! sppeye
P1a5tWhoolromgaynA'sssoMciilaltCesouIrntt]Suite | Frederick, MD 21701 September 29,2000
CDro.vaPnecteeJrL.abTohroamtioroireds,IPnch..D. 3301 Kinsman Blvd. Madison WI 53704 Dear Dr. Thomford,
Enclosed please find a copyofthe Draft Cell Proliferation Report for the Study identified below:
Pe2r6f-lWueoreakocCtaapnsoualteeT(oPxiFcOit)y SintuCdyynwoimtohlgAumsmMoonnikuemys Covance Study Number 6329-231
Sincerely,
Kim Claggett
RCeelsleaKricnehtAiscssisDtiavnitsion
301-624-2917
8 Lahoraloriss
corFaison, of
27 02 2000
Enclosure
Recaived #15
{x 5 11SST Class mal
Y7 sso Imma
3Jl
SC hing reese
--_--
7 \ ADD-- L DIST.
\ | -- -- _--
TOX-- FILE
-- e1e 5 Worm-- on's Mil-- Cour, Se ue| Fe reder-- ick. Mayland 21701 -- GOT)663-1644 + (301-- ) 863-8994 FAX
000s
EEE| rnotcoy associates temational == A Company of Science Applications International Corporation Erosaneicirssy
DRAFT CELL PROLIFERATION REPORT 26-WEEK CAPSULE TOXICITY STUDY WITH AMMONIUM PERFLUOROOCTANOATE (APFO) IN CYNOMOLGUS MONKEYS COVANCE STUDY NUMBER 6329-231
PREPARED FOR: 3M
TOXICOLOGY SERVICES BUILDING 220-2E-02, 3M CENTER
ST. PAUL, MN 55144-1000 PREPARED BY:
PATHOLOGY ASSOCIATES INTERNATIONAL 15 WORMAN'S MILL COURT, SUITIE FREDERICK, MD 21701 SEPTEMBER 26, 2000
--_--TS Wormans Mill Cours, Suite 1+ Frederick,Maryland 21701 + (301) 663-1644 + (301) 663-8994 FAX. 009."
TABLE OF CONTENTS
Section
Report Narrative
1
Tables
n
Figures
m
Individual Animal Histopathology Findings
wv
Signature Page
v
Quality Assurance Statement
vi
000.
Covance Study No. 6329-2TM31 Draft Cell ProliferanonPaRgeepo1r1t
CELL PROLIFERATION REPORT FOR: PER26F-LWUEOERKOCOACPTSAUNLOEATTOEXI(ACPIFTOY) SITN UCDYYNWOIMTOHLGAUMSMOMNOINUKMEYS
COVANCE STUDY NUMBER 6329-231
INTRODUCTION
The purpose of hormones, and
the study was other selected
to assess the biochemical
effect of the test parameters when
material on critical administered daily
enzyme levels, by capsule
cynomolgus monkeys for at least 26 weeks.
"This report, Toxicology
Sseurbvmiictest,edrebpyrePsaetnthsoltohgey
cAeslslopcrioaltiefserIanttioenmaftiinodnianlgs(PaAnId)
to the study interpretation
Sponsor, 3M for Covance
Study Number 6329-231 entitled "26-Week Capsule Toxicity Study with Ammonium
Periluorooctanoate In Cynomolgus Monkeys"
REGULATORY COMPLIANCE
wAlilthastpheectEsnvoifrtohnemteanstkaslasPsrooctieactteidonwiAtghePnAcIy'sGopoordtiLoanobofrtahtiosrystPurdaycwtiecree(cGoLnPd)ucRteegdulinatcioomnpsliasansceet
forth in Title 1983effective
D4e0ceomfbtehre 2U9,S19C8o3)d,eaonfd
wFietdheraanly Raepgpulliactaibloensa,mePnardtme7n9t2s,.
issued
November
29,
MATERIALS AND METHODS
Treatment Group. 1 (Control) 2 (Low-dose) 3 (Mid-dose) 4 (High-dose)
Experimental Design Dose Level (mg/kg/day) 0 3 10 30
NumberofAnimals
Main Study Recovery
4 4
2 0
4
2
4
2
A1l,l3aannidma4lswe(rmeaidnessitgundayteadndasrerceocvoevreyr)y waenirmealtsr.eatTerdefaotrmuepnttoin2t6hweeseekasn.imTalwsowaansimdaislcsonitnignruoedu.ps and the Sponsor determined the recovery period.
000.
Covance Study No. 6329-2TM31 Draft Cell ProliferationPaRgeepolrzt
Tissue Collection for Cell Proliferation
Representative each of the 22
samplesof animals
the was
left lateral fixed and
lobe of the processed
liver, lef and right testes, and pancreas from to paraffin block by Covance per protocol
sspleicdiefsicwaetiroensp.reTpiasrseudefbolrocHk&s Eweerveaslhuaitpipoend taondPAiImmfuonrosheicstitooncihnegmaincdalstdaeitniencgt.ionForfopmroelaicfherbaltoicnkg,
cell nuclear antigen (PCNA), a markerof cell proliferation.
Immunobistochemistry for Cell Proliferation
Sections of (Superfrost
paraffin-embedded tissues were cut Plus, Fisher Scientific, Pittsburgh,
= 5 um PA) to
and placed on positively ensure adhesion during
charged slides processing for
sPtCaNinA.tissSuteas.ndaBrrdieiflmym,untoishsiusetsoecchteiomniscawlermeetihncoudbsatfeodr PwiNthAa m(oEnldorcildognea,letanatl,ib1o9d9y3t)owPerCeNuAs(edLotto
(#M1s0l7gEGxKpi.t1L1o/t0#0 PDKA6K1O0,2 ECaxrpp.in4t/e2r2i/a0,0,CAV)ecatonrd,rBeuargleintnsgarmeeq,uiCreAd)fmoretthheodavfiodrint-hbeiodteitnecpteiroonoxifdtahsee
antigen-antibody complex. and M) was localized by
PCNA expression in cells in all phases of the cell cycle (G1, S, G2 the chromagen 3,3-diaminobenzidine (DAB Lot# 108HS210 Exp.
820/01; Sigma Chemical Co., St. Louis, MO). hematoxylin.
Tissue sections were counterstained with
Cell Proliferation Measurements
bPorsoiwtnivetostbalianicnkg rfeoarctPiConNAprowdausctcattheagtorciozrerdelbataesdedwiotnhcetlhleuldairffdeirsetnrtibupthiaosnesanodfinttheenscietlyl ocfyctlhee
(fEorldSripdhgaeseet cale.,lls.199A3).celUlniinfotrhem,G,daprhkabsreoofwtnhteo bclelalckcynculcelehaardstdaiiffnuisneg,wsatsipjpuldedgenductloebaer psotsaiitniivneg
that was lighter than cytoplasmic stippling
a cell with or
in S phase. Cells in the G, phase exhibited distinct, diffuse without nuclear staining. Mitotic figures were conspicuous with
dciofnfsuissetecdoytfosptluadsmyitcissstuiepp(lainngi.malAno.ne1g0a5t7i0v9e)ctohnattrowlasslniodte iwnacsubaitnecdluwdietdh itnhetphreismtaariynianngtirbuondya.nd
For cell quality
proliferation of staining,
evaluations, slides were fist perused at low processing and sectioning, pattem of cell
magnification labeling (c.g.,
(100X) to judge centrilobular or
panlobular, extrahepatocellular proliferation, endothelium), and histomorphologic changes.
such as The later
Kupffer cells, bile was further assessed
duct epithelium, by evaluating the
serial H&E slide for each animal evaluated for cell proliferation. Cell proliferation was then
quantified at higher magnification (200X) as described above.
For cell proliferation measurements in the liver, the percentage of dark, nuclear-stained hepatocytes that represent cells in S-phase was determined by scoring at least 3000 hepatocytes in 10 randomly selected fields per animal. Cell proliferation within islet and exocrine cells of the pancreas was scored subjectively with 3 = exocrine stained greater than islets, and 4 = islets and exocrine stained heavily as determined by positive PCNA staining. The entire tissue section
0085
Covance Study No. 6329-2M3m1 Draft Cell ProliferationPaRgeepo1r3t
represented on the slide was perused at 100X and 400X. For measuring cell proliferation in the testes, the section farthest from the slide label was scored. The percentage of PCNA-labeled Leydig cells was determined by scoring at least 100 Leydig cells in the entire section that was examined.
Statistical Analysis
Due to the small samples sizes within main study and recovery groups, and because not all animals within 2 treatment group were sacrificed on the same day, statistical analysis was not performed on cell proliferation data.
RESULTS
Cell Proliferation
Individual animal cell proliferation data are presented in Section I (Table II-1) and graphically in Figures [11-1 - 3. Clearly, cell proliferation was not increased by treatment in the pancreas or testes of monkeys as determined by examining the scatter plots in Section II, Figures III-2 and IL-3. In the liver, however, there did appear to be an enhancement of cell proliferation in the highest dose tested (30 mg/kg/day) as revealed in Section II, Figure (III -1). Data points 6, 8, 9 and 10 (30 mg/kg/day; animals 105704, 105713, 105711, 105722, and 105703, respectively) were greater than or equal to the highest control value (data point 1; animal 105714). The lowest dose tested (data point 3; 3 mg/kg/day), however, had one animal (animal 105706) with a labeling index that exceeded all animals examined. Thus, an apparent increase in cell proliferation was not necessarily dose-related.
Histopathology
Sections from the same tissue blocks used for preparation of PCNA-stained slides were stained with hematoxylin and eosin (H&E) for histopathologic evaluation to facilitate the interpretation of the immunostained slides. Individual animal findings are presented in Section IV.
Representative histologically.
sections of liver, pancreas Each tissue section was stained
and with
testes from hematoxylin
22 and
monkeys were evaluated eosin. The purpose of this
evaluation was to determine whether or not morphologic changes were occurring in these tissues
that may alter or confound the specificityofthe PCNA staining observed in these animals.
The results staining in
showed that no significant this study were observed
changes in the
that would alter liver, pancreas
the interpretation of or testes from male
the PCNA monkeys.
Aoclctuhroruegdhacchrroosnsicallingfrloaumpmsa.tioFnurwtahserrmeoproer,tetdhefoPr CseNveArallabaenliimnaglsi,nditewxadsidminnoitmacolrrienlasteevewriittyhatnhde
observation animal with
of inflammation the highest liver
in the liver. For example, inflammation was not observed in the labeling index (animal [05706). Numerous findings were reported.
for animal [05724 that included hypertrophy, inflammation, fat infiltration and possibly bacterial
enn
Covance StudyNo. 6329-2M31 Draft Cell ProliferationPaRgeepolrat colonization. Based on the substantial non-specific PCNA staining observed in the liver of this animal, clearly these lesions confounded the ability to measure hepatocellular proliferation; therefore, no attempt was made to evaluate the PCNA labeling index in animal 105724, DISCUSSION In the present study, cell proliferation was measured within the liver, pancreas and testesofmale monkeys from control and treated groups after up to 26 weeks on study, as well as a recovery period. An increase in cell proliferation, as determined by the PCNA labeling index, was not observed in the pancreas or testesofmale monkeys. Cell proliferation in the liver, however, was equivocal. SUMMARY After up to 26 weeks on study, enhanced cell proliferation was not evident in the pancreas or testesof male monkeys, whereas in the liver the findings were equivocal LITERATURE CITED Eldridge, S.R., Butterworth, B.E., Goldsworthy, T.L. (1993). Proliferating cell nuclear antigen: a marker for hepatocellular proliferation in rodents. Environ. Health Perspec. 101: 211-218.
[LTE
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IIL FIGURES
Legend for data points on Figures III-1- 3
Group Treatment Day of Death
1 2
Omgkg/day Omgkg/day
26 weeks Recovery animal
3 4
3mgkgiday 10 mg/kgiday
26 weeks 26 weeks
5 6
10mgkg/day Recovery animal 30 mgkglday 26 weeks
7 8
30 mgkg/day 30 mgkg/day
Sacrificed day 29 Stopped dosing day 43
9 10
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IV. INDIVIDUAL ANIMAL HISTOPATHOLOGY FINDINGS ofa
Individual Animal Findings
Counce SudsynNo. 329231 Page V.1
26-WEEK CAPSULE TOXICITY STUDY WITH AMMONIUM PERFLUOROOCTANOATE (APFO) IN CYNOMOLGUS MONKEYS
ANIMAL SEX DOSE
NUMBER
GROUP
HISTOLOGIC FINDINGS
T5705 M
105714 M
105715 M
105725
M
10s718
M
105720 M
T0570
TM
105706 M
105717 M
105721
M
T Tver - chrome inflammation, minimal PTeasntcersea-scr- uasuhtoalrytsiifsa,ctfocal Spleen - NSF
' LPiavnecrre-acshr-oNnSicFinflammation, minimal Testes - NSF
! SLpilveeren- -NNSSFF TPeasntcersea-sN-SNFSF
1 SLipvleeren- N- NSSFF PTeasntcersea-sN-SNFSF
1 SLipvleeren- -NNSSFF Pancreas - NSF TSepslteeesn--cNrSusFh artifacts
' LBiavnecrre-aNsS-FNSF TSepslteeesn- NNSSFE
7 CPiavnecrre-aNsS-FNSF TSepslteeesn--NhSemFosiderin deposition, mild
2 LFiavnecrre-aNsS-FNSF TSepslteeesn -- NNSSEF
2 LPiavnecrre-aNsS-FNSF Tests- crush artifact
2 SLipvleeren- -chNrSonFic inflammation, minimal PTeasntcersea-sN-SNFSF Spleen - NSF
Legend: NSF = no significant findings
000.5
Individual Animal Findings
Covance Stud3yMNo. 6329-231 Page 1V-1
26-WEEK CAPSULE TOXICITY STUDY WITH AMMONIUM PERFLUOROOCTANOATE (APFO) IN CYNOMOLGUS MONKEYS
ANIMAL ~~ SEX NUMBER
DOSE GROUP
HISTOLOGIC FINDINGS
05707
TM
105708
M
10710
M
105712
M
105716
M
105719
TMM
105703
TM
10704
M
108711
M
105713
M
3 Tiver - NSF
Pancreas - NSF
Testes - NSF
Spleen - hemosiderin deposition, minimal
3 PLiavnecrre-aNsS-FNSF
Testes - NSF
Spleen - NSF
3 Liv- eNSrF
Pancreas - NSF
Testes - NSF
Spleen - NSF
3 Live-r chronic inflammation, minimal
Pancreas - NSF
Testes - NSE
Spleen - NSF
3 Liver - NSF.
Pancreas - NSF
Testes - NSF.
Spleen - NSF
3 PLainvecrre-aNsS-FNSF
Testes - NSF
Spleen - NSE
7 PLiavnecrre-aNsS-F.NSF
Testes - NSF
4
Spleen Liver -
- NSF chronic
inflammation,
minimal
Pancreas - NSF
Testes - NSF
Spleen - hemosiderin, minimal
4 Liver --chhermoonsiicdeirnifnl,ammmiantiimoan,l minimal
Pancreas - NSF
Testes - NSF
4 SLipvleeren- -chNrSonFic inflammation, minimal
Pancreas - NSF
Testes - NSE
Spleen - NSF
Legend: NSF = no significant findings
000557
Individual Animal Findings
Covance SnadayMNo. 6329-231 Page V1
26-WEEK CAPSULE TOXICITY STUDY WITH AMMONIUM PERFLUOROOCTANOATE (APFO) IN CYNOMOLGUS MONKEYS
ANIMAL SEX DOSE
NUMBER
GROUP
HISTOLOGIC FINDINGS
108722
M
105724
M
4 Liver - hemosiderin, minimal Pancreas - NSF Testes - NSF, Spleen - NSF
4 Liver - ppeerriippoorrttaall,, cfeatlliunlfairlrhaytpieonr,trsoepvheyr,esevere `pemriidpzoorntaall,, ncehcrroonsiics,imnofldaemrmaatteiotno,smeovdeerreate centrilobular, fat infilration, severe centrilobular, cellular hypertrophy, severe random distribution, bacterial colonies???
Pancreas - islets, at infiltration, mild to moderate Testes - NSF. Spleen - NSF
Legend: NSF = no sigaificant findings
000-30
V. SIGNATURE PAGE
Submitted by: Project Manager:
Sandra. Eldridge, Ph.D.
Date
Project Pathologist:
Carolyn Moyer, D.V-M., Diplomate, A.C.V.P.
Date
Qa
VI. QUALITY ASSURANCE STATEMENT 000s
EEH retPartohloolgogyyAAssssoocciiaatteess Iinntteerrnmaattiioonnaall SpE
----------------------------------------------------------------:
Cell Proliferation Report 26-Week Capsule Toxicity Study With Ammonium Perfluorooctanoate
(APFO) in Cynomolgus Monkeys
Covance Study Number: 6329-228
QUALITY ASSURANCE STATEMENT
This cell proliferation project has been inspected and audited by the PAI Quality
Assurance Unit (QAU) as required by the Good Laboratory Practice (GLP) regulations
promulgated by the U.S. Environmental Protection Agency. The cell proliferation report
iisnsapnectaicocnusr/aatuedirtesflpeecrtfioonrmoefd tahnedrreecpoorrdteedd bdaytat.he QTAhUe.following table is a record of the
Date of Inspection 1009//2065,/0979/00
09/06,07,25/00
Phase Inspected.
Date Findings Reported to PAI Management/Project Manager
PStCuNdyADDaitlautainodns/Staining
Supporting Documentation Draft Cell Proliferation Report
10/25/99
09/07/00 09/07/00
Qed) cnet
Doraine Dundee
Quality Assurance Auditor
Loa Tomn fut #5 2000
Date
00a"
15Worman'sMillCourt, Sue| Fradenck, Maryland 21701 + (301)663-(3101)68634-89494 FAX
APPENDIIX 00a:
Date:
Study Number:
Title:
Protocol Deviation 1.
Reason:
PROTOCOL DEVIATION REPORT
September 28, 2000
Covance Study No. 6329-231
26-Week Capsule Toxicity Study with Ammonium Perfluorooctanoate In Cynomolgus Monkeys
Representaive samples of liver, testes and paneress
were to be collected for cell proliferation
eSlviadleuaftoirocn,omwhliacihveinmcolrudpehdoplroegpiarmattieopnorfeaatnoHnXoEf
the cell proliferation findings. Samplesofspleen
were inadvertently submitted to PAI and the H&E slide examined for this tissue.
Spleen was inadvertently submitted The HAE
slide was inadvertently evaluated microscopically and the histologic findings reported. This deviation had no impact on the study.
Submitted by:
SPaAnIdrParoRj.ecEtldMraindgaeg,ePrh.D.
LrSe
Sandra R. Eldridge
PAI Project Manager
22p 00
Date
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3215T STORY of Level printed in FULL format. copyrightcopMyarningihntg P1u98b5liWcMaItioInnsc.;fnc 1386; BusVienremsosntoaBtuesliinnees;s anary, 1985
secTIoN: Sec 1; pg 24 LENGTH: 1745 words HEADLINE: Grand Tsle's one Manufacturer a One-of-a-Kind BYLINE: Michele Pacenauds DATELINE: South Kero; VE: US s00T:here is only one manufacturer in the entire county of Grand Isle -- Phoenix oWniere-ofIn-ca.-kiNnodtionnltyheiwsortlhde, faicrcmorudniinqguetoincoimtspancyounotfyf,icibaults.it is alse insu"lHaetedowiornelywointeh Ttehfilnogn,"."saTyhse Hcoomrpaacney'Csorbcilna,imthteo ffaimrem'sisprneostidiennti,nsu"lwaeting wiinrethewitwhorlTde.flon. Many companies do that. Phoenix insulates the tiniest mires hunaCnallhaeidr.micrSoingmlieniastturarnedswirceasn, besomveirocfualtlhyemianrveisisbelveeral times finer than a he TshteayrtewderweeatroiTnogmglPaasriszeos, siPxhomeonnitxh'ss vagioc.e pr"ePsrioddeunctt aqnudalpirtoyduhcats einmgpirnoeveerd, until cremendously since I got them." he jokes humaTnhesberaitninoyrwiarnesinmsatyrumeenndtuppanienlsounchtehextrspaaocredisnhaurtytlpel.acesTheascothmebiniantsiiodne ooff a msemdaillcinseizeandanedleTcetfrloonniccsoating makes them ideal in applications involving at IPnhomeonsitx ctaoseiststhfeinawlirehommeakeisn aa plioencgeanodf ecqoumipplmiecnatt,edsojoCuorrnbeiynfrisomnoittssourreigins wehaetraebliitshnaellntsendfsamuopu.s aBruotunNdAStAheiwsorald.regulHeardoceusstokmneorw afnord ssuorearethamtediictalis used in cardiac catheters (cubes), pacemakers, probes and sutures uniTqeufelopnr,opeartDiuePsontthattramdaekenamiet efsorpecpioallyltyetarpapfrloupcreitahteelenfeoroufsePTFiEn,sidheasthseomebody. Cthiesmsiuceasllayn.d fitluiidss,inwerhti;chitmakdeosssni'ttonreeacoft cthoeotshaefrestsumbasttearnicaelsssuacvhailaasblbeodyfor implantation in the body.
Also, because Teflon can be applied to wire in extremely thin layers, it is 00052"
Vermont Business, January, 1986
Pages
miadteealriaflosr
use for
eilnecmtirniicaatluriiznesudlaetlieocnt.ronics.
And it's one of the best of all
The modern
kmoisttcheobnvi-o- usisprtohapterntoythoifngTefsltiocnks-- tooneit. knowFnortothaatnyorneeasofnamisolmiearofwith
a
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scoimdpeansyt.reetOnliyn afivbeuilfduilnlg-taismesamanldl tawnodpaurnta-stsiummeingempasloyietsesprwoodrukctosn. theExcSeoputthfHorero
wLoirsdt-inogfs-moiuntThhoamfafsa'irRegister and the Yellow Pages, advertising is a
ptohopnOlehamcecexallCanorhbeoirndr,eercHeoifrvoeardces'oismseciownuidrsieicnatheiavnedhaodtfhebeheofnwirmst'hhsaotwnswaoblreykssa.maSnpaAagnneirsI,hridssohacystdoorcataortrecaecnatlled conference in Isreal. The wire had been coated at Phoenix. theCuUsntiovmeerrssitycaolfl Vferrommonats 2f0armialweasy asosutFhr.ance, India and Japan, and as nearby as
PhoeAnLiLx,chewhewroerk itis idsonceoatoenda tocusthteomspbaesciisf. iedThtehicckunsetsosmerandshcioplsort,he anwdirethetno Lsihvieppweidthbianckfitvoetmhielecsustoofmetrh.e buHsoirnaecses.andThOahtm,erpCroorbbaibnl,y masoreweltlhaansanTyomotPahreirzo, factor, is the reason for the plant's location on Station Road in South Hero
affoBredcsa,useGratnhdeyIasllle'slovLeakeliCvhianmgplnaeianr tehnevirwoantserofafnedrtthehebmoaatpiengrfeacntd pfliascheingtoitlive banedatewonrkp.athAnhdelpmsuckheetpo stahleeirspedoeplilgehtfrotmhebyeahtaivengdaispcaotvheretod tthhaetcobemipnagnyofdofort.he The fitiramnmyahinatradienrstoa pfirnodf.ileCosonspliowcuotuhselyy'dabhsaevnettoiscaamnoyufkliangdeoftheanbuiidlednitnigfyitnogmaskiegn
The location, for the business.
whiPlreodcuoctnivoenniernetquifroersthleittplreincsippaacle,s,
feisw
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COor3T
Vermont Business. January, 1986
Pages
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organization, one public and private
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volunteers
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000847
Vermont Business, January, 1986
Pag6e
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"We'"rWeitmhuc3h50happepoipelre dyooiun'gveitgotthi3s50wapyr.o"blems," Corbin says of the decision.
the Iptriwnacsipaalgs.ood Tchheoicleargfeorwimraenycoremapsaonnise,s ntohtatjhusatd bteheenpecrosaotnianlg pmirneifaetruerneceswiroefs
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for
(Corbin says it takes a minimum of two years to properly train an operator.)
worlEdvenwthouanleleydPhthoeenitxinywasTeftlhoenonilnysuolnaetedlefwti.resAmnudstsodocusbtuosmienresssfwriotmhalGlranovder the Zsle's one and only manufacturer
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The question is -- where?
LANGUAGE: ENGLISH
UMI-ACC-NO: 8602610
LOAD-DATE: October 9, 1995
008:4%
133
0008E5
Jon
IN THE UNITED STATES DISTRICT COU!
FO TEE OTDC+1] PYBawsoheeron
TWEINLNBAUNRT,EAJRALMETSENDNAAVNITD, TEERNWNIANNTJ,ADCKESLOLNA MARIE TENNANT, and SANDRKA. TENNANT,
red
Plaintiffs,
v
mSp imsmToEm | CIVIL ACTION NO. 699-0488
.1 DUPONT DE NEMOURS & CO, INC,
Defendant.
SECONDAMENDEDCOMPLAINT
Now come plaintiffs Wilbur Earl Teanass, Erwin Jackson Teanaat, James David Teanaat, Della Marie Tennant and Sandra K. Tennant ("Plaintifi") and state as follows for their Second Amended Complaint agaiast defendant E.I. DuPont de Nemours & Co, Inc. ("DuPoat") herein
NATOFUACRTIE ON
I This is a civil action for declaratory, injunctive, and equitable relief, monetary damages, and response costs incurred and to be incurred by Plaiatifs or bodily injury and property damage to Plaintiffs and ther property arising from the acts and/or omissions ofDuPont during the ownership and/or operation ofDuPont's Dry Run Landllin Wood County, West Virgiai, defined herein as the "Site" under the authority of (i) the Comprehensive Environmental Response, Compeasation and Liability Act of 1980, as amended ("CERCLA"), 42 U.S.C. 1 9601 et seq; (i) (he Federal Declaratory Judgment Act, 28 U.S.C. 2201 ef seq; (i) the Resource Conservation andRecoveryAct of 1976, 5 amended (`RCRA"), 42 U.S.C. 6901 et seq. the Clean Water Act, 2s amended ("CWA"), 33 US.C. 1251 ef seq; (+) the West Virginia Hazardous Waste
0a0::n
ManagementAct (the "Waste Act"), W Va. Code 2-1-1er seq. and (vi) princoifcpolmmeosn aw
JURISDICTION AND VENUE 2 This Court has jurisdiction over this action pursuant to: 23 US.C. 1331, 1332 1367, 2201. and 2202, Sections 107 and 113of CERCLA, 42 US.C. 9607 and 9613, Section 7002(2) of RCRA, 42 U.S.C. 6972(a), and Section 505o(fCaWA), 33 US.C. 1365(a). 3. This Cours has pendant and ancillary/supplemental jurisdiction over Plaintiffs claims arising under state statutory and federal and state common law. 4 Venues proipntehirs District pursuant to 23 U S.C. 1391(b); Sections 107 and 113 of CERCLA, 42 U S.C. 9607 and 9613; Section 7002(a) of RCRA, 42 U S.C. 6972(a); and Section 05(c) of CWA, 33 U S.C. 1365(c), because the discharge, disposal and/or release of solid, toxic and/or hazardous wastes, substances, pollutants, and/or contaminants that gives rise to these claims occurred and/orisoccurring in this District, because the real property that is the subjectofthis actions located within this District, and because a substantial partofthe events or omissions giving tise to these claims occurred and continues to occur within this District
PARTIES
5 PlaintiffWilbur Earl Tennant is an individual residing at Route 3, Box 17, Washington. Wood County, West Virginia 26181
6. Plaintiff Erwin Jackson Tennant is an individual residing at Route 3, Box 174. Washington, Wood County, West Virginia 26181
7 Plaintiff James David Temnant is an individual residing at Route 3. Box 372 Parkersburg, Wood County, West Virginia 26101
000:
S$ Plaintiff Della Marie Tennant is an individual residing at Route 3. Box 372 Parkersburg, Wood County, West Virginia 26101
9 Plaindff Sandra K Tennant is an individual residing at Route 3. Box 17. Washington Wood County. West Virginia 26131.
10. Defendant E 1 DuPdeNoemnourts ("DuPont") isa Delaware corporation authorized to conduct business in the StateofWest Virginia and has a principal place of business at 1007 Market Steet, Wilmington, Delaware 19895
GENERAL ALLEGATIONS 11. Since approximately 1952, DuPonthas owned and/or operated a facility known as the. E1. DuPont Dry Run Landfill located adjacent to Route No. 68 in the Harris District of Wood County, West Virginia. near the town of Lubeck, which facility i referred to herein as the "Site" and identified generally for illustrative purposes only as the "Site" on Exhibit A to Plaintiffs First Amended Complaint 12. During DuPonts ownership and/or operation ofthe Site, DuPont has disposedof one or more solid, toxic, andor hazardous wastes, substances. pollutants, and/or contaminants at the Site. including but limited to, asbestos, fly ash, bottom ash, boiler ash, coal ash, filter cake sludges. polyamides, acrylics. polyacetal, polyvinyl butyral, polyethylene terephthalate, fluropolymers, paraffin wax, sludges from DuPont's Washington Works plan, Siter aids, construction dirt, paper, cardboard glass, scrap piping and metals, and railroad tes. 15. During DuPont's ownership and/or operation of the Site, DuPont has failed to compact wastes appropriately at the Site.
00925
14 During its ownership and/or operation of the Site, DuPont has failed to adequate control fugitive dust at the Site
15 During its ownership andor operation of the Site. DuPont has failed to maintain adequate slopes of its landfil surface areas at the Site
16. During its ownership and/or operation of the Site. DuPont has failed to properl: control stormwater runoff at the Site.
17. During its ownership andor operation at the Site. DuPont has failed to adequaieis control landfill leachate and runoff at the Site.
1S. During its ownership and/or operation of the Site, DuPont has failed to install and or maintain an appropriate leachate collection and/or treatment system at the Site
19 Duringits ownership and/or operationofthe Site, DuPont has failed to install and or `maintain appropriate catch basins at the Site.
20 During ts ownershipandor operationof the Site, DuPont has failed to install and or maintain appropriately lined sedimentation/settling ponds at the Site.
21 During ts ownership and/or operationofthe Site, DuPont has filed to install and of maintain appropriaterunoffleachate diversion ditches at the Site.
22 During its ownership andlor operationofthe Site, DuPont has failed to appropriatels close and/or retrofit surface impoundments at the Site
23 During ts ownership andior operation ofthe Site, DuPont has failed to submit timel: notice ofits violation of applicable surface and/or groundwater protection standards at the Site
24 During its ownership and/or operation of the Site. DuPont has failed to nous: appropriate goverment officals that i changed the natureof the waste DuPont disposed at the Sie
4
000.37
35 During its ownership and/or operation of the Site, DuPont has disposed of wastes including cerain sludges, without first ubtaining appropriate government approvals.
26 During its ownership andior operation at the Site, DuPont failed to close a drain valve for one of its leachate'sedimentation ponds resuiting in the discharge of pollutants into the environment, including the nearby Dry Run stream
27 Asaresultof DuPont ownership andor operationofthe Site, one or more solid toxic and/or hazardous wastes, substances, pollutants, and/or contaminants have been and continue to be disposed, discharged, and/or otherwise released into environmental media at the Site (the "Contaminants"), including surface and groundwaters at the Site, including the nearby Dry Run stream.
23 Ac all times relevant hereto, Plaintiffs collectively have owned, leased, and/or otherwise possessed several hundred acres of real property adjacent and/or contiguous to the Site which properties are collectively referred to herein as Plaintiffs' Properties" and are depicied generally for illustrative purposes only as "Plaintiffs' Properties" on Exhibit A to Plaintiffs' First Amended Complaint
20 Acall times relevant heceto, one or moorftehe Contaminants originating from the Site have entered and continue to enter one or more portionsofPlaintiffs' Properties through various pathways, including but not limited to the Dry Run stream, resulting in the contamination of environmental media, including but not limited to soils and surface and groundwaters, at Plaintifts Properties (the "Contamination").
30. Several hundred ofPlaintiffs cattle have been and continue to be killed, injured. or otherwise adversely affected by the Contamination
00829
31 The Contamination has adversely impacted and continues to adversely impact flora and fauna at Plaintiffs Properties. and has impacted and continues to otherwise adversely impact the value of Plaintidfs Properties.
32 The Contamination has made and continues to make Plaintiffs physically ill or otherwise physically damaged, and has caused and continues to cause associated emotional and or mental stress, anxiety, and/or fearofcurrent and/or future illnesses.
(CERCLA) 33. Plainifls incorporate herein the allegations contained in Paragraphs | through 32 of this Complaint as iffully restated herein. 35 Plaintiffs and DuPont are each "persons" wichin the meaning of Section 101(21) of CERCLA. 42 USC 960121) 35. The Site is and was at all times relevant hereto, a "facility" within the meaning of Section 10o1fC(ER9CL)A, 42 U S.C. 9601(9) 36. At all times relevant hereto, and at the time of disposal andor release and or threatened release at the Siteof one or more "hazardous substances," as that term is defined in Section 101(14) ofCERCLA, 42 US.C. 9601(14), DuPont owned andor possessed hazardous substances and/or materials containing hazardous substances and by contract, agreement. of otherwise arranged for the treatment and/or disposalofsuch hazardous substances and/or materials containing hazardous substances at the Site, and is, therefore, a liable party within the meaning of Section 107(2)(3) of CERCLA, 42 US.C. 9607(2)(3).
6
[DER
37 At all umes relevant hereto, and at the time of disposal andor release and or threatened release at the Site of one or more "hazardous substances," as that term is defined in Section 10114) of CERCLA. 42 U.S C 9601(14), DuPont is andor was at the timeofdisposal of such hazardous substances, an owner andor operatorofthe Site and is. therefore. a liable panty within the meaningofSection 107(a)(1) and/or (2) of CERCLA, 42 US . 9607(a)(1) andor (2)
38 Ac all times relevant hereto, and at the time of disposal and/or release and or threatened releaseof one or more "hazardous substances, as that term is defined in Section 101(14) OfCERCLA. 42 US.C. 9601(1), DuPont is and/or was a person who accepts or accepted one of more such hazardous substances for transport to the Site and is, therefore, a liable party within the meaning of Section 107(a)(4) of CERCLA. 42 US.C. 9607(2)(4).
39. Asa result of the actions of DuPont as referenced in Paragraphs | through 38 above. a "release" and/or "threatened release," as those terms are defined in Section 101(22) of CERCLA. 42US.C. 9601(22), of one or more hazardous substanceshasoccurred, is continuing to occur. and all relevant times hereto was occurring at, under, and/or from the Site.
30 Plainifis have incurredand will continue to incur costs to investigate and/or otherwise respond to the release and/or threatened release of hazardous substances at, under, and/or from the Site, within the meaning of Section 101(25) of CERCLA, 42 U.S.C. 9601(25).
41 Plain actions takenin response to the release and/or threatened releaseofone of more hazardous substances at, under, and/or from the Site and the costs incurred incident thereto were necessary and undertaken in a manner consistent with the National Contingency Plan set forth at40 CFR Part 300
7
CO0:2
42 Plains have satisfied any and al conditions precedent to the undertaking of response actions, the incurrenceofresponse costs, and 0 the recovery of sich costs from DuPont under
CERCLA 43 Under Section 10o7fC(ER2CL)A. 42 US C 9607(a). DuPonits strictly liabl0e
Plaintiffs, jointly and severally, for all response costs, including prejudgment interest, incurred and to be incurred by Plaintiffs in response to hazardous substances at, under, and/or from the Site
43 Under Section 113(9)of CERCLA. 42 US.C. 9613(0), Plainuitfs are enviled to contribution from DuPont for DuPont's equitable share of all liability, response costs, and damages incurred and to be incurred by Plaintiffs in response to hazardous substances at, under, and/or from the Site
SECOND COUNT
(RCRA)
45. Plainiiffs incorporate herein the allegations set forth in Paragraphs | through 4 ofthis Complaint as iffully restated herein.
46. Plaiuifs and DuPont are each "persons" within the meaning of Section 1004(15) of RCRA, 42US.C 6903(15).
47 DuPont is a past or present generator, past Of present transporter, and/or past of preseat ownerand/or operator ofa treatment, storage, and/or disposal facility, who has contributed andlor is contributing to the past and/or present handling, storage, treatment. transportation. and of disposal of"solid waste within the meaningof Section 1004(27) of RCRA, 42 U'S.C. 6903(271 andlor "hazardous waste"vithinthe meaningof Section 1004(5) of RCRA, 42 U'S.C. 6903(5). x. under, and/or from the Site, which may present an imminent and substantial endangerment to health
s
009.2%
or the environment. within the meaning of Section 7002(a)(1)(B) of RCRA, 42 USC 6972(a)(1)(B)
33 Asa direct and proximate result of DuPont' acts and/or omissions contributing to the past andor present handling, storage. treatment, transporiation. and/or disposal of solid and or hazardous waste a, under, and/or from the Site, which may present an imminent and substantial endangerment to health or the environment, DuPont is lisble for such endangerment under Section 7002(a)(1)(B) Of RCRA, 42 US C. 6972()(1)(B)
49. DuPont does not dispute that Plaintiffs have complied with the notice requirements Set forth in Section 7002(b)(2) of RCRA, 42 US C. 6972(b)(2), and at least ninety (90) days hase past between the date of such notice and the date of filing this Second Amended Complaint.
50 Plaimiffs have complied with all conditions precedent to bringing their claim against DuPont under Section 7002(a)(1)(B) of RCRA, 42 U S.C. 6972(a)(1)(B), and no action has been taken which could prevent the filing of this RCRA claim under Section 7002(5)(2) of RCRA. 42 USC. 697206)(2)
SI. Plainiffs are entitled to an injunction against DuPont ordering DuPont to undertake andor pay for any and all investigations, studies. monitoring, response, removal, and remedial actions and/or any other activities and/or actions necessary and/or required to respond to, abate, remediate and/or otherwise address any environmental contamination a, under, and/or from the Site and of Plaintiffs' Properties that may present an imminent and substantial endangerment to health or tie environment, and ordering DuPont to take all such other actions as this Court may deem necessary pursuant to Section 7002(a)(1)(B) of RCRA. 42 U' S.C. 6972(a)(1)(B)
9
ean
THIRDCOUNT
(DECLARATORYJUDGMENT) 52 Plintifs incorporate herein the allegations set forth in Paragraphs | through 51 ofthis
Complaint as if fully restated herein. 53 Anactual. substantial andjusticiable controversy existsbetween Plaintifs and DuPont
regarding their respective rights and obligations for the response costs and/or damages that have been and will be incurred in connection with the release and/or threatened release of one or more hazardous subscances at. under, and/or from the Site.
54 Plaintiffs seek a declaratory judgment against DuPont under Section 113(g)(2) of CERCLA. 42 USC. 9613(g)(2), and the Federal Declaratory Judgment Act, 28 US.C. 2201. 2202, holding DuPont sricty liable, jointly and severally, for all and/or DuPont' equitable share of the response costs incurred and to be incurred by Plaintiffs that will be binding in any subsequent
"action to recover further response costs or damages.
55. Pursuant to Section 113(g)(2) ofCERCLA, 42 USC. 9613(2)(2), 2nd 28 US C 2201, 2202, Plaintiffs are entitled to a declaration from this Court that DuPont is strictly liable. jointly and severally, to Plaintiffs for all and/or DuPones equitable shareof the response costs and damages incurred or to be incurred by Plaintiffs
[EQURTHCOUNT (CLEANWATERACT) $6. Plaintiffs incorporate herein the allegations contained in Paragraphs | through 55 of this Complaint asoffully restated herein. 57. Plaindffs are each "citizens" within the meaning of Section 505(g) ofCWA. 33, US.C
1363(2).
10 00a:
53 DuPont is a "person" within the meaningofSection 502(5) of CWA. 33 USC 3 136205)
59 On April 14, 1998, the West Virginia Division of Environmental Protection ("WVDEP")renewed and reissued a National Pollutant Discharge Elimination System permit (Permit No. WN007(th6e "2Per4mit)'), to DuPont for water discharges from the Site through authority of Section 1342 of CWA, 33 U'S.C. 1342
60 Monthly monitoring reports submitted to WVDEP by DuPont for at least the months of May, July, and August. 1998 confirm that DuPont has discharged and continues to discharge waste from Outles 001 at the Site in amounts and concentrations that exceed applicable limits established under the Permit for atleast iron, manganese, aluminum, and total suspended solids, thereby violating atteast conditions Al, B.1, C.1. C3, C12, 0.1, F2,F.3,F4, G.7, and G.17 of the Permit
61 Monty monitoring reports submitted to WVDEP by DuPont for atleast the months of May, July, and November of 1998 confirm that DuPont has discharged and continues to discharge waste from the Site into the nearby Dry Run stream in amounts and concentrations that exceed applicable limits established under the Permit for at least aluminum and iron, thereby violating at least conditions C.1, C3, C12, D.1, F2,F.3, F4, G7. G3, and G.17ofthe Permit
62. Monthly monitoring reports submitted to WVDEP by DuPont for at leas the months of May, July, August, and November of 1998 confirm that DuPont is currently in violation of at least Paragraphs 1 and 3of the Compliance Order set forth on Page 4 of the April 14, 1998, Findings and Order issued by WVDEP to DuPont as a result of violations of the CWA and Permit standards and limitations referenced above (Findings and Order No. 4015)
n
COREY
63 DuPont' continuing and on-going violations referenced above constitute continuing and on-going violationsofat least Sections 301(a) and 405(a)of the CWA. 33 USC 1314(a 1345(2). and Sections 22-11-6, 2211-8, 22-11-16, and 22-11-13 of the West Virginia Water Pollution Control Act, W.Va. Code 22-11-1 ef seq. (collectively the "Law")
63 The Permit limits, Law, and compliance order provisions referenced above constitute "effluent standards or limications" within the meaningof Section S05(9)of the CWA, 33 S.C 13650)
65 By vine ofDuPont's violationsof the effluent standardsorlimitations referenced above, DuPont is in violation of "(4) an effluent standard or limitation under this chapter or (B) an order issued by the Administrator or a State with respect to such a standard or limitation" within the `meaning of Section 505(a)(1)ofthe CWA, 33 U S.C. 1365(a)(1)
66. DuPont does not dispute that Plaintiffs have complied with the notice requirements set forth in Section 05(b)(1)(A) of the CWA, 33, US.C. 1365(b)(1)(A), and at least sixty (60) days have passed between the date of such notice and the date of filing this Second Amended Complaint
67 Plainiffs have complied with all conditions precedent to bringing their claim against DuPont under Section 1363(a)(1)ofthe CWA, 33 US.C. 1365(a)(1), and no action has been taken which could prevent the filingofthis CWA claim under Section 505(b)(1)(B) of the CWA, 33 U'S C 1363(5)(1)(B)
63 Plainiffs are entitled to an injunction against DuPont ordering DuPont to comply with the effluent standards or limitations and compliance order referenced above, to pay appropriate civil penalties under Section 309(d)of the CWA, 33 USC. 1319(d), to pay all costs of litigation
12
eon"
including reasonable attomey and expert witness fees) and to take all such other action as the Cour: may deem necessary, pursuant to Section SO3()(1)ofthe CWA, 33 US C. 1363(ai(1)
WEST VIRGINIA HAZEAIREDTOHUSCOWUANSTTE MANAGEMENT ACT) 69 Plaindff incorporate herein the allegations contained in Paragraphs | through 67 of this Complaint as iffully restated herein 70. Plaintiffs and DuPont are each "persons" within the meaning of Section 22-13-31) of the Waste Act, W Va. Code 22-18-3(11) TL As a result of the acts andor omissions of DuPont as referenced in Paragraphs | through 70 above, DuPont has and continues to operate the Site in violation of applicable permit requirements set forth in Section 22-18-3 of the Waste Act, W.Va. Code 22-18-8. 72. As a result of the acts and/or omissions of DuPont as described in Paragraphs | through 71 above, Plaintiffs are entitled to bring a citizens suit against DuPont to obrain DuPont's compliance with applicable aw, pursuant to Section 22-18-19(a) of the Waste Act, W.Va. Code 2313-19(a). 75. Dupont does nor dispute that Plaintiffs have complied with the notice requirements set forth in Section 22-18-19(a)ofthe Waste Act, W Va. Code 22-18-19(a), and at least sixty (60) days have passed between the date of such notice and the date of filing this Second Amended Complaint. 74 Plaintiff have complied with all conditions precedent to bringing their claim against DuPont under Section 22-13-19(a) of the Waste Act, W.Va. Code 22+18-19(a), and no action has
[H
000525
been taken which could prevent the flingofthis Waste Act claim under Section 32-18-1901 of the Waste Act, W Va Code 22-13-19(2)
75 Plainifs are entiled to an injunction against DuPont. ordering DuPont t0 comply "sit the requiremenstest forthin Section 22-188ofthe Waste Act. W.Va. Code 22-158. and ordering DuPont to take al such other action as this Court may deemed necessary, pursuant to Section 22-15 19(a) of the Waste Act, W Va, Code 22-18-19(2)
SIXTHCOUNT
76 Plainifs incorporate herein the allegations contained in Paragraphs | through 7% of this Complaint as iffully restated herein
77 To the ent Plaintiffs have incurred damages and response costs and will continue to incur damages and response costs inthe future in response to the release and/or threatened release ofone or more solid, toxic, and/or hazardous wastes, substances pollutans, and/or contaminants at under, and/or rom Site, DuPont is liable, jointly and severally, to Plaintiffs for contribution pursuant to Plaintif rightof contribution arising under Federal and State common law and applicable statues
(NEGLIGENCE) 78 Plaintiffs incorporate the allegations contained in Paragraphs| through 77of this Complaint asiffully restated herein. 79. In connection with ts ownership and/or operationofthe Site, DuPont has had and continues to have a duty of ordinary and reasonable care to operate and manage the Site in such + way 2s 0 not create & nuisance or situation causing any injury or damage to human health or the environment
14
00aL2T
30 DuPont breached its dutyofordinary and reasonable care by negligently operat and/or managing the Site andor conducting other operations and/or activities at the Site in such a manner as to cause, permit, and or allow the release and/or threatened releaseof solid, toxic. and or hazardous wastes. substances. pollutants. and/or contaminants at, under, andor from the Site
$1 DuPonts negligent acts and/or omissions proximately caused and continue 1 proximately cause damage to Plaintiffs in the formofproperty damage and bodily injury, in addition to creating a situation harmul to human health and the environment, for which DuPont is liable
EIGHTH COUNT
(NEGLIGPEENRSCEE)
82. Plainiffs incorporate herein the allegations contained in Paragraphs | through 81 of this Complaint as if fully restated herein.
$3. Byits acts and/or omissions resulting in the release and/or threatened release of one ormore solid, oxic,and/or hazardouswastes, substances, pollutants, and/or contaminants at. under. andlor from the Site, DuPont violated and continues to violate one or more applicable State and or Federal statutes, including but not limited to Sections 22+11-6, 22-118, 22-11-16, 22-11-18, 22:15 10, and 2218-8ofthe West Virginia Code, constituting negligence per se.
34. DuPont's violation of law proximately caused and continues to proximately cause damage to Plaintiffs in the formof property damage and bodily injury for which DuPont is lizble
NINTH COUNT
(NUISANCE)
85. Plains incorporate herein the allegations contained in Paragraphs | through $4 of this Complaint as if fully restaced herein.
is
06529
86 DuPont's acts and/or omissions in operating and/or otherwise managing the Site caused and continue to cause a substantial and unreasonable interference with Plains use and enjoyment of Plaintiffs' Properties and has materially diminished and continues to diminish the value of Plaintiffs Properties
$7. DuPont's substantial and unreasonable interference with the use and enjoyment of Plaintifs' Properties and continuing substantial and unreasonable interference with such use and enjoyment of Plaintiff' Properties constitutes a continuing private auisance
88 DuPont' creation and continuing creationof a continuing private nuisance proximately caused and continues to proximately cause damage to Plaintiffs in the form of property damage and bodily injury, including diminution in the value of Plaintiffs' Properties, for which DuPont is liable.
TENTHCOUNT
(TRESPASS)
89. Plainiffs incorporate herein the allegations contained in Paragraphs | through S8 of this Complaint as iffully restated herein.
90. DuPont acts andlor omissions resulting in the release and/or threatened release of one or more solid, toxic, and/or hazardous wastes, substances, pollutants, and/or contaminants at under. and/or trom the Site have resulted and continue to result in the release and/or threatened celeaseof one or more such solid, toxic, and/or hazardous wastes, substances, pollutants, andor contaminants at, under, onto, and/or into Plaintiffs' Properties.
91 The solid, toxic, and/or hazardous wastes, substances, pollutants, and/or contaminants present on Plaintiffs Properties originating from the Site were at all relevant times hereto. aad continue to be, the property of DuPont.
16
000s
92 The invasion and presence of DuPons solid. toxic, andor hazardous wastes. substances, pollutants, and/or contaminants at. under, onto, and/or into Plaintiffs' Properties was and continues to be without permission or authority from Plaintiffs or anyone who could grant such permission or authority
93 The presence and continuing presence of DuPont' solid. toxic, and/or hazardous wastes, substances, pollutants, and/or contaminants at Plaintiffs Properties constitutes a continuing trespass
94. DuPont past and continuing trespass upon Plaintidfs' Properties proximately caused and continues to proximately cause damage to Plaintis in the form of property damage and bodily injury, including diminution in the value of Plaintiffs' Properties, for which DuPont is liable.
(PUNITIVE DAMAGES) 95. Plainiffs incorporate herein the allegations contained in paragraphs | through 94 of this Complaint as iffully restated herein. 96 DuPonts acts and/or omissions as described above were conducted with such malicious, wanton, willful, and/or reckless indifference to Plaindiffs rights and/or flagrant disregard for the safety and/or propertyof Plaintiffs that DuPont is lable for punitive damages. WHEREFORE, Plaintiffs hereby demand tha this Court A Entera judgment against DuPont, pursuant to Section 107of CERCLA, 42 US C 9607, that DuPonti strictly lable, jointly and severally, to Plaintiffs for all response costs and damages that Plaintiffs have incurred and will incur in connection with the release and/or threatened
7
conuen
eiease of hazardous substances at, under, and/or from the Site in an amount according 1 the proof at rial, plus attorneys' fees (to the extent recoverable). costs. and prejudgment interest
B In the alternative. enter a judgment against DuPont. pursuant to Section 113) of CERCLA, 42 U'S.C. 9613(t). that DuPont is siriclyliable to Plaintiffsfor DuPoncsfair. equitacle. and proportionate contribution for all response costs and damages that Plaintis have incurred and will incurin connection with the release and/or threatened release of hazardous substances at, under and/or from the Site in an amount according to the proof at trial, plus attorneys' fees (10 the extent recoverable) costs, and prejudgment interest;
C. Ena dteclaeratrory judgment against DuPont, pursuant to Sections 107 and 113() of CERCLA, 42 U.S.C. 9607, 9613(g), and/or 23 US C. 2201, 2202 that DuPont is strictly liable, joinly and severally, to Plaintiffs for all response costs and damages that Plaintiffs have incurred and will incur in connection with the release and/or threatened release of hazardous substances ar, under, and/or from the Site in an amount according 10 the prooaft rial. plus attorne:s fees (to the extent recoverable) costs, and prejudgment interest;
D. Inthe altemative, enter a declaratory judgment against DuPor, pursuant to Section 115(6) and () ofCERCLA, 42 U.S.C. 9613(9. (), and/or 23 U S.C. 2201, 2202 that DuPont is suictly liable to Plaintiffs for DuPont's fair, equitable, and proportionate contribution for all response costs and damages that Plaintiffs have incurred and will incur in connection with the release andlor threatened releaseofhazardous substances at, under, or from the Site in an amount according to the prooaft trial, plus attorneys' fees (to the extent recoverable), costs, and prejudgment interest
E Eneraninjunction against DuPon. pursuant fo Section 7002(a)(1)(B) of RCRA. +2 USC. 6972(a)(1)(B), ordering DuPont to undertake and/or pay for any and all investigations.
13
eoosen
studies. monitoring, response, removal, remedial, andor any other actions necessary aon fothders nc required to respond to, abate. remediate. and/or otherwise address any environmental contamination at. under. and'or from the Site and/or Plaintiffs Properties that may present an imminent and substantial endengerment to health or the environment, and ordering DuPont to pay all costs of litigation (including reasonable attorney and expert witness fees) and prejudgment interest.
F Enter an injunction against DuPont, pursuant to Section S05(a)(1) of the CWA. 33 USC. 1365(a)(1), ordering DuPont to comply with the effluent standards or limitations and compliance orders that DuPont is violating, to pay appropriate civil penalties under Section 309) of the CWA, 33 US.C. 1319(c), and ordering DuPont to pay all costsoflitigation (including reasonable attorney and expert witness fees) and prejudgment interest,
G. Enteran injunction against DuPont, pursuant to Section 22+18-15(a)of the Waste Act W.Va Code 22-18-15(a), ordering DuPont to comply with applicable provisions of Section 22-18 $ of the Waste Act, W.Va. Code 22-138, and ordering DuPont to pay all costsofliigaticn (including reasonable attorney and expert witness fees) and prejudgment interest
H Enter a judgment against DuPont under Federal and/or State common law thit DuPont is liable to Plaintiffs in contribution for DuPont's fair, equitable, and proportionate share of al liability. response costs, and damages incurred and to be incurred in connection with an: environmental contamination at the Site;
I Enterajudgment against DuPont that DuPont is liable to Plaintiffs for negligence in an amount to be determined a trial;
J Entera judgment against DuPont that DuPont is liable to Plaintiffs for negligence per se in an amount to be determined at trial:
19
eRuEe
K Enterajudgment agains: DuPont that DuPont is liable to Plaintiffs for nuisance in 40 amount to be determined at rial;
L Emerajudgment agains: DuPont that DuPonti liable to Plaintiffs for trespass in an amount to be determined at trial;
M Enter a judgment against DuPont that DuPont is liable to Plaintiffs for punitive damages in an amount to be determined at rial, and
N. Eneajudgment agains: DuPoat for Plaintify costs, attorneys' fees, and interest and all such other and further relief as this Court may deem just and appropriate
JURY DEMAND Plaintiffs hereby demand trial by jury on all issues so triable.
TWEINLNBAUNRTE,AJRALMTEESNDNAAVNITD, TEERNWNIANNJT,ACDKESLOLNA MARIE TENNANT, and SANDRA K. TENNANT
Larry A Winter Carey. Hill, Scott. Winter & Johnson PLLC P.O Box3884, Charleston, WV 25338 (304) 345-1234 Robert A. Blot J Steven Justice Ta, Stettinius & Hollister LLP 1300 Firstar Tower 425 Walnut Street Cincianati, OH. 45202-3957 (513) 381-2838
0 0po5eY
CERTIFICATE OF SERVICE hereby certify thaat filed, date-stamped copyof the foregoing Second Amended Complaint, which was filed with the Court on October 21, 1999, was served upon the following parties by regular US. mail. postage prepaid, this 21" day ofOctober, 1999
`The Honorable Janet Reno Attorney General of the United States S111 Main Street Building 10 Street and Constiution Ave, N.W. Washington, D.C. 20530 Carol Browner, Administrator United States Environmental Protection Agency 401 M Street, SW. Washington, D.C. 20460 W. Michael McCabe, Regional Administrator United States Environmental Protection Agency, Region [11 1650 Arch Street Philadelphia, PA. 19103-2029 Michael Miano, Director WV Divisionof Environmental Protection 10 Melunkin Road Nitro, WV 25143 Eric M. James, Esq Paula Durst Gillis, Esq Spilman, Thomas & Battle P.O Box 273 Charleston, WV 25321
Larry A Winter
000%;
SStEinEssWeheCaney Pr8iConrr rata [ FlR v Sp ew
Gena seo
CAREY. ILL. Sn C1O30T1TB.ae sWkIOnNeTCe EoRre&n JoHyso.
CHARLESTON.PWOEBSoxT3V8IaRGINIA 25338
October 21, 1999
LicovoreeivOedCT- I25s2a5t wy.
unTea ososes roiieen Ema smears chon vorn
we fon
Samuel L Kay. Clerk United States District Court PO Box 1526 Parkersburg, WV 26101
Re: Wilbur E. Tennant, etal. v. EI DuPontde Nemour&s Co. Inc. Civil Action No. 699-0438
Dear Mr Kay, civil action. Lenclose herewith a Second Amended Complaint for filing in the above-referenced
Thank you very much for your assistance in this matter. [f you have any questions. please do not hesitate to contact me.
Very truly yours,
LAW sms Enclosure cc: The Honorable Janet Reno
Carol Browner W Michael McCabe Michael Miano, Eric M. James, Esq Paula Durst Gills, Esq.
Larry A. Winter
oan
TAFT, STETTINIUS & HOLLISTE.. LLP
IPA,
513.381.2838
res oat Crate St
hSotm
August 18, 1999
RREEGTIUSRTNERREEDCEIMPATILRNEoQ.UESRT4E1D0003615 $S0t10a7tDuMutasororknyettAgdeeSnttrNeeemtours & Co., Inc.
wilmington, DE 19898
RE ct E
dS,
Re: Notice Of Intent To Amend Complaint To Bring Citizens Suit Under Federal Clean Water Act In Connection With
CVDoiurrtPgoinntIi'nasc:. DrT(ye5nDnR.aunntu,.Lvaan.edtfiCalli.lvilIv.nAcWBt.o1io.odnbCuoNoub.notnyts,:d3W9ee-s0Nt4e5m5ours & Dear statutory Agent:
On behalf of our law firm's clients, Wilbur Earl Tennant (Route 3, Box 17, Washington, West Virginia 26181), Erwin Jackson
Tennant (Route 3, Box 17A, Washington, West Virginia 26181),
James David Tennant (Route 3, Box 372, Parkersburg, West Virginia
26101), Della Marie Tennant (Route 3, Box 372, Parkersburg, West
Virginia 26101),
Washington, West
VainrdgiSnainadra261K8.1)Ten(ncaonltlec(tRiovuteely 3,theBox"Te17n,nants),
E.I. DuPont de Nemours & Co., Inc. (*DuPont) is hereby notified
that the Tennants intend to amend their Complaint currently
pienndtihengSoaugtaihnesrtn DDuiPsotnrtictinoftheWesrtefVeirregnicneidaactotiborninign aFedcelraailm Court against Dupont, pursuant to Section 505 of the Federal Clean
Water Act, as amended ("CWA"), 33 U.S.C. 1365.
Section 50S(a) (1) of the CWA permits the Tennants to
commence a civil action against "any person . . . who is alleged to be in violation of (A) an effluent standard or limitation
under this chapter or (B) an order issued by the Administrator or State with respect to such a standard or limitation." 133 U.S.C.
1365(a)
the CWA
t(o1).incl"uEdfef,lueanmtongstoatnhdearrdtohringlsi,mit"aatipoenr"mitisordefcionnedditiuonnder
thereof issued under Section 1342 of this title, which is in effect under this chapter (including requirement applicable by
reason of section 1323 of this title)." Id. at 1365(f).
eases
SAutgautsuttor1y8, Ag1e9n9t9 Page 2
the stBaatseedofupoWensta Vriervgiienwiao'fsthDeiviisnifoonrmoaftioEnnvpirroovnimednetdaltoPdraotteectbyion t(h"eWVTDEeRn"a)ntisn hraevsepondseetertmoinaedFretehadtomDoufPonItnfoisrmcatuirornentAclty irenquest, pveiromliattiorneisofsueatd tloeasDtupotnhte fbyolWlVoDwEiPngonprAopvriislion1s4, of199t8h,e uNPnDdEeSr areustpheocrtitytoofdisScehcatrigoens 13f4r2omofDuptohnet'CsWADr(yPeRrumint LNaon.dfiWlVl007i6n24W4o)odwith County, West Virginia:
1. Mfoornthatlylmeoanstitotrheingmonrtehpsortofs Msauyb,miJtutleyd, toandWVADuEgPusbty, Du1P99o8n,t
dciosncfhiarrmgethawtastDeuPofnrtomhaOsutldeitsch0a01rgeatd tahned DcuoPnotnitnueDsrytoRun
Laapnpdlfiiclalbleinpearmmoiutntslimaintdscofnocrenattralteiaosnts itrohna,t meaxncgeaendese,
aatlumlienausmt, caonnddittiotoanls
suspended A.1, B.1,
solids, thereby C.1, C.3, C.12,
violating D.1, 7.2,
F.3, F.4, G.7, and G.17 of Permit No. WV0076244.
2. Mfoorntahtlylmeoanstitotrheingmonrtehpsortofs Msauyb,miJtutleyd, toanWdVDNEoPvembbyerDuoPfont t1o398d,iscchoanrfgiermwatshtaet DfurPoomntthehasDuPdoinstchaDrrgyedRunandLacnodnftiilnlues cinotnocentthreatnieoanrsbythDarty eRuxnceesdtraepapmliicnabalmeoupnetrsmiatndlimits for catondlietasitonsaluC.m1i,numC.3a,ndC.i1r2o,n, D.t1h,erFe.b2y, viF.o3l,atiFn.4g, aGt.7l,east G.8, and G.17 of Permit No. WV0076244.
informInataidodnitpiroond,ucetdhetoTednantaentsbyhaWvVeDEPdettheartmiDnuePdonftromisthceurrently in vsietolaftoirotnh oofn Patagelea4stofPtahreagArapprhisl 114,and19938,ofFtihnedinCgosmplainadncOerdeOrrder sitsasnudeadrdbsy WorVDElPimittoatDiuoPnosntraesferaenrceesdultaboofvevi(oFliantdiionngsofandtheOrCdeWrA No. 4a0l1s5o).ConsTthietuctoenticnounitnignuianngd ovino-lgaotiinognsviooflataitonlseasrtefeSercetnicoendshe30r1e(ian) aSnedcti4o05ns(a)22-o1f1-t6h,e C2W2A-,11-383, U.2S2.-C1.1-16, 13a1n1d(a2)2,-111-31485(ao)f, thaendWest Virginia Water Pollution Control Act, W.Va. Code 22-11-1 etseq.
referAesnceidndiicnattheids abnoovtei,ce thaere cboansteidnuuipnogn antdhe oni-ngfooirnmgatviioonlatthiaotnshas WaVcDtEuRa'lslypubbeleinclpyr-oadvuacieldabtloedaftielesbymaWVnDyEPo.f tWhee mdoindthnloyt, fqiunadrtweirtlhyi,n atnodWUaDnEnuPalundmeonrittohreintgermrsepoofrtsPertmhiatt DNou.PonWtV00i7s62r4e4q.uireThdust,o stuhbemit
eoates
sAutgautsuttor18y, Ag1e9n9t5 Page 3
Tennants reserve their right to allege and assert additional violations of the CWA, if additional information is obtained from WVDEP, U.S. EPA, or any other source indicating additional CWA
vTaiegonalnianatsnittosnDsu.iPnotnetnNdevientrotthhaeemleenasdbso,vteh-DeuirPreofneCtroemnpiclsaeidhnetrleibtciyugrnartoeitnoitnfliyetdpoentidhnaictnlgudtehe a referenced above. citizens suit claim against DuPont, pursuant to Section 505(a) (1)
of the CWA, within sixty (60) days after issuance of this notice to obtain relief at least for DuPont`s violations of the CWA
The following are receiving copies of this notice.
1. ACdamrionlisBtrroawtmoerr
REGISTERED MAIL NO. R410009616 RETURN RECEIPT REQUESTED
UniPtreodteScttaitoensAEgnevnciyronmental
4W0a1shiMngSttorne,et,DC5.H2.0460
:
2. RW.egiMoincahlaelAdmMicnCaibsetrator
RREETGUIRSNTERREECDEIMPATILRENQOU.ESRT41E0D009617
United States Environmental
165P0rotAercchtioSntreAgeetncy, Region III
Philadelphia, PA 19103-2029
3. MDiicrheacetlorMiano
REGISTERED MAIL NO. R410009620 RETURNRECEIPT REQUESTED
WesEtnviVriorngmiennitaalDivPirsoitoenctoifon
10 McJunkin Road
Nitro, WV 25143
4. RegE.iIs.teDruepdonAtgendte Nfeomrours CT&ccoor.p,oraIntei.on System 7C0h7arlVeisrtgoinn,iaWVStre2e5t3,01East
RREETGUIRSNTERREECDEIMPATTLRENQOU.ESRT4E1D0009621
earn
Asutgautsuttor18y, Ag1e9n9t5 Page 4
5. Paula Durst Gillis, Esq
REGISTERED MAIL NO. R410009622
SSppiillmmaann cThoonmcaesr & Battle, PLLC RETURNRECEIPTREQUESTED 230000. KBaonxawh2a73 Boulevard, East Charleston, WV 25321-0273 very ~t~ri/lyyous /\ ,
& ft / [= Ll
Liert A.L8TTyok~ie" L
#28 mdm
cc: WEJairmlwebisunrJDaEacavrkilsdonTTeenTnnneaannnnttant
DSealnldaraMXa.rieTenTneaanmtant
.
Larry A. Winter, Esq.
.
J. Stephen Justice, Esq.
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rer wo - v `RETURN excazerREQURETER Owrt.ticweilolfiaWmat0.erBrRaezsaoouar,cesAccisg Chist DC1i2hv0a1irlseiGsortenoenon,fbriEAenvrviS2r5to3rn1em1eetntal Protection Attpacion: Iaduscrial srasch Re: WU/NPDES Permit Nusher KVOOTEAL
Deaz wr. Brasson
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Zinncdluossterdialis2atshaeti1l9l9.9 anaual report sumarizisg the operations of our Dry Run c2alyoumehaovne8a6n3y-42q7u1estions ox seed additional information, please Very truly yours,
RSt.LFuaviiczocnnaesyntal Control Consultant Washington Wozks
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1229CRYRUNLAVDEILL OPERATIONAL 8220RT Bain Works siAellanhdetwsasstue diisspo,sed of i the Dry Run Landfill rginaes rom E. I du Pout nd Company, Washisgton
LandSillShipments.
Asmamaofrthye 1999 lands shipments s atached.
Surface andGroundwaterMonitoring A summary ofthe 1999 surface and groundwater monitoring activities is attached.
LandsillOAppeprratoixoinm.Caotnesltyruc6.1taicornesaonfdeMsacihnatetnaconlcleeActcitoinsviyttySeummwmearreyconsucdiureindg 1999 at the andfil. Project work included consucion of:
26p7mr,ep0iar0a0ttieosnxq,uuar1rt,ed67fH0eDtlP(i6Ee.1sgesfoeexmteeson)fabornfaclzeheao,crhHawtDeenPccEohld,lre1ac6itniooaungnescyees/tts,eqm.u10aTroiuysaacriednlcmslqouudoaewrdeosyvuaebrgdgraeaoodieoewxivleea seotextle, aad 12-inch sol aye.
2= 33961,0043le0litinneeoaafrfo8fs-etoitfcohifdnoicmcehthedridapiemaremfteoetrrealtreepadecrhHfaoDtrePastEeeedppiHpcDeolPlleeEcatcpihoianptederlcaeaialnce.hcatieoncodlraeicni.on drain. + 1,6O0Dn9l0einlgeianurefvaercefteatf24o-fisinpcrhadpiadimtecthe.r comugatedmetalpipe culvert. Revegetation of 12 acresofdiswbed area. spproximAtneleyxi3st5ingfelatnodfslpidaepwadsiatlcshorreecopmisrneudctjesdt.sou ofthe andlarea,Theareawasregradedand hroughAoucthte cooreylseysst.lem2.t9oeemnilalobiloentgnraulclkontsroafnslpeoarcthaotfleewaecrheatGe gaenaersabfotypWtaehsdoehilnragndtftoilnlWeroermdkaisneodrinwseearvmimceenit 1999. seacheAd aupdatedtopographicmap ofth andland crosssection apshowiagtelandfillspacefilled s
2
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DovRunLandfillRemainingCapasityCaloultions
`Calculationof1999Gl NetWasteFillVolumeMethod:
Waste vo=lu3m,e85h7autlreudckinl1o999ax:3d9.s7 yd3truckload(avg) = 153,123 153,000 y&3
Average netwaste compaction (dailycover allowance include)d estimataetd 80% for 1999:
Taal 1999 ill volume = 153,000 x 80% = 122,400ya
122,400 ~ 122,000
|
(eRxiasvtiingoecel#l1) Cbaepgaicnintiynrgeomfa1i9ni9n9g a he = somos
Capacity used in 1999
= 2200058
Cbaepgaicniitnygroefma2i0n0in0gate = 6800038
Based on 122,000 yd3 per year se ill volume consumption:
688,000yd3 122,000 = 5.6voarsremainingieonexitingsell
009%:
9
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Mueal Coal Ash GPlaapsesr,, MCiasrdcbeolaarndc,ouWsood NSoolniadssb,eMsetaols,lasulation P(PlPoaolslytysiaccmeWiaadlse,stP,easAlcyrcytlhiyclse,neTFelrueoprhoiptoallytmee,rs) Dinfl
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1999 DRYRUNLANDFILLSHIPMENTS
SuNupmmbeernosf 1294 us
ToTuolmWesight 18.604
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TotPaloWuenidghst 37,207,060 81,529340 15230320
2490620 136,465,340
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END076137
23
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1999DRYRUNLANDFILLQUARTERLYLEACHATEANALYSIS REPORTSUMMARY
DateSubmited.
Report
017000009999 11400
T`SheicrodnQduQauratretrerLeLaecahcahtaetMeoMnointiotroirnigngReRpeoprotrt Fourth Quarer Leachate Monitoring Report
DateSubmited. o1m00e199
14/00
Report `"STehcirodnQduQauratretrerPoPnodndUsUdnedredrrdarianiMnoMnointiotroirnigngReRpeoprotrt Fourth QuPaondrUndeerdrrain Monitoring Report
DateSubmited. 04/1399 0170/0062/9999 01/0700
Report `FiSresctoQnudaQrutaerrteMronMiotnoirtionrginWgelWlelRlepRoerptort `TFhoiurrtdQhuQauratretrerMoMnoiatiotroirinngWgeWlelllReReppoorrtt
DateSubmited
Report
172100
SecondHalfStormwater Monitoring Report
= No samples obtained for firsthalfstormwatermonitoringreportbecause ofack ofadequate rainfall.
9
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EID076138
a
ozs DateSubmitted avons ous asus asians
07115199
08/13/99
09/16/99
102089 108s 122009 ozo
Repors
JanuaryDischacge Monitoring Report FebruaryDischarge MonitoringReport Mace DischargeMosioringRepos Ape Discharge Monitoring Report MayDischarge MonitoringReport
June Discharge Monitoring Report
July Discharge Monitoring Report
`August Discharge Monitoring Report
September Discharge Mosioring Repo Octobe Discharge MostoringReport NovemberDischargeMonitoringReport Desembe DischargeMoitoisgReport
ot oes ctaded wih errors ted sve No bess surveys performed din heyes bessofcxemely dey washer,
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DRYRUN LAND/FISLLURFACE
OUNDWAT12E90R ITEC R ANITL ORING
GURMMNARYAFLC-1Y43*TWA
MO RESULTS
SA O F
Sample Date: 072299 Sample Location. Well #6A wets Well #124 wen #128 well #13 We #134
EC:143Remit gL) 0096 0134 0081 54 36 0070
Well #14
25
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0263
Sample Date: 122999
SampleLocaiion.
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Steam Sampling Son No. 1
ose
Sucam Sampling Soa No. 2
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Property Lise
39
* FC-143 is ammonium perfuoroocianoate iosic srfctant
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006831
EIDO76141
ET
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RLR/OVPLA
1995 ANNUAL LANDPILL REPORT HU/NPRESPERMIT NMRSR.WVQQIS244 (Letter, R.L. Ritchey to W.D. Brannon, dated 01/31/00)
BCC: AM..A.V. BMraaldilneoyw,skiS,pilLmeagna,l,ThDo7m0a7s8 & Battie AWso.L mparzecsese,n,CimWNo-r2k7s
1az3u. m8: uiccie 3W.8]0. hRuagmesrey, or. W.. KB.asoespikeieng 5R. Lc.. KRoistlcshcehy
GL. KW.. IKzleelsaenld//Jd.. 5.F.DMeedoere/33.05.02.05
moo.a7. Altman AWw.. eA.. Lcirvaenley wa. wa.raMgeenltsiak G. Woytouich
I
egonns
EID076143
\WU/2N0P0O0EASNPNEURAMLITLANNUDMFBIELRL:RWEyP0O0R7T6244
(Letter, R. L. Ritchey to A. G. Tumer, WV-DEP, OWR dated 1/26/01)
BCC: A.V. Malinowski, Legal, D7078
A. S. Hartten, BMP-27, 2160 M. L. Press, CH Works M. A. Bradley, Spilman, Thomas, & Battle
Tum: PHJ.E..J.. BARouasgsmeesrrety,.JrJ.r. R0..CB.anKeorsilesech
R. L. Ritchey
-
+
J. F. Moore/33.05.02.05
In Tum
G. W. Klesel
J. S. DeBee
-
In Tum:0. F. Atman AA. Crane JWM...J.ME.MPeLanigvteeillnysk
G. Woytowich
} dswi2:107
EID114142
ECEIVE
'
JAN 29 201
00052
gervex cory
50NOT REMove:
a
@
pens
Frnes w 0
January 26, 2001
CERTIFIED MAIL RETURN RECEIPT REQUESTED
Ms.AlynG.TumeCrhi,ef ~~ 2 Y02 787 /70 DOifvfiiscieoonof fWaEtnevrirRoensmoeunrtcaelsProtection C1h2a0r1leGsrteoenn,bWriVer 2St5r3e1e1t Attention: Industrial Branch
Re: WV/NPDES Permit Number WV0076244
Dear Ms. Tumer:
Enclosed is the 2000 annual report summarizing the operations of our Dry Run industrial landil,
Ifyou have any questions or need additional information, please contact me at (304) 863-4271
- Sincerely,
.
SRr..LEnRviitrcohnemyental Control Consultant Washington Works
ARtLtRa/cghwm.ednstsw
|
. cc: JOfofhincGe.ofBWraittveerc Resourc1e7s
+ D1i3v0i4siGonooofseEnRvuirnonRmoeandtal Protection
.
AFtatiernmtoinotn,: WInVdust2r6ia8l54Branch
[T----
x eeout
EID114143 Frise
2
1 certify under penalty of law that this document and al attachments were prepared under my direction or supervision in accordance with a system designed to assure that qualified personnel properly gather and evaluate the information submitted. Based on my inquiry of the person or persons who manage the system, or those persons directly responsible for gathering the information, the information submitted is, to the best of my knowledge and belief, true, accurate, and complete. | am aware that there are significant penalties for submitting false information, including the possibilty offine and imprisonment for knowing violations.
RL RLichAey L
1126101
Sr. Environmental Control Consultant
Washington Works
00057
EID114144
3
2000 DRY RUN LANDFILL OPERATIONAL REPORT Facility"AUllsetrhse waste disposed of in the Dry Run Landfill originates from E. |. DuPont, Washington Works and its auxiiaries.
andfil
Shipments "A summaryofthe
2000
landfill
shipments
is
attached.
Surface and Groundwater Monitoring "A summaofrtyhe 2000 surface
and
groundwater
monitoring
activites
is
attached.
Landfil
TOhpeeralteiaocnh,atCeoncosltlreuccttiiononsaysntdeMmacionntsetnraunccteedAcdtuirviintgy
Summary 1988 remained
in
service
throughout
the entireyear of 2000, Almost 3.3 millongallonsof leachate were transported to Washington
Works for treatment in 2000.
and a tAopocgrrosasphsiecctmiaonpmofatpheshloanwdifnilg itnhdeicaaptpirngoxtihmeaptreolpaonsdfeidl feilneavlagtriaodnaintgthpelaennadreofattthaechyeeda.r 2000
`Dry Run Landfil Remaining Capacity Calculations Calculationof 2000 fill Net Waste Fill Volume Method: Waste v=ol4u,m1e47hatruulcekdliona2d0s00x:38.6 yd/truck load (avg.) = 160,074 ~ 160,000 yd* Average net waste compaction (daily cover allowance included) estimated at 80% for 2000:
Total 2000 fil volume = 160,00x0 80% = 128,000 yd*
Ravine#1 Capacity remaining at the (existing cell) beginningof2000
= esso00yd
Capacity used in 2000
= 128000y
Capacity remaining at the. beginning of 2001
= se0000yd
Based on 128,000 yd" peryearnetfll volume consumption:
560,000 yd?/ 128,000 = 4,4 years remaining life on existing cell
EIDI14145
:
[TEES
4
Material Coal Ash Paper, Cardboard, Wood Glass, Miscellaneous Solids, Metal, Non-Asbestos Insulation Plastic Wastes (Polyamides, Acryiics, Polyacetal, PolyethyleneTerephthalate, Fiuoropolymers) Dirt, Construction Total
2000 DRY RUN LANDFILL SHIPMENTS
NShuimpbmeerntosf 1347
TotaTloWnesight 19767:5
ToPtaoluWnedisght 39,535,000
1362
6178.78
12,357,560
1073
6339.32
12,678,640
365
6502.38
13,004,760
a1a7
38,787.98
77,575,960
EID114146 [SDE
s
2000 DRY RUN LANDFILL QUARTERLY LEACHATE ANALYSIS REPORT SUMMARY
Date Submitted
Report
03/20/00 0772000 10/09/00 1/16/01
First Quarter Leachate Monitoring Report Second Quarter Leachate Monitoring Report `Third Quarter Leachate Monitoring Report Fourth Quarter Leachate Monitoring Report
2000 ORY RUN LANDFILL Date Submitted 04/05/00 07720100 10/09/00 116101
QUARTERLY POND UNDERDRAIN ANALYSIS REPORT SUMMARY. Report
First Quarter Pond Underdrain Monitoring Report Second Quarter Pond Underdrain Monitoring Report Third Quarter Pond Underdrain Monitoring Report Fourth Quarter Pond Underdrain Monitoring Report
2000 DRY RUN LANDFILL QUARTERLY WELL MONITORING REPORT SUMMARY
Date Submitted
Report
04/12/00 07120100 102000 147101
First Quarter Monitoring Well Report Second Quarter Monitoring Well Report `Third Quarter Monitoring Well Report Fourth Quarter Monitoring Well Report
2000 DRY RUN LANDFILL SEMI-ANNUAL STORMWATER MONITORING REPORT SUMMARY.
Date Submitted
Report
7124100 1723001
First Half Stormwater Monitoring Report Second Half Stormwater Monitoring Report
. eentny
EID114147
5
2000 DRY RUN LANDFILL MONTHLY DISCHARGE MONITORING REPORT SUMMARY
Date Submitted
02/03/00
Report
January Discharge Monitoring Report
0313/00
February Discharge Monitoring Report
04/14/00
March Discharge Monitoring Report
05/16/00
April Discharge Monitoring Report
06/15/00
May Discharge Monitoring Report
07/17/00
June Discharge Monitoring Report
08/15/00
July Discharge Monitoring Report
09/18/00
10108100 11102100
August Discharge Monitoring Report
`September Discharge Monitoring Report `October Discharge Monitoring Report
-
12/15/00
otra
November Discharge Monitoring Report
December Discharge Monitoring Report
2000DRYRUN LANDFILL BENTHICSURVEYREPORTS
06/27/00
Benthic Macroinvertebrate Survey: May
.
11/28/00
Benthic Macroinvertebrate Survey: August:
00-20
EID114148
'
DRY RUN LANDFILL 2000
'GROUNDWATER/SURFACE WATER MONITORING
`SUMMARY OFFC.143* ANALYTICAL RESULTS
`Sample Date: 07/19/00
`SampleLocation
EC-143 Resutlugl
Well #12
0.160
We #124
0.128
`Sample Date: 07/20/00
Well #6a
0212
Well #128
0.028
Well #13
8
Well #134
99
Well #14
01s
`Well #15
0.763
`Sample Date: 10/3/00
Leachate
. 27.4
.
)
Outlet 001
315
-
Stream Sampling Station No. 1
0.758
Steam Sampling Station No.2 27.6
Property Line
103
*FC-143 is ammonium perfluorooctancate ionic surfactant
All analyses performed by:
Lancaster Laboratories
2425 New Holland Pike
PLaOncBaostxer1,24P2A5 17605-2425
-
.
e0082s
: EID114149
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VOLUME AVAILABLE
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REE t""oWThoehnnteay3Mdpe"hcTishdseandlg1ojouhaosoeonlooofkohpefend"irffeorecnt tpcrhioediyuscel,y".
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pE e e el Ene hcSekaowanit,5iC84e0at0y8iGnaHclhRDphas.S eDrusPocrapsoempe loyerpBsorowvuhghe
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January 25, 2001
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ie
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ntSauykrgev,niPleilniilnHicoeroofoytuonrgyereP(oAPngFtQi,nyCgEAxSep#xo3ps8eu2r5le.54.
TThoreseoskuelrtss
owfitthe
blood
4 Summary serym 1
of
pe "sultEs Uwh2e0n00nefr,omSeWcoarmkeerAshautnlugbtlhe,atDuPont
Yeu
HSe are mp poC yh numa op this year
Ty
W Samples
CT
Mima
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Maxim
's"esults
S 200l0
No
m72 rI
20 l0o.p07
ion
, TT
i
em Concentration
TT Mean
i Concentration
te ihe following "ONC thi abr
T ii e Tos 1o.3m3;
7 8 PEmv.e 2sxaADmioplnseousnr,ge tpihe jfroojn wa ith poteng One Pica ji, Sreater t
Cols
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8
gives
upoearmy
mai
a? EUjyS fIAPN TFO etxhipeuiguCqraeg,1ehiogr 4p0a0 gsshloeuvladhtihned5a.0e
=
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m SORCNEICN of 3 5 porn "0d 4 mpoeracnsscfotnocmentghreasgeyy
z z
APFO
lMevPellosyienesthinso,81FUOUDROEFLpYeuwpolrking e
uigy
APEO
orovideq
p
i =
EIDI14198
He Consistently Tess han
iggy Samples. 2 ppm,
000535
ee
DJra.nuCahrayrl2e5s,
2001 M. Auer
"BlSveomaoandsa saenmrtousmngwAitPwhoFrpOkoetcreosnnticiaenlnatAsrsaPitFginoOmneesnxetpseosmwusirett.hbeDuaefutnocvtairoinanocfefsenigtlheonfgeumoey in luenegtsh omfasyerbveicienofflutehnecevdolruontteoenrlygrboyupe,xposuproetepnottieanltiAalPFbuOt egx1poyosbuyrea.avvereargaege
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Fp F. Pincliot
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cmoentaatc(t3R02o.b3e6r6t.
Attachments
Vers tnuly yours,
Ll eens
Gerald L. Director,
Kennedf Applied
Toxicology
und
Health
C0050
EID114199
>
a
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.
Oo --Oo ot = -- A
RdetvuinsteadesfamCnEaPr.y 2A00mma Peetluoeonctamare VoluAntmamroynUisuemanPderEfxlpuoosruorocetaInnofaotrema(tAiPonFOP)rofile
(revised January 2001)
revisionealndalortmiodoifnicucioonined in is dent bid slaty and my be syct a
CONFIDENTIAL BUSINESS INFORMATION REDACTED
L
CHEMICAL IDENTIFICATION
CChAeSmiNcaulheNarme: ANmmoEnium Perfluorooctnoate
mw COMPANY IDENTIFICATION
Company Name:
Site Locations:
E. 1. du Pont de Nemours andCompany
Site where APFO is used is 4 resction aid RWoausthein8g9t2on Works Washingion. WV 26131
wSietepsrwohceesrseedAPFO containing products made at Washington Word.
Parlin Plant
.
PCahreleins,eqNuJak0e88R5o9ad
SSp3r01uanJecsetePrlsaonn: Davis fy Richmond. Va 25234
Site which disposes of waste containing APFO:
RCehe.am1b3e0rs Works
g~
Deepwater, NJ 08023
H
Contidential Business toformaion Kedscted
Caan.
EIDI14201
ReascesfaCnEnRy, 2N001ini Pesunontanate
Technical Contact. Robert Pinchot (302) 999-3074 CDhuePsotnntutFRluuonroPplraozdaucts CBelntgre7B1o1u2l2e1va0rd Wilmington, DE 19805-0711
II. DUPONT AND CUSTOMER ACTIVITIES Narrative Description of APFQ Use
The block diagram on the back page titled "DuPont US APFO Balance descrihes te
WDwauisdPhoinntgisoenisWsAorPkFisO nfuosramareTkEaicntigGonPpTiFdEiunnetdhne,cop-rapTdohileeycmptreoorncseoscfsopnousltiyislteiszeodrfopfoelDyumnpontts tong p15 5 "{aindinotthheerrecaoc-timoon,nomersifdered in in ances media twih 3 smith urnereriaztingof TAFPEES
#aFquoudlelooAuwPsiFndiOgsptoehrercspiooonnlc.yemnetTrrihazteaetddriio(enrdesmptoeopvl.iynmteghrespcooomnletyamoifenrsthvdeiesrApyPelFriOsti)lo,en,isitfaebaiintylh,iezreAddPraiFneOdd tsoolrdeamsovane witer 1oT0fhfaesiirAtoePriFnwOaatnreerimnacotivnteehrdeatWfoarrso,hmciatnphgtetuoprnoedlWyaomnerdrkissenrtetcoovaenreofdfsfiotre riencdyucslter,iaclaplatnudr#eidl.anadndd/eosrtreomypeirr:ic
StThphereuUasSntacbueinldPilzoaeundttspfioodlreytmthheeerpUrdSio)sdpuecfrotsriioaonnvsaorfaisTeeteysfoollfdounbsyefsi,DbueiPrnsotneamtnadltloPyiTntFdeuEasntscrtoieaarltreecddusstytoaottmheersDu(bbootnht i
intemally
transferred
to
the
DuPont
Parlin
Plant
for
the
production
of
hetie fibers, or Teflon Finishes.
CgAehnasemmrabaletlredsamaWotourWnkatss.hoifnTnghotinos-nhmaaWztoaerrrdikaoslus1isswtearssetathteeerdpeoirlnmyiamteewrda.sitwneattweharet,eCrhAatPrmebEaetrmaesnndtWoofrtachkielsritwayadadttietrDiadvbesont's
or captured on carbon and landfilled in u secure landfill
ischuree
{Th0eMionstteronfalthperopcreosdsucatt,t4he"sDiuntPeornintg"Spsrtueapncine destroyed by the following reaction:
Plant which
to produce the APFO
cToenftlaoinnedfiibnertsheipnvrooldvuecst
is
3 z
:
DS1uuu4PdoineKtdrutbsnycteH,rinDgl.hC.RTeepRmoorpete..ra"tTuhreermGaals-Dpehcaosmepo'sFiNtiMoRn.of AC3NFeuwvcAulntaertneadtiSvuesttsotTanhtesrmaanldGrRealvaitmeedrMiacteArnitaylusts'.
Confident Business Information Redacted Coa.ol ID114202
Pug
RYoeluimtdacLymUiaIrPs, 2N00oman Pertlusronciamate
CE{CFCOONH, >CFuCF CEH + CO, +NH,
sPomasrll}taemcrotouiocnnetsgosofeedrsesi1i0dDcuuaolPmopAnlPteF'tOsi.oSnprT4uhse3ns5ce0epCprolndaudnctd0.so2 casrenroetsigdeetncseinttiemree.d
A small and hus
amountof commun
compressor packing materials.
used for industrial pump. valve and
aoTnphdeefppairtgoomcneensotsfs.ffolrTurhmaoekpsiomnlagylmlTeoarrmldooiusnnpterofsifinoiAnssPheFwsiOtathetmohiteshesDriuoaPndosdnitttoiPvaersliinncPluldainnginsvoollvveenstsa.blbeinnddeirnsg dPaerssotcereosysgieendngcarttahtceoendAtPdruaFcrOtinfgaaccpciroloirdtdeuiscntgwhc1 hearnegetohveemras.terSioamie odfritehdewaafttletureomrfporeporomalttyuhmriesersfda3ciis3lpi3etr0ys+iisosndnuees to
ths reaction aon: This dried material 1s
{tThaeinseafionSapolerartoi0osnss)copnsrivsiostcaoefetobovsmearttshepedtrassypertLa4h50yaitnagipssoefitrhoieatirores cracpottahutirtneg.appElmyistsheiopnsrooftAPoFraGSfirboinr,,
15sheenhtypi1c8a0llyatseirnteevrieldinugt {he APFO from the substrat
in nai temperatures
sion. Pilidtoank upproaching S00F
fiiltaerpspalneds lbaoncdoftiymeaq rorae resulting in the semana) ot
e and subsequent destruction according to fhe reaction soore
"ossCmuatsltloamnpeuprlmsibceaorftdoiifosnasppepirlnsivicooantlivpaoernosd"us[citntseruisneg"thsetempatwehreiarle ftohre aAvPaFriOetiysodfesptprloiyceadt.ionTsh.ereHoswueevser
eedmiissspseirostniso.nopTrhoeEdruAectMasrEetSoaltseoomptesrmaFatleulreendsumthbsaeatrvaoliflnoapptlhiecaAtionP ws1h|e0rsFeubtlhO eimceusrteosmueirinhgea1tsat1ihewehere
These
applications
include
indusirial
packings,
1 Sh and
APF staying industrial (les
iththe fabrics
produ
1V. SUTE RELEASE AND TRANSFER INFORMATION FOR TRI CHEMICALS
Not applicuble- APFO is not listed on the TRI z V. SITE REAL NDTE RANSA FERS INFOE RMATION FOR NON-TRI CHEMICALS
A. Onsite Air Releases
C [FugitivT e |I WashNiengm gltuosinvlWeorw ks T Para lin| Sos ruance|TaChmambeerWsorks --
Stack (PointSource) | 24000
OO 01 0
0 oo
Confidential Business Infacmation Redacted
EIDI14203 0095.
Page t
RYeovliusnetdaeLsaUnEaPr.y 2A00m1monium Perflusromtanosie
Comments
fAiumriteemdismseiaosnusraermeeensttsimoaftsepdecuisfiincgpeonignitnseoeurricnegsccaolcnudluacttieodnsuinntdhejupdasgtements and B. Onsite Water Releases
LPT oint Source Wahin5m5o0E0ns0Wtiomraktsed|ToPt3aar0ll0inA|nnual SRo1real5aecea0s7es
(165.1999)
hamb1e8r.s50W0orks
1
Comments
WaEteIr eSmissUionEs aSre esOtFimSaPtEeCdIuEsi"nigteengsinCeeoritngtcealculatthieopnsnand fudgemente nt. RWiaivsehrianfgrtoomntShWetoDrouknPsoyenmteivsWisaisohniTsonrogctcounrHWAfo)orrdkaapsyprPslo.axnitmRaweteiercleeysms3os5d0oefldaeAydPs/uEvsOeinw0ghittlhheee tOheo EEPxrPocAbealbOisflpfirisectaeidcosfDhiePleoutltlimuootndieoMln.odPreAe!vPe(FnPOtiDorMnelaeBanesrdeaTdoVaxeriracssifo)ornu1n49d.09a6BcewotenarsetJruuinsceeted1d1i,nMi1bc9or0to6hs,orU'ts2. HmoAdPeFlOinNg wexoeurlcdisbees.e"xTceheedePdDaMboiuntdi5c0at%edofthtahteAtPimFeOducroinncgentthreatyieaorn.s oAfP1F.O0 ducronicnegnttrhaetiyoenasroafndin 1t0heugrivAePrFwOo/uIldsheoxuctee2d.20%.1ofwgthAePtFiOm/eldu9r0i6ngofthtehevetrime
MAivcerroasgoefatnnuEaxlcelAPsFprOeacdosnhceeenttrwaattiso0n.s42in3
the tg
OAhPiFoO/RLi.verMocdaleclueldatAedFbPyOusing
a
fhclioognwhcsoe,nftrreastp0i.e9oc6tn5isuvegilnyA.tPheFAOvr/eivrLearignreaSnOeghpeitdeomfRbrieovrme,r4wfhllioowcwhsofcaon0rd.r1ev9so9plouungmdeAtdoPaEhtiOagIchaLlacinnudlMalatoerwdchrfirvtoeomra
ostfhpertehUaeSdsWhaGeessohtlionmgogidtceoalnl.WSTuohrrevkesByelPwllaeavsni.lcloelTlhDeicsatemrdiviesartoftnlhoetwhBeedlOaltheaivoi1llRteihveDecarlmo1s3easnmtdilleuossceadtdoiwoinnnstthreear
downstream from the plant where this type of information is available
iInmm1e9d9i9a.te4ldyridnokwinnsgtwraetaemr osnamtphleeOohbitoaiRnievderfrformomGEDupPloanstticWs,asWhaisnhgitnognto"norWkYs.
z Z
showed0.552ug/} APFO.
3
R+eRporBteErMt,SE"M0o5d4e.l00i.ng Releases of Annona Periluormoctanoe into ihe Ohio River", DuPont ferns!
EIDI114204
Confidential Business formation Redacted 0095.5
Faget
KSaelviiitnacLyanuGaIrPy,2A01on Declan amass
RLIinuvbaeedrd,cikcsihPoounbw,leisdcam0Sp.el8r4evgsi/cloe,btD0ai-is4tnr4eiudcgti,/nduJonawdnnu0sa.ir3cy1e52a0mu0go0/flfWrAaoPsmFhOit.hnrgeteSoudnbisfWeeoqrureenktnstwoenlltsheatOthye
April. May. 007ugn
and
Auge
2000.
showed
a masimum
of
0.59
ug/l
and
samples 1 3 minima of
C. On-Site Land Releases
sCEonhugarimcnbeeseerriisnntgWhoecrapklacssutltaertesiattoisnmsaAtuPenFdthOjatucdoagnpetpmareionnxitinsmgaatwneadlsytlei3mi0int%eadowfmaestahteseuwAraPteemFreOnttrisneaotthfmeesnptecsiyfisccem
Twhaessteewlaatnedr
treated releases
iasraedessotribmeadteodn
(0 to
a he
carbon 8.000
Imed4ia19t0h0at
is
landfilled
on
site.
PridorriolpleraatpiaonrsthabvyetrheesWulatsehdiinngimoeansuWroarbklse iAnPWFesOtcoVnicregniter,atioAntsLoitnontth:reeans
J32W4i0akcge/lw.alwtierthmeaansauvreermaegnetosf i1n 3199929 .andGr2o0u00ndywtadtrearngmeeafsruormem2e.n2t3s0t9akteon during :
ule te find average of 2537ug/l.
at Lett tdtid sage At the "local landfill",
orm 60.331 0 the groundwater
17300811, with concentrations
an
range from samples at
0.046ug/l the "local
to 39pg/l with landfill" range
an average of from 0.54!
$.S3ug/l. 0 87/1,
Surface with an
water average
of
a1n8d.5suug/rlf.aceAtwaDtrery,RwuinthlatnhdeSimlla,xtihemruemarceonlciemnitterdatmieonasiunrgemreonutnsdowfagtroeofrun1d5wuagt/elrand
Ot1fh9e9sm2u.arfxsaaicmempuwlaemtsecrionnwtceherenetr"tauatpkipeoennr"aiannndtdhseh"olpoewrwemedirt"ctoerndcoeonnusttfraanlteliaoronfDse2ay0s0Ruhgii/gnlh.LasaTnn1d61im9g9im0l,e*..soacmIpsnlses
22001 and landfill have
2si3nc0e0s,horwesnpelctoiwveerlyc.oncSeanmtrpalteisonst.aken
tn
these
locations
at
Dry
Run
In 1999, 4 RCRA Facility Investigation as completed for Washington Works ZarnoduwnadswastuebrmictoniceednttoraEtPioAnsReofgiAoPn F[1O1 iant JWuanse.hi1n9g9t9"o.n WTohreksr,eport contains data on
tMecTahhnesiqvuoaefl,idttihhteeyLhoafntdnaeiosfelcio1uc9sat9toni0odnaysn,asltnyhdseessspaecmcapiflniencaumsboiettvoyerriicfoningetdelowolcaiaqteuiaotlnhtseyaesntduhreiascnacusescspdereoocarevdaauinrlaealsby.sliesa,unpdhotneerrseeoqrmumiepnsitte.the 23 a?Rcecpuorarctywoafshseubemsiutlttesda0re Mnaoriknn.owT.nKotsch. Remedial Progen Manager, EPA Region II, Philadelphia
Connffdeindteinaltial BusBuisnens essTIuntformation Redaeted Cons.iSyplines
Paget
VRuelvuinvtearLyamUuEaIrPy. 2\00n1musnium Perflusenctanoate
D Teansfers 0 Off-site Locations
Washingion Works: _--
1incineration
|
Wastewater treatment [Underground injection
1
OHtahzearrdloanudsfiWllaste Landfill
Recycle or recovery
]
VI. ONSITE WORKPLACE EXPOSURE
Teanste(rlsb, 909)
16000 13400
--}
0
!
2600
0
25000
|
A. Information on the Number of Employees Potentially Exposed
2T0h0e0tdbuireisngbetlhoeiwr
dneosrcmrailbewiohreknaucmibveirieosf
workers for each
that may be of the three
exposed to sites where
APFO APFO
in is
year ter
[Rr ouno sDaay --TT
----NuWwashhiinnggltoonaWWooDrrakkyssslor
.
<033 i<0
10-100 ;
1100-350 15230
T
I
[0251
i
Lg) 1
--7
m2
i7:
>
-
=
--
--
Routine workeractivities that have potentialfor exposure.
%
Handling Handling
raw raw
material APFO dispersions containing
APFO
> MPaoilnytmeenradnrcyeeorfoppeorlaytmieornizaantdiomnairnetaectniaonncesystems
~~"POapcekroautitonofaPndTFmEaainndtecon-apnuolcefmeArPdFiOspreercsoivoenrypryodsutcetmss
* Transtemetdo Cuamibers Works Fi (sc esion 8 snd C shoves Confidential Business information Redacted COO5.15 EID114206 Pages
LReovliuvteadcfyaCmEaPr,y 2A00m1 ani Peelluornoctamste
FoursiDay
i<3
[<0 !
0.25.1 18
I 1
8
Partin Plan
710-100
Dayle (100-350
I I
i 8
1
Routine worker activities that have potential for exposure:
--------------
550
I
1
[ ji
> OHpaenrdaltiinognoafnPdTmFaEinatnednaCnoc-epooflbylmeenrdidnisgpefracsiilointiepsroducts > Puckoutoffinished product
hNhoetaresethtahteAaAtPPnEFoOtaitcmhoeiulsisdutsshiueibtmlyia.mtee.riAalTllhheeaxanptdorlseeu.deeahtpeottrheeentPiisaarllliiinsePhplroaotneutngtahtiaaslnkfeolreevxatpeodsutreemp1esrature . ehoamndtliinnigagof<t0he2p5o7lymAePrPdOispersion materials. all of which contain <i1n %conAtPacFtOduwriitnhgmost
i Hours/Day
| <10
[035
7025.1
T
Spruance Plant Daysiir
_ --
T 10-160
1100-350
5330
<i
|
fs >
: i
S I T I --
Routine worker activities that have potential for exposure:
> 7
OHpaenrdaltiinognoafnPdTmFaEinatnednaCnoc-epooflfyimbeerr dciosapteirnsgiofanciplriotideuscts
> #
Operation Packaging
aonfdnomna-isnitnetnearendceproofdsuicnttering
rolls
<N0ot.e9%thAatPFthOe,PwTiFtEh amnodstcoc-onptoaliynmienrg daipsppreorxsiimoantperloydu0c3ts%usAePdFOat, the Spruance site contain
B. Information on the Exposure Levels of Washington Works Employees
hSiynitgneicreemnemedoidsaattteaosfiastnchdeonppcrreooncdteurscasttisendgisadtdootnnheaetiunsttetW.haesTUhhiSengwltiitomhnitAWedPorFmkeOsa,saunDrduePAmoePnntFt'Oss coaofinratbiaorirbnnoiernnigendAusPtrFial
3 z
cmouncchentlroawteironlsevaetlsth(emoostthleyr sniotne-sdwetheecrieabAleP)FlOevceolnstoafinAiPnFgOp.rodTuhcetsdaartea uinsetdhehatavbelesbheolwOonw
2 :
Confidential
Business
Information
Redacted
~~
| EIDI14207
CO0%.17
Page"
RVeavliusnetdaeFyaGnEaIaPr,y 2A00m1onivin Perflaoranctannste
tareetlaecctoimnboinintaotriionng odfonceheomviecralthoepelarsatto3ryaenardsmaatiWnatesnhainncgetownorWkoerrksp.ers"o(nhaelsasmapmplleersesults
Year| Sample
|_| Type
11999 [Paral
[110999877]| (smhoisttely, 1996 6:8 1995 | hours)
| Fol Samples
| __100
10 [33
| Minimum
Maximum | Mean| Standard
| | Concentration || Cm Concentration || (inpbj | Deviation
| <0.01
053 [0061] 0151
| <00l
24
01037 0.145 jo46| 047 |
0069 |
0063
Partial shift air samples that has been pretreated
awriethtaskoedniautmthheydrraotxeiodfe/2e0t0hymlLe/nemignlyucsoiln/mgeathTaenonla.x
collection be The APFO is
desorbed from the thes using methanulic hydrogen chloride. derivatizing reagent, converting the APFO (0 its methyl ester.
which Alter
also serves as a workup, the methyl
aster is quantified using 3 35 CAroMALoZrph The mths!ester of pertluorudecanois acid 1s
equipped with un electron capture detector. used 4 an internal standard. and at fest
+
three calibration samples Precision is estimated to
are prepared (0 cover be +/- 10% relative
the
concentration
range
of
interest.
o`Tnhleydaatvaeraybofveew sshamopwlaevsearabgoevse ctohinesiTsLtVe.ntlyWhbeerleowretshueltAsGarCeHaIboTvLeVoronfear0.t0o1mtgh/emT',LVw,iththe
events investigated and corrective action (additional personal protective equipment or
engineering controls) (0 reduce the exposure levels is undertaken. Older data from the
1980's show higher levels of exposure. In the early 1990's. Washington Works switched
from receiving the APFO as a powder 10 receiving it 4s an aqueous solution. This change
was done to reduce the potential for exposure during handling of the dry powder. lu
should be noted that in the 1997 time period. the site was starting up new APFO recovers
facilities. facilities
Operating and maintenance difficulties sssociated may have contributed ( the higher levels of APFO
with the start-up of these in the personal samples
during that yea.
Task specific monitoring data and wipe monitoring data exist. However, these data are not indicativeof employee exposure and are not presented here. These samples are takers 0 identity areas where additional exposure controls may be necessary.
Engineering controls ( reduce exposure Zonsist of the follow ing:
> Reaction systems are closed systems with continuous ambient monitoring for
Vmeonntiolmaetironcosnycsetntermastairoensstalled hereairborne concenteations are significant 32
The polymer dryers operate under negative pressure ( contain APFO and
z
other materials. > Recovery systems are in place to reduce airborne emissions
=
7phe moles ee billion. 0.56mpb ts equivalent 0 the ACGIH TLVof 0 0lmy/m'
Content Dniness Information Redacted (fp ED114208
Pages
VReovliusnetdarJyanUEaLrPy, 3A00m1uonium Peefluoranctanosts
Person protective equipment that workers regularly wear consist of he following
> *
SpIramofpdeeutrcytvsis.ohuosesglaonvdessiwdeh-esnhiehladndslaitnegtyAgPlaFsOsessoilnutaillonasreoars.aqueous dispersion
~ oCfhsepmliacsahlesporfoteAcPtiFvOe ccoovnetraailnlisnagnsdolguotgigolnessisorprfeasceents.hields when the possibilicy
hAiarvleinheigrhesepxirpaotsourrseorpoctaernttriaild.ge respirators where monitoring has shown to
AMvatelauWseausrinheimansegsntetsossnionWfgobrelkxopsoo,dsbuflrloeuoo0rdisdAeePrlFueOvme.llsevAhealsvseuomfbmeAaePrnyFtoOafkehrneasvpuerlitboseroetnfo me1em9ap8sl1u,orybeeudetssairwneictoehf1il9di8emn1itted
iAnPtFheOteabxlpeosbuerleow.poteDnuteialtothseign1i9f9i5c.an1t9j8o9b-0a0s,si1g9n5m5e,natndmo1v9e84mevnotludnutereirngstchmipslpienrgioedveonftisric.
OtfFoirAmee.PmFapnlOaolyyiesniebssloofiotndclrsuedereudnomifncddatahnisteabe1a9rc9eo5mdpisfanfripceuldlit..ngTThdheaeteadntasitoraethidanatttchaeosmteptaabolrfeisbbolenolsoodwofcpofrneicloearnt1it0vrea1ti9e9v8elysre*
available upon request
ions is
I
Year
7!
#of Samples
T
Minimem Concentiation tppm)
|
Maximum Concentration
| |
Mean Concentration
1995 1989-90
75 ; 23
012 04
1
(om) 45
|
(pom) LST
i 85
30s
TP o1s98s5 o | 591 or 00..0067%
18"
243
owTe ss
saTTmhhpiilssesiinndwdieivrviiedduutaaalklecnwo.anssiTswhtoiesrnkelimynpghlaoisyneaasejodItthheaahntighAhaPessFtAOlPcaFxnOpdoescuxonpnecoepsnoteireapntutitaoelnniaoasflsAiagBtntFhmOentstiiinmncee1oA9f9Pt1FheOsInaspm1op9cli9ef5icsis
2%
mployee"s blood seeunt level was 4 Sppm
Confidential Business Information Redacted
EIDI14209 ODED
Pages
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=
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