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COMPILATION OF HISTORICAL C-8 DATA DUPONT WASHINGTON WORKS MAIN PLANT AND LANDFILLS
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13 PhysicochemicalDataforAmmoniumPer{luorooctanoate (C-8)............1-2
14 RERCTCNCES.rr
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20 Washinglon WOrkS Main PION...
21 Introduction.d......
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22 ENVITONMEDNA] SEUNG ..rrrrreren
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222 Hydrology, HydrogeoloagnydGroundwater Flow.............. 23
23 Wer QUIRY.co
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231 Surface Water Quality...
rem 26
232 GrOUIWAIETQUAY
censors 26
233 Drinking/Tap Water QUality.....vrrormrormrororersroninen 21
24 SHECOCOPNUE! MOC...
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322 Water
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331 Surface WaterQuality
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332 GroundwaterQuality...
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36 References...
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442212 HGyEdOrIoOloRgYy,cHoydrrogeology and GroundwaterA FIOW................4-3
43 WAC QUAY. 43.1 SUITSCeWAerQUAIRY
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Table of Contents
LIE
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52 ENVIONMENE) SCHING vr
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a S31 SUT WRRE QUI cmrmmermsmsmnsenemeemmerermeeren So
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532 GrOUDIWaterQUAIIY Si6 CONCEPUA MOBelcor
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55 DHAGHS.merrormrmomn 35 RUS mmm
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TABLES
Table 2.0 Washington Works Main Plant Monitoring Wells Construction Data
Table 214 Washington Works Main Plant Analytical Data Table Surface Water
Table 2B Washingion Works Main Plant Analytical Data Tabl~e Groundwater
Table 2.1C Washington Works Main Plant Analytical DataTable - Drinking Water
Table3.0 Local Landfill Monitoring Wells Construction Data
Table 3.14 Local Landill Analytical Data Tables~ Surface Water
Table3.1 Local Landfill Analytical Data Ta-bGrolundewatser
o
Table40 Letart Landfill Monitoring Wells Construction Data
Table 1A Letart Landfill Analytical Data Tab~lSurefasce Water
Table 4.1B Letart Landfill Analytical Data Table-s Groundwater
Table 5.0 Dry Run Landfill Monitoring Wells Construction Data
Table S.1A Dry Run Landfill Analytical DataTables - Surfoce Water
Table 5.18 Dry Run Landfill Analytical Data Tables-Groundwater
FIGURES
Figure 1.0 SolubilitiesofC;F15 COOM in Water as a FunctionofTemperature
Figure 20 Washingion Works Main Plant Location and SWMU Map
Figure 2.1 Washington Works Main Plant and Loeal Landfill 1-mile Radius Map
Figure 2.2 SWaamshpilnegLioocnatWioornkMsapM.ain Plant Monitoring Well and Surface Water
Figure 23 Washington Works Main Plant Cross Section Location Map
Figure 24A Washington Works Main Plant Cross Section A-A"
Figure 248 Washington Works Main Plant Cross Section B-B
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Figure 24C WashingtonWorksMainPlantCross Section C-C*
Figure 24D Washington Works Main Plant Cross Section D-D"
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Table of Contents
FFiigguiree 22445E WWaasshhiinnggttoonn WWoorrkkss MMaaiinn PPllaanntt CCrrosssSSeecttoionn EF--E*
Figure 2.5A Washington Works Main Plant Groundwater Elevation Map - November
2000
Figure 2.58 Washington Works Main Plant Groundwater Elevation Map - February
1999
Figure 25C W1ashington Works Main Plant Grunt Elevation Mop -Novenber
Figure 26A Washington WorksMain Plant C- Concentration Map - February 1999
Figure 268 Washington Works Main Plant C-8 Concentration Map-November 1998
Figure30 Figure 3.1 Figure32
Local Landfill Location Map Local Landfill and Washington Works Main Plant 1-mile Radius Map Local Landfill Monitoring Well and Surface Water Sample Location Map
Figure33 Local Landfill Cross Section Location Map Figure 3.47 Local Landfill Cross Section A-A" Figure 34B Local Landfill Cross Section B-B*
Figure 3.5A Local Landfill Groundwater Elevation Map-November 2001
Figure 3.58 Local Landiill Groundwater Elevation Map-December 2000
Figure 3.5C Local Landfill Groundwater Elevation Map - November 1999 Figure 35D Local Landfill Groundwater Elevation Map - November 1998. Figure 35E Local Landfill Groundwater Elevation Map - November 1997 Figure 3.5F Local Landfill Groundwater Elevation Map- December 1996
Figure 3.5G Locel Landfill Groundwater Elevation Map- December 1994 Figure 36A Local Landfill C-8 Concentration - May 2001
Figure 368 Figure 3.6C Figure 3.60 Figure 40 Figure] Figure 42 Figure 43
Local Landfill C-8 Concentration - May 2000 Local Landfill C-8 Concentration - May 1999 Local Landfill C-8 Concentration - May 1998 Letart Landfill Location Map Letart Landfill 1-mile Radius Map. Letart Landfill Monitoring Well and Surfice Water Sample Location Map Letart Landfill Cross Section Location Map
Figure 444 Letart Landfill Cross Section A-A"
Figure 448 Letart Landfill Cross Section B-B"
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Table of Contents
Figs 450 Lett andl F-Zane Gods Evin Mop Jory 201 Figure 4.5A Letart Landfill F-Zone Groundwater Elevation Map - November 2001
Figur4e SC Letart Landfill F-Zone Groundwater Elevation Ma-p October 1999
Figure 45D Letart Landfill F-Zone Groundwater Elevation Map - October 199
Figure 4.55 Letart Landfill F-Zone Groundwater Elevation Map - December 1994
Figure 4.5F Letart Landfill F-Zone Groundwater Elevation Map - December 1992
Figure 4.6A Letart C-8 Concentration Map - July 2001
Figure 468 Letart C-8 Concentration Map - January 2000
Figure 4.6C Letart C-8 Concentration Map - July 1999
Figure 46D Letart C-8 Concentration Map - November 1991
Figure 50 Dry Run Landfill Location Map
Figure 5.1 Dry Run Landfill 1-mile Radius Map
Figure 5.2
Dry Run Map
Landfill
Monitoring
Well
and
Surface
Water
Sample
Location
Figure 5.3 Dry Run Landfill Cross Section Location Map
Figure S.4A Dry Run Landfill Cross Section A-A"
Figure 4B Dry Run Landfill Cross Section B-B*
Figure S.5A Dry Run Landfill Groundwater Elevation Map - October 2001
Figure S.5B Dry Run Landfill Groundwater Elevation Map - October 1999
Figure 5.5C Dry Run Landfill Groundwater Elevation Map - October 1998
Figure 5.5D Dry Run Landfill Groundwater Elevation Map - October 1993
Figure 5.5 Dry Run Landfill Groundwater Elevation Map - April 1992
Figure S.6A Dry Run C- Concentration Map Bedrock Wells- July 2000
Figure 5.68 Dry Run C- Concentration Map Bedrock Wells - July 1999
Figure S.6C Dry Run C-8 Concentration Map Bedrock Wells-July 1997
Figure S60 Dry Run C- Concentration Map Overburden Wells - July 2000
Figure S.6E Dry Run C-8 Concentration Map Overburden Wells - July 1999
Figure S.6F Dry Run C-8 Concentration Map Overburden Wells - May 1998
Appendix 1 Consent Order APPENDIX
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Introduction
1.0 INTRODUCTION
AEnvmiurlotin-mmeendtiaal CPorontseecnttioOnr(deWrVwDaEsP)en,tethreedWienstto bVeirtgwieneina tDheepaWretsmtenVtirogfinHieaaDletphaarntdment of
Human Resources-Bureau for Public Health (WVDHHR-BPH) and DuPont on
cNoonvteaminbeedrin14A,p2p00e1n.dixA1c.opyofthe Consent Order (Order No. GWR-2001-019) is
`(TWheVDCoEnPs,enWtVODrdHeHrRi-deBntPiHfi,edaandscDriuePsoonftr)eqiunoirrdeemretnotsdteotebrempienerfwohremtehdebrythtehreePhaarstibeesen
paenryfliumoparcotocotnanhoutmea(nC-h8e)a,lCthAaSndNuthmebeenrvi3r8o2n5m-2e6n-t1a,staortehseuletnvofirreolnemaesnetsoffraommmDuoPnoinutm
``aonpderDartiyonRsuna).theThWeasCh-i8ngGtroonunWdowraktsermaInivnesptliagnattiaonndSttheeeraisnsgocTieataemd l(aGnIdSfiTl)lsw(aLsocal, Letart
cesotnadbulcitsehdedtoinatshseesCsotnhseenptreOsrednceer atondovcexrtseenetoifnvCe-st8igiantdiornisnkainndgawcattievri,tegsrotuhnatdwwaitlelrb,e:and
surface water at and around the main plant, and the Loca, Letart and Dry Run Landfills.
aPnurdseuvaanltutaotetdabcyhtmheenGtISATo,fTtahseksCoAn,sBe,ntanOdrdCe.r,TthhirseeretpaosrktsawdidllrebsesepderTfaosrkmeBd. bTyheDuPont
pdertiemramriynoebsjtehcteipvreeosefnTcaesaknBd sextteondteovfelCo-p8ainnddriimnpklienmgewnattear,mognriotuonrdiwnagtpelranantdhasturface
o
pwraotveirdienaancdomapriloautnidotnhoefmaavianilpalbalnet,graonudndtwheatLeorc/aslu,rLfeatcaertwaalnedrDmroyniRtuorninLagndrfesiullltss, aanndd to
hmyedertotgheeoldoagtiaccochmaprialctteiroinzaotbijoenctdiavtea for each location. Thisdocument was prepared to.
14 Document Organization StheecLtoicoanl,st2h.0e,3L.e0,ta4r.t0,anadndth5e.0DrpryesReunnt tLhaendhiiisltlosr,icraelspdeacttaivaevlayi.labElaechfosretchteiomnaiinnclpuldanets atenxdt, staebclteiso,n,andadtafiggaurpessasrpeeciidfenitciftioedt.h Tsihtee bseaimnegoduistcluisnseisduisnetdhaftorseecatcihons.ecAttiotnh.eDeantdoaf each pavraeislcaabtleed)ian eraecqhuessetcetdioinniTnacblluedeAsIionffortmhaetiCoonns(etontthOerdeexrt.entIntheadtdiitnifoonr,mastuipopnlewmaesntal ifnofurorlmoactaitoinonissdpirsocvuisdseedd.as needed io develop and presenta site conceptual model for the
1.2 C-8 Historical Laboratory Analysis of C-8
hTahsecahnaalnygteidcaolvmeertihmoed., mPertihorod0d1e9te9c1t,iDonuPliomnitt,apnedrfolrabmoerdatCo-ry auntailliyzseidsfaotrtChe-8DuanPaolnytsis
IEnxvpeesrtiimgeantitoanlwSatastcioonndiuncWtieldm,ihnegtaonna,lyDseilsawwaarse.conItnra1c9t9e1d,twohtehne CthHeyMRHCiRllALVaebroifriactaotriyonin
Mbaosnetdgoanmaelrytyi,caAllambeatmhao.d wBiotthhdaetbesctuisoendlaimGitassfoCrhrCo-m8atthoagtrraapnhgye/dMfarsosmS0p.e1cttoro1m.e0turgy/l
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c`eCaHs:eMdEiolplercaotniodnu.ctAetd tCh-a8ianmael,ysDiusPfoonrtDuhPaodnctomnptloettehed foanlleorfou1n9d9o8fwahnealnytshieslfaobrortahteory.
RLaCboRrAatoFraiceisl,itLyaInncvaesstteirg,atPiAo,n (fRoFIt)h.eTRhFeTasneacloytnidcraoluwnodraknawlayssitsrainnsFfeebrrreudartyo L1a9n9c9aster
OLcantcoabsetrer20L0a1b,orwahteorniedsevceolnotipnmueendttaoncdotnedsutitngCw-a8sainnailtyisaitsedusoinnag nGeCw/ManSalyftoricDaluPmoentthoundtil
`dCehvreolmoapteodgrbayphEyxyTgaenndReemseMaarcshs,SIpnec.ct(rloocmaetterdyi(nLSCt/aMteS/CMoSll)e.ge,DPuPAo)ntthaatduotpitleizdesthLeiquusiedof
LCIMSIMS for C-8 analysis in November 2001.
DusuiPnognttheinLtCe/ndMsS/toMSsu.bmiTthetoaWnaVlyDtiEcaPl m/eEthPoadAlolldoogcyu,mesnatmaptliionngrmeeltathiondgoltoogCy-,8aanndalysis
Aasppsluircaanbclee qPuraoljietcytcPolnatnro(lQquAaPli)ty0absesusruabnmcietptreodgtroatmhewiGlrlobuenddowcautmerenItnevdestiingaatQiuoanlity
Steering Team (GIST) i carly 2002.
1.3 Physicochemical Data for Ammonium Perfluorooctanoate (G-8)
mCa8n,ufsacotuirdienngtaitftiheasmaFiCn-1p4la3nt,.i aFifgluuroeri1n.a0tesdhsouwrsfatcthanstoluusbeidliincsthoefluFroypoClOymOeMr in
wfiastts teahre pahyfsuincctoicohneomfictaelmpdeartaatauvriel(aFbilgeurfeor6.9C-8in(KKiissssaa,, 11999944)).: The folowing summary
Q Molecular Formula = CFy(CF:),COONH:
Q Molecular weight = 431.098 gimole
OQ LDio acute oral rat = 680 mye
0 BCF=18
Q pH ~5 (0.5% aqueous)
Q pKa=28(-CO0H)
Q Meliing Point = 56-58C (COOH)
9 COD =700 mye
Q Koe=25
Q Water Solubility > 1000 mg C-91L
Q Vapor pressure (at 22C=) 7.1 x 10% mm Hg
Q Krall Point =25C 0f0QLe aCriDtioca0l MiDceelolevCo0n%centration = 33 mdmeo,l-- /L DXCNoT envce Sons t mbrsais ccoshsen-Mesa afc orish
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Introduction
1.4 References Kissa, E. 1994. Fluorinated Surfactants. New York: Marcel Dekker, Inc.
WCamago ion, r OE. gsai mbaa nzoeown teo z lhey -
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2.0 WASHINGTON WORKS MAIN PLANT
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Fipwe 25h Wabiogin Wks Mai Pa rundats Evan Mop Neer3600
Fiwe250 Waigin aks MamFist Gamer Ecaon Mop Ferry 1099
Fic 25C WaingonWerks Mon Past Godt Eatin Map Novant 1990
Finc20n WaWksiMonPn otC3Cocenrton op Feb 199
Fione263 Waingao WksMain farkC3Centon ap oven 1998
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@ 21 introduction
`The Washington Works Main Plant (main plan) is located along the Ohio River in WViarsghiinnigat(oFni,guWrees2t.0V).irgAiniwaa,taeprpursoexiamnadtweellylsseuvrevnemyiilsecsusrroeuntthlwyebsetoinfg Pcaornkdeurcstbeurdg,foWr ethset a(rFeiaguwriet2h.i1n).a 1-mile radiusof the main plant and Local Landfill property boundaries
Significant historical hydrogeologic and groundwater quality data for C-8 at the main
plant is available from previous investigations that have been conducted. The most
sIingvneisftiicgaanttiosntu(dRyFTw)ascoandRuecstoeudrcien tChoensfearlovafti1o9n98anodnRfeocuorvSeorlyidAcWtas(tReCMRaAn)aFgaecmileintty Units
(WaSsWtMeUASm)enatdtmheenmtasin(HplSaWntA)toPseartmisiftyNrueqmubierremWentDsof04th-e58R7C-2R5A91H(aDzuaProdnotu,s 1a9n9d9)S.olAid
briefdescriptionofeachof the SWMUs investigated is presented below. SWMU
Tocations ere shown on Figure 2.0.
Q SWMU A-3, Riverbank Landfill: The Riverbank Landfill is about 4,500-feet
Tong and lies along the northem edge of th site near the Ohio River. It was
oipnecirnaetreadtiboentawsehe,npl1a9st4i8csa,nrdubtbhleel,ataend19p6l0anstatnrdasrhe.ceAifvteedr pcloowseurreh,ouitsweaasshc,overed
wdietnhse6v1e0ge3t5atiinocnhe(soonftshiels.loCpeudrearneat),orthbeyRibuvielrdbianngks Laannddpfaivlelmsecnotveirnetdhewith
o
manuf ring ares,
Q SdiWgeMstUionB-p4o,ndAsnaacrreocboi-cloDciagteesdtiwointhPionnadspo(rDtiigoenostfitonhePoRnidvse)r:baTnhkreLaendffoirllm.erOne pond: dates from the 1950s and two others from the 1970s. The ponds received wwahsetne tfhreopmotnhde cfolnutoernotcsarabnodnumpapneurfafcetwurfieentgopfrcolcaeyssli(nienrcalunddinpgonCd-8b)eurnmtilma1te9r8i8a,l wwietrhetroepsmooivl,edanadndthdeiasrpeoaseidsocufrorfefnstiltye.vegTehteatpeodnwditahrcgarawsass backfilled and capped
Q S`WWasMteUInCc-i6n,erPaotloyrascceotnasliWstaesdtoefItnwcoinebrraitcokr-sli(nWeadsptietsIinncitnheerawteosrtse):rnTphoertfioonromferthe
manufacturing area.TheWaste Incinerators operated between 1959 and 1990.
The Waste Incincrators have been excavated andbackfilled with clean soil.
.
Q SWMU H-14, Buming Ground: The Buming Ground is located in the central
portion of the menufacturing area and was operated betwen 1948 and 1965.
Sgrianvceel,1a99n0d,ctohveerBeudmbiyngbuGirlodiunngds haansdbaespehnalletv.eled,backfilled with clean fill and
gAropurnevdiwoautserVeartiftihceaRtiiovnerIbnavnesktLiagnadtfiiolnl(,VDIi)gefsotuinodnePvoinddesn,ceaonfd rBeulemaisnesgoGfrCo-u8ndto(sDouiPloanntd
I1n9c9i2n)e.ratLoirttsl.e eFuvritdheenrceinovfersetliegaasteiosnwsearnedfeovuanlduaitniosnoislawertehepesirtfeoorfmetdhedfuorrimnegrthWeasRtFeI to
determine the extentofreleases in groundwater.
CWoinmtmoneOFrce Dzes
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Washington Works Main Plant
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sinasmtpallliendgweevlelnstassfsoocciuasteeddownitehvatlhueatBiunrgngirnoguGnrdowuantderaqnudalRiitvyeartbeaxnikstLianngdafnidllnDeiwgleystion
Ponds SWMUs.
2
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Section 2.3 Water Quality.
22 Environmental Setting
22.1 Geology
t"ThheeVgIeo(lDougPyoontf,th1e99m2a)iannpdlarnetviissesdhboawsnedononsiaxddgietoiloongailcfcirnodsisngssecftiioomnsthdeevReFIl.opeTdheduring
sleocctaitoinosn,soAf-At"heangedoFl-oFg!i,cacrreosssh-oswenctioonnsFiagruersesho2w.n4AinanFdig2u.r4eF.2.3.FouTrwnooretahs-ts-owuetsht ccrroossss.-
sreescpteicotnisv,elByB. ,ThCe-Cc,roDsDs-'s,ecatniodnsE-wEe'raeredesvheolwonpeodnfFriogmurdeesta2i.l4eBd,g2e.o4lCo,gi2c4lDogsanrdec2o4rEde,d
uprroidnugcttihoenVw1ealnsdaRnFdI,geaontdecfhnriocmallbeosridnetgisdlreidlhliesdtoirnicthgeeoaltoegi1c95l0o5gsthrroomughtestth ncdarly
19805. Some monitoring wells shown in Figure 2-3 were later abandoned. The current
site map (Figure 2.2) shows the monitoring wells that currently exist at the site.
""TThhee malaliunviapllatnetreasctesisontoQpuogartaepmhaicrayllalyluflvaitalantderiaecseadpepproosixtismaitnetlhye5O0hifoctRiavbeorveVatlhleeyO.hio
Risivuenrd,erwlhaiicnhbfylaowfslate,asrtivteorw-escsoturpeadstbtehderomciknspularntfo(asfcetheFeiDguunrkear2.d0). SeTrhiecsaltlhuavtirailsetserrace
steeply and outcrops in the southern edogfthee site (0 form the vallcy wal.
TdhoewnQwuaartedrnuanrcoynaslolluivdiatuemdrrainvgeersdfeproosmit6s0of1p0o1o0r0lfyee0t ienldle-pstohriaendd, cbornoswisntsaonfd cgoraarysseannidn,g
vsairsi,coclloaryeadnsdangrdayveslh.aleT;hegrDayu,nkgraeredn Saenrdiebsrboewdnroscakndcsotnosnies;tsanpdrmiinmoraobifelrdseyodfacnods,
claystone, black carbonaceous shale, and limestone.
c"TiheevaavieornaofgethrieveOrhwiaoteRrivleervaetriroanceisdeapboosuitts55u0ndfeerethaebomvaeinMeplaanntSaeraeLaebvoeult(6M3S0Lf)eeta:nd the
:
athbeovneorMtSheLr.n bDouunedtaoryroivfetrhbaenmkauinndeprlcauntttianlgo,ngsotmheesrliuvemrpsiendggoef.cFliagyuarend2.si4lCt esxhisotwssaalonng.
exampleofth relationshipoffil and clay ayers along th riverbank.
22.2 Hydrology, Hydrogeology and Groundwater Flow
Hydrology
Regional water needs are primarily satisfied by the Ohio River and Lite Kanawha River
near Parkersburg. These sources provide water to the cities of Parkersburg,
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from production wells srcened in the Quatemary river alluvium.
wSaurlfeasc.e wSaeteeprsaltotchaetemdaailnopnlgantthdeirsicvhearrbgaensk tmharyouogrhigdirnaaitnesfarnodmsptroercimpisteawteirosn,tahnatdhdarsainage
idnifsiclhtarartgeedstaolposonigltohrefrlilvearnbdantkh.at Tlwoowsdraalionnaggethsewtaolpeos,ftohnee ulnodcaetreldyiinngthsehaflalciolwitcyl'asy and
ssuoruftahcweesrutncoofmfedru,rianngdrtahienyotwheeartlhoecratteodtohenOthheioexRitvreerm.e cDausrtienrgednrdyowfetahtheerfa,ctilhietyd,rcaionnavgeey
swales are dry.
Hydrogeology RRievgeironaalllugviraoluntedrwraatceerdespuopspiltise.sTaheesoabttuarianteeddfrpoormtitohneoDfutnhkearOdhiGoroRiuvpebreadlrluovcikalantedrOrahcieo Pderpoodsuicttsiocnomweplrlisscothmeplperitnecdipianlhriesgiaoqnuailfearquhiafveer ubseeedn fkonrowwantctrosyuipepldlyupputropo5s0es0.gallons pceormmmeirncuitael(wgaptme)r (sSucphpulltyzc, o1m9p8a4n)i.esBaosbetdaionnwathteesrefhriogmh tyhieeladlsl,uvniuamlearqouiufseri.ndTushteriyailealndd fwerlolmaasllfuovrimalataiqounifgerraiwnelsliszeisarnedlattheidckonetshse well' position with respect to th river, as `plTahnetO. hTihoeRwivaetreraltlaubvliealoctceurrrascaetdaepdoespitthsocfonatbaoiunta6s0intgol7e0kefeyetaqbueilfoerw ugnrdoeurnldyisnugrftahceemianin
`tchoemspluetredfoianfctthheeeiutnedearqluyiifenrgyDiuenldka2r0d0G1r0o4u5p0.gTpmh.e oTn-hseituendperroldyuicntgioDnuwnaktaerrdweGlrlosup is
nwhoitcahmcaojnosrisatqsuipfreir.marTihleyoufppseharlzeoannedosfiltth,eliDkuelnykbaorudnGdrsotuhpe (lWoawsehrienxgttenotnoFfortmheatsiiotne),
aquifer. bedrock
wTinlladidkiteiloyn,rerseulgtioinnalupgwraorudndgwraatdeiernctosmtmoutnhiecaaltliuvoinalbeaqtuwiefeern.
the
Ohio
River
and
`hiGgrhoeusntdwmaetdeiraqnucahllioyriidne,thseulaflatleu,vihuamrdinnesthsis(arsecgiaolncituemndcsartboobneatnea)t,uriarolnl,y apnoodrm,ahnagvainnegstehe
`aclolnucveinutmragteinoenrsaolflayillsahcyadlrcogioulmogbiiccaurbnonsatien ttyhpeer,ewgiitohn n(eSacrhunletuztr1a9l84p).H aWnadtehirgfhrdoimsstohleved
solids content,
Natural recharge o the alluvial aquifer comes from various sources, including:
Infiltrationofprecipitation falling dircetly on the alluvium
Q gLraatveerlalzmonoevsement of the river water through the alluviumvia permeable sand and
Q Seepage from stream tributaries that discharge to the Ohio River
hTyhderamualixcicmounmneactmioounnttoo fthweartiever.avaTihleabdleegtroeetohefahlyldurvaiuulmicdecpoennnedcstoionnthiseadefgurnecetioofn ofthe pemeability and thicknessofthe riverbed, permeabilityand thicknessof the alluvium,
and hydraulic gradient between the groundwater and the iver. Pumpingofon-site active
_ CVionond,p08tavayidaonra o2f0 Jan -- 11.02 --3
000507
EID168072
MAHO00444
iPlrtand Lois
Washington Works Main Plant
well fields near and parallel to the river (i.., the Ranney Well, the DuPont-Lubeck Well
Field, and the East Well Field shown in Figure 2.2) lowers the groundwater level in the:
aalllluuvviialumaqtouwiafrtedorthbeewleolwlsr,ivwehriscthagree.plTahciessiwnadtuecrepsuwmapteerdffrroommtshteorriavgeerion tfhleoawqiunitfoerthaend
helps sustain high-yield pumping wells. ~
Groundwater Flow
gGrroouunnddwwaatteerregleenveartailonlsy,lfolwosw doirtehcetisoonus,tha-nsdouftlhowwesrtatiens otnh-esailtleuvairaelsatqruoinfegrl.y iHnofwlueevnecre,d by
ithneclOuhdieothReivRearnnanedy bWyelplu,mapriandgiaolfcoonl-lseictteorpwreoldlucwthiiocnhweplulms.psTh8e00ont-osi1t,e00p0rogdpumc;titohnewills
saonvdetnhewefilvle iDnutPhoentEa-sLtubWeelclk Fwieelllds,,wwhhiicchhppuummpp aabcooumtb7i0n0edgapvmercaogmebriatneeod.f2,000 gpm;
``mGeraosuunrdewdatienrNeolveevamtbieonr c2o0n0t0o,urFembarpusarfyor19t9h9e,alalnadviNalovaqeumibfeerrd1e9v9e8loapreedprfersoemntdeadtaa5
Fthiegufrleosw2a.r5rAo,wsB., aAnsdsCh,orwenspoecntitvheelgy.roTunhdewdaitreercteiloenvoaftigornouconndtwoautremrafplso,wgirsoiunnddiwcaatteedrby
cfelnotwrailn ptohretinoonrotfhetahstepsatret, ogftrhouendswiaetiesrtofwlaorwdisthteowEaarsdt
Well Field well. the Ranney Well.
In the north In the central
aLnudbewcekstWeelmlpoFretlido.n oPfhumepisntgeo,fgtrhoeunpdrwoadtuectrifolnowwiellsso(uRtah-nsnocuythWweelslt, tEoaswtarWdesltlheFiDeludP,oanntd-
the DuPoni-Lubeck Well Field) eliminates off-site migrationof impacted groundwater
othbattaimnaeyd ofrriogmintahtee GfernoemratlheElSecWtrMicU(aGrEca)s.proApdedrittyiolnoaclatgerdotuondtwheatweersteolfevatthieomnadiantaplwaants.
`Dgartoaunfdrwoamtetrhemomdaeiln p(lDaunPtonatn,d G19E99w)e.reThuesegdroiunncdawliabtreartimnogdtehle cWoanschliunsgitoonsniWnodrickasted that
tghreousnidtwpartoedrucftoiomntwheellmsa.in plant area is contained to the DuPont property by operation of
1D1u1P2o1n9t9-0LuhbyedcrokgWeeollolgFiieeladssaensdsmtehnet,EapsrtodWuecltlioFniewledlwlasspeccoinfdiuccctaepda.citTyhetesrtesiunlgotsfwtehree
(usDeudPotnotca1l9c9u0l)a.teItnhtehteravniscminiistsyiovfittyhaenDdutPhoenhty-dLruaubleicckcWonedlulctFiievlidt,yotrfatnhsmiaslsliuvviitayl vaaqluuiefser
rviacnigneidtyobefttwheeenEa1s1t4W,e9l0l0 aFinedld1,2t7h,e50tr0agnaslmliosnsisvpietry dvaalyupeesrrasnqugaerdebfeotowte(ensp16),0.50Ianntdhe
5va0l,u0e0s0 fgorptdhe.EaHsytdWrealulliFcicco.nduFcotrivWietlylvsalAuXe1s 3w-erPeWOcaIlcaunldatAedZIf3ro-mPWthOeIt,ratnhsemhiysdsriaviutlyic
c0o.n0d1u1c0ti0v.i0t4y9vcamlusecsc,rarnegsepdecftirvoemly0..013 10 0.055 centimeters/second (cm/sec) and from
vUasliunegstdheetheyrdmrianueldicfrcoomndgurctoiuvnidtwyatvaelruleosvfaitoimontsheme1a9s9u0rsetdudiyn a1n9d90thaendhyadsrsauulmiicnggraandient
esfefveecrtailvweeploropsaiitrys wvaalsuecaflocrulsaatnedd.anTdhgergarveolunodfw3a5te%r,ftlhoewgvreoluocnidtwyawtearsfelsotwimvaetleodciatty for
o
5pofrteieotndoafyt(h1eds)itbe,etAwegernomuonndiwtaotreirngflwoewllvselTo1ci3t-yMoWfO3LfdanwdaLs1e8s-tiMmWaOteId ibnetthweeesnouthwest
monitoring wells POG-MWOT and K14-MWOL in the westem central portionofthe sie.
CWionmrgmoen,n0d amomze mo
25
000508
ED168073
MAHO000445
MNaannPPelwtdaindoLnasts
WaWasshhiinnggtonWWoorrkkssMMaaiinnPPllaannt
foInrththeecsaitsetaequpiofretriboneotfwteehnemsoint,itaorgirnogunwdewllasteArLf1l0ow-MveWlOocIitayondf2A.O50f9d-MwaWsOLestimated
`(thGDeruoPRuoinvndetwrab1t9ae9nr2k)c.LapnAsdnfialatlcttshieivneRcFierve1en9r9cb1ha.-nDkTrLahaienndRfgFirIloluvnwedreiwrfaeiteieddretnhctaoitlfltiehecedtiacoonnldlhesacastmibpoenleesndyisdntueormpienrgatthieonVIat
effectively captures waterat the seep area.
23 Water Quality
2.3.1 Surface Water Quality `mHsieasamtspourlrieceladlocisanut2ri0foan0cs0eaawrneadtseh2ro0Cw0-1n8aoctnotnFwcioegnuotruretaft2a.il2lo.sn,sS0au0rre2fpaarcneedswe0an0tt5eerdaCnin-d8Taatcbotlnwecoe2nr.ti1rv.aertiloSonucsratfwiaoecnrese.waTthere cooulnfcaelnltsrahtaivoensbeheanvesarmapnlgeedd mfornotmh1l.y43siungc/elFeb1r9u9aruyg/2l0w0h1.ilOeutOfuatlflal0l0050C2-C5-8 ocgefonniecnresantlta,rllaOatutitiofonanslolofvCae-r8caalclrobnhocanevnaetdrbsaeotreipnotnmisounhcathvreelaostwimegernn,itfrisacyansngttilenymgdifenrcoltmihne0e.ld4ui3rn6o2pu0o0gl1/y.m(e0Tr.h8si.p5sr4oiuscegtsh.se. rIeTnshulet system isdesigned to emove a major percentageofC-8 from the process wastewater,
232 Groundwater Quality
bbsieeneecnne vm1aor9ni9ia1tblo(er.TeadbSlqoeuma2re.t1ewBre)ll,ylhssothwaaevvteeirbni,egnethnJeamnwouenalirltyso2sr0ea0dm1pa.lnenTduwaalonldypltshaienntcs-eawm1ipd9le9i6gnragonfudrnedoqtwhuaeetrnescry.hahvaes. qsaunaadmlpialtriyenfdgrieosvcmeuensxtsisesdwticbnerglcoawcn.odndnTuehcwetlesydaimanpsltpaialnrlgtedoefvwteehnltlessRafFsoIscou(csiNeaodtveoednmwebivetarhlu1tah9te9i8nBguargnnrdionFugenbdGrwruaoaturenyrd19a9n9d) RiverbankLandfillDigestion Ponds SWMUs. LadAenltldefcpiltaelndltDiwinegglerlssotuisnoadnmwpPaloteneddrsdauanrrdienapgr(eitvnhietohRueFsIwsecwseetprerseanampnpoalrletysiz.oendoFiffgtourhrCec-s8R.2i.v6eACrtbatanhnedkR2.L6Diadvnedefripblailn)c,ktC-thewas wHweeEll/llLs..lomCcoaantxciioennmsturamantdcioornnecsseunlwttesrraeftoirboeCn-ls8o.rwan4Mg0eeaudsgfu/rrLoeimdn3c28o8n0co0efntt1hre3a,t36i70on0wseulrgla/sLn.gseadTmhpflereodhmi;g<hi0ne.st1the10ot1h3e,r6090 cDoingceesnttiroantiPoonnsdswearrcea.measured in monitoring wells PO4-MWO2 and RO4-MWO2, near the TwehreeRpFrIepCa-r8edcoanncdenatrreatpiroesnevnatleudesinwFeigruruetsil2iz.e6dAfaorndco2n.t6oBu.ring. Isoconcentration maps
CVinaingpione, OnFheybe
000509
_. Eotesors MAHO000446
deMannfPoowaadnlgnotanndtts
WaWasshhiinnggttoonnWWoorrkkssMMaailnnPPllaanntt
@ 3? DrinkingTap Water Quality
dPtihrseotdrmuiacbiutntiioponlnaWnpteo.lilnCtAs-MoOnc7otn-hcePepnWltOarnIattpie(orhniisosdtioinrciadclralilynlkysikingnn/cotewapnMawaaystwe1er9lhl9a93v3(e6T)abbesleuenpp2ml.ei1Cae)ss,uproetadbaltefwoautrer to s0`C.ao4mn2pc3leinuntgrga,ptoirioennstspsercitaninvgteheledy.dfirsNtoromib0ou.bt2vi1oi3nouussgy/stltre(e0mnd0os.na5r8Oe9ctsueogebn.erinC1-1t8,he2cd0oa0nt1ca.enwterraeti0o.n5s07d,et0e.c4t5e,daantdthree
24 Site Conceptual Model
c`alTnahdsesfmiufatiiuerndeaphsluacnmotamsnpiltaeentcdeoneocrceoiplntocugoaimlcpamlleortdeeec.elptdoerssc.ribPeostetnhteiaploteexnptoisalureexproosutuersewreoruteeesvfaolrucautrerdeanntd
DnGoirnro-euecnxtdies,txeWpnaotss,utrbeeeIctnaocuisCne-er8tahtbeoesraser,imaantgnedmraiDtaielgrseisahtlaisvoecnobnPetoeannidnsre)edmoworivtcehodivneartnehdde raSenWgdrMavdeUgeesdtaoitrsepdm.aivneiTdmhea(rlBeofuormrien,g
contact with these materials is considered to be an incomplete exposure pathway.
wAatlearrgceopnotratcitownoitfhtCh-e8pliamnptaictteedissociolvscorredgrwoiutnhdawsapthearltisannodtcloinkcerleytei.n tHheesnecaeresausr.face
s`etTxhoperormseufsorerewee,prasstu,hrwfwaahyci.ecwhMautulecirhmcoaotfnettlahycetdipinrsgecchCia-pri8gteaitmiipnotanoctftaehldeliOsnohgiiloosniRssicivtoeenr.sisirdPoeruretceeiddpitttoboawteiaoarndnfdairlnaicinongmspoalnnedte
tohcecurrivienrpblaanckesslaolpoencgitthheerrpievrecroblaantkcsarientportohbeabsoliylcoarursuendsboyfpteforctohleatrievderw.atTehrethsaetcps that
catohcanctsuiumdnuedleraretldeisetoatbobeposvaoeinltiahnencdosmlfpuilmlepateledo,enxglpotowhs-euprreiervmeperaabtbaihnlwki.atyyCdoculncatyaatconttdwheistialhctotiifmvpetahcferteeOndhcihso-edRrpaiivwneartedrepjossits
`groundwater collection system.
prDoiaurttehecutfaoeyrxbpgeorcsoauuursneed0wgargotruieonusrdnwvdaiwtaaetcroenritailcmotpcawactitetedhdawtbayatbcCor-up8tu6ims0paelfesdcotfcbroynossm.ipdTrehordeeudocn0tlioybnepowatenellnist,niacloWmcapotlneteratcet
ppruomvpiedidngfriondmusptrroidaulcptrioocnewseslwlastie.used for two purposes, supplying drinking water and
emWiaegilhlnt tApliMamnOets.7.-OMPtehWeaOrsLuwreielsdlosncoeaonrcefetAnhtOrrOeaetSi-poPrnosWodOufIctCia-onndiwAneQlthlOis9s-twhPealWtlOpsLruo.vgigAdeesMstOeddTrit-nhaPktiWntgOhiwsawetaxesprostsaoumrtpehleed
pdorawitenhkrwiatnyhgawinsatcthoeenrsmiiadpxeoriiemndtutmoofubcseoneccoe(mnwpthlrieacttheio.inssHaodmewteeivcetxre,dtoiafnvuewaranratygeeesricnfogrnlcoeemwnettlhrl.eattihCoronensetowafeclCtl-ws8i)wtiihnllbe:
impacted drinking/tap water is a complete exposure pathway,
`VCO-S8-wPaWsOdIe,teacntdedLiOn4p-rPoWdOu1c)t.ionTwheellmsapxriomviudmincgonicndeunsttrraitailopnroofceCs-s8wwataesrd(eKte1c6t-ePdWiOnIw,ell
iKnId6us-tPriWaOl Ipr(o1c6e.s2seusg/li)n.cluWdaitnegrnfonr-ocmonthteascet waenldlscoinstnaoctt ucsoeodlifnogr wdartienrk,infgi,rebwuattreart,hperrofcoerss
CVioinmigpoen S6 yao zee
57
000510
Entesors MAHO00447
HdaiePofrtensnLan
WaWasshhiinnggttoonnWWoorrkkssMMaaiinnPPllaanntt
o
`aemxtapeneruc,ftaeccdotnutvoreibrnesgimpoirnoncitemosadslee.sm.iAnveTreharelarigezeeisdcoawnapcotetenertnrttaiotaigloefnnosoerrflaitmCi-st8teediancmo,pnrtaoanccdetls,osrhwocawotenevsreuram,iptthhiieospncooiinntttahocetf is
pmuasaetxh(wiwahmyiocihsccioosnmcapemlniettxreta,utriioetonissfdcweoatntesecirtdeefdrreiodnmatsoneybveesrimanilgnlpiermoawdlel.ulc.tiTohnewreelflos)rewiwlhliblee tlohwseerxtphoasnuce
TrevehaselouuRartcFieosenmccoaloyongcbilecuadelexdepvotashleuadasttuioronfsiaftcoeec-sruolsiaeltdeatdontchoiendsRetniitvtieuferynbitansngkrweLhlaeentahdseferidlsflirDgoinmgieftsihcteainoStnWePMcoUonlSod.gsiicaTlhtihse
ocIonnncltiyancpctortawetinottishaalCn-edcoBilumorgpniaiccnatlgedeGxrspoooiulsnsudroerSgmWreModuUinusdmwaarwtieetrchoiisvnentrohetedlRiwFkiTetlhsygtbrueadcvyaeular,seeaa.stphhSeaulWtr,faaogceebwuaitledrings
`gagrnrodouudnnoddwwnaaottteeprrrdaoorveeidsneontoetceoxdlpioosgsciuhcraalreghmeaebtdiotiasatuo.rffSacucoebsnwucarteferarcfeaotrstoehicelol(sogierg,eiactaelrrtehcaenpi2orfse,eta)nadnd
25 Data Gaps
The following data gaps were identified for the main plant:
oo
9 gArrdodouiuntndidwownaaattleermrolanniodtwo0riinentvghaelwuebaletldesragorrceokunbneedclwdoaewtdettrhoelfuounrwtchodenirfvdieecnlteiodnneasal,tleupvaCirat-licaucqlouanircfleeynrtfroartions in
3 Continued refinementofthe groundwater model for the msi lant fs requir 0
arneedvathlautatneootfhatsgirtoeumnidgwraatteironcoafptCur-e8biympthaecpeudmgprionugndewlatserisisococcucurrrriinngga.t the ste
Q pSluarnfaicsecuwrateenrtlqyuableiitnygindetshiegOnefdiotoRiavdderresshsotuhlids bisesuecv.aluated. Aseparate work
Activites o fil the data gaps will be proposed and discussed in the work plan.
26 References DuPont.Wa1s9t9e0.&WGaesohliognigctaolnEWnogrikneser1i9n9g0DPerpealritmmiennatr,yHydrogeologicAssessment. Solid
Wo1r9k92s.AprVierlif1i9c9a2t.ion(VIonlv.es1t)i.gation 1. DuPont de Newours Co. Washington
30,919999.9.RCCoRrApoFraactieliRteymIendviesattiigoantiGornoRuepp.ort, Dupont Washington Works, June
Haskell Laboratory. 1991. Ammonium Perfluorooctanoate (FC-143).
CarnCS iti a S on2a nT,
000511
enissors MAHOOO4s8
MiMapnwaitmnoguawentss
WaWsashhiinnggttonWWekekssMMaaiinnPPllantt
o
Schultz,vRr.A,. W1e98s4.VGirgounnadwaterHydrologyof theMinor TributaryBasimsgihe Ohio
-- Vines 5 FE
-
--
000512
Enters MAHO00449
TABLES
000513
.
eee eowem
oo
oo
MAHO000450
Table 2.0
Monitoring Well Construction Data DuPont Washington Works Main Plant
mmm TT `Washington, WV
Sooap)h|| Dniaemester
Fon sTsmEe eT]P E Re ovW W mwaT] CeCiTnYYao l O H |--3--u ------n t a |a--[ssoefe-=eseoe]||
[bie tewT or |ersTbIawsTerniia| 0 | || see5e-5somr]
Sr ET EETn C 5 i t a 2% |
T 2 c Lavo 1tA isTe5 s 0| A 3r w --T--S ---- 5--E ----+n --
m ism rvore 1c bu agsn eeanr
we [wp
--e --t ---- B---- --
[s7 m immoo |itswaassn{eeeosn|-- wS ma |--e--s ------S--a-- i
[oC I oCmT wor{we2 ar cam[esos0|e 172T o J] m777a% 7]
[[arosesamTor
war |twas
[oepnier0T7ame
||g e 2J S 0 s7o5a]
Fa Foen inswo oorf1twwege [[se0aisanr[{ 05fT -- e-- --s ---- --o --S --] --e --
[[aacosmneisstawmoor| [trvevasno T[eeowi7 esnr[ 7T 2|e g--------e-- 2e --
[[o --E ammsaveor{| tvm i s seesws | |m g e --------e --------------------||
wwweeer1----1--1
--
@ T e CEyr 2 e TCCEo T7w w S 727a eTr s wnt7 s on r]
Page 1012
000514
cores MAHO00451
Monitoring WeTlalblCeon2s.t0ruction Data
DuPont WasWhaisnhgitnogtnoWno,rWkys Main Plant
-
mmm
Newid
DTeotpatlh
SLecnrgetehn|| ScErloeevnatiinotnerovfal
Forme Fo
(eo)
1
fee
ee
y
ee
TT Foto
ens eo [ge]
2 rs
| eneETr| 72| I g WO ] 75
eso 1 rw so
sonsTag[a] mas [ef]
oe| wes TH 2
Fano
en|e 57
------------ 72%
|
aso Er
wes vn
S | e p To pe ise e]
v2TE 10
[aoa
2E5 ene0 [2T2700
1 75 |sesso]
[ Fe ABoT TWaIs STeessisor[ 2Th aio o0OiNjoo
25m |ssa]
srei-seser|
Eo ws ess| 2
Ti 0 oTio]st1si5ae.r]
Feder
2 Twn
5 30 1 wisTo
[ewes
Tio
20 --io{smssens]
fon I savor |
wees{t ve e[[3366[ 7 20 i0T a o| wer nas [8 7Tio
sre sere] srresere]
2 ET 0 TC EON NJ
| io] setaesere]
0
ta
CH OT 1 F517 |
[sI eve Tw2 as |
EJ 3 esis [gs |
sano
[0 100 io[517S5e2-w5s6s53.218|
[vawesaor TW w tvs s
sn ToToes]
eenoosrT705 7172 --io[ eoe Ts sers25sssseaisze]r]
[iaMworTwoT6993T9020]
Zev FZavo
est s:
el| Taio eserTnTaio]
0 srr ser] io]sserseser|
2
0 1
0 1m
[nsmworTry
ETE
2
ei|
Co7o T r 1m 1wsw E 0_ o setr s |
`BRoeldda-ndTalkaelnicfsr-omapRpFrIoWxPi.mate ~ takenoffcross-section
Pago2ol2 -
000515
Entssos MAHOOO4S2
Summary oTfaAbnlaely2t.i1cAal Results:
DuPoCn-t8 WinasShuirnfagcteonWaWtoerrkSsaMmapilnesPlant
Washington, WV
I -- COAL sor -- I 1-- ---- -- -- 7-- t -- --]
FFrLm ---- ose -- ]
Ea T Z7um s -- --
SRS a oozn o --a ----
meme 7
---- ------
T eRe e i e mr e e n or |
OL.7
OLOW 7X
o
= estimated value (blow laboratory quantaton mit)
000516
|
Eotsa01
MAHOO0453
Table 2.1B
Summary of Analytical Results:
C-8 in Groundwater
DuPont Washington Works Main Plant
WashingtoWnv,
sme TomTeam
= He eesTe ee zsTe a EE------ a ---- Tess |or] a or --2=Ton--s
a 1 -- --
= = EE = E = a = = = = T ness--os
oe a | Ime
on
=E 35 [nee
1
Z 7; Y S--
ea e |= Ea
CE o -- e E = --e e -- 2958 Te; i B= i [e1 ssae es s|
we amoTe 22 i femme
fees Tp
sme es 1
000517
--
-81n Groundwate`rSDuumPmoanrtyWoafsAhnTiaanlbgyltteoi2cns1W8RoerskusltMsacionn'Ptl)a:n, Washington, WV
EE a EE-- rv-- r---- -- TT --
a ToT m a= m w=] --
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wm
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000518
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MARO0O4SS,
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000513
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Table 2.1C
SuDrminmkiaonfgr/CTy-a8p AWnaatleytriScaalmpRleseuslts:
DuPont WasWhaisnhgitnogtnoWno,rWksVMain Plant
== == ES---- E m-- em T --r op YoTre -- ------
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000520 Einres08s MAHO00457
FIGURES
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Ept6s102 MAHO000474
MainPlantand Lands
3.0 LOCAL LANDFILL
Local Landfill
h or m sm mo m tomato m rss E te eI rsee rir es m mL i m mm e ee ee @ I Tn I m meI eeT e e ee en
ee ee e
=e Compiatonobeloydnb zisJ 02
31
00538 saoncoosrnnss
Nin lot oct
Local Landfill
3.1 Introduction
p"TehreimLeotcearl(LFaingdufriel3.i0s).locTahteedlainmdmfieldliaantedlpylaandtjaacreentlotcoattehde amlaoinngptlhaentOohfifotRhievseoruitnhern WViarsghiinniag.toAn,wWaetsert uVsiergainndiaw,ealplpsruorxviemyatieslcyusreevnetnlymibleeisngsocuotnhdwuecsttedoffoPrartkheerasrbeuargw,itWheisnta 1-mile radiusofthe landfill perimeter (Figure 3.1). T25h0e-aLcorcealsitLea.ndTfihlel cceolnlssiswtesorefotpherreaetseedpfarraotme 1c9l6o4setdoctehlelsmliodcdalteed1o9n80tsheunhdeearviWleyswtooded V0i0r7g6i5n3i8a./NaTthieonpalePoilluistacnutrrDeinstclhyaurngdeeErlgiomiinngatrieonnewSaylstaendm (isWeVxpNePcDteEdSt)o PbeeremfiftecNtoiv.e in `Jgarnouuanrdyw2a0t0e2r.moTnihteorpienrgm,it requires monthly surface water sampling and semi-annual MPaotweerrihalosusleanadsfihl.leAdppinrcolxuidmeadtseclryap14pr4otdouncsto,fswcarsatpemeptearl,yewaorowderpaelldeitsspaonseddbiinnst,haenldandfill. Powerhouse ash comprised abou 70 percentof the fotai waste. The specific sourceofC8haisnrhoitstyoerticbaelegnrodeutnedrwmaitneerd.anTdhseurcfealclse wwaetreercslaomsepdleasndcoclolevcetreeddfwriotmhoanp-psriotexilmoactaetiloynstwo feet of low permeability soil. sFaimguprlein3g.2posihntosw.s Tthheelcoeclaltsiohnaovfe tnhoe ctohmrepeaccetlelds,omrosnyinttohreitnigc wbeoltliso,manlidnesrsu.rfaHcoewweavteerr, a
composedofreddish conductoifvaibotuyt
brown clay and weathered 5 X 10" cm/sec (DuPont,
shale 1990)
having a very low hydraulic and ranges from 3.5 to 19.5
feet
in
thickness.
32 Environmental Setting
32.1 Geology
`"TThhee sLloocpaelsLaapnpdfairltoibseiatuactoemdbiinnaathiiolnloy afrenaatwuriatlhrteolipeofgorfaapphpyrwoixtihmtaetrealcye3d0ou0tc4r0opfseeto.f
mJaansdsfiilvlelsaatncadusst.oneThanedlsoiclaitsitoonnseoufntdweorlycirnosgsv-asreyctiinognasmdoeuvnetlsoopfedsofiolr tchoeveLroacanld Lmaannd-fmilaldea:re
shown in and 3.48,
Friegsuperceti3v.e3l.y.The
two
cross-sections,
A-A'
and
B-B,
are
shown
in
Figures
3.4A
TAhsehcallalyowcotnitgahtincslasyolmaeyemrisntoarrisnagndatygarnodusnidltsyuzrofnaecse,raanndgessofmreompetbhbrleees1a0.n2d5ffreaetgmtehinctks. of
scaonmdpsatcotneed,inosftoemnedilsocpaltaiyoinns.g aTlhaemicnlaarysstarruecotfurleo(wDupPloasntti,cit1y99a0n)d. aUpnpdeearrltyoinbge twheellshallow
bcleadyrloacykerisipsrweesaentthearteddepsthhaslerraannggiinnggffrroomm211010to3450 fefeetetbtehliockw.grBoeulnodwstuhrsfcceo.mpetent
CWiorapgeiomn a08nmabe mE
.
-
;
000539
32
Etesios MAHO00476
MsiPintsnd Lots
Local Landfill
"cTahlecabreedoruoscskhaatlt,haenLdocgarlayL,agnrdeielnl, aconndsibsrtoswonf isnatnedrs-tboendeodefdtrheed PaenrdmviaarnicaogleorDcudnskaanrddy or
c`Grroosusp-.secTthieonmsasxhiomwutmhatthtihceksnaensdssotftonheelDayuenrksadridpGgrenotulpy itnowthairsdrsetghieonnoirst5h.70Mfoesett.ofThteh.e
sHaatnedrsatlloynedilsacyoenrtsinluoocuaste.d Tinwtohelautpepraelclypcoonrtitnouifotouhsensasntdrasttiognreaplhaiycerssecatrieonloacraelteedntiinctuhlearand
Tower stratigraphic section.
3.22 Hydrology, Hydrogeology and Groundwater Flow
Hydrology In general, infiltrationofprecipitation is limited due to the very low hydraulic conductivity (5 x 10cnvscc)ofthe surficial clays (where these clays exist) and the `weathered bedrock (DuPont, 1992). In addition, infiltrationofprecipitation into the cells oisftlhiemitceeldlsb.y Laepapcrhoaxtiemaftreolmyt2h-efeseotoutfhelroncweplelrmaenadbitlhieteyassotielrnancdelvefgleotwastifvreocmovteher sceaepppsinign the steep valley walls to leachate collection ponds, Pond I, 2 and 3 (Figure 3.2). wLehaecrheatitepfasrsoemstthhersoeupgohnsdtsoirsdmiwsacthearrOguetdfailnltonoa. p0i0p1eliinnetoatnhdecOohnivoeyRievdert.o tMhoenmiationripnlganotf `combined pond effluent conveyed in the pipeline is conducted at Outlet 101.
Hydrogeology
GzornoeuncdwoantesroiufnsdtehtrellyianygstahnedLoucnadlerLlaynidnfgilwleoschceurresdinbtewdroozcokneasn.dThhse adivsecroyntlionwuous upper
hydraulic conductivity (DuPont, 1992). The lower zonc consistsof the continuous and
discontinuous sandstone layers having low permeability of 1 x 10 cmsec. The
sandstone layers are separated by laterallycontinuous shale layers. Well yiclds from the:
suapnpdesrt(oannedltahyiecrksearr)eovfetrhyeltowwo, rlaatnegrailnlgy fcroonmti<n0u.o5usgspamndtsoto1.n5eglapymer(sDluoPcoantte,d i1n99t2h)e. loTwheer
zone at clevations between 710-740 feet above Mean Sea Level (Figures 3.4A and 3.43)
has been designated as the "underlying significant aquifer" and is currently monitored
`semiannually as required by the permit
RInic1h9a8r9d,seoing(htLmLoMnWit-o1ritnhgrwoeulglhs8w).erHeoiwnesvtaelrl,edfaitvetohfetLhoecsaelmLoanndiitiolrlwbeyllTset(rLaLTMeWc-h1, 2,-
3,5, and ~7) were closed in 1996 because hey were screened in the discontinuous
shallow clays and underlying weathered bedrock. LLMW-8, 2 bedrock well, was closed
iinnst1a9l9l7edbienca1u9s9e5iat nwdas19d9ry7., rTeswpeoctaidvdeiltyi.onaLlLbMedWr-o9ckwwaesllisn,stLaLllMedWa-s9aabnadck-g1r0wouenrdewell
These wells are screened within the significant underlying aquifer. Table 3.0 summarizes
the well construction data for the existing monitoring wells.
Groundwater Flow
e`lGervoautnidownactoenrteoluervamtaiponssfhoarvtehebesiegnnimfeiacasnutruenddseermliyianngnuaaqluliyfesrinhcaeve19b9e4e.n Gprreopuanrdewdatferorm
pthriessednattamaaprseqfourir2e0d0b1ytthhreouWgVhN1P99D6EaSndPe1r99m4i.t NToh.e0g0r7o6u53n8d.watFeirgucroenslo3u.r5sAwtehrreough 3.5G
CWirinogionmOF pudotmzeees mE
33
000540
etes1os MAH000477
sinPian arama
Local Landfill
transferred from the original maps submitted for the permit to the updated Local Landfill
base map.
iEnvsatlaulaltatiioonnoifnlfiomrimtaetdiognr)oiunnddiwcaatteesraeldeovwantwieonarddatvaerftoircatlegrcaldoiseendtwbeeltlwse(ebnastehde uopnpweerll
`duinsdceornltyiinnugosuisgnwiaftiecranbteaaqruiinfegr.zonIen aadnddittihoenl,oCw-e8rpsraensdesnttoninetlhaeyeurnsdceornltyaiinngisniggntihfeicant
aquifer provides further support for adownward vertical gradient.
`fTrhoemgtrhoeunsoduwtahtetro cthoentnoourrthmatopwsarfdorstthheeupnladnetr.lyTihngessiagnndisfitcoannetsoaqfutihfeerusndheorwlytihnagt.flow is
sHiogwneifviecra,ntgarqouuinfedrwaotuetrcrmoapyinatlhseo fvallolweydowwanllsslowpheerweitdhiisnchthaergferamcatuyreodccruorckassosfeetphse.valley
wallsand ultimately enter the alluvial terrace deposit on the main plant. Groundwater
cdiasncdhiasrcghianrggteodsoewepnswualrtdimtaotelleyacmhiagtreactoelsletcottihoen pploanndtstharnodupgihpaesn1u0mbtheeromfapiantphlwaanytsw.herIte it
enters storm sewers and discharges fo the Ohio River. Groundwater also can seep to
stmeamlalcesturnecaomnsfidnraeidnaiqnugitfheer pwrhoepreertpyutmoptihnegnoofrtohn-asnidtefalcotwiivnegwoellthfeieQludsatceonmtarroylsalluvial
ogfrtohuendLwoactaelrLfalnodwf.illG,rioutnodwwaartdesrtfhleopwuimnptihnegalwleulvlisalloacqautifeedrn,eaadrjaacnedntpatroaltlheelvoaltlheey Owahlilos
River. The pumpingof these well fields also lowers the groundwater level to below river
pnstudamgpeW,iningidwuecmlilns.gissWudraiftsaecchreawfrargetodemrtfhertophmuOmthhpeiiornigRveiwrveleol.sflisowusiendtofotrhenoanl-lcuovnituamcttocwoaorldisngthpeurposes
3.3 Water Quality
33.1 SurfaceWater Quality
Table 3.1A presents the historical C-8 concentration data available for surface water.
Figure 3.2 shows the surface water sampling locations,ifthe location currently exists.
`hSaavmeplbeesenfrcoomlltecwtoedouptefrailold,icfaolulryosuitnlcetes,19t9w4,o sCt-reamcso,ncaenndtroartieolnesaicnhattheesoautmfpallilsnganldocation
outlets range from <0.2 uy 10 80 ug/l. Stream sample C- concentrations ranged from.
4.12 ug/l to 15 ug/l. The leachate sample, collected in the pipe fiom the leachate ponds,
.
had 2 concentrationof 31 ug/} (February 1994). For sample locations having more than
two sampling events, the concentrationofC-8i decreasing with time although it is
cdiofnfciecnutltrattoiaocncuatraOtuetllyetid1e0n1t,iflyotcraetneddsaitntsheamnpolrethsewaisttehrtnhpeolritmiiotnoedfdtahtea sseitd.e,ThhaeveC-
decreased from 54 ug/l to 12 ug/l over the course of three sampling cvents.
3.3.2 Groundwater Quality
Analysisof C-8 in groundwater has been conducted annually on a voluntary basis since
1996. Table 3.1B presents the data available for C-8 in Local Landfill monitoring wells.
o
GLrLoMuWn-d4w,a-te6r,waansd s-a9.mplLeLdMaWn-nu1a0llwyaisn s1a9m96p,leadndtw1i9c9e8inth1r9o9u8ghan2d001199f9o.r tThhreeelwiemliltsc,d
CWoinmimogeonn0d8 aba me
4
000541
EID168106.
MAHO000478
Nain ioandLatte
Local Landfill
``maomnoiutnotroifngdwaetallmsaakreesloitcaditfefdicaultthtroeedesveepalroaptecorneceanstr(caetlilosn) cofotnhteoulramndafpisl.; tIhneraedfdoirtei,on, the
annual data for the past four years is posted in Figures 3.6A through 3.6 but is not
contoured.
}
C8 concentrations in LLMW-9and-10range from non-detectable to 0.22 ug/l. The
outg/hleratndwofrweolmls1,.3L2L0MW15-4ug/alndre-s6p,echtaivveeltyh.e Ahligthheosutgchotnhceernetriastliiomnist,erdadnagtian,gthferodmata1.s4h1o0ws3.9
a distinct reduction in C-8 concentration over time for wells LLMW-4, -6, and -9.
3.4 Site Conceptual Model
"The Local Landfl site conceptual model describes the potential exposure routes for
current and future human and ecological receptors. Potential exposure routes were:
evaluated and classified as complete or incomplete.
Access to the Local Landfill i restricted by electronic and locked gates at the road
entrances. However, a posted nature tral has been established on the east sideof the
elannddifnilglnperaorpetrhtey.lanTdhfeiltlrsaiellelcotorpiscaallryouonpdertahteedcagsatteer.n Tpahret nofatthureeltaranidlfiislastmaartriknegdantrdail and
docs not cross the cells. Access to the site from surrounding roads is possible but is
discouraged due to the heavily wooded nature of the property and the hilly terrain.
"The three cells at the Local Landfill are covered with a low permeability soil and
o
vegetative cover, "This cover prevents human ad ecologies HCeplors" sxposurs to the
lHaonwdefivlelre,d mtahteesreiamlastearniadlstoctohueldoiplostepnottieanltliyalbleyeixmppoascetdedbybyexttheenslainvdefidlilgmgaitnegrioarlrso.oting in
the soil by animals or unauthorized people. Therefore this pathway is considered to be
potentially complete but minimal,
An additional potentially complete exposure pathway exists fthe soil and vegetative cap
iisnesrpoecdteedd bqyuaprrteecrilpyitfaotrioenv.idPeenrcmeiotfWcVr0ac0k7i6ng53or8crreoqsuiiornes(wthhaitchthceolualnddfailllloswursfuarcfeacweilwlabteer
o1f0seunrtfearctehewastoelri)d.waPsetreCdoenpdoistiito)naGnd-1e6voifdetnhceeopefrsmeiti,liangsotforsmowlaitdewraesrotsi(ocnauisnisnpgecptoinodniinsg
conducted annually. Therefor, this potentially complete pathway i considered to be
minimal.
dAottwhnewalarnddftilhlr,opurgehcitphietavteigoentaisteexdpseicltecdovteortaaknedoinnetoo fthtwcoellpsa.thsH.owTetvmeary, itnhfeilltorawte
permeabilityofthe soil cover reduces the amountof inflration.Ifthe precipitation
idnofwilntwraatredsst.he1stoimlacyovbeer,priet vweilnltepdosfsriobmlyfeunrtchoeurndtoerwnthwearladndmfiilglramtaiteornibalystahnedlwoiwll continue:
pdeorwmnewaabrildi,tyitcslhaoyusladnednwceouanttheerretdhebesdarnodcskt.oneHsowaenvdesrh,aliefthlaiyserwsa.teGrromuignrdawtaetderfurftlhoewring
through the sandstone layers that outcrop in the valley walls located above the plant site's
o
sToocuatthieonmofesdcgeepwsouatldsboemeexpplaocseesdoant tthhee spurrofpaecretyinhaseveepsb,eeifnseoebpseserxviesdt,.paTrthiecuelxairsltyetnhcoesaend
mentioned ncar the leachate collection ponds. Muchofth site remains unexplored,
CWoanmaiginodn0,s8o mom za mE
000547
3%
Etestor MAH000479
Main lantsnd Logit
Local Landfill
tghreoruenfodrwea,tceormtpolseutrefaecvealwuaatteiro)niosfctuhriesnptoltyenntoiatlaveaxiploasbluer.e pathway (surface water (0
oAvneortlhaenrdpfolsoswibdloewmnisglroaptei.onIrnouthtiefsocrasperetchiepiwtaatteironwoisuldidrencottleoncwouanstseurrftahceefwllatmeartevriiaals at
any point it time. This potential exposure pathway is considered incomplete.
aConndtafuctturweithhugmraonunadnwdaetceorloigmipcaacltreedcebpytoCr-s8. iHsoawneovtehrer,pcootnetnatcitalwietxhpogsruoruenrdowuatteerfourncduerrrent
vtihae slaenedpfsililsipsolsismiibtleed,inaltthheovuigchi,nictoynotfacPtownidth1,lenaecahrattehetshotuhthaesrrnemaocshetdcetlhle.gProonudnsd asurreface:
ogpreounnadnwdataecrcefslsoibwliengtothlriomiutgehdtnhuemsbaendrsotfonDeuPlaoynetrsetmhpaltooyuetecsr.opAis tthaetevadllperyevwiaolulssly,located
baebcoavuestehseepelpasntinittheissasroeuaathreernnoetdgeeviwdeonutl,ditbies alipkoeslsyitbhlaetcgornotuanctdwlaotcaetriofnl.owHsodwoewvnesrl,ope.
tweirtrhaicne.thDeeftrearcmtiurneidngrotchkesoexfisttheencvealalnedy wlaolclastiaonnodfdsiesecphasrgoenstthoetphreompaeritnyphlaasntnoalllbuevieanl
completed therefore, this potential exposure pathway cannot be fully evaluated.
35 Data Gaps
"The following data gaps were identified forthe Local Landfill
Identify the locationsofsecps in the valley walls anddetermine water quality
o
with respect to C-8 concentration.
Q Determine the C- concentration in streams and other surface water bodies.
Q Acquire additional geological data to refine the Site Conceptual Model.
aInnsdtagllroauddnidtwiaotnearl qmuoanliittoyrdinagawells to provide additional groundwater low data
Gdealtihneeartiaodnd.itonal C- concentration data from monitoring wels for plume
Activities to fll th data gaps will be proposed and discussed in the work plan.
36 References DuPont.Wa1s9t9e0.&WGaesohliognigctaolnEWnogriknese1r9in9g0DPerpealritmmiennatr.y Hydrogeologic Assessment. Solid
Wo1r9k9s2.ApVeerlif1i9c9a2t.ion(VIonlv.es1t)igation EI. DuPont de Nemours Co. Washinglon
We inigion, OFT
000543
Emtes108. MAH000480
TABLES
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MAHO000482
Table 3.1A
SCu8mmian rSyuroffaAcneaWlyattiecralSRaemspulletss:
Local Landfill
Washington, WV
eF Fr ae e mOUToFAw LL 60%
Tews15
|
ema Tams
[emnes 1306}
Pe TT er [apne Tw 1
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LI = oe== : [eaneeTw
re ==> STREAM 2
T mmaw}
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Table 3.1B `SummaryofAnalytical Results:
C-8 in Groundwater Local Landfill
Washington, WV
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000566
EID168131
MAHO00503
eimai `MainPlant andLandfils
Letart Landfill
4.0 LETART LANDFILL
EnvironmevsalSets... -- ------------
harris ws
tl
WS i meV en-, rots m isese oe mh I m eee eIE ions @ ID IE eee Fa e ----e--e --o--e a ee wma ln mtm--
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000567
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ES MainPantandLandsils
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@ 41 introduction
wTWiheteshtiLneVatiarrg1ti-nmLiiaalned(frFialidlgiiuussrleforc4.oa0)t.medtAhjeuwslatatnnedofrirultslheopafenrtidhmeewtetelorlw(nsFuiorgfvuLereyetai4sr.1tb)e.iinnMgacsoomnplCeotuendtyfo,r the area oTWpaheserhalitannedgdftiaolnlndcWcoolvroeksrsesd.aupInptdrweoarxsiWmeianstotepleVyriar1tg7ii-noaincarfeSrsoolomifdtahWe2a0es5at-realycNra1et9pi6ao0rnscaetllo Po1of9l9ll5au.ntadnTothwDenielsadcndhbfriylglDeuwaPso.nt r`Emloaiuimnnitdnewanataitnocener.SmyosntietmorPienrgm,iotutNfoa.llWanVd 0su0r7f6a0c6e6w.atTehris.mopneirtmoirtirnegquainrdesenqguianrteeerrleyd cap
ssFloyoiincgltauthrrieeeotsni4sec..n2btToshtuhetnoodwlmeasrnldtitfhniheelerlsll.awannaddHfsfoiilcwllolenevmsxeatttrree,nurtcia,taeolhdryiidwserincottohagmtieinpoolonaos,gnetiadotepuoerofavghlarilargupahahvtlyii,ynoenpalnaiandnsddtmii`occhnaaltiseatndoyortiahcnnaotgdmtwpshefaeltclntaetduroarl
pfeeertm,eaavbeirlaigtiyongfaabboouutt10f7ecetmiinstehcic(kDnuePssant,
1993).
The
sol
thickness
ranges
having a
fro4m to 14.
@ onevede iobeesuc os C-nheis pmLlieatsnactretltlhLaaatnnedcfooiunlsslitsrrteaescdhe.ipvrAeidpmpawrraioslxtyioemfwastacesrlfayrp5o,pm0ro0td0hu,ec0Ft0,l0uspocorruoanppodmlseoytmfaelr,wamwsaotnoeudfpaepcratlyuleeratisrnagwnepdrreobcidneisss,spaoatnsedtdhe
in the landfill. This waste is believed tobe the sourceofC-8 in the Historical sTehoesyLmetthaerttiLcanadnfdilsloiwlacsappe(rDmuaPnoenntt,l2y0c0l1)o.sedIbncyluindsetdalilninhgeancleonsguirneeaecrteivditmiuelstwioleaysetrhe cihnastianl-llaitnikonfoencfaingl.eacThhateeccaopllceocntsitornuscytsitoenmw,aesrocsoimopnlaentdeddrianiAnpagre] c2o0n0tr1ol measures and
4.2 Environmental Setting
4.2.1 Geology
TV-hsehaLepteadrtvaLllaeyns.dRsesisdiutuaaltesdoiloncovehresavmiolystdilsasnedcftield aprleaast.eIaungceonnseirsatli,ngthoefsseovileraat lthseeseipte
has been described as residual in nature, consisting primarily
athmeawxeaitmhuerminthgoicfkbneesdsroocfk2.0.A5tfmeeo.st landfill areas, the soil is
of heavy less than
clays derived ten feet thick,
from with
The underlying bedrock at the Letart Landfill consistsofiner-bedded red and variolored
ifsDenauetnFr.dikgyTauhrordere Gcl4aro3lco.cautapirT.ochnooeuTfshtewsthowmalocaer,xcorsiaosnms-sdus-emsgcertctaityhoi,inocsgnoksrnf,eeesAnts-,oheAaf"untndahdenbedrrDlouBywn-inBkn"ags,ragdcncrdoGoslrstosooginuynepgoafirtnchetsthhhleiasonPwdrefneirglmilioaanrnefsasg5he7o0wn
-
4.4A and 44.
on Figures
EVEinton 5
--
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000568
Enis
MAHO00505
MeaoiPiaowaLrdcstttwss
LetLaetratrLtaLnanddffiillll
o
Gbeeaorlionggiczoinnevsestthiagtatwieornes dceosnidguncatteedd aatstZhoenLeetAartthLraondufgihllZoindeentFi,fiweidthsiZxosnteraAtigbreaipnhigctwhaeter-
sfihnaellgorwaeisntedzocnryestaanldliZnoenseanFdstthoendeewepietsht.occTahseisoenazlosnheaslecolnesnissets.ofZmoansessivAe,tvherroyugfhinFe taore
tsheipcakrnaetsesd. bZyolnoecsalAlytchornotuignhuoDu/sEshaarleeudnisictosnttihntuoaurse.geZnoenrealFliystetnhefefeitrsorlagtreeraatlelry in
caonndtailnuoonugsthzeonOehiuondReirvetrhenelaanrdftilhle. soZuotnheesrnAe,nCdo, fD/tEhealnadndFfilolu.tcrop on the valley sides
4.22 Hydrology, Hydrogeology and Groundwater Flow
Hydrology
`lTahnedfLieltlaerdtmaLtaenrdifaillsl.enPgrienceipeirteadticoanpfsalylsitnegmopnrtehveenctnsgisnucrefraceed wcaatpesryfsrtoemm ctoankteascotnineogftwo
piamtphesr.meItamblaeygienfoimltermatberdaonwenawnadrtdhtehnrfoluogwh ltahteeravlelygetdaotwendsslooilpeanodne0ncpooufnttehrethe
vgeegoemteamtbivreanlea.yerAdloiwenmsaltoipveel.y,Inpreeictihpeirtsaittiuoantmioan,ytfhlisowsuvrifaacoevewraltaenrddfolcoswnoont tcoonpotafctthte.he
aldanjdafcielnltedtomattheerciaalpssaynstdemm.igrParteecsipdiotawtnisolnofpaelltiongwaorndsthdernaoirntahgweedsittcshiedse cooftnhsteruucptpeedr pinarotr of
tdhietcchatphaftlofwlsowdsotwonaslsoepdeimteonwtartrdasptnhearsoLutMhWw-es6t., aPwraecyipfirtoamtitohnefallalnidnfgiolnitnhtoe aredmraaiinniangge,.
o
portionsofthe cap flow downslope and towards the south in drainage ditches.
Hydrogeology
CH,ydDr/aEulaincdcoFn)doufcttihveitbyetdersotcikngzfio. nessilnudgictaesttess(tZhoantehAes)eaznodnebsordeihsoplleaypalcokwehryfdersatusl(iZcones
croanndguicntgivfirtoym(1Te0tracmT/escehc Rtioclheasrsdtshoann, 110990)c.miZseocn.e(AThheyrderaaruelincocwoenldlusctmiovniittyoirsinlogwZ,one
rBa,ntghienrgefforreo,m it10wascmn/ostectesttoedl.e) sZtohnaens1C0annsdeFch.avZeonveerDyIlEowhyhdyrdarualuilciccocnodnudcutcitviivtiiteisesare
also very low and range from 10" cm/sec to 10% emjsec.
ZViorngeinFiahaSsolbiedeWnadsetseigMnaanteadgethmee"nutndReergluyliantgiosnisgnbiefcicaaunsteaiqtuisifelrat"eraaslldyefcionnetdinbuyoutso tuhnedeWrest
tTahnedfllaln.diilMlosantdciusrrtehnotugghrtoutnodbweathyedrrmaoulniictaolrliyncgoinsnceocntdeudcttoedthienOZhoinoeRFi.ver southofthe
:
wTahteerl-obweahryidnrgauulniics.conIdnuacdtdiivtiitoyn,camnanbeyastarnidbsuttoendetuonitthse ivnertyhefrineeg-igornaitnyepidcnaalltyurdeiospflatyh.e
effilfleecdtiivnebpyoraoustihtiygeansiclomwinaesra1lpser(cee.ngt,.kaTohliinsitleo)wspoomreotsiitmyeraefstuelrtsorfirgoimnaplosreedsipmaecnet being
deposition.
tZhoenseoFutghrwoeustndawnadtefrroamvetrhaegenolritnheatrovtehleocsiotuitehsewasetre(DcuaPlocnulta,te2d00f0o)r.flTohwesferovmaltuheesnaorreth to
rzeolnaetiivnedliyclatoew,th0a.t01graonudnd0w.a0t0e3rff/ldoawybreenspeeactthivtehley.lanTdhfiellloswvveerlyocsiltoiwe,s actatlrciubluattaebdleintothteheF
CoWamrpiwsgoonno08vesabe ma
43
-
000569
EID168134
MAHO00506
veresieets Main PlanadLanncft ils
LoLtetaarrttLLaandnfdilml
ry low hydraulic conductivity presen nth F zone and al th overlying nits as wel, Low vertical hydraulic conductivities in the overlying shallow zones limit infiltration and recharge down to the F zone.
`The saturated thickness ofZone Franges from 22 feet in the upgradient well (LMW-24)
mtoabneytiwnesetnan2ceasn,dth8efmeoetniitnofriivnegdowewlnlgsraatditehentlwaelnlds (cLanMnWo-tSbAe,sa-6m,p-l9e,d-u10r,an4d8~h1o1)r.s I(nor slcorngeeern)natfrtveralp.urging, when a sufficient quantityof groundwater has recovered in the well
`ThGirroteuenndmwoartietrorFilngowwells have been installed at the Letat Land in the Zone A, C, DLIMEW,-a1n0d2FsnadndLsMtWo-n1e1u,nitwser(TeetirnasiTaelcedh iRnicOheatrbdseorn,301091891;0 1p9r9o0v)i.deTawtodoifiotnhsesdeotwselflse,m 2Z0onnce aFndtoptrhoevindoersthwealnldcsoonuttrhuocftitohne liannfdofirlmla.tioTna.bleWa4t.0erlilsetsvetlhemewaelslus.remmoennittosrainng each
calculated groundwater elevations have been measured quarterly. Figures 4.5A through
4tfo.or5tFhtehperupopevdriamdtieet.davLaTeirtlaiarsbtldeLataaannnwduaaisl rbgaarssoefuenmrdorw,cadtefrieolmevtahtioorngcionnatloumrap`msapesufbomriZtodnefFor haserpeequrimrietd TrelheenvaltsoicoantdsieomtneearamsniudnraloitdmiioitnneodtfhnegumrmoobnueinrtdoowrfaitmneogrnwiletlowrsidniingrdeiwccetalitloesnaswdiwtoihwtihmniwnZaotrhndeesseveAzr,otinCceasl.angdrHaoDdwiIeeEnvterw,ithin ctheentsirtoefgtrhoeunldawnadftielrl snyastneomr.th-WsioluitnhdZiroencetioFn,.a gGrroouunnddwwaatteerrdiavsitdeofehxiestsdicvaiddeerltohews rssthowoeuttumhoaensandstdtenstooroutwtlahhwroeedwrsst.mtinohenZGiOarthnooieruoinFndRgiwivawetehrel.srl iGiaernrvodeauitncidaowtneaadstaestri,wgeihsntccloofumdtiphnoegnehdnievtiondefewofllryoiwiwsnactirotwdeadrdLsAtWhe-11, Rsiinnyadsptitiecesdampcdoisenncstre2he0aatt0os1aetsniheniwndiintchesaeqatuleoiabtltshiiaebotrrnvgiueormdfotsvuhtonaeltdeeuanmftgoeiorenfgefrweloraouetwndeudranwdapdetiressrcytshhftaeelrmogA.winGhgIanTsfranod1odmibtytihieoenn.lbgee(arehcnerhaaretteedayucccohstleeliddeoucncteidon eCvoanltuiantueeldomnogn-tietromricnhgoanfgegsroiunngdrvowsutnedrwaelteevratfiloonwsroefsZuolnicngs(ArotmhrcoluogshurFeiss eretqusire 10,
4.3 Water Quality
4.3.1 Surface Water Quality
TUVhpoilpsuenrdtaaatnradyissLuporrwfeaescerenptwoeandtdeisrn,sTnaaombpllloinengge4.r1f4.eorxiTCth-.e8 Dthuwsroiblneogcecatopioennrsfcosirammrepdcleopidefrotmihoonedsitecnaeglqilunycssenirtnelctye,c1o9tp9e1,
o
scyxsctaevma,ictdheasnedppolnadcsedweinrelodwewaarteesroefdtnhedlatnhdefisleldpirmieonrts uhnedermlaytianlgitthoenpoonfhde wceerpe
Currently, only two surface water locations still exist (due to landfill cap construction)
Sn te Complain tMhottoeryyddaotaarOrka 22 cJmaneaz2
a34
_--
00057
eoesiss
0
MAHO000507
Meiaess `MainPlant and Landfils
LeLteatrarttiLaannddffilill
`and are being sampled. These locations include the leachate from the landfill [location
o
002(leachatc basin)] and the stream located slightly eastofthe property line along Rt. 33,
`The locationsofthese surface water-sampling points are shown in Figure 4.2.
4.3.2 Groundwater Quality
-
GforroCun8dwpaetreiordifcraolmlytsheinmcoeni1t9o9r1.ingHowweelvlerh,assaalmspolibnegendivdolnuonttatraikleypslaamcpeloend aanndanannuaallyzed
`aabvdaadsiielsdaubntltoeiltfhoe1r9pC9e-6r8mainftrdoaqsmu2ammrotoneniritltoyorsiranimgnpgwleiplanlrgsabmaeettgetarhn.e tLheTetaabsrletecLoa4n.ndd1fhBiapllrlf.eosTfehne1t9sl9ia9ml,litwheihdsetdonartiCac-as8lotawnmaaaslkyseiss
ccoonnttoouurreidn.g tFhiguvraelsue4s.d6iAfftihcruoltugthhe4re6foDrep,retsheenvtatlhuecsCw-erceonpcoesntetdatoinonmavaplsueasnfdo noJtuly
2001, January 2000, July 1999, and November 1991, respectively.
caAopnnpceieannrittsiratalhtaeitxoantmhtiernceanotdniscoe(nnTotarfbaltteihoe4n.gs1rBm)oe.uansdFuworaretwdeerilndla1t9ha9ad1voiewnsegrndeoatttahsehfilooowwmeast1n.9y9o1Fbrtvhioromouus1g9oh9v1e2,r0a0tl1hle, it
concentrations in all wells increased. Currently, concentrations are now `decreasing again
cipnoemrtpfhloeirmcmoatsthetedraebncyaelntythssesafmabptelthiwanelgeetnvher1ne9tes9.1diafHnfordwee2n0vt0ea1rn.,alIiyndtieacndatdliiftlyisiobnngo,rtatrhteeoenrdifss ihfn atvehoeeftbdteahsteean iicsnosnttarlalcattieodn to
onoftthbeeeonbgsienrevearbeldecianpthsysltimeimte(dprreevceennttidnagtafurther surface water inflation) may or may
Fanoarlytthiecamlosptrorceecdeunrtess,amapnlditnhgeeavneanltytaincdalainnasltyrsuimse(nOtcattoiboneru2se0d01w,ertehemosdaimfpileidngaangdain
cbfooerntacelerlntafrcuacttuuirroeancasyniainlnygstrihoseuoCnf-dgw8raoatuneanrldywitsiacrtaeelqruriessrauelmdtpstl.oesaTcfhcoeursrCeat+me.oldyCiefovinaelidunaputreeodhceemdoulnroientsgo-rwtiielnlrgombfefrCaetn8ldisziend
`oundwater quay,
ulIFiitmiatealsysummiegdaltchsat 0impthaectOehdiogrRoiuvnedr,wattheerCl-o8whsistforroimcaZlomneeanA fdoorwLnMwWar-dSBto(ZToaneblFean4d.1B)
cfiavnerb.eTuhseedfaollloonwgiwngitasthsumpesttiiomnastwedergeromuanddewaitnetrifslucxalctoulcaatliconu.late the C-8 loading to he
O Tgrhoeusnadtwuartaetredetlheviactkinoenssmiesa2s5urfeamtenLtMaWn-dSBth.ereTfhories,iisshaigchoenrsetrhvaantitvhee mvaolsuet.recent
-
@ Tgehoelolgeincgtchroofstsh-seecatqiuoinfser discharging to the Ohio River is 1000 ft based on the Q The historical mean value of855 ug/l for LMW-SB, adowngradient wel, TrleihnpeeraevrseevlneotlcsoicttiyhteioefcsognfrocoreuntntdrhwaFetaitzoenoroniefnaCtrh-ee8caailnqcutuhileafteaieqrdui10f0.e0rb1.ef0i.d0a1y.dGaroyunfdrwoamttehreanvoerrtahgteo
the southwest and 0.003 fUday from the north to the southeast (DuPont, 2000).
o
Using these assumptions, the calculation for loading to the Ohio River is shown below:
CVoimnmotn88 ym es
3
} 00057)
Enotes
MA000508
E [H-- EBSEEEEEEESE--------Le--tartELandn fill
o
A=Area=1000ft length x 25 ftsaturatedthicknessforZone F = 25,000 fi!
V = Velocity = 0,01 Uday (estimated)
Q=flux=AxV=(25,000 f)x (0.01 fdayx) (7.48 gal') x (365 day/yr.)
= 682,550 galiyr
Me=s(8s55 ug/l x (12/x1(10kg/10u00g)x)1 10/2.205 ke) x(4.785 gal)
= 147610" Ibigal x 682,550 galiyr
= 1x10" bly
sEhsotuilmdatreedsualntniunaal vleoraydilnogwtoC-th8ecOohncieontRriavteironisivnetrhyelOohwiobaRsievdero.n Tthheeclaolcwulcaatlecdulmaatesdsmaansds oisbsreearsvoendabinlethgeiFveznotnh.e low hydraulic conductivitaineds low average linear velocities
4.4 Site Conceptual Model
c`TuhrereLnettaarntdLfautnurdeihusimteacnonacnedpetcuoallogmiocdaellredceespclroirsb.es Ptohteepnottieanltieaxlpoesxuproesurroeutreosutweesrefor
evaluated and classified as complete or incomplete.
TenhgeinLeeetraretd Lcaanpdfsiylsltecmlo.suTrheewaensgcinoemeprleedtecdapinsyApsriiclm2p0r0e1vewnittshhtuhmeainnsatanldlacteioolnoogficaanl contact with the landfilled material. Contact with landfilled materials would only be
pbinoysstseaixltblelenedsiiffvetenh,ceivncigagporerssotyurssitcdtesimgawgceicnregsesbtyboybaneuinmiaanulttseh.notiroHinzoaewldelyviebnrdri,evadicdehuneasdlesbvayengwdeotaranktieimroanslsao.rndtTrhaeepsrpperaofsporerireas,toerly
dpiartehcwtaye.xposure to landfilled materialsi a potentially complete but very limited cxposurc
Esstyxosprtomesmurrudenrooaffifnliaasgnedaflcisolonlaterdoplomtsaetwneetririaaelldhbeuesmciaagunnseedaonftdoeecrcooonslvioeogyincotafhletehrxeupnoeosnfugfrifenrepoeamrtehtdwhaecyal.pansdHfyioslwtleecvmaedpru,teoct1aop
dceaspi.gnIantaeddddiitsiconh,artghee lpaonidnftilalncdaptoiselriemqiuniarteed tthoebpeotiennstpieacltefodrartulneoafstf-qrulaartteedrleyro(spieornmiotfthe
PrreeqvueinrteimoenntPlCa.n1.2.TAh)erfeofroerev,idtehniscepooftenetrioaslioenxpaosspuarretpofatthhewsatieysSatsoorma WpaotteenrtiPaollllyution
complete but minimal exposure pathway.
TclaahnpedfsLiyelstltaerdetmmaLatanenrddifaiilslsld.iesnScguhiranfreageceredewdaacttaehpre smsyiosgutrtahetemerpnsrteeodvwegnaetrosdftsshudrrefaailcanenadgfwiealltd.eirtcBfherecosamcuoscnoesntttrhaiucscttiseundrgfaicnet.he
`wcaotnetarctdoweisthnotthicsosnutrafcatctehewaltaenrdfiisllaendimnactoemripallest,eitexisponsoturiemppaatchtweadyb.y C-8. Therefore,
`thGirsouinmdpwaactteerd cgornotuancdtwiangtetrheprleasnednftilslaedpmoastseirbilaelhhuamsabneeanndimepcaolcotgeidcablyeCx-p8o.suCroentpaactthwwaiyh
pdruieortotogrthoeunidnswtaatlleartifolnoowfptahteteemns.ginGereoreudndcwapa,tesurrfflaocwe uwantdeerr itmhepilnagndifnigllohnasthsehloanwdnfiltlhat
CoVmimpntgoionn s2hetoyaan bona wmv
5
000572
Enter MAHO00509
MawionnPlranwtwanidLbaentdisss
LeLaetratrtlLaannddfimlln
@ ovina he cued rock orb vay hen a 1 `migrated downward through the landfill material. These waters continued to flow as
o
groundwater downward towards Zone F where it then flowed laterally to the west and
south. Currently, the engineered cap prevents surface water from contacting the landfilled
`materials
may still
caolntthaocutgthhegrloaundnfdiwlaltedermamtiegrriaatlsi.n
g laterally and
Groundwater
vertically
under the
underneath
engincered
the
cap
landfill
migrates to the leachate collection is piped to an outfall (002(achate
system. basin)]
Discharge from where it enters a
the leachate collection system small, shallow, wet weather
stream that flows with leachate is a
approximately 400 feet beforeitdischarges to the Ohio potential pathway exposure route for current and future
River. human
Contact and
erecsotlroigcitceadlarcecceepstootrhs, aca however, this pathway is considered complete but limited due to the
`ZGornoeusndDwIaEtearndflFowoicncgurfraomcltehvesaeioznsolnoweoertthehasnoutthhe ldeiascchhaatregecsoltolcthteonOhsiyostReimv,er,
`Contact with this water is limited 10 the areas where these zones may outcrop on the
valley walls. However, in general, groundwater flows downslope within the shallowsoil,
scuorlflaucveiiufms,eeapnds
ferxiasctt.ureCdurrroecnktsloyf,tthheerevailslneoy
wdaaltlasavaanidlawboluelodnotnhleyebxeisetxepncoeseodr
at the
location
of
seeps on the slopes adjacent to the landfill or along the Ohio River. Therefore, evaluation
orfetschpitsorpsotiesntnioalppsastihwsaeyaetxhpiossutriemeroute for current and future human andecological
iGrnoaungdewastyesrtetmhastnfldow0s tuolitmheatweelsytmfigormatZeo0netFheisOhkieolRitvoerd.iscAghaairng,egfroonuenadrvbiynvearllleoyws
pltohoteceansttuiiroafnolacpfeasiftesheewpeaspyisnexetxphioests.aulrlCecuryosrutrseoyfuot,h ctohfuterrheeenitslaanndnofdidllaf.tua aTrvhaehirlueamfboalern,oaenvtdahleucaeotxliioosgntieconafclehrioescreptors s
not possible at tis time.
45 Data Gaps
"he following da gaps wer identified fr the Letar Land:
cwoIandlcelenniltforyanttgihoetnhleocOahtiioonsRoifvesre,eapnsdndettheermvailnleeywawtaelrlq,upaalrittiycwuliatrhlyreisnptehce tsoteCp.8valley
.
2 Determine the CS concentration in the Ohio River.
3 Detemine the C-8 concentration i streams and other surfacewaterbodies.
Q
9
Acquire additional geolog
sInrsotualndaadtdietrioqnuaallimtoyrdittso.r
iwcealllsdattoaptroorveifidncadtdhietSointaelCgornocuenpdtvuialteMroldeolw.
data
and
dGealtihneeartiaoin.ional C-8 concentration data fom monitoring wels for plume
o
Activities to il the data gaps will be proposedanddiscussed in the work plan.
Siren 58
I
0090.
00573
EID168138.
AHO00510
MteannPPteaatngtLneontiss
LeLfeatratrtlaLanndffiill
@ 6 References DuPont.Rem19e9d3i.atLieotnarGtrLoaunpd.fill Hydrogeologic Evaluation, July 1993. Corporate
WY2000007.60L6e6t,arJtaLnaunadrjyi7l,2G0r0o0u.ndCwoartpeorraPtreotReecmtieodniaPtliaonnSGWrIouNpP.DES Permit No.
Co2r0p0o1r.ateCeRrteimfeidciaatitoinonReGproorutpL.etart Landfill Cap Construction, June 2001.
Tetra Tech Richardson. 1989. Monitoring Well Installation Program, October 1989. `Re1p9o9r0t,. AMuognuisttor1i9n90g.Well Installation Program at Letart Landfill ~ Summary
CViomomgiioon,nOdFoywRDAZEE nT
000574
3
ED168133
MAHO000511
TABLES
000575
EE
--
AR000S12
3% [3sl8l-[al=lelzlalw]s)
2sRRREERE EE
HE &{8l=lal] 3121315] 3}
ug BREREEENEEERE
%
588
i=l!
z
weg
S13]
@ 3% [ad LEl lle $055 | REEpiERERRErEEy
F283 3
2
13(3[8]5 [=z (38 855)
=
a LL 1
LEE]
000578 .
Entssrer MAHO00513
o
Table 4.1A
SCu-m8minarSyuroffacAneaWlyattiecralSRaemspulletss:
Letart Landfill
Letart, WV
E Ea a ------ m --a -- Ye r-- ----
TERE
[ e77ew e -- ege ia-- ----s ----
OER
[msmemsoser [io I -- --
--TToziiesese-- s
2i02000
mre i r
1500
a ----
oo
o
ZSee sar nae
ee
|
PRR FLOW RTS
[ oemre oso mao
[ mecror m Bm es --
TREATS [ EFirs:m -- e--e
S TPPERFOND s mpesss e
m ormies e aZowewnr
Snsriorss
oaoo --]
Somtiosenres Tfe o
Sao
70
. 000577
Eotssie2 MAHO00514
Table 4.1B
`Summaryof Analytical Results:
C-8 in Groundwater
Letart Landfill
Letart, WV
TsWmAe
aie Teme
cay
E E E s H H s E H e = = LeHS=a e e e = e = = [sare Te E I 77 T _--
E= =e=== = 300uy]
3020
* E H Saae= e = e = [ Vignr e TT 0 e| = e e ow r e --eswr
Cows TT ome
os
E Sm e E e = m a eT = aa g ag = e]
m wee
I
ee
000578
Table 4.18 Summaryof Analytical Results (Con't): C-8 in Groundwater Letart Landfill
Letart, WV
taeTe sme
TT beeTem [ametTw
TeEa e e S ES -- TI -- -- TT -- E =a = --to 1 arm 0600o001
[meee Tie
1
L E = a e H EF==--B--=e =e a anogoot I
ae
|
= 2160
fame TTT
[nseemsTai
foe ae -- s [eam omes [a[ nimg esT a TTom m 00 er
| wvearom TaT
~
000579
EID168144
Table 4.18 Summary of Analytical Results:
C-8 in Groundwater Letart Landfill
Letart, WV
Ee S ma m [e vm eTa ------] He [es Ea [names
o = E E E m H e e H t ==a =--e a e e a e e = TAWss
7 -- [go de o |--_T200ticup|) ao I e ea ) 1
[avre s s| [7ronses
Ear 530
IEeaIe==: = os
[Seno
eee
5------ or]
Sng Tae
= E E = e e - |
BEE
= ee e |sowien1
ew
|
CC ee eens Top 1
=
--
000580
EID168145
Table 4.1B
Summary of Analytical Results (Con't):
C-8 in Groundwater Letart Landfill Letart, WW
= [e Siew The eeTa ee y [s 1asi e n
FF
= Some
awa
1i mDaatee------ c ----h se-- e ----m ----
e ri y s|
[eI v merr --riaio-- ----1 --
o
[ass
momoorTp
a 1a04n720e00-- m [g ama n]1
mwems
eemy
I 7 7-- -- -- = -- -- --
7 -- --1
ee I eazon TT
ow0
I amoo00 To T e}
*
T [w o -- m we-- e| [mone TT ie [s1 owi are os|
EE 22a00
7]
-
000531 ~
Enissten
MARO00518
FIGURES
--
000582
ems MAHO000515
eee
-
'
oy
Fura
- "ary >
LETART LANAcDcFesIsLnoLsy
- PERIMETER
:
| wo
:- F
v \. ga]
Sl
Ve
el
.
CF
&
nT mN
a
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ome
we Sel
PT Ne Joo
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.
ne
~
i
52
s wotoo23k) g iNE ed en
sone
LE NH
FeiC d FE E
PE
J
<
f=) Ns 3
CEA
-i
-
5'
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NO5 NNwE
fa
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RN
NN
rg NE
3
%
: LEN
He
re
-
co
i
scale
200e 0 3d2000
fone mn om sna 19 se
aw & Corporate Remediation Group
:
rE
Letort, WY.
pny, [Eoe e l
---
-
OWES
cosas 1n000520
--
=
|8
&
#
ao
ANDFILL
ee
~
:
Twbmile
----TeEy
-
& 7 y
-
CH
~
ar Jisetl)
fe
LETART
LANDFILL:
----
/
accesspodgh | N\A
"ga
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;
SC
J
7J
2 ol To
.|
A
otDob SL l ET
PA4 pe
2
Ne
EVA 7i
eX TINK jo Coa !
Nd and ES , .
|
o
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/
25 fury oF Mud un J ES / Lt
i
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COINS
oOTN he LT
a Les
eng
SL
5 te
ee
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i wok
lh
NE ih etar van
AA
tes e
wr N >, N
p= SEs Pali
Con en
. Pe S 2
SCALE
ri, ac
ta nt en wna
PTo ERS `Corporate Remediation Group
rr
Letort Landfill Site
F= m tr ea tent, WouT t. Viegivlr a
200ESE
eoissies MANO000521,
"
eo
N=
NN
9S SEL
wo PN
A ey
Ses
S 7 AN a
CEA aa
=N \J ) = / = BL
A|,FkR= OGx
A = 5 RY \ N = Nie
T NS 7 VA 4 wh = ro J yi In Wkp>
000536
g
.
:
i% i
IF i
aly Uy ar
rie il
Lafe Eaf Ll
f|
LL e i
ol, Hbli:
Ts
8wl
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5.0 DRY RUN LANDFILL
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Taber Teso Dry Rn Landi MoWer t Coni sncionrDsn TSI iyRunLand AscDasTbe -SrcWr TSB DyRuaLas Abt DasTbs Gromer
Fipseso Dry Lard Lecstcn op Fim
Figees1 Ory RnLandi ileRadinMop
Figees2 Dry Rn Landi MoWei lndSnc WtSplLocoMsp.
Fines Dry unLandi CrsSectionLacsion sp
FipreSan Ory Ron Lad Cs SciAon
o
Fiwesdn DyRonLand CosScien 85
FieSSA Dry RonLad GenterEvo Hop Oc 201
FneSSh Dry RonLoni GentsHratonMap Ochs 197
SIC ny on Land Granda Bevstionbip- ctr 198
Finne350 ny Kon Ladi GreamvnerHvston Mop- Octonr 19)
FipneSSE Dry Ron Lal GreaterBeton Map-Ape 172
Fipresen Dry Ron ConcMopnrtockWaelk isy2n000
Fines Dry Ron Consmain Mop Denk Wel. cy 199
FigneSC Dry Ron Concenicn Mop ick Welk cy 199
FigresD Dry Ron CA ConcopeOcrhrne Welk lyX00
Fipne SE Dry Run C8 ConcemaionNopOcc Weliy 1959
Pipa S6E Oy Ran C3 CocenMaspOtvoind Wilh May 198
.
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Emtestss MAHO00537
isn tartnstants
Dry Run Landfill
@ 51 introduction "`TWheestDVriyrgRiunniaL(aFnidgsuirle i5.0l)ocaantdedisweasbtooutfetihgehttomiwlneosfsLouubtehwceks,tionfWtoheodWaCsohuinntgyt,on Works `cmoamipnlpeltaendt faonrdtthheeaLrocacawlitLhanidnfaill1.-miAlewaratdeirususreoamndtwheelDlrsyurRvuenyLsaenadrfcihllispbeeriinmgeter
(Figure 5.1).
"bTyheDuDProyntR.unThLaendlfainldlficlovbeergsaanpoppreorxaitmiaotneilny 11978-6acarnesd oisfati5ll35c-taicvree aptarpcreeslenotf. laTnhd eowned lEalnidmfiilnlatiisoonpeSryastteedmuPndeerritWeNsot.VWirVgi0n0i7a6S2o4l4i.d WTahsitsepeNramtiitonreaqluiProelsluqtuaanrtteDrilsychgarroguendwater `monitoring and monthly outfall surface water monitoring. Fsicgmuprlein5.2g posihntosw.sTthheellaondcfialltwoifatsohnceonlsatndrfuicltle,dmownitihtionritnhge dwerlalisnaagnedbsausrifnaocfeDwratyerRun, a RtruinbutLaarnydofifllthheaNsonrothcoFmoprakcotfedLeoerCsryentchke,twichibcohttiosm ltirnierbsu.tarHyoofwtevheer,OhniaotuRriavlers.oilTphreeseDnrty under the landfill materia is composedofclay and weathered shale. "wTahsetDeriyncRluudninLgansdcSriapl percoediuvcet,s swcarsatpemfertaolm,twheoomdaipnalplleatns,t fcloynsaisshtianngdofbinrso,n-ahnadzasdous dmiisspcoesleldanicnouthsetrlaansdhf.illA.ppCruorxriemnaltye,lyth5e0C,0-00s,o0u0r0cepisobeuloienfvwedadsttsoebpeerthyeeaslrudhgaevsefbreoemn the r1e98m8a.iniTnhge fDifreyonRutnheLcaxnidsftiilnlgrceemlaibnaisncgd coanpaaci1t2y8c,a0l0c0ulyatdio'nsnfeotrf2ll00v1olsuhmoew c4o.n4syuemaprtsioofn (DuPont 2000).
52 Environmental Setting
521 Geology
@ RT penne vel nsalanpom pred Te `VT-hsehDarpyedRvuanlleLyasn.dfRielsliidusailtusaotiledcoovnearshmeoasvtyladnidsfsielctaerdeaps.latIenaguecneornasli,sttihnegsoofsileaverthaelssitteeep hthaeswbeeaetnhedresicnrgoibfesdhaalser.esidual in nature, consisting primarily of heavy clays derived fiom "AThgeeointveecshtniigcaatlioinnvceosntsiigsatteidoonffoardtvhaencDirnygRsuoinl Leasntdfbiolrlinwgass, ecsotmpplitest,eldabboyraDtuoPryonttes(t1in9g96o)f. dsoeitleprhmyisniecdalthpartoptehretineast,ursatlabrielsiitdyuaanlasloyisleusn,daenrdlysientgtltehmeenltanadnfaillylseeds.matDeurPioalnstc(o1n9s9i6s)ted of Stsiafnfd.toThveertyhhiackrndessisltoyfctlhaiys anantdurcallaysoeiylsrilatnwgietdhforcocmas1i2ontaol2r8ocfkeetfriagtmheenttesstanbodraintgrsacweiotfhin the landiilled area. A 1989 monitoring well installation program, prepared by Tetra Tech
CoVannmiingoonnd58he amazesno
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MAHO00538
Mo ltang Lois
Dry Run Landi
o
overburden 1017 feet.
wells
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124,
12B,
13A,
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depths
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11
vTahreicuonldoerreldysiangndbyedorroccaklcaatrtehoeusDrshyalReu,nanLdangdrfaiyl,l gcroenesni,stasonfd birnotwr-nbseadnddesdtroendeoafntdhe:
tPheerDmiuannkaargde DGurnokuapridn Gthriosurpeg(iToentrias T5e7c0hfeReit.chTahredsloonc,at1i9o8n9o).ftTwhoecmroasxs-ismecutmiotnsh,icAk-neAs's of
TanhdeBt-woB,crcorsoss-ssiencgtitohneslaarnedfsilhloawnndidnoFwinggurraedsi5e.n4t7ofatnhedl5a.n4dB.fill are shown in Figure 5.3.
`tThheelraenadfriellon(lDyRaMWli-m1i4t)ed.nuDmabsehreodfgdeeolcopgmiconciotnotraicntgliwneelslswearreoudnrdaawnndounpcgrroasdsi-esnetctfiroonmA-
DA"RM(FWi-g1ur4e,5.t4he4)upbgercaaduiseentthweerlel,isannodtDsRufMfiWc-ie1nt3,dattahetodocwonngfridaednitelnytewxetlrla.poMlaotreebetween
dgoeowlnoggriacdailednattacriossasv-asielcatbiloen,(BD-RBM"W(-F6ig,ur-e115,.-412),waintdh~m1o3r)eacnodnfwiadsenucsee.dCirnodsesv-eselcotpiionng Bt-he
sBtYrastuipgproarphtisctuheniisntoefrspraentdastitoonnsemlaadyeersinsecpraorsast-seedcbtiyonshAa-leA"laoyferras.ther flat ling
5.2.2 Hydrology, Hydrogeology and Groundwater Flow
@ a a reelynshh fed soe,Ny Hydrology `VT-hsehDapreydRvuanllLeayns.dfiDlrlyisRsuintudartaeidnosnthaehevaavillyledyisinswehcitcehdtphlealtacnaduficlloinloscaiteods.ftseMivaennragylssmtaelelp
North Fork of Lee Creek.
Potesta & receiving
sAtsrseoacmiabteels,owIntch.e(D1r98y9R)ucnomLpalndeftielld.a
Thyhderyoldoegtiecrmainndehdytdhraatutlhiec
waanatleyrssihseodftsohiels
aa1re48s1pictubbeitcwfeeeetn pheyrdrsoclcoognidc (stohialtgirsogurpesat(eHr StGha)nCthaen1d0D-yaenadre2s4t-ihmoauterdsttohrem)f.lowPoctaepsatcaity
(co1n9d8i9t)ioalnssoatevtahleualotceadttihoen 2w4h-ehroeutrhpereccaippaictiattyiownaasmeosutnimtattehda.t wPooutledstraedsueltteirnmiunleldltohawt
precipitation values between 5.25-5.99 inches in 24 hours would result in fll low.
TinhaectiinvsetallolwateironhoafaolfltefhaechalatnedfciollllewcatsiocnosmypslteetmedabtyhePoDtrcystRau&n ALsasnodcfiilalteesncInocm.pianss1i99n9g. the
tLheeaclhanadtieillfr(oFmigtuhreel5a.n2d)fitllhrdoiusgchhapregrefsoriantoedapliepaecshabtuericeodllaetctthieonlsouwmepdgleoocafttehdenofrilthawreeas.t of
T"Tohceatleedacathattheeitsoppuomfptehde hfirllomLtehaecchoaltleecstiponumspuemdp tforoam50t,he00c0o-lglaecltlioonnctoalnlkecttoioantnankker
ttrruecakt,mewnhticplhanst then hauled 0 the main plant for treatment in the site's wastewater
Hydrogeology
bGerdoruoncdkwaatqueirfeirs fisoucnodnsiindtehreedovteherbuunrddeernlyainndgsitghneiufnidcearnltyaiqnugibfeerdrfoocrkNaPquDifEeSr.peTrhmeit
o
rDerqyuiRruedngtroomuonndiwtaotretrhmeoonvietorrbiunrgd.enAantdotabledorfo1c5k maoquniifteorrs.ingAtwehlilss htaimvee,bfeoeunr oinvsetrablluerddeatn
CVommepioenn0d8ia raoza ne
5
000602
-
Eotsster MAHO00539
MnP a Lats
Dry Run Landfill
awnedlls15()DRsMtiWl-eGxiAs,t -T1h2e4,ot-h1e2rB,seavnedn 1v3eAl)s,waenrdefaoubranbdeodnreodckiwne1l9l9s9(bDyRMPWo-t1i2,&-13, -14,
Associates, Inc. as required by the permit because they were not being utilized for
quarterly monitoring (Potesta, 1999). Table 5.0 provides the well construction data for
existing monitoring wells.
:
Groundwater Flow Water levels measured in November 2001 indicated overburden groundwater was. encountered betwee4n and 6 feet below ground surface. Although 3ofthe 4 wells completed in the overburden monitor the same hydrogeologic unit, well DRMW-GA is `Ncoomgprloeutenddwaataterrelfaltoiwvemlayphsigwheerrezopnree,pawrheidchforistdhiesschoanltlionwuowuasteatrleonwceorunttoeproegdraipnhtihceareas. overburden section.
Annual groundwater clevation maps for the underlying significant aquifer were available. forthe years 1992-1994, and 1998-2001. These maps are presented in Figures 5.5 through 5.5G. The groundwater contours were transferred from the original maps. submitted for the permit to the updated Dry Run Landfill base map. These maps show that groundwater in the bedrock aquifer flows from the southeast towards the northwest. '`TDhReMgWro-u1n3dwaantder~1el3eAv)atairoenssimmeialasruraendd tfhoer nsecsrteeednewdelzlosne(sDRarMeWc-o1ns2t,ru1ct2ed,realnadti1ve2lBy,calonsde: to each other, indicating thatthe overburden and bedrock aquifers may be in hydraulic communication downgradientof the landfill
i werQuality
5.2. Surface Water Quality Hpoiisnttosr.icaSlamsuprlfiancge lwoactaetrioCn-8focrosnurcfeancetrwaatteiraonrsasempprleisnegntpeodinitnsTsatbillein5e.x1iAstfeonrcseixcasnambpeling found on Figure 5.2. Surface water samples have been collected periodically from these (lDocRaLteiaocnshastien,ceOu1t9l9e6ta0n0d1 haanvdeabtetehne cporlolpeecrtteydbcoounsnidsatreyn)tlsyinfcoret1h9r9e.e loTchaeticonosneeniation of uCg-/8l)inwhtihleelceoanccheanttersaatmiopnlefsrhoamvtehebeoethnedrelcorceaatsiionngs oavreervatriimaebl(efarnodm 6d2o ungo/tlidnodiwcnatteoa27c.le4ar trend (Table 5.14).
5.32 Groundwater Quality
cHoisnttoirniuceasl (grDoRuMndWw-a6tewrassamapblainndgobneedgainn i1n99199;96P.otFesotra,we1l9l9s9)t.hatCc-urcroenncleyntexriastti,osnawmeprle.ing
ccoonncteonutrreadtifoonr scoonmteooufrtshceansabmepfloiunngdeivnenFtisgufroersth5e.6oAvetrhbruorudgehn5a.n6dF.beDdartoackshweolwlsn. inThese
FDiRguMrWe152.-6BwaansdplDoRttMedWbIu3t-noAtfcoornJtuoluyre1d9d9u9eatpopetahresdaantaomsaprleoauds.cTohmepadraetda ftoorthe other
diasttasfoirntmhoensiettowroinwgelwlesl.lsT1h3eacnodnt1o3uAr,mbaepdrsoschkonwdthaotvethrebuhridgehenswteclolnsceenstrpaetcivoenolfy.C-8
CoWmipmrpaivonno0i6hewysa Onzoe snv2 -
000603
54
etesies MAH000540
oaPtan Lact
Dry Run Landfill
These two wells are located downgradient from the central axisof the landfill. For the
`majorityofthe sampling evens for mostof the other wells, both overburden and bedrock,
the C-8 concentration has been less than 1 ug/l. The C-8 concentration for the 1999
sthaamtptlhiinsgweevleintsainn DopReMnWb-e1dr4ocwkaswehlli,ghaenrdtihanreoltahtievrevlyalculeosscmetoastuhreeldandffoirllt,hitshiwselhli.ghGeirven
concentration may indicate communication ofsurface or shallow aquifer waters through
the open well, particularly because groundwater flow in the underlying significant
gberdoruoncdkwaatqeuriffelrofwlionwgsffrroommtDheRlManWdf-i1ll4tonwoartrhdwtehsetDtRoMwaWr-d1t4hewlealnld.fill area as opposed to
5.4 Site Conceptual Model
"The Dry Run site conceptual model describes the potential exposure routesfor current
and future ecological receptors. Potential exposure routes were evaluated and classified
as complete or incomplete.
a`AncdcelsosckteodthgeatDersyoRnusnmaLlalnedrfirloladbs.y iIsncaodndtirtoilolne,dbbecyaeulsecetrtohneiclagndaftielslosnatchteimva,jtohrerreoaisds2
crewofworkers on the landl] area during normal working hours. The daily activity
discourages trespassers on the ste. Therefore, direct contact with landfilled materials is a
complete but minimal exposure route, limited to the workers in active portionsofthe
Tend. Direct contact with landfill materials in the inactive, lower halfofthe landfill is
incomplete due to the leachate collection system's geatextil and geomembrane cover.
o
Contact with leachate at the landfill (or at the main plant where the leachate s treated) is
considered a potentially complete but limited exposure route fo the landll and plant
workers and samplers.
Currently, the inactive lower haoflthfe landfill i covered by geotextiles and
`pogretoimoenombfrtahneesloanfdftihlle dloeaecshantoe ccoolmleectiinocnosnytsatcetmw.itThhetrheefloarned,lplreecdipmiattaetriioanlsf.alTlihnigson this
dprreaciinpaigteatdiiotnchleoswasnddoewvnesntluoaplelyviraeaocvheerslaDnrdyfRluown zCnrdeedki.scThhaerrgeefsoirnet,o tshtisorpmotweanttiearl
exposure route is considered incomplet.
Precipitation falling in the upper haolfthfe landsill may also flow via overland flow
dthoiwsnprseclioppietattoitohnemdarayininafgieltrdaittechaensd, acgoamine,ianncoinntcaocmtplweitteh etxhepolsaundrfeilrlouetde.matAelrtieamlzstaisveitly,
:
mcoilglreactteesddboywntgheraldeiaecnhta.teHcoolwleevcetrio,ntshyisstiemmp.acItheidswaitmeprafcltoewdwinagtewirtmhiignrathteesladndofwilnlwmaaryd be
tshharloeusghantdhesalannddsftiolnleeod fmattheeribaelsd,roitcmk aayndevmeingtruaatlelydocwommgeraidniceonnttawcitthwiinththtehebeudnrdoecrklying,
aaqlutihfoeru.gh Ccounrteancttlyw,itnhotiemnpaocutgehdhgyrdoruongdewoalotgeirci da2tpaoetexnitsisaltloyaccocmuprlateetley eexvpaolsuuatree trhoiuste.
exposure pathway.
Plans are underwayforthe expansionofthe leachate collection system and foar final
o
cinafpillctroavteirngsaysntdecmo.ntTahcetsinegalcatinvdiftiilelsedinmattheerifaultsu.re wil further reduce precipitation
CVoimnitngeiond08he
me
000604
55
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Mia rana Lets
Dry Run Landfill
@ 55 DataGaps
"The following data gaps were identified for the Dry Run Landfill: Q Identify the locationsofseeps in the valley wals and determine water quality with respect fo C-8 concentration. Q Determine the C-8 concentration in straendaotmhesr surface water boics. Q Acquire additional geological data to more accurately develop the Site Conceptual Model. Q Install additonal monitor wells to provide additonal groundwater flow data and groundwater quality data 9 Gather additional C-8 concentration data from monitoring wells for plume delineation.
Activities to fill the data gaps will be proposed and discussed in the work plan.
5.6 References DuPont. 1996. ReportofGeotechnical Investigation Dry Run Landfill, Washington `Works Main Plant, Parkersburg, WV. Geotechnical Group, Civil Engineering Systems, DuPont Engineering. April 23, 1996.
2000. 2000 Dry Run Landfill Operational Report. Submitted January 26, 2001
Pot&Noe.As1s.socOitcattoeabse,rIn9c,. 1918998.9. LeHtytderroflroogmicD.anMdarHykdrKiasuelrictoAnDaalnysWiseobefrD.ry Run, Area
1999. Monitoring Wells MIW-1, MIW-1.4, MW-4, MW-44, MW-, MIV-10, MI10 Abandonment Report, Dry Run Landfill, DuPont Washington Works. March 1999.
"Tetra Tech Richardson. 1989. Monitoring Well Installation Program, October 1989.
Cfroamtmareawe
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Table 5.1A
`Summary of Analytical Results:
C-8 in Surface Water Samples
Dry Run Landfill
Lubeck, WV
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SummaCr8yionfGArnoaluyntdiwcaalteRresults:
Dry Run Landfill
Lubeck; WV
E ----mmwiaS sTIe-- T T --o Ti T-- m I mmeearnT -- --o -- -- m ---- ------
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[ mao n wee r s mes ------se572 --------1
[rssToo] B 7 o [e Ce o --w3s e --s| [o1 e7mmm a --om-- [m [e [ moessr Te o m eor rms ] [ Tr o [[rrawvmaeeew sseT Tw o o om m w ) ] [sa mmTreees ro oosm------1 2 timated value below Iboratory quanision li),
000609
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APPENDIX 1
CONSENT ORDER
(ORDER NO. GWR-2001-019)
000629
-
GOS
A00566
CONSENT ORDER ISSUED PURSUANT TO
ARTICLES 5 and 12, CHAPTER 22 AND ARTICLE 1, CHAPTER 16
OF THE WEST VIRGINIA CODE.
TO: E.1.DU PONT DE NEMOURS AND COMPANY DATE: November 14, 2001
West Virginia Departmentof Environmental Protection Order No. GWR-2001-019 `West Virginia Department of Health and Human Resources
`This CONSENT ORDER is issued by the Directorofthe Divisionof Water Resources and Director ofthe DivisionofAirQuality, West Virginia Departmentof Environmental Protection, and the Commissioner of the Bureau for Public Health, West Virginia Department of Health and Human Resources, pursuant to the authority st forth in more detail below.
1. INTRODUCTION OF PARTIES.
@ cou"ThisnConPseetnetcOirodnerWisDeEnt)er,ed tinotoWbeykanVdibregtiwneseDnetghaeiWmeesnttVoifrgsinhiahDeapnadrtHmeentnof
Resources - Bureau for Public Health [WVDHHR-BPH], and E. I. du Pont de Nemours and Company [DuPont[collectively referred toas the "Parties").
IL. PURPOSE OF CONSENT ORDER. This Consent Order sets fortha seriesof tasks (0 be performed by the Parties in order to determine whether there has been any impact on human health and the environment as a result of releases of ammonium perfluorooctanate (C8), CAS Number 3825-26-10 the environment from DuPont operations. C8 is a material used by DuPont in its luoroproducts manufacturing, process at its Washington Works facility located at Washinglon, Wood County, Wes! Virginia. C8 is not identified as a hazardous substance, hazardous waste or otherwise specifically regulated under West Virginia or federal statute or regulation. "This Consent Order has been negotiated in good faith and the actions undertaken by DDuuPPoonnttpruertsauiansntthteo rtiigshtCtoonscoennttroOvredretridnoannyototchoensrtpirtoucteeeadninagsd,motihsersotfihaaonnnpyrolcaebieldiitnygosntoits part. iamwplseemtefnotrtohrheernefionr.ceDtuhPisonCtonasgernetesOrtdoecro,mtphleyvawliitdhitayonfdtbheebofiunnddinbgys tohfeftacetrmasndofcotnhicsluCsoinosnesnotf Order and further agrees in any proceeding to implement or enforce this Consent Order that it
1
000630
Etestes MAHO00567
@ notcots the validity of his Consent Ordes the uiditon of WVDEPand WVDHHR-
BPH to issue it.
IIL. DEFINITIONS. `Whenever the termsidentified belowareused in the Consent Ordero in any exhibit or
attachment hereto, the following definitions shall apply:
Bureau|for Publ"iTchHeeaAlgtehncaineds"thsehaDlelpmaretamnenthteoDfeEpnavritrmoennmteonftaHleaPlrotthecatnidonH,uimnaclnudRiensgouthreces, DivisionsofAir Quality and Water Resources.
2. "C8" shall mean the chemical compound ammonium perfluorooctanoate.
5. "Detection Limit means th lowest analytical level tha can be elsbly achived wspietchiifniesdpemcaitfriiexd. liItmistsboafsperdecoinsqiuoanntaintdataiocnc,urparceyciusnidonerarnodutaicnceurlaacbyoruantdoeryrcnoonrdmiatlioonpserfoartiaon ofa Jaboratory and the practical need in a compliance.monitoring program to have a sufficient umber oflabortorisavilable to conduct the analyses. Order. 4 "Effective Date" shall mean the date sct forth in Section XVII ofthis Consent
5. "EPA" shall meen the United States Environmental Protection Agency. controlo6.fDuPo"nFtorwcheicMhajceouurled"nsohtalhlavmeebneecnonodvietriconosmeorbcyidrcuumdsitlaingceenscebeaynodnsdhatlhleirnecalusdoen,able Jwuidtihcoiualt tleibmiutnaatlisono,racottshoefGtohidrd,paacrttiiocn, oorr isntarcitkieosnoorflgaboovredmimsepnutteasl(apgreonvciidcesd,, ohrowademvienri,stDruaPtiovnetor Shall notb required to concade to anylabor demands), which prevento delay DuPont from complying with the work plan {he grou7.nd mad"eGbryoudnidgwgaintge,rbMoorniintgordirnlginWge,lldr"ivsihanlgl, mjeetatinnga,noyrcoatsheedr emxectahvoadtsiofnororthpeepnuirnpogsientoof dteetme"rmmoinintitohnreigngphwyeslilca"li,ncchleumdiecsapli,cbzioolmoegtircasl,aond orbasdieorlvoagtiicoanlwperlople,rtwiheiscohfgarroeunindswtaaltleerd.forThe ppruorvpiodseeas ostuhpeprltyhoafn ptohtoasbelleiwstaetdera.bove, but docs not include wells whose primary purpose is to
8. "Groundwater Well" or "Well" shall mean any drilled or excavated groundwater Qo collection system that sauptplsiesdweatseersfor es Comsestoi sim esol public, private, industrial, or agricultural use and shall
2
000631
eotestes MAI000658
Qiong
`workof9D. ec An"nReSitmaabtusr,sPahb.lDe.Cionsttshe" nsheagloltimaetiaonncaonsdtsiamtptlreimbeutnatbaltei(oonnoaftnhhiosuCrolynsbeasnits)Ortdoetrh,ethe icnosAttstaatcthrimbeunttabClettootahinsyCootnhserenptarOtricdiepra,nwtshoonatrheesCer8viAnsgseinsstmhaetnptoosfitTiooxniacsitcyonTteraamct,orass tdoescribed 'AtWtVaDcEhPm,enctosCt,sainndcucrorsetdsbayttrWiVbuDtaEblPe tion acnonynceocnttiroanctwoirtrhetthaienpeudbalticthmeedeitriencgtsiodnoesfcrtihbeed in Groundwater Investigation Steering Team (GIST).
located 1i0n.Wash"iWngatsohni,ngWtooondWoCrouknst"ys,haWlelsmteVainrgtihneiam,aansudfeapcitcutreidngonfacEixlhiitbyiotw1nefodtbhyisDCuoPnosnenttand Order.
11. depicted on
"The Exhibit
Facilities" shall man 1, the Letart Landfill,
the Washington Works and the Local Landi, depicted on Exhibit 2, and the Dry Run Landfil,
depicted on Exhibit 3
@ Eston i lly bith an vce okof trios perhaps1a2n. orde"rRoeffemraegnncietDudoeseo"r ogrre"atRerD)o"fshaaldlaimleyaenxpaonsuersetilmeavteel(fwoirtthheunhceurmtaaninptoypsuplaantniionng,. including sensitive subpopulations, that is likely to be without an appreciable risk ofdeleterious exposure to a compound.
water, o1r3.soil, t"haStcrieselniiknelgyL(e0vbeelwishtahlolutmeaannaptphreeccoinacbelnetrriastkoiofndeilnetesrpeicoiufsicefmfeedctisadsuurcihnaags ar, lifetime in the human population.
IV. WAIVER OF RIGHTS. requiremDeunPtosontfwtahiisveCsonasneynatnOdrdaellr,riagnhtdssihtamllaynothacvhealtloeanpgpeetahleojrurcihsadlilcetinogneotfhtehvealAigdietnycoires to issue this Consent Order. assigns."This Consent Order applies to and is binding upon the Parties, and their successors and
V. FINDINGS OF FACT.
1. emission
C8isa standards.
chemical
substance
which
has
no
established
state
or
federal
effluent
or
2 C8is a perfluorinated surfactant manufactured by the 3M Company and others.
3
000632
Etes1sr MAHO00569
@ piroccescsescatutts W1a9s5hi0ngClosn Wobrkesnfactilitbyy, lDoucpaotnedtiinnWsoodoCropuonttya,eWesstlVeidrgimnaaturing
Washing3l.on WoRrekssidauresocohnatvaeinbienegnCr8elferaosmedMoutorhoepaorl,ymdeirscmhaanrugfeadcttoutrhiengOhpriooceRisvseers,adtisposed of caatptthuereFsafcoirlre,eancd oystihgcenriwfliiscaeensthpioprpteidonofoFfsiutseedorC8d.estruction andor disposal. DuPont also
contain4s.pecificNloimpietmatiitosnsiossnutehdetaomDouuPnotnotfaCu8thotrhaitzimnagyrebleearseelseoafspeodloltthaenesntvoitrhoenmeennvtironment aHsowpaervteircu,laCtBe mrealteaes,esPrMeyoad(darretsiscueldamteormeatgteenrerwailtlhyain aWeVroDdEynPamDiicvidsiiaomneotferAilresQutahlaintoyfpeeqrumailtsto 10 microns), or 3s a volatile organic compound.
to detect5. the preSsienncceeaasncdarlleyvealo1f99C08, iDnuaPnodntrohuasndpecrefrotarimnedofirtesguFlaa,cvioelsuntinarWyewsatteVrirsgaimnpilaianngd shaasmprleepsoratnedd trheeporretssuCl8socfotnhciesntsraamtpiloinsngintowavtaerrio3ussrgeoqvuierremdebnytpaegremnictisesi.ssuCeudrrbeyntWlyV,DDEuPPonatndiso EPA.
6. Asa result ofDuPont's sampling, C8 has been detected in varying concentrations @ p7ubalinc waartoeurndsucpeprltiaeisn. ofits Facilities in West Virginia, including private drinking water wells and
Service7.DistricAtn(a"lLysPeSsD"o)fwdartienrkisnagmwpalteesrhsauvpeplry:eported levelsofCS in the Lubec Public
is the ik5ely souDrucPeoonft,C8bypraensdentcheroiungahntdsaursoeuonfd cC3ecinathoefiftusoFraocpioliltyemserinmWaensuftaVcitrugriinniag.proces,
paricip9.aed in mAulloinpglweistthudeinevsireoxnammeinntianlgstahmepploitnegntoiarlCe8f,fecDtusPoofntC8haesxppoesrufroeromnedhuanmdan health
and he environment
.
doses i.10... consSitduedriiensgpbeortfhoarmmoeudnbtyaDnudPdounrtatainodno3fMexhpaovseurdee,teirsmoixniecd ttohaanCim8alinsstuhfrfoicuigehnt ainngdestthieone,nviinrhaolnamteinotn and dermal contact. Studies hve alo found that C8 is persistent in humans
ihe envi1o1.nmentA,ltthheouAgghenDcuiPeosnbtehlaisvecotlhlacttaedddiatloanragleianmfoournmtatoifonawtialloansshisetpthreemsineodneflciCne8eatiinng @ cihe edxtentBaynDducPoonntcedntrsatoihfoCrn8sCiBnstherensvirtonmhenteaso sneaandhgerFoaucnidlee.r AvhaielaLbelettdaatand
s
000633
eta AH000570
Dry Run Landfill and ator near the Washington Works facility.
sourceof12d.rinkiWnVgDwaEtPerafnodr pWeVrsDoHnsHpRot-eBntPiaHllhyaevxepodseetedrtmoinCe8ditnhagtroituinddweastierrabolrestuorafsacceerwtaaitnertshe in the area ofthe Facilities.
another,13h.ave rEeqPuAe,stWedV,DaEndP,DuaPnodntWVhaDsHsHuRbm-itBtPedH,,ininfocromnastuilotnatainodn danodcucmoeonptersarteiloantiwnigtthootnhe:e hdeutmeactniohneaalntdh sptruedsieenscebeoifnCgSpeirnfaonrdmeadroruelnadtetdhetoFaCc8ileixtpeossaunrde.documents with respect to the
14. 'WVDEP,
and
Based upon information submitted by WVDHHR-BPH, the Agencies believe
DuPontand reviewed to date by that additional data would assist
EPA, in their
`eevxaplousautrieonpoaftwhhweatyhteorhtuhmeagnrsouanndd awnhdetshuerrfapceerswoantserisnnaonwd acroontuanidntihneg FCa8cilhiatvieesaarceomaptlreitskeof
adverse health effects rom C8 exposure.
perform1e5d. on thTehehruemhaanvehebaelethn enfofiencdoepfenCd8enetxpgoosvuerrenmfeornttahle pourrnpoons-einodfuessttraiballissthuidnigesan exposure standard for C8 applicable (0 the general public
10 ascert1a6.in thTehexeteAngteanncdileesvehlaovfe Cco8nccloundceendtrthaattiofnulslisnitteheanednvhiearlotnhmeanstseasnsdmetno.tsasasriestnetcheesmsairny pdaertteircmiipantienganwdheatsshiesrt iCn8thpisresefefnotrst.any possible danger to the public. DuPont hus agreed to
emission17s. for ciTthheerftlhueoryoepaorly1m9m9e9rsorintdhuestyreyarha2s00c0ombmyit5t0epdetroceEnPtAwittohirnedtuhrceeettotoalfiavcetyuaelarCs8of cach company's commitment date. DuPont committed to this goal in 2000.
18. Washington
WoDrukPsonfatciilnisttyatlhlaetd,isindeMmaorncshtr2a0t0i1n,g
arefmilotveralanfd ciarcbonioterfe9an0tm-ce9n5ty%syosftetmheaCt 8itsin
its
major Ci-containing wastewater stream,
VI. AUTHORITY TO ISSUE CONSENT ORDER.
1. environment
inTWheestWVViDrgEinPia.is
the
state
agency
vested
with
the
authority
to
protect
the
Act, gra2n.ts to tAhsetWicVleD1E2,PCthhaeptaeutrh2o2roitfy ttoheprWoetsecttVtihregiSntaitaeC'sodger,outnhedwGartoeurnfdrwoamtearnyPrcootnetcatmioinnant
5
.
- 000634
Ent6s199
MAHO000571
[|J requi-- ring that groundwatergrboeurnemdewdaiatteiersd.found, to institacuivtiel action or issue an order grants o3.the WVAdDiEclPe t5,heCahuatphtoerrit2y2oofptrhoeteWctesttheVSitraglien'isaaCirodfer,omthpeolAliurtaPnotlsluatnidontoCoinnsttriotluteAcat, civil action or issue orders to enforce the statute. protect d4.rinkingThweatWerVsDuHpHplRi-sBinPWHesits tVhiergsitnaitae.agency vested with the authority to regulate and the autho5.rity toAprrtoitcelcet1t,hCehpaupbtleirc 1d6roinfkitnhge wWaetsetrVsiurpgpilnyiaofCotdhee,stgartaenatnsdtotothpeerWfVorDmHaHllR-BPH tihneveasuttihgoartiitoyntnoeciensstsiatrutye(a0catsisounrseaintds piusrsiutcyoarndderssaffeotyr,esatnordeftuhrethpeurrigtryaonftsstaoidthweaWteVrDsuHppHlyR.BPH
VII. REQUIREMENTS OF CONSENT ORDER.
@ etterTr which tTohdeetAegremnicnieetshehasvceopceonacnldudpeotdentthiaalitriissokoffgrtehatpirmpeorsteaonncfecCt8eo hianvtehesuefnfviicireonntmdeanttaiunpaonnd around the Facilities. Therefore, the Agenciesrequire th following:
`member1s. of theAt"eGarmouconndswiasttienrg oIfnvWesVtDigEatPi,onWSVteDeHriHngR-TeBaPmH",(GEIPSAT)ReshgailolnbeI,esatnabdliDsuhPeodnwti.th t`TehaemWaVreDsEetPforretphriensefnutlaltiinveAtwtialchbmeetnhteAteoafmthliesadeCro.nsTehnet oOrbdjeerc.tivHeoswaenvdersp,ectihfeipcrtiamskasryofptuhrepose rofeqtuhierGemIeSnTtwsislelt bfoerttho oinveSresceteioannseAxptehdirtoiuoguhs,C.phTahseedwaoprpkropaecrhfotromfeudlfwililtihngovtehersmiagjhotriftryoomfthtehe GIST shall be funded by DuPont in accordance with Section VIIIofthis Consent Order.
GIST
2. shall
issuUepionntecroimncolrusfiinoanlorfekpoerytsmsieltetsitnognfeosrtihn
the tasks st forth in Attachment A, the findings of fect and conclusions regarding
Ab.ackAgnryougnrdoudnadtaw,atgerroumnodnwiattoerrinmgonpiltaonridnegv,elaonpdedplpuumrseuaidnetnttiofiActattaiocnhmaesndtesAcrsihbaelld siunrAvtitvaecthhmeent
ttheermFiancialtiitoienos.ftDhuiPsoCnotnsreesnetrOversdetrhearnidghsth0alrbeequiensctormpooirfaitceadtaisonaomfitnhoer pplearnmsitupmoodnirfeinceawtiaolnoffotrhe
Facilities' permits.
B. National Pollutant Discharge Elimination System Requirements.
6
000635
Eot5200 MAH000572
o samplin1g. for CBExactetphteaLsocoaclcaLsainodnfeildlbay cneor-tfalionwocuotnfdailtsioindse,ntDifuiPeodnitn sWheaslltpVeirrfgoirnima/mNoanttiholnsy! P0o0l4luatnadnt00D5i.scharge Elimination System ("WV NPDES") Permit No. 0076538 as Outfalls 101,
samplin2g. for C8ExactetphteaWsaoschciansgitoonnedWboyrnkos-ffalcoilwitcyoantdicteirotnasi,n oDuutPfoanlts sihdaelnltipfeiredfoirnmWmYontNhPlDyES Pemit No. WV0001279 asOutalls 001, 002, 003, 005, 007, and 105. samplin3g. for C8ExacteDprtyasRuocncLaasnidoinieldl batyanllo-ofullofwalcsoniddietnitiofnise,dDiunPiotsntWsYhalNlPpDeErfSorPmermmointtNholy. WV0076244.
samplin4g. for C8ExacteLpettaarstoLcacnadsfiilolneadt ablyl nouot-fTallolwicdoenndtiitfiioendsi,nDiutsPoWnVt sNhPalDlEpSerPfeorrmmimtoNnot.hly WV0076066.
Orion neers sos samplin5g. shall WbeitpherrfesopremcetdtpoutrhseuarnetqutioreesmteanbtlsiosfhedpaErPagAragpuhisdeVlIiLnBe.s1, whtherroeugaphpVliIcLaBb.l4e,, lanld
results shall shall record
abneddreelpiovretreadlltaotttheempWtVs DtoEsPamwpiltehiunndtehirrtnyod-afylsowofcornedcietiivoinsn.g such
results.
DuPont
`oObhiiaoinRiavsearmipnltehefraormeaeeaxcthesnudrifnagcetenorriavlelruvmiiallewsadtoerwnisnttarkeeamforofptuhbelicWawsahtienrgstuopnplWioesrkaslofnagcitlhiety athnedDoenteecrtiivoern mLiilmeitupasretrfeoaumndofinthaenyWassahmipnlgetdonpuWbloirckwsatfaecrilsituyp.plIyfwciotnhciennttrhaetiuopnsstorfeaCm8orsbove dshoawllnsbtereexatmensdeegdmetnottsweinnittyialrliyvesrammpilleesd,dotwhensstcrgemaenmtosrwtiwtohirnivwehrimcihleisntuapksetsraeraem,oabseapsparmopprlieadte. sIfamcopnlcienngtrwaitlilobnes paebrofvoermtheedDoentewcattieorniLnitmaiktesarweitfhoiunntdhiirntyaniyvesregmmielnest dsoowenxstterndeeadm,oarddtihteicoenrailver miles upstream, as appropriate.
incorpor7a.ted inTtohethaeddFaictiilointailesm"oWneitsotrViinrggirneiqau/iNraetmieonntaslcPoonltlauitnaendt DinistchhsarsguebsEelcitmiionnatshiaolnlSbye:stem
:
preerqmuiitrsembeyntmsinuopronmordeinfeiwcaatlioofnt.heDupPeromnittsr.eserves the right to request a modificationof these
C. Toxicological and Human Health Assessment, Order by1. establDisuhPionngtanagersecesrotwo afcucnodunthteavtaariboaunsktaasgkrseesdettoorbtyhtbheelPoawrtiaess,a porarbyofsothmies Cotohnesrent
7
000636
Enresz01 MAH000573
ToxicitaygrTeeeadm10LebaydtehreaPnadrtiDeusP.onDtisrbeuprrseesmenetnattsivferjoominstaliydacssdcersocwrisbheadllbbeeloawu.thorized by the C8
member2s.oftheAtCeaBmAcsosnesissstmienngotoffreTporxeisceinttyatTiveeasmof(:"CAT Team) shall be established with
WVDEP WVDHHRBPH
EPA Region I NICS ATSDR DuPont
3. The WVDEP representative shall be the Team Leader.
set
4. forth
in
ull
The individual in Attachment
team Cof
tmiesmbCeornsse,nttheOrtdaesrk.sof
the
team,
and
the
team
objectives
are
issue a f5i.nal repUoprtosnectoinncglfuosritohnfoifnadlilngtshoeftafsakcst ascntdfcoornthcliunsAiotntsacahsmteonwthCa,ttehxeteCnAtTthTereeammasyhablel: health risks associated with C8 af the Facilities.
D. Emission Modeling Assessment ('DAQ")1. withinTh3e0 fdoalylsoowfintgheinEffofremcattiivoenDsahtaellexbceesputbwmhitetreedadtoiftfheerDenit vdeiasdolifiAoinisenrpQruoavliidteyd in this subsection:
structures locatae.d withiAn ctohempWlaestheianngdtoanccWuorartkeslsftacoilfbiutyitlhdaitnhgavdeimaensisginoinfipcaarntamiemtpearcstfoonr atlhle dbiasspeedrsoinontohef"Ca8reaeomifssbiuoinlsd.ingSiwgnaikfeiceafnftecitmsp"aacst dfeofrienaecdhinsttrhuectEurPeoAnUstehre'ssiGteuishdaelltobethdeeBtueirlmdiinneg.d Profile Input Program (EPA-454/R-93-038 Revised Feb. 8, 1995), emission rates abond confAircmoemdplaecttueaalnCd8aeccmuirsastieonlstraotefsDiunPpoonutn'dsscpuerrenyteaprerfomritttheedyeaalrlo2w0a0bl0efor aalclcsoorudricnegs(l0oictastsetdawckitLhDi.n tahnedWcaosrhrienspgoinodninWgorpekrsmiftacinluitmyb.erE.acFhoermciascshiosnacpokinitdesnhtiafliebdealbiostveed as emitting C8 DuPont shall lst all relevant stack parameters to be used in air dispersion modeling. @ Meic. For each emission point (stack) emitting C3, the following information
8
000637
EID168202
MAH000574
i. PhaseofC8 (solid, vapor or aqueous solution) at stack conditions. ppaarrttiiccllee sdieznesidtiyst(rgilbeumt?i)oi.in.(microTnhse),patrhteicmleacshafrraacctteiroinozaftiCo8n tionbceacuhsepdarftoirclmeosdiezleicnagteignocrlyu,dainngdtthhee
Forgoons cisions, scavenging eens smobth both liquid and frozen ipiri.ecipitFaotriopnarttoibcueluatseedemfiosrswioentsd,espcosaivteinogninmgodcoeelfifnigcibeantssed(hu/pso-nmtmh)e for p(aErPtAic-l4e5s4i/zBe-d9i5st-r0i0b3ubtiSoenpatn.d1t9h9e5)EP(A"1'SsCIGnduuisdtarinacle)S.ourDcuePCoonmtplmeaxy,sVuebrmsiti,onwi3tMhionde3l0 dGauyisdoafnctehe EIfSfCecGtuiivdeaDnactee,(Fiingfuorrema1t1ioonftIoSsCupGpuoirdtanhcee)usfeorofCt8h'es nsocramvaelnigziendg csoceaffviecnigenitnsg. coDefAfiQcisehnatllinatphperove oDruPdoisnatppshraolvlehwaivtehjtuhsetriifgihcta,tiwointhiinnwrsietvienng,daDyusP,o0nt'rseqsuuesbtmiassmieoent.inSghwoiutlhdDDAAQQadnidsaUppSrEovPeA, to daedcdirseiosns.theFodlelfoicwiienngciaesmesettifnogrothfinthDe paQrtiesl,etDteAr aQndshtalolriesqsuueestardeeccoinssiiodnerlaetttieornroefgaDrAdiQn'gsC8's smceaavseunrgeimnegnctooelflCic8i'esntsscwaivtehnigninsgevceonefdfaicyiseonftstihneimtesedteicnigs.ionDaAnQd rDeusPeornvetsrtehseerivgehsttthoerreiqguhtirteo asserta claim ofconfidentiality in the event such a measurement is made.
Jfiuqnucitdioannodffdrroozpelnetprseicziepiutsaitnigonftoormbuelaucseidn ftohrewoeptendelpiotseirtatiuornemboadseeldionngtwhiellphbyesipcraolvipdreodpearstiaes of
`tCh8e aEnffdecctoinvseisDtaetnet,wiintfhorSmecattiioonn o1.4osufpptohretItShCe Gpuriodpaonsceed.scDauvPeongnitngmacoycsfulbimciitn,t wfiorthgianse3o0udsays of
efmoirms.sioDnAs QincshlauldlinagppirnofvoremoartidoinsaopnprtohveepewrictehnjtuasgteiofifcaCt8ionemiinswsriiotninsgt,haDtuPwoonutl'dsbseubimnigsasisoeno.us
SwihtohulDdADQAaQnddiUsaSpEprPoAvet,oDaudPdroensts sthhaelldehfaivceietnhceiersigshet, fwoirtthhiinnsDcvAenQdaylst,ietroarnedquteostreaqumeesetting
dreecciosnisoindelreatttieornroegfaDrdAiQn'gsC8d'escissicoanv.engFionlglcooweiffnigacimenetsewittohiifnnthsgeovpeanrtdeasy,soDfAthQesmhealeltiinsgs.ue Da. AQ
reserves DuPont
the right reserves
lo the
require right to
maesassturaemcelanitmooffCc8o'nsfisdceantvieanlgiitnygincotehfefiecvieennttssuinchtsa
decision and measurement
is
made.
diagram
for
d. C8 with
reTsopetchtetoexptreenstsutrheaatnhde
phases exist, temperature,
aThsoelitde,mlpieqruaitduarnedavnadpporrespshuarsee
(T-P) ranges.
osfhaCl8l'sbeerrieicpalrperospeerntoitefsaestxhahilalvusbetegparsovciodnedditailoonnsgbweiftohremaenadsuarfteedrrconatrnoolfgepqhueiapssmeenttr,ansEisttioinmates
temperatures.
9
000638
Eo165203 MAHO00575
equilibrium betewe.eInnwaiteeruanodfCa8,bitnhaerysoplhuabisleit(yT-axn.dy)KrdaifaRgrPaominrteoprfesCe8ntiinngaqtuheeovuasposro-lluitqiuonisd, `comnecaesnutrreadtpioKnsvaolrureelfaotreCd 8acdiidsssoocbisaetrivoendinwhaqeuneoteusstesdoliuntiaohnes,adansdpamceeaGsuCreamt evnatrisooufs C8 coopnecreanttirnagtcioonndsi,ttieomnsp.eraFtuurrtehse,ramnodrepa HdirsecpursessieonntarteigvaeordfintghethreavnogleastiolbistyeorfveCd8duirnianqguaecotuusal ssoulbumtiiotnesdatsoathfeunDctAioQnowfitphHinw6i0lldabyesoprfotvhideedE.ffeTchteivienDfaotrem.ation in this paragraph shall be `The coefficientshall beHednerfyi'nsedlaatwvcaoreifofuiscietnetmpfeorraCt8uraensdcoavdeirsicnugsstihoenroafnigtesodbespeernvdeedndcuerionngpH. actual operations.
& Any carbon adsorption data in th formofisotherms for C8 adsorption. assumptDioAnQs pwriilolrptroofviindaeliDzuinPgotnhteamnodoeplpiorntgunreistuylttso.comment on modeling methodology and
requeste2.d aboveAnshyalelxbpeencsoevserinecdubrryedDuasPoantr.esultofaccurately supplying the information
o reserves3.the rigUhtpotondsiusbampipsrsovieonaonfythdaetaiinfftohrmeaatniaolnytriecqaulimreedthboydtohliosgSyubosreqcutailointyVcIoLn.tDr,olDAQ procedures arc deemed inappropriate.
VIL REIMBURSEMENT OF COSTS.
this Cons1. ent OrdDeurP.onEtxpaegndeistutroeesstfarbolmisthhaisneacsccoruonwt sahcaclolubnetmtoadfeunudpRoenijmobiunrtsaapbplreovCaolstbsyaudnudelry dnoetsiicgenoaftesdurchepdreseisgneanttioaontfsihtvahlel bWeVsDenEt P10atnhde poefrDsuonPsonitde(nt"idfeiseidgnpautresduarnetprteoseSnetcattiivoens"X)V.I Worfitthiiesn CanonessetnitmaOtredeorf.RePirmiborurtsoatbhleeeCxocsctustitohnaot fWtVhiDsECPonsexepnetctOsrdoer,inWcuYrDuEndPerhtahsisprCoovnisdeendtDOurdPeorn.t with
account2.funds iWnitthheianm1o0unbutsoifnefsisftdyatyhsooufstanhde dEoflfleacrtsiv(e$5D0a,t0e0,0)D.uPEoancthsehxapllenddeiptousriet firnotmhetheescrow eSasicdroewscarcocwouanctcomuunsttbshealslubpeporretpeldenbiyshaendiwtietmhizaedddiatcicoonaulntfiunngd,siwnchleundeivnegritnhveoibcaelsaanncde risecleeispstst.han tuennextphoeunsdaenddadmoolluanrts (r5e1m0a,i0n0i0n)g, ionrtahseaegsrcereodwtaocbcyoutnhte datestihgencaotnecdlruespiroensoenftatthievews.orkAntoybe performed under this Consent Order shall be returned to DuPont,
3. DuPont's obligation to pay Reimbursable Costs under this Consent Order shall
10
00063
Ei0168208 MAH000576
@ wchiechearde atddnroehsusendtseedpanradteilytyintthhiosussaencdtidoonlalllst(h5e2r50c0o0s0t)s.incEuxrcreepdtbty DouPRoenitmbiunrcsaarbrlyeinCgoosutts it obligations under Consent Order shalbe the sole responsibility and obligation ofDuPont.
IX. QUALITY ASSURANCE/QUALITY CONTROL. uidancAellresgaamrpdlinigngquaanlditaynaaslsyusreasnpcee/rqfuoarlmietdy cpounrtsruoal,ntdattoathviasliCdoantsioenn,taOnrddcehrasihnaolfl ccounsfioodrym to EPA Sparomcpeldiunrge.s. The laboratory performing the analyses shall be approved by the Pasties prior to
X. C8 REDUCTION PROGRAM. 1 Notwithstanding current permitted emission levels, DuPont agrees to limit yoveearrablalsCis8aenmdissshailolnsfutrothtehrepsriorvtiodneotomotrheeWthVaDn EecPtamloncatlhelnydaermiysesairon2s00r0eploervetlsreognaradicnagleCnSd.ar iTshseuarnecpeorotifangSreerqcucinrienmgenLtevceolntdaeirnievdedhefroelilnowsihnalgltbhee pmroodciefdiuerdetsosqeutaorutterilnyArteptoarctshmuepnonC.the
o collect2i.vely byD5uP0o%ntfiaogmreaecstulaolr1e9d9u9celeevmeilsssiboynDsetcoetmhbeearir3a1n,d2d0i0s3charges to the watoef Cr8 system3.at its WaDsuhPionngttoshnalWloorpkersatfeacailnidtymwaiitnhtatihne tghoealfoiflcerhiancdvicanrgbo9n0-b9ed5%trCe8atrmeenmtoval efficiency in ts major C8-containing wastewater steam. des: 4. DuPont shall conduct th following construction projects and abide by th specified TOIZC on perma.it R13-D8u1P5oDn.t sChoanlsltirnuscttalilonanshiamllprboevgeidn nscorluabtbeerrthfainleFetborrueaprlyac2e8,re2c0o0v2e.ryIndietviailce wopheircahteivoenrshisalalrblecgrin no later than the dateof sar up afer the April shutdown, or June 28, 2002, b. DuPont shall modthiesftayck for emission point TOIZCE so tht the ebmeissiszieodn(p0opirnotveildeevaetfifoenctiisve17di0sfpeeertsiaobnoovfe pgarratdiec.ulTatheeesmtiascskiodnisaamcceo,rdvienlgoctioty4,5aCnoddfeloofw rSattaeteshall Rublegeisn,nSoerliaetser2t0ha(nGoFeobdruEanrgyin2e8e,r2i0n0g2.PraIcntiitciael aospeArpaptliiocnabslhealtlobSeagicnknHoeilgahtters)t.hanCotnhsetrduactteioofn ssthaarltl
@ up afeCrr the Aprileshmutdtownc, ornJunne 2o8,n200s2, wbhichTevRerCissearllier. iAtt etidmesowchernodenvicie nTIZC 1
00j06a29
eptes0s 1AH000577
@ roc: 5. DuPont shall conduct a scrubber optimization and recovery improvement program
that shall consist ofa stofuscdrubbyer operation for device C2DWC2 on permit R13-614A. The study shall be complete by the endof March 2002. Provided the results are encouraging, the `unciotmspCan2yDsThCal2loinmppleermmeinttRi1d3en-t6i1f4ieAd,iCm2pErHovCe?m2eonntspeforrmitthiRs1d3e-v1i9c5e3a,ndansdimCiIlaFrSiCm2proonvpermoepnotssedfor permit for R13-2365A. Implementationof the improvements for the latter devices will be complete no later than the endof November 2002.
XI. COMPLIANCE WITH SCREENING LEVELS. 1. The following requirements shall apply only if the procedures set out in Atiachment C have been followed:
A ---- a Nolater than 60 days aftr receiptofnotification from the Agencies that data or information developed pursuant to this Consent Ordero other information that is recent and valid demonstrates that DuPont's operations have resulted in C8 exposures above the Screening Levels derived following the procedures set out in Atiachment C, DuPont shall submit a plan for review and approval by the Agencies that i designed to reduce such exposures to levels below the Scrcening Levels within a reasonable time (the "Remedial Plan" or "the Plan").
WVDEP shall, upon consultation with the WVDHHR-BPH and based upon accuracy, quality, and completeness, either approve or disapprove the Plan. If the WVDEP disapproves the Remedial Plan, the WVDEP shall notify DuPont in writing that the Remedial Plan has been disapproved and shall specify the reasons fo such disapproval. DuPont shall resubmit the Remedial Plan as revised 10 address the deficiencies identified in the notice. DuPont's failure to submit an approvable Remedial Plan shall be deemed a violationof this Consent Order.
2. Inthe event EPA or the WVDEP develops and finelizes a reference dose/screening level for C8 in accordance with applicable statutory and regulatory requirements ("the Regulatory EPA Standard") that would be applicable to Dupont's activities or the Facilites independent of ths `Consent Order, DuPont's obligations under this Section shall be determined with reference to the Regulatory EPA Standard. DuPont reserves all rights it may have to comment upon, object to, or appeal the Regulatory EPA Standard in proceedings separate and apart from this Consent Order.
XII. COMPLETION OF CONSENT ORDER. 1. Except as to DuPonts obligations under Section XI, this Consent Order and DuPont's obligations hereunder shal terminate upon issoufaacomnplcetieon lette(s) from the. Secretary ofthe WVDEP or his designee and from the Commissionftehre WYDHHR-BPH to
2
jovgs4 1
E0168206 MAHO000578
@ runt. stint manner lowing epof writen request fom Dont he respective
tAhgeenocbliiegsatsihoalnls aisnsduewothrekctohmaptlheatvieonnoltttbre(esn)ctoomDpulPetoendtoirn aschcalolrdiasnsuceeawiltihetrhtios CDounPsoenntt dOertdaeirl.inTghe dPuatyr.ts agree that the Agencies" obligation to ssue this letter shall be deemed a non-discrtionary
as
2. provided
in
SDeucPtoinotn'XsIoobfltighaitsioCnontsoaecnhtiOervdeearnsdhamllaisnutraviinvecotmhepltiearnmcienawtiitohnotfhte iScsreCeonnisnegntLevels
Order. Parties
Such
obligation
shall
terminate
only
as
provided
in
Section
XI
or
upon
agreementof
the
XIIL ADDITIONAL ACTIONS. `may det`TehremAignenthcaitesa,ddiintdiiovniadluaacltliyoon,r cboelyloecntdivtehley,tapsukrssuseatntfotroththinerthsitsatCuotnosreyndtutOyrdaenrd,aiustnheorcietsys,ary a10s prreosttercatinhinugmoafnphreeavletnhtianngd/tohretAhgeeenncviiersonfmreonmt.takNiontghsiuncghiancttihiosnsC.onNsoetnhtinOgrdienrthsihsalClobnesecnotnsOtrrdueerd cloianbsitliittuytietsmaasyathiasvfaectpiuornsuoafnotr1r0etlheeasfeedferroaml aCnlyeacnlaWiamtoerrcAacuts,eothfeafcetdieoranlaCglaeinasntADiurPAocntt, tfohreafnedyeral Safe Drinking Water Act, the Wes! Virginia Groundwater Protection Act, the West Virginia Air NPooltlhuitnigoninCotnhtirsoCloAncste,nottOhredresrtaitnutaensyawppalyiccaobnlsetittouttehsisammaotdtierf,icoartiWoenstorVwiarigvineiraofcostmamtuotnorlyaw. arcetqiuoinrsemneonttsspeocfifDiuePdohnetreiann.d nothing inthis Consent Order shall obligate DuPont to undertake any
XIV. ENFORCEMENT.
AgencieEsnifnorthceemCeinrctuoifttChoisurCoonfseWnotoOdrdCeorunmtayy, bWeeshtadVibrygitnihae.fliVnigooflaactoivfiitlohanecttieonrmbsyaanndyof the
croesnudlittiinonesnoffotrhciesmeCnotnsaectnitonOrbdeeirngbytaDkeunP,onitncilsuadviinaoglarteiqouneostftohre cWievisltpVeinraglitncisa aCsosdeet afonrdthmbayylaw.
DuPont shall condition.
not
be
lable
for
violationsof
this
Consent
Order
du
to
any
"Force
Majeure"
XV. CONTENTS OF CONSENT ORDER/MODIFICATION. in any a"tTthaecehnmteinrtestyoorfetxhhiisbiCtosnrseefnetreOnrcdeedrhceroenisni.stsMoofdtihfiectaetrimosn oafndthceontdeirtmisoansndstconfodritthiohnesroefinthainsd OCrodnesernsthOarlldebreimnacdleudoinnlgyabnyyamgordeiefmiecnattioofnotfhetPiamretifersamineswroirtidnega,dleixnceesptestthaabtlmioshdeidfiicnatthiiosnsCotnosaennyt
3
-
000642
Eotss207
MAHO00579
mreembqeursiorfestehmetoeGuIntStT oinrthethaettCaAchTmeTnetasmt,o 2tshiaspCproonpsreinatte.Ordermaybe made upon consensusofthe
XVI. ADDRESSES FOR ALL CORRESPONDENCE. correspAolnlddeonccuem,etnotbse, siunbcmluidtitnegdruenpodretrs,thaipspCroovnaslesn,tnOotridfeircasthiaolnls,bedisseanptpbryovcaelrt,iafinedd omtahielr, return orercteoipsturcehqauedsdtreeds,sehsanDduPdoelnitveorry,WoVvDerEniPghmtamyaidlesoirgbnyatceoiunriwerritsienrgv.ice to the following addresses
Documents to be submitted to WVDEP should be sent to: `13W5V6DHeapnasrftomredntStorfeeEtnvironment! Protection Charleston, West Virginia 25301
AAtttteennttiioonn:: DAeremaAnndno SBteanatisn,caPsha.,D.Esq Phone No.: (304) 558-2508
`Documents to be submitted to WVDHHR-BPH should be sent to:
BWuVrcaDuepfaorrtPmuebnltiocfHeHaelatlhth and Human Resources C8h1a5rlQeusatrorni,crWSetsrteeVti,rSguiintiea42158301
Attention: Phone No.:
W(i3l0l4i)am55T8o-o2m9e81y,
ManaofgSoeurrce
Water
Assessment
Program
Documents o be submitted to DuPont should be sent (0: WE.as1.hdiungPioonntWdoerNkesmours and Company P.O. Box 1217 Parkersburg, West Virginia 26102
Attention: Phone No.:
P(a3ul04B)o8ss6e3r-t4305
and
14
000643
Ent6s208 MAHO00580
1 daorcNemous nd Company
L1e0g0a7lMDaerpkaerttmSetneete,tSuite D-71
Wilmington, Delaware 19898
APthtoennteiNoon.: B(e3r02a)r7Jd7.4-Re5i4l4l5y, Esq.
XVIL. AUTHORIZED SIGNATORIES/NON-ADMISSION. review t"hTihseCuonndseernstigOnredderreparnedsehnatvaetihvaesd sotpapotrtthunaitthyetyohaalvleowhafdorftulhlearncdoufnasireolp0pordtountihteystaome, and the"rTehfeoruenednetresritghniesdCodnosheenrtcbOyrdceornffirreemlythaatndthweiythhafvuleltkhneoawultehodrgietyoftiotesntteerrmisnaontdhicsonCdointisoennst. Order aNnedihthaevretthheetaeurtmhsoroiftythoisbCionndstehnetiOrredsepre,ctniovreepxaerctuy.tionthereof hall constitute an aadnmdidsesfieonnsebsytDhuatPomnatyobfeaanvyaialcbtloeroinfaannyyplreogcaeleldaibnilgitiyn.volDvuiPnognhtirexdppraersstlcys roesienrvveoslvaillngights
@ oWVrDEeP"ThaPinsadCioWsnYsseDnlHtoHOwRrd(-eBrEPmHtayienbeanDsyiigonteehderinmactouenrterparts ind shalbeeffective upon signature
Entered this_ day of
2001, by:
WEST VIRGINIA DEPARTMENT OF ENVIRONMENTAL PROTECTION
BY.
WWeIsLtLVIiArgMinEi.aADeDpAaMrtSm,enDtoEfPUEnTvYirSonEmCenRtEaTl APrRoYtection C1h3a5r6leHsatnosn,foWredsSttrVeeitr.ginia 25301
Entered this___ day of
2001, by: 1s
000642
Eo165209 MAHO00581
`WEST VIRGINIA DIVISION OF HEALTH AND HUMAN RESOURCES - BUREAU FOR PUBLIC HEALTH
BY:
co
DR. HENRY TAYLOR, COMMISSIONER `West Virginia Department ofHealth and HumanResources
e
i
000645
Attachment A
C8 GROUNDWATER INVESTIGATION STEERING TEAM
A teamof scientists shall be assembled to assess the presence and extent ofC8 in
d`rWionrkkisngfawcialtietry,, agnrdoutnhdewLaotcearl,anLedtsaurr,faacnedwDartyerRautnanLdanadrsoiulns.d tThheeDGurPoounntdWwaastheirngton IBnPvHe,stiEgPatAioRneSgtieoenriInlg TaenadmDu(PGoInSt.T) sDhuaPllonitncslhuadlel sfcinedntitshtesGfIrSomT WviVaDaEn Pes,cWroVwDaHccHoRun-t
as provided in Section VIIIofthe attached Consent Order ("the Consent Order").
aDnidsbtuhresDemuePnotnstfrreopmretsheinstaatcicvoeu,nAtnshdarlelwbeS. aHuatrhtoreinz,ed jointly by the WVDEP GIST leader,
Athescehnedoduflethsiusmdmoacruimzeinntg. key GIST tasks, submittals, start and end dates is provided at
GIST Member Organizations/Represcntatives/General Functions WVDEP
David Watkins-Groundwater Protection- GIST team leader; escrow funds
Y
disbursGeemeonrtgeovDearsshieghrt-;adpvriosjoecrtamnadntaegcehnmiecnalt raenvdiecwoordination
Dee Ann Staats, Ph.D. advisor
EPA Region II
Garth Conor-seience advisor Jack C. Hwang - Hydrogeologist RogerRheinhartEnvironmental Engineer
DuPont
pArnodjercetwmHaanratgeenm-PernitncainpdalcoPorrodjiencattiLoenaodefrf/iHeylddriongveeosltoiggiatsitotnecahctniivcitailesr;eveisecwr,ow funds disbursement oversight.
WVDHHR-BPH
Public HWeiallltihaamdvTiosoormeyManager, Source Water Assessment Program- Bureau for
a
-
000626
Ee wARO000SE3
o GIST Team Objectives and Efforts
and
sur`fTahceepwraitmearrymoobnjietcotriivnegofatnhdeiGnvIeSsTtigiasttiooneffaictciiveinttileysre3sviperwesacnrdibdeidrecitn
groundwater the Consent
OtredaemrdaencdisiinotnhismaAktitancghmteonwta.rdThmeeeGtIiSnTg witlhle utrielqiuzieraempehnatssedinapparnoaecfhficainedntemapnldoytirmapeildy
`pmeasnfnoerrm.edUbnyleDsusPoonttheorrwitsseredpirreescetnetdatibvyest.he GIST, the tasks outlined below shall be
groundwTahteerGIquSaTliwtiyllinissauned a afrionualndretphorei(sF)aciwliitthes,finadnidngsthaendexctoennctluosfiongsroruengdawradtienrg croenctoammmiennadtaitoinonins arengdaradrionugndthethneeeFdacifloirtiaens.y fuTrhteherGwIoSrTkfoirnaalctrieopnosrtthsathanlleefdurttohbere mtaakkeen 10 assure protection ofgroundwater quality and human health into the future.
performTehdebtyasDkusPsocnttfaorntdh
tbheelGoIwSaTndpuirnsutahnet
CtoontsheenCtoOnrsdeenrt
are the Order.
mAdidniitmiounmalttaasskksstmoabey.
be necessary identification,
to assure the and receptor
igdoeanltsifi(fcualtliogn]rooufndtwhaetGeIrSaTssaensdsmtehnet
CaonndseCn8t
Oirmdpearct,areplmuemle
Those tasks shall be agreed upon by the GIST.
Key Tasks of GIST
@ rai Groundwater seand WeSureGroundmate Monin
+ OabLj-emctiilvee(sa:nCdopnodsusicbtlyad2isatnadnc3e-m-iplhea)serdadgiarloudnidstwaantceerorwedlilreacntdiownaatlelry ufsoecussuerdvediyswtiatnhcein
+
ofthe Washington Works and Local, Leter, and Summary: The phased approach fo the water and
Dry Run Landfills.' groundwater well use
survey
will
acelalsoew atchteivGiItiSesTitnodfiorceucstieofnfsorwthsearleonigmpeascttabslairsehendotC8priemsepnatctortrwahnesproertthpeartehawraeys and
malilnoiwmatlhecGonIcSenTtrtaotmioenes., eDvaatluaarteesutlhtesdtaatbal,esanwdildlebteergmeinneerattheednienxtactoiumresleyomfaancntieorn.to
`The GIST released.
will
determine
when
the
final
groundwater
well
use
survey
shall
be
an agreed-toDutPhiorndtpaargtrye,esa tgoropuenrdfworamt,erunudsecratnhdewseulplersvuirsvieoynoifdtenhteifGyiInSgTanadndsatmhprlouignhg
atlhlegWraosuhnidnwgattoenr wWeolrlksswiftahciilnitay.1-Tmihleeprhaadsieusd oafptphreoatchhremealyanbdfeialsmesentdefodrtbhyabthoeveGIanSdT
sohfoquuladliftiyelsdacmopnldiintgiopnosinrtesquwiirteh,ine.tgh,e
lack ofsampling 1-mile radius.
wells
in
the
1-mile
radius,
lack
`measuring tShaemCpl8icnogncsehanltlrabteiopnerifnowramteerd.wiSthhouthledscpoencciefnictrpatiuonrsoopffCfoi8nsdfioenugndanind
`groundwater wells exceed 1 ug/l within the I-mile radius, the GIST wil determine
Jee
ON
a2 000647 eptesz1z
MAHO00S84
wdihreetchteiorntoonelyx.panDrditnhkeinweglwlasteurrvweeylltso ath2at-mmielaesraudriuasb,oav3e-m| iulge/lrasdhiaulsl,boerrien-asasmppecliefdicat
a frNeoqtuee:ncTyhteo bleevedletoefrm1 iunge/ld ibsyuttihleizGeIdSTin.this Consent Order for monitoring
paudrjpuossetsaesodndleytaenrdminnoetdatshae bGeInScThminarfkurftohrerdaentceeormfintihnegtarsiksksaannddtohbijselcetvievlesmaseyt bfoerth in
TitmhiisnAgt:taTchhmeeinntital well survey withina 1-mile radiusofthe Facilities will be
`scuornvdeuyctaecdtiwviittiheisnw6i0l dbaeycsoofndtuhceteCdonosnena tscOhreddeurl'es tEoffbeectdievteerDmatien.edAbddyitthieonGaIlSTwe.ll
Task B: Assessmentof Existing Groundwater and Surface Water Monitoring Data
* Oabnjdecetixvets:oefnDCet8veilnodprainndkiingmpwalteemre,ngraoumnodnwitaotreirn,gpanldansutrhfaatcedewtaetremrininesantdheaprroeusnednctehe
cWoamsphiilnagtiioonn oWfaolrlksavfaaiclialbitlyeagnrdouLnodcwaalt,erLeltsaurrtf,aacnedwaDtreyrRmuonnitLaonrdifnigllasnadnhdypdrroovgiedoeloagic
+ cShuamrmacatreyr:izaTthieonGdIaStaT fwoirlebaechftaacsikleidtyw,ietsh raenfleexcpteeddiitnedTaebvlaeluAa-tLionofexisting historical
dcaotnatiannudinhgygdrrooguenodlwoagtiecrimnofnoirtmoartiinogn einndodaenyratdodpirtiioorniatlizientvheestiingiatitailonscaoctpievoitfiwesor(ek.gf,or
pmroonviitdoerianllghwiesltloriincsatlaldlaattaioannsd) rheyqduriorgeedoluongdiecr ipnlfuomremaitdieontnifiitcmataiyon.havDeuProelnattesdhatlolthe
Facilites.
Taniamliyntgi:calWiatnhdinfa3ci0lidtayyhsyodfrotgheeocloomgpilceitnifoonromfatTiaosnktoA,dettheerGmIinSeTthweilscroepveioefwwaollrtkhefoCr8.
sscrhoeudnudlweatfoerrtmhoonsietaocrtiivnigtiaesn.d addiistiaonntailciipnavteesdttihgaattiaons.umTmhaerGyoISfTallwihlilsttohreincaelstablish a
Oirndfeorr'msateifofnecftoirvecadcahtef.acility willbe submitted to GIST within 60 days ofthe Consent
Task C: Plume Identification/Groundwater Assessment
+ Ogbrjoeucntdiwvaet:eDreetxecmeiednientghe1 vuergtiocarlaasnddirheocrtiezdonbtyaltheextGeInStTo,fawnhiycahnmdaaylldCe8teirmmpiancetead Tiomwpearcttehdregsrhooulnddtwhaatner1 uagt/lL.etaTrhtisLatnadsfkilslhaalnldalistsoiimnpcalcutdeoanntahessOehsisomeRnitvoefr Can3d public
+ Swuatmemrarsyup:plTiheseaGlIoSngTtshhealrlivefirr.st review historical data and results ofTask A to dgertoeurnmdiwnaetearn palpuprmoepsricaotnetrsicboupteiongf{w0oorrk.witAhcttihveitpioetsensthioaulltdobfelporwiotroiwtairzdedotfof-asditderess rweacteeprtosrosu,rcwei.th emphasis on those arcas where groundwater is usedgs a drinking
as
000648
Etes21s MAHO00585
`Upon completionofinvestigation activities, DuPont shall provide the GIST with
p`mriegdriactitoend. groundwater flow and contaminant transport models to assess future plume
+ Tbpriyimoitrhniegt:iGzIeSUpTpl,ounmthereeiGdveIineStiwTfoifwcaialltlilocna.ovmapilleatbleeainnfionirtmiaaltieovnalaunadtioonnofscdahteadutloedetotebremdienteearnmdined othe`rThacetitviimtiiensgwoiftlhebeinointiaal spchhaesdeuolfe epsltuambeliidsenhbteiyfdictahteiGonI/SiTn.vesFtuirgtahteironinavcteisvtiitgiaetsoraynd abcetipveirtifeosrnmeeeddbeyd aDnudPoangtreoednatoscbhyetdhueleGIesStTabtloischaerdrybyoutthethGeIgSoTa.lsof the GIST shail
M`Aondyelanidngall modeling performed pursuant to this attachment and the Consent Order sGhIaSlTl.use Groundwater Modeling System, or some other model as approved by the
a
000849
Enisszis MAs000SES
TABLE A-1
[FT COMPILATIOONFWISTORICALBATAAND MONITORING FLAN
a Dependentuponthe [+ A Tocation map.
aivnafiolrambaitliiotnyo,fancertain | + historical deta summary|
mwAaotnsieitrteosmruiapnppglsywehwloilwtsih,nirngesatihde1e-nlmtoiicalaletigroarndooiuufnsdatlwlhaetkFenarcoiwwleinltilgessr.aonudndpwuabtleirc
dthoactuimneclnutdeesd: in areport | + Tsoapm-polfi-nggrloiufendowfatthesrimtaepasn.d Tshheousledsbheounlod lsepasnthtahne eynetairrley::
17DuPont
then these
has only one
maps should
year's
be for
worthof data
each quarter;
for a given site,
if DuPont has
csaevnebraelaynenaurasl.worthof data for each site, then these maps
+ C8 concentration contour maps. These should span the
ygeeinatvrielrnye.ssiatIemf,pDltuhiePnnogntlthifeehsoaefsmtoahnpelsysisothneoeaunlyddeasbrh'esofuwolrodrctbahechnoofqudlaaertstasertf,ohraifna
tDhuePsoenmtaphasscsaenvebrealanyneuaarls. worthofdta fo each ste, then
+ All the C8 groundwater data that has bocn collected to dae.
o
T"Thheessee tdaabtlaesshsohuoludldbeusseubtmhietmteetdhionde,a"s<yx-"to,-rtoeaddestaibglneas.te all
concentrations below the laboratory's minimum detection
limit (not "ND" or some other abbreviation), and they
+ tushhneoaurlbedalsueosnetso"wpmhrgoy/v"iitdoeirst"uhunega/ab"bloeavsteothdgeaattuahn,eirtDuadPensodingstnuabtshimaoilntl. tdhoecument
| A growndwater
+
monitoring plan for the|
iCn8fosrammaptliionng. The samples should be taken From all the wells at the three landfil sites and from a select numberof
Facilites which should | wells atthe Washingion Works plant, These sleet wells
address, ataminimum: |
|
admarotenait/toibonrfeoirncmghaotpisroeonng.rbaTymhetbhefegriGenIqsuSebTnacsbycedfoofornesaetmhvpeallgiuranotgiusonhndaowlflahtbiees.rtorical
-
!
mDaotnethalnyd fqouratrhterflrystthferoeuarflmeorn.thAsnyfonlleowwiwneglltshereEqfufiercetdivfeor
minotneigtroartiednginorepalcuhmseitei'dsegnriofuicnadtwiaotneprumropnoisetsorwiinlgl pberogram
on a schedule agreed to by the GIST.
as
000850
eoisszis MAHO000587
| |
|
+ R'eWpVoDrtEoPfGRreosuulntds.watReerpoPrrtoignrgasmhoautltdhebefoqlulaorwteirnlgyaaddnrde1s0sthe GWrVouDnEdPwatDievrisPiroongorfamWater Resources C1h2a0r1leGsrteoenn,brWieesrtSVtirreegtinia 25311 Re: DuPonyCB monitoring
Each report should include the following: (@) Asite location map.
well loc(a6t)ioAns.site map showing the groundwater monitoring. () A top-of-groundwater map. (@) A C8 concentration map. (e) Groundwater elevation and well screen data
where a(vfa)ilAablteabilnefooframlaltithoen hailsltoowrsi,caalbCbr8evsiaamtpiloinsngshdaotual.d Nnoote:be aunsedd"1p0pdme"sisghnoautledNnootDbeeteucstedc.oncentratiaonds the units "ppb"
(@)CLahboiratnoryaansalysis shects.
a6
000651
_ eoteszie
MAHO00588
@ Humes
Name Address:
|
:
GROUNDWATER WELL USE SURVEY
Phone:
Best Time to Contact Owner:
1. DInooy,outohpanvoewonacndorrmeotruemwsautrevreyw.ell(Yse)son_t_hi_s properNtoy?_(I_t_n_eed not be in use curently.)
County Water Well PemitNo.
2 Isthe well(s) curently circle one) used unused or filled in?
@
eel ud brining ied Yes No
4. Isthis well(s) usedforother purposes? IFyes,pleasespecifyuses below:
5. Whats the approximate frequency ofuse? Circle One:
Daily Weekly Monthly Summer
6 Dauclastused?
7. Isthereapumpinthewell? Yes
No
s8.ystem?IstheraYeecson_di_ti_oner, Nsooftener, chlorinator, filter, or other formof treatment for the
If0, what is the formof treatment?
B1
000652
Eoisszir MARO00SES
@ 5 tein sy cer whorewater docs no fst as hough te csmentsyst?
Yes
No___
Ifyes,isit (circleone) inside or outside?
10. What year was the well constructed?
1. Please provide thefollowing information regtahewrelld(s)iifknnogwn: (cir one)
A. Total Depth (feet below ground surface)
30-60 60-90 90-120 120 or more
B. CasingType:
PVC steel
stone none other
C. Well Construction:
dug drilled openoruncased bedrock
o
D. Sercencd Interval (lengthin fect):
010
1020 2030 30-60 60ormore:
E. WellDiameter inches):
06
612
224 24 ormore:
B2
-
000658
Enteszis MAIH000590
Attachment C C8 ASSESSMENT OF TOXICITY TEAM
health aAndttehaemoenfvsicireonntmiesntts ashsaslolcibaeteadssweitmhbleexdpotosuarsesetsosatmhemtoonxiicuimtypaenrdflruiosrkotoocthaunmoaatne "(TCe8a)mr)eslheaaslesinfcrloumdeDuscPioenntti'sstsafcirvoimieasc.adTemhieaC,8goAvsesremsesnmte,ntnoofn-TporxoifciittoyrTgaenaizmat(iConAsT, and iNnidxuosnt,rya.s TahreepCreAsTentTaetaivmeoaflsWoesshtallViirngcilnuidae'sthceitWizVenDs.EP Environmental Advocate, Pam contract`TwhiethWVanDoEn-Pp,roufiiltiozrignagnifzuantdisonf,rotmheaNnaetisocnraolwIancstciotuuntte ffournCdheedmbiycaDluPSotnutdi,esshall T(aNyIlCoSr),,Pfho.rDt.heTsheervNiIceCsSdeshsaclrlibseudbchoenrterianc.t PwoiitnhtoMfarcsohnatlalctUnfiovretrhseitNyI'sCSCesnhtaelrl bfeorJRaunral aM.nDd.Enavnidrohnismesnttafa.l HDer.alBtehcfkoerrsesrhavlilcefsamiinlriiasrkizceohmimmusneilcfawtiitohntphreotvoixdiecditbyoyfJCa8m,esthBeecwkoerrk, pinerrfisokrmceodmmbuyniTcEatRiAona.s dTehsecrNiIbeCdSheshraeliln,suabncdonattrtaecntd pwuibtlhitchmeeneotni-npgrsoftiotpsrcoievnitdiefiecxpertise coorngtaancitzaitsioJno,anToDxoilclaorlhoigdye,ExPche.Dl.lenTcheefoTrERRsAk sAhsalslespsrmoevnidte(sTeErvRiAc)eswihnotsoexipcooilnotgoyfand risk assessment. Work assignments, tasks, and deliverables are described below.
CAT Team Member Organizations' Representatives'/ General Functions
WVDEP
Dec AnndiSstbauartss,emPehn.tD.ov-erSsciigehntc,eprAodjvecitsomra-ntaegaemmelenatdearn;descocorrodwinfautnidosn; toxicologyrisk assessment and communication;
Pam Nixon - Environmental Advocate- advisor;
NICs Jan Taylor, Ph.D. ~contractor administrative oversight;
James Becker, M.D. (Marshall University) - consultant in risk communication;
TERA
(pointofcontact: assessment;
Joan
Dollarhide,
Ph.D.)-
consultant
in
toxicology/risk
qualifcarons.
ci
000654
Eotss219
MAHO00591
Dubont
Gerald K~ernenveideyw,erDitroexcitcoorloogfy;ApepslcireodwTfouxnidcsodliosgbyuarnsedmHeenatltohv,erHsaisgkhte;ll Laboratory
John Whysner, M.D. toxicology/risk assessment and communications;
Paul Bossert ~ Washington Works Plant Manager - communications; The following membersof the CAT Team shall ct s reviewers or advisors. WV Department of Health and Human Resources - Bureau for Public Health
(WVDHHR-BPH)
WBairlblairaam TTaoyolmoe~ry ~DiMreacntaogre,rO,ffSiocueorcfeEWnavtierronAmsesnetsaslmeHneatlPtrhoSgerravmic-esad-viasdovri;sor;
Local representative - advisor;
Eavironmental Protection Agency (EPA)
o
RTeeagdigounarItlerPshi-lJaedoenlipfheri-aSeed - reviewer and advisor toxicology;
SamuelaRsosteesnsbmeerngt,; Ph.D. ~ reviewer and advisor toxicology risk RGaorgtehrCRoeinnnhaor-tr--ardevviisoerwehrydarnodgeaodlvoigsyo;r Safe Drinking Water Act; Cincinnati - John Cicmanee, DVM - reviewer and advisor toxicology;
Agency`AftolranTtoax-iJcoShunbWshteaenlceers,aPnhd.DD.i-seraesveieRweegrisatnrdya(dvAiTsSorDiRn)toxicology risk Philadelapshsieass-mLeonrta; Werner - coordinator for ATSDR;
Non-CAT Team Efforts
TeaOmthteorwielfifzoer.tsTahee cCuArrTenTtelyamunwdielrwcaoyorwdhiincathemaanyd pcroomdmuucneicianftoermcaltoisoenlyfwoirtthhethCesAeT
-
other efforts. These include:
1. Dupont's sic modelingof C8 emissions from the Washington Works plant;
2. WVDEP's air modeling ofC8 emissions from the Washinglon Works plant;
c2
000655
Eots6220 MARO000SS2
@ r3egUaSrdEiPngACD8r,afttotHhaezaxrtdenAtssceosmspmleenttedwphriicohr tsoumthmearaiszseessstmheentavcaoinlatbelmepltaoxtiecdithyerienifno,rmation w4.itAhTCSBDiRn'dsriHnekailntghwCoanrsulftraotmiotnhethLautbeesctkimPautbelsitcheSerrivsikcteoDtihsetrciocmtmountihteyexatsesnotciated completed prior tothe assessment contemplated herein. 5. Existing C8 concentrations in Lubeck Public Service District da. U6.seGrSouurnvedywa(tsecre eCx8aAmnpalleyssuirsv(esyeeinGAItSaTcahcmtievnittieBs)daetstchribreedsiindeAntcteascihnmtehnetaAre)a oafndthWee3ll Jandsillsand the Washington Works lant.
Tasks ofCAT Team in more"dTehteaitlasbkeslotwo.beTpheersfeortamsekdsbayretdheisCcuAsTseTdebaemloawewidtehsicnrihbeedcborniteefxlty oinfaTaSbeloepe1,oafnd Work for both Dr. Becker and for TERA as wll
remmirineii, ie hose taTsakssknsecoefstshaeryCtAoTprTeepaarmesfhoarllanbdehoorlgdantihzeefdrsnttoputbhlriecempeheatsiensg.. PIhnasPeha|sienIcTl,uTdeEsRA hstuumdiaens;hdeealvtehl;oepvianlguPartoivnigesxiiosntailngReifnefroernmcaetiDoonserselaatnidveSctoreeecnoilonggiLcealvehlesalfotr;parnotdection of ccoonncdeuncttriantgioonnsetgoeSneerranliinsgk aLsesveelsss,mefnort tihnevotlhvrieenglcanodmfpialrsiasnodnstohfe Weaxspohsiunrgeton Works fPlianndti,ngasn.dPthhaeseLu1b1eickncPuudblsicthSoesrevitcaesksDisntercicets.sarTyEtRoAprsehpaalrleprfeopraarnedahroelpdorhteonsetchoenrd ppurbelsiecntmeedetiinntgh,e sTehceonrdsupulbsliocf mteheetCinSg,grounder analysis and risk asessment shall be TERA sNhaollcobmempuenrimciattteidonwibtehtowuetetnheDpuaprotnictipraetpiroensoenftDart.iveSstaatns.d NAIClS,inDfro.rmBaetcikoenrw,ilolr be fproovtidbeyd DtoupDor.ntBeshcaklelrbaensdenTtEiRnAtribpylicWaVteDtEoPDr;. tShtuasa,tsallfoirnffoorrmwaatridoinngcotnotDrri.buBteedck0erhaend TERA Phase I TASK A-L: First Public Mesing shall oc"cTuwroinpuPbhlaiscem1eeftorintghseaprurpaonsteicsiopaftiendtfroordutchiisngprtohjeecCt.ATThTeeaFimrsatnPduboltihcrMeisnvtoilnvged
@ LpuaberciktsoPutbhleicpuSbelrivcicreeplDaeitsitnrgichtiswtaotreicraasluipnpfloyr;mniatnifmoonrmoeinngprtbheeviccoiutsiizceonesnocfaetnheftreniastuoieifnoCgnn8ssin efforts in the Groundwater C8 Analysis and Well Use Survey. In order to prepare for he
cs 000656 etenzzt
A000593
First Public Meeting, CAT Team members shall familiarize themselves with the available toxicological information concerning CS.
A CAT Team meeting shall be held immediately prior to the first public meeting 10:(1) conduct a sit visit to the three landfills and the WashingtonWorksPlant, and sumounding residential areas; (2) discuss the toxicity ofC8 and other pertinent data; (3) p`mreeeptairneg.anFiangaelnlyd,atfhoerFtihrestpuPbulbilcicmeMeeteitnign;g(w4i)lcloboerdhienladteaannddpupbrleipcarqeuefsotritohnes paunbdlic `comments will be recorded by WVDEP.
--_--
TABLE 1. TASKS OF CAT TEAM
|
| "OTbajsekctAi;veP:ub0liicnMfeoertmitnhgesl(otcawlocmietcizteinnsogfstahrceafnotilcliopwaitnegd:)(inMeeting#1) inten to perform
|
a groundwater well and 0 ask for their
cuosoepesruartvieoynainndcaonnadluycstiisnfgorthCe8w;aitnetrenutsteosduervveeyl;opanSdcr(eiennMiencgtLienvgel#s2;)
resultsof survey, chemical analysis, and risk assessment. Note thal an interim public
`meeting may be required should six monthspass from the frst public meeting and the
`CAT Team Final Report has not been issued.
Primary Responsibility:Staats
"Task B: DevelopmentofProvisional Reference Doses
o Objective: 10 develop Provisional References Doses for C8 for the inhalation and
iPnrigmeasrtyion (Reasnpdodnesribmialli,tiyf:poTssEiRblAe) roouf texpeosusre.
Task C: Developmentof Screening Levels Based on Protectionof Human Health
SObcjreecetniivneg:LteoveultsilifzoertCh8e Pinroaviir,siwoantaelr,Reafnedrseonicl.e DNoosteesatdoedteevremlionpathiuonmaofnthheealptohternitsika-lbased
carcinogenicityof C8 will be conducted as well.
Primary Responsibility: TERA
oo
Task D: Ecological Data Review
| Objective: to review available information odetermine whether sufficient studies have
| been performed and data have been collected to develop screening criteria for ccological
|rePcreiptmoarrsy. Responsibility: TERA
| Task E: Draft Report and Final Report
OPbrjiemcatirvye:Res(p0opnrseisbeinltitayn:d TdiEscRuAss the resultsof the above tasks
SPchraeseeniIIngTasLkevselsB,, aC,ndD,RiasnkdAEssDeesvsemlenotpmen ofProvisional Reference Doses and
In Phase I, TERA shall conduct the toxicological and risk assessment activities. o TAEeRrAhashvailnlgcronesvuiletwewditthhetotxoixciocloolgoigsitcsalonintfhoerCmaAtTionTeraemga,rdasincgooCr8dipnraotveiddebdybDry.WSVtaDaEtsP,,
regarding its proposed approach for this project. Following such consultation, TERA
000657
ce
eoies2zz MAHO00594
o sphoaslslibdleev)elroouptePsroovfiesxipoonsaulrRee.feTrheennceTEDoRsAesshfaolrlCc8alcfuorlattheeSocrarle,eninihnaglaLteivoenl,safnodr dweatremra,lsioifl atinsdk aaisrsbeasssemdenotnitnhveolrvisikngfaccotmorpsartihseoynhoafveexepsotsiumarteedc.onTceEnRtrAatsihoanlsltpoeSrcfroeremnoinnge gLeenveerlaslfor tDihsettrhircteelwaantdefrilsluspaplnyd, tthhaetWfaoschusiensgioonncWurorrekntsrPilsakntt,o ahnudmathnehLeuabltehc,kiPnucblluidcinSgewrovrikceers and rleasniddeunstes,. suTrhfiasceriwskataesrseasnsdmgenrtousnhdalwlatienrcluusdee;:((21)) iiddeennttiiffiiccaattiioonnooffrerceeapstoonrasb;ly(3a)nticipated cidoemnptairfiicsaotnioonfofexepxopsousruerecopnactehnwtaryatsi;o(n4s)tiodaepntpirfoipcraitaitoenoSfcerexepnoisnugreLecvoenlcse.ntTraEtRioAnss;haalnld (5) gurioluznedwdaattaerobCt8aicnoendcfernormattihoenostihnerreesfifdoernttsidalisacnudsspeudblaibcovweellssu;chreassidaeinrtimaoldeglrionugn;dwater wCeolnlsuulsteatsiuornve(iyf;avtahielaUbSleE)P.A'TsEDRrAaftalHsaozsahraldl Arsesveiseswmeanvati;laabnlde AiTnfSoDrRma'tsioHnetaoltdhetermine wschreetehneirngsucfrfiitceireinatfsotrupdrioetsehctaivoenobfeeencopleorgfiocramlehdeaalntd,dpaatratihcauvlearbleyeanqucaotlilcecltifee.d toTdEeRveAlop sshuamlmlaprriezpaerset2hderdaafttaauntdilaizefidnaflrodmocoutmheerntcftfhoatts.disAcsustsheesttahseksroesfultthseofCAthTeirTeefafmoratsndanodther ievnivdoelnvte.dTphaersteiss'haplrlogbreesisn,clduadteadgianpsTEanRdA'rsesreeaprocrhtraescsoumgmgeensdtiaotnisonfosrmfaurythbeercroemseearch to elucidate the toxicityofCS.
Phase Il Second PublicMeeting ofthe ef"fTohretspourfptohseeGoIftShTeaSnedcConAdTPTubelaimcsMeienctliundginigs 0C8prceosnecnetnttroatthieocnistiinzegnrroyutnhedwarteseurlts afsrsoemssrmeesnitd.entAiiarl mwoeldleslianngd rpeusbulilcs woefltlhsetehfefosrctrseoefniWngVlDevEePlsaannddDtuhpeognetnewrialllibsekdiscussed also. The WVDEP will address any futher actions that may be necessary.
cs -
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Enteszzs MAHO00595
SJCAOMPEESOBFECWKOERR,KMF.OD.R
Dr. Becker is a medical doctor speciianelnviirzonimenntagl health at the Marshall University SchoolofMedicine Center for Rural and Environmental Health. He wil be assisting the WVDEP in his specialty area of risk communication at the two anticipated public meetings. The specific tasks assigned to Dr. Becker are described below.
Phase I Task A-1: First Public Meeting
Dr Becker will assist in preparation for the first public meeting, and attend the meeting providing expertise in risk communication. He will familiarizehimselfwith the eavmapihlaasbiles toonxitchoeloegpiicdaelmidaotlao,giwchailcshtuwdiilcls.beNportoevitdheatdtthoehtiomxibcoyloWgVicDaElPd,atawiatlhrepaadrytihcauslar been summarized in the Draft Hazard Assessment prepared by USEPA. No literature search or document retrieval will be required. Specific sublasks required in Phase I to prepare for the first public meeting are described below:
`Subtask 1 - Familiarization with toxicological data provided by WVDEP including but not limited to:
o
a. 8 compactdiscs of information provided to USEPA under TSCA by 3M Corp
(note only a small portionof this information concerns C8);
b. Draft Hazard Assessment document from USEPA;
.d. AJoCuGmIalH aTrhtricelsehsoalnddLoitmhietrVianlfuorem(aTtLiVo)n.provided by WVDEP.
`Subtask 2 ~ Attenad meting prior to the first public meeting to:
a. conduct asite visit ofthe 3 landfills and the Washington Works Plant, and
local residential arcas;
b. discuss and prepare an agenda;
c. discuss the toxicology and risks associated with C8 with the other CAT Team
members.
.
Subtask 3 ~ Attend First Public Meeting
Phase I Task A-2 Second Public Meeting
Dr Becker will assist in preparation for the second public meeting, nd attend the meeting providing expertise in isk communication. The following sublasks will be required:
`Sublask 1 ~ Familiarization with the toxicological and risk assessment report
prepared by TERA;
cs
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emteszze MAHO00596
bt 2 ted a mesorrto he scond pli mcg:
a. discuss the toxicology and risks associated with C8 with the other
CAT Team members;
b. discuss and prepare an agenda.
Subtask 3 - Attend Second Public Meeting
Note that the second public meeting is assumed to be the final public meeting; however, resultsofdata collection may warrant additional public meetings and an expansion of the. Scope of Work
00066e c7
Ent6s225 MAI000597
SCOPE OF WORK FOR TERA
TERA (Toxicology Excellence for Risk Assessment) is anon-profi organization that applies sound toxicological data o the isk assessment process to find common pgrroovuinddinbgetsweerveinceesnviinrtoonxmiecnotlaolg,yianndudsrtirsyk,aasnsdesgsomvenetm.meTnEtRgArouscpise.ntiTsEtsRwAillwiblel be developing risk factors and screening criteria; and conducting one general risk assessment for the 3 landfills, Lubeck Public Service District water supply and the Washington Works Plant. The specific asks assigned to TERA are described below.
Phase Il Tasks B,C, D, and E: Development of Provisional Reference Doses and Screening Levels, and General Assessment of Risk
Subtask | ~TERAstaffwil familiarize themselves with the toxicological data provided to by WVDEP. No literature search or document retrieval will be required. Toxicological data to be provided to TERA shall include but s not limited to the following:
a. 8 compact discs of information provided to USEPA under TSCA by
3M Corp (note only a small portionof this information concerns C8);
b. USEPA Draft Hazard Assessment for C8;
o
c. JDouuPomnatl.articles and other information submitted to WVDEP by
Subtask 2 ~ TERAstafwill:
a. diedveenltoifpyinalglRpeofsesribelnececrDitoiscaelstfooxrictohleoogriacla,lisnthuadliactsiosnu,itaanbdledefrormal (if possible) routes of exposure;
b. outline methodology for developing said Reference Doses and for developing Screening Levels for air, water, and soil based on said sRuebftearseknc2e-2D;oses corresponding to cach critical study identified in
c. tchoenivrefniendainmgeseitninsgubattatshke2T-2EaRnAdfa2c-ibl,itaynidncoCnisnuclitnnwaittih, COhAiTo,Tteoapmresent toxicologists as coordinated by Dr. Staats;
d. finalize Reference Doses and Screening Levels based on recommendationsof the CAT Team toxicologisats coordinated by Dr. Staats
Subtask 3 ~ TERA shall conduct one general risk assessment for the three slaunpdpflilylsbaasneddWoanschuirnrgetnotnisWkortko shuPmlaannt,haenaldtht.heTLhuibseicskkPausbsleiscsSmeernvticsehaDlilsitnriccltudwea:ter
a) oidaenntiifvicaateisonovferseasonably anticipated land use, surface waterand
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Etesz2s MAHO00598
b)) iiddeennttiiffiiccaattiioonnooffreexcpeopstuorrse;pathways;
4) )
icdoemnptaifriicsaotinoonoffexepxopsousruerecocnocnecnetnrtaattiioonnss0; appropriate Screening
Levels;
TERA shall uilize the following data in th risk assessment process:
ba)) aaiirr mmooddeelliinnggddaattaa ffrroomm DWuVPDonEtP;; 0)) wgartoeurnduwsaetdeartadaftraofmrtohmetWheelGlrUousnedSwuartveery;Well AnalyosfiCs8 for residential ) wdreilnlk;ing water data from Lubeck Public Service District well; 5) aefnfyecatvsaiflraobmleeAxpToSsuDrRe oHeaClBthinCopnusbullitcastuipopnltyhdatriansksiensgsewseprot.ential health
sufficienStubitnafsokrm4at-ioTnEtRoAsusphpaolrltrtehveiedwevtheeleocpolmoegioncftalCda8ta SacnrdedeentienrgmLienveewlhefotrhperrotteecrteioins ofecological health
@ comSmubetansk p5 o~ rTE(RGAnshaanlldcfomopirlesiaondnsdi)scwuhsiscthheshreosuelisfof2thedabopvreovtaisdkessainrtoiat summary of the following:
5b)) UDSEuPA'PsaiDorramfnotdHeatlzianr'gddaAstsas;essment ofC8; <0)) WgrVoDuEndPw'astearirdamtoadferloimngtdhaetGs;roundwater C8 Analysis and Well Use Survey of ) LAoTcSalDRResHiedaelntths,CoannsdulLtuabteicokn tPhuabtliacseSsesrevsicpeotDeinsttriiaclt;health effects rom
exposure to C8 in public supply drinking water, if available
for futuAreddrietsieoanraclhlyg,leTaEneRdAdsuhrailnlgitnhcilsupdreoicnestshethraetpowrotualndyfiunrstihgehrteslourcirdeacteomtmhentdoaxticiiotnysof Cc8a.rciAnlosgoe,niTcEitRyAofsCha8lli prroavsid0e ihunmtahnesr.eport of summary discussionof the relevance the
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Eteszzr 1AH000599