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Taft/ Deborah McCrea / Legal Assistant a 125 asSr&ehe aotke 1(51050 Cincinnati, Ohio 45202-3957 CAE 355s Fan 10381 coos www.taftiaw.com / mccrea@taftiaw.com
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ES
CONTAINS NO CBI
2 RR,
am 189 8 Shiv nog
ps
25 Wut Set,SeC 1800/Coocinnc a, OHo5Co2ba0ro239n D5oi5n1a3.38p1 2o83l83a51r3.3i8etn0ts20eF5torswo8 naottSemoiUonP
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-
June 12, 2009
FEDERAL EXPRESS
EPA
U.S.
EDnovcikreotnmCeennttearl, PMroCte2ct8i2o2nTAgency
EPA 1301
WCeosntst,itRuotioomn
3334 Avenue,
NW
`Washington, D.C. 20004
Re: Submission to IRIS and AR-226 Database For PFOA/PFOS: 'ORD-2003-0016
EPA-HQ-
To IRIS Database for PFOA/PFOS:
In
USEPA's
response
efforts to
tcoontshiedNeortpiecrefilsusoruoeodctbaynoUiScEaPciAd
o(n"PFFeObAr"u)araynd23p,er2f0l0u6o,roroecgtaarndei:ng
`sulfonate ("PFOS") within the Integrated Risk Information System ("IRIS"), 71 Fed. Reg.
9333-9336 (Feb. 23, 2006), we are submitting the following additional information to
USEPA for inclusion in that review, and for inclusion in the AR-226 database:
i Fenton, S.E.,etal., "Analysis of PFOA in Dosed CD-1 Mice Part 2:
Dispositionof PFOA in Tissues and Fluids From Pregnant and Lactating
dMoii:ce10a.1n0d16T/hje.irrepPruoptsox,."
Reprod. Toxicol. 2009.02.012;
(2009),
2 dvMoioiln:k1Eo0hf.r1Be0rn1es6at/se]it.nfr,eeep0dr.ioSnt.go,xW.eot20ma0le.9,n.,"0P3"o.l0Ry0ef1pi;urooardno.adlTkoyxlicCohle.m(i2c0a0l9s),in the Serum and
3.
xHipnoessu,rEe.P.,oeteralf.l,u"oPrhoeonctoatnyopiicc
Dichotomy Following Developmental
cid PFOA) n emale D-1 ice:
ow
E Doses
tP Induce
Elevated
A( Serum Leptin
and
iF Insulin,
and
OCverweMight
L in Mid-
Life," 304 Molecular& Cellular Endocrinology 97-105 (2009).
CONTAINS NO cB}
nesurazs
JPuangee 122, 2009
Cdl oe in
RAB:mdm Enclosure cc: Gloria Post (NJDEP)w/ encl.) (via U.S. Mail)
Helen Goeden (MDH)(w/ encl.) (via U.S. Mail) Lora Wemer (ATSDR)(w/ encl.) (via U.S. Mail)
sen
ps
Accepted Manuscript
`Title: Anoaf PlFOAyinDsoseidCDs-1MicePart2: DispositionofPFOA intissuesandfluidsfrompregnant and
lactating mice andtheirpups
JLT
L-a
L5
NAauSktahaloylrSays,m:WaSh,uizAtaemn,nyAeDn.Ed.DrFeeewlnntBos.nk,LyiJnJedssostirncoamPL,..MSRtaearinnkkeoJr,,BSSrhuioyjnniaP.rF,H.ines, Syrago Syliani E. Pecropoulon
DoPOl::
Reference:
GS08o90-i62318(00e9)p.0r0o0t14o0x-0290019.6020/12
RTX 6230
Tosppearin: ReproductiveToxicology
.
RReocvesicvdeddadtaee:: 240222.0200909
Accepeddue: 25:2.2009
Pleas cit this atc a: Fenton SE,Reine JL, Nakayama SF, Delinsky AD, Sanko oJfPfr,oRmHiOpnreAesgniEanPn,tDoWashneiddtelCaDcSt-Sa,1tiLnMgiinmcdiesctePraonamtndA2B:t,hDeiSistprpoyosnpiasdr,oMnRJeo,pfroPPdeFutcrOtoAipvoeuinlTootuxiisSce-ocSlsEo,gaynAdn(a2fl0yi0s8d)ie,s 0i10,1016) reprotox200802012 "ATshisa sisearvPiDcFtoofiulrofcausntoumneerdsitweed mraenupsrcorviipdtintghatthihsaseabrelyenvearcscioenpoldftfohr mpuabnluisccartiiopnt. ber`Tfohorersmeamniutaisyscrbpieputdiwbsiclloluvienirdnseeidrhsgwohieciaocdlphycfeodorilmtd.iPnalgfefeaycspteetsnheoettcieontrghi.ntatdn,udrariennvgidetawheeopgraolhdeudcritcieloinlmeiprrspocrheosotf 36ply tothejournal eran.
RSE
CE TIE
ns eee sas
1
AnalysisofPFOA inDose CD MicPart2: Dispsition of PFOAinGusand usfrompregnantand catingmicandthelrpaps.
`Suzanne E. Featon", Jessica L. Reiner", Shoji F. Nakayama, Amy D. Delinsky', Jason P. Stanko", Erin P. Hines", Sally S. White,Andrew B. Lindstrom", Mark J. Stryoar, and `Syrago-Styliani E. PetropoulouTM
* Repodscive TasiclogyDivison NedoralHeathandEviromSemctes Rnesiearlch Laboratory, ORD,US EPA, MD-57, Reseach raParknNC2i711, USA
*Oakridge InstinuteforScienceandEducation (ORISE)Research Pariicipani, Human
~ExpasreandAmosphericSciences Divison, NedoralExposureReseachLabor, ORD, Us EPA. Research TaParkmNC2e7711, USA
manExponentAmospheriSinesDivision,NetnalEpos Research Laborato, ORD, US. EPA, Research TinglePark NC271, USA
Curriculum in Toxicology, Universityof North Carolina, Chapel Hill, NC 27599, USA
"HCeuartrhe,ntmaddrest sf:oDriDviirssieoansoefCLaboorataonnrdyPSrcoieenvceelsn, ,NaAtilonial,CeGnAter3f0o4r1E,nvUiSroAnmental
Comspaoonrddiasnsg:
URVSei5sieuaEDrrvEzT oFiraeanann,PPaPhakg tD,c.NiCo2en77A1gcyUSA FTax aolsess)
`E-mail: fenion.suzanncfiepgoav..
20009 [
EEE TEER
Ese
-
2
Runsogte: PFOAdisoasctatoionn
Avbrovations ANOVA saoftvarisance
BW
`bodyweight
pessoas
Lop lm ofdetcion
Log imitofqunintion
WS ms ectonse
FAA petioroaylacd
PFOA peorocimecidc
PROS peforocme inne
PD pestis
SM sandndocofthomenn
VLC ui petoinidmchroomatocgraephy
20m Pao 20132
ps
-
XoTNE ie
3
Absa Prvions siein icewith liplegaolexpo 0 perros
cid(PFOA)demons mame os depen growthad develope fics
`whichappearedtoworsen if offspringexposedin uteronursedfromPFOA-exposed.
ams.Tocasetsdisosion ofPFOAinthepregaanad cating ama her offen,imepregoanCD.1 ic ceived sige,0.1, ,or mgPRONG BW dose(425d rv)bygavage ongainday17,Mataedpropniaslnd
tissueswere colleovcetrteimde.Pupsexhibited signifbigihecr saernumtPFlOyA
cononrionsthanteresecve dus,ad ibyburden oes fr inh ladat ys,re egiss ofdose.Toediofsilkstna i PFOAvn aried oy osead ie,btwas pial ces of 02,These dtssgotmt ili bsnlPFOAexposurerou in mi andshou beconsidered nikassent [I --
Keywords:PRON: erasmoi us io: ilkmammary gd: doses dposion
2202009 ----
.
re
EON er perio ATA)
+ StS ron-- A --H --
? ----------------------T
6 carpeting,andupholstery,andthestabilityofthecarbon-fluorinebondhavemadethem
7 +
ckpamsmoephyemd asetopeekl g ee ubiquitousinthe environment.Thepredominantrouteof exposureinNorthAmerican
1F0ri
rn A rere PFAASarcpersistent,readily absorbed,notknowntobemetabolized, andare
12 13
fn eon
mt
ome tis
el9e65dint,55)
15rSoeatn 1 or A 4 OL25 0R 41 RY OA HA
16 Toe iri in reterbot
17 ratesortettn AOA
1+ thdt ,A etyy iteri
we----------------------
20 donorsindicated areductionof60%inbloodperfluorooctanesulfonate(PFOS)and 25%
521 yodwimcttyi m ms cr e EAS inblood PFOAlevelsbetween theyears2000and 2006{10). However,whilethe
23 reducedinthe USinrecentyears, it inotclear that perfhorinatedcompoundsproduced
sn rte
p10
:
5
1 ncthorcoun wil nt contin ts her te US kel or oe 2 comtiowboradsiegoosn, 3 Michoftherectbestffsreece onPFOA in ic,commnly 4 ssidvith stim goss of 001.5mg ROAg BY,basoudon 5 devclopmenaloie ch deredmal weigh enced esl 6 aviv aby weight, well ter ft:ft chspcr del,marary 7 ndshore, mdccssiveweightgin 1116,Bay posaladverse beh Observations rompedses arinin effect of PFOA on mane aonsnd 5 both ffs fhe sin fio,Whe tl (14 desribodreed pte 10 ftroiaion on osedy(PND) 10 amy endsof CD msedams 1 exposed 5 mgPOA BWfrmGDI,30 wellasdelaysi piel invlicn 12 snd emis in ilk rotigee crs on PDR0. In dio, omeoffspring 1 of xpos dm ilyedsted marypict rcin ndgh on PDI
14 andPND20. In across-fosterstady utilizingCD-1mice, Wolfetal.[16]reporttehadt
15 althoughin utero exposure to 5mgPFOA/kg BWfrom GD1-17inthe absenceof
16 tocion) poe wes suc postal body weigh ets1nd 17 devlopmenat ays opsri om bit weanwsaftaly inthos oh 18 introsd onlycps, sen se [15] eveshow ha 19. unexposedsonate taal ose10 PFOA qui developedmammary god
20 growthdeficitsandthatcontroldamsnursinginutero-exposedpups (damsexposedvia
21 pupgoamin) demons showedfran oftei ov maar ans
22 was evidentinwholemountpreparationsofthe tissuebytheS*dayoflactation.These
20009 [re
: ++ wa eiri---- ------------------ 6 + sseere--r--rT------------------r--it--n--t--n :o er--m----------------------T------ ? rerie--------p--T-------- n8;C m-- ete-- ---- ----------------T -- from1996-2004inSwedenat 8concentrationof492 pg/ml (0.492ng/m; (18),and 8
11 growthindices in childrenwithmediancordserumlevelsof1.6ng/m)PFOAintheUSS.
12 [20]and 5.6ng/mlPFOAinDenmark(21). Whileonlyonesamplewasfoundtocontain 13 PFOAintheKarman etal. 18]stady, theseresearchersreportad asignificantmilkto 14 serumcorrelation(7 =0.7-0.8, p<0.05)forotherPFAAsdetected. FurthermToaroee,t 15 al. [19)suggestedthattheremaybepreferentialpartitioningofPFOAtomilk compared.
I ete----------r---- ------ 16 tootherPFAAS andalsoindicatedthatwomenwhowerenursingforthefirsttime. =o19 -- e---- ---------- ------ -------- concentrationwere nottakenintoconsideration.Theonlystudythatbasevaluatedthe
22 Althoughfemalerats are knowntohave &serumPFOAhalf-lifeofonly afewhours[23], 23 unlikemicewhichhave a%-lifeofabout 15days (13),thestudy[22)indicated
-- ens
p12
,
1 concentrationsinratmilk approximately 10timeslessthanthatofmaternalplasmaand 2 thatthemilkconcentrationsweregeoerallyofthesamemagnitodeastheconcentrations 3 inpupplasma.
4 Tessas brit
5 PFAAsinanimalstudies,coupledwiththeirdetection inbumancordbloodandmilk, 6 supportstheneedfor examiningthedisposition of PFAAsduring pregnancy/lactationin 7 anappropriateanimalmodelinordertofullyestablishtheassociationbetween
ronson xpos adafro ffs.Whi erstehavecain 5 phumacokineisof PEAS ilindsoins, ledtcentlycis nh
10 disposition ofPFOAinpregnantandlactatingmiceorthei offspring.Werecently
11 developedananalyticalmethodfortheanalysisofPFOAin mouseserum,urine,milk, 12 mammarytissue,amnioticfluid,andpups [24].Utilizingthesemethods,we reporthere.
13. tan nthe inionof PFOA vrsmisopregoant nd acingCD-1. 14 mice awell heserumconcen dolbodyln fhi offiprin,folowing 15a single poeofPEOAonOD17,Thesedeawilllowstorue Wo sin pr spis ed SA w i" w 2 2
2n0m009 Pave 7e32
pis
'
'
| 2Materndimaetlhosds 3 21Chamicts 5 POA (ummaniumsks290% pu),wdinanimalcons, waspurchased 4 fiom Fh Chemical(Scien,Swix. FORwas compel disohvdby 5 anionindno apwt inwhichPFOAwasbelowte eveofdee (LOD 6 050g focwate,snpeered shot rir we ' 22dnime 5 Alon is wee conduct provedby hoNoon Hess nd. 10 EnvironmentBf Reese Laborstoryatta]Asi)CaeadUse: 11 Comite.Confmed medpregrac eseCD mice (100) erepurchasedfom
12 CharlesRiver Laboratories(Raleigh, NC).Pregnant mice werereceived atthe U.S.
13 EPA'sLaboratoryAnimalCarefacilityongestationday (GD) 14(dayofsperm-positive
14
15
designatedasGDO).Uponamival,mice (approximately
radonlydistintedsong PFOAwestmeotgroups.Th
12 weeksold)wereweighed
eywerehosed svat
and
in
16 polypropylenccageswithAlpha-dri(ShepherdSpecialtyPapers, Kalamazoo,MI)
17 beddingandnestingmaterials.Theywereprovidedpelleted chow(LabDiet5001,PMI
18
19.
NPutFrOitAiaotncIntoeronatcioenanlLiLbCeal,otBwrhieenotLwOnoDos)d,,MAOv)ianadftalpiwaetserwadeelicbiotnumt(rbootlhfecodorntained
20 tcmpenture(204C)adreliveBid (40-60%), ndkeptmda 1:10 lig
21 dorkcys.Mic (r-25doegrou)recivedsith wate veilor single oe01,
2 100r50mge) of PFOA mer; 10 byon evagean GDI.
220009
Page8of32
, s r------A t----
3
}
rmoekt.me--t----mt--w ----ri ----d--nt -------- PND (dayafterparturition),andPNDs2,4,8,11, and 18. OnGDS, 24br afterthe
?6+ crmpaein tmose--tom--eor--es--sv--n--m--at--eo glandwerecollected.Liverweight,totalnumberoffetuses(live,dead,orresorbed),and. #5 seeoeerr--et--te--i--bm----s--o i -- " c-- rm ---- F 3 vr wpmn--TP -------------- 4 Te --------rm --------------a --------. 1i eraomems eooenst eeeetm Anr. ovr e--t--ee------------------"h--r--r ---- 2r#1T ns--e------------------"-------- ---- PNDs4,8and 18(n= dams/dosegroup),althesametimeofday.
sod nt
p15
EER EETE IE ie
0
1 collectedonPNDs2,8, 11, a0d 18folowing a 2b separationof tepupsfromthedam 2 endam oxytocinstimulus,ThemillwasvacuumaspiredusingJow,pulsatilepressure, 3 into:pro-weighedmicroccatifig tbe.Collctedmilkwasweighedsodfrozenwil 4 analyzed.Biologicalsamplesiochodingurine,damaodpupsean,amniotic uid, 5 mammarysuc, wholepup,andmilkwereanalyzed orPFOAusingthemethods 6 described briclybelowadinourcorspanonpaper[4].
7 8 24PFOAsampleanalyses 5 Briel,th analysisofPFOAwasperformedusing aWaters AcquityTM Ulra 10 Performanceliquidchromatographysyteminterfacedwith a WatersQuatroPremierXE. 11 plequadrupolemassspectomedsr(UPLC-MSIMS) (Waters,Milford,MA). Eiter 25 12 or SOLofserum ndamaioti fd(50 ul.usedforcontro),20uL.aliquts ofurine 13 andmilk,and300uLofpupormammaryissueboxmogemateswere lizedasstarting 14 mateinfo hes analyses. Sumpleswere extracted,purified,and concentratedordiuied 15 exactlyasdescribedbyReineretal. 24], 10-40uL.oftepreparedsample dependiogon 16 theconcentrationofthe origoalexposure,was injctedaodrunonthe UPLC-MSMS 17 (24).RefertoReestal.[24]formethodperformance ndqualitycontrol sips hat 18 wereperformed fomare theprecisionandaccuracyofthemethodsused.The lit of 19 quantitation (LOQ)for thee experimentswere g/ml (serum), | ng/ml(amniotic uid, 20 urine,milk), and 1ng (whalepups,mammarytse). 2
2
2
2700009
Page 100132
pts
:
n
| 2
25UrCa crnatitne mierens weeemecan onbisn0carb oPOAninusse
3
4
u2r0inLeO.TDh0e0Qu1a0ntiChromndcrewastiniinneasss5a1y0(3Bi0o0AssanyShyTsthemys,Hoayfwaxrcdh,cCAo)sexhpibeitweds
prepared sdcad 510 msi or pl (vepceprof 20
6 samples)accordingtothe manufacturer'sinstructions.Theinter-assaycoefficient of
7 variation (CV)rangedfrom 4.0-6.8%andtheintra-assayCVrangedfrom0.3-16.1%,
5 wilhan avengeof 49%.Thesay stadtsry ranged om 028.4% sory
9 ROA repo as conocercent cocetions (og PRON cet)
W126
ComputatndiSotintess
1 Ror PRO containbvi tedfr dicorcoscnnion
15 ators,awela tine els ngs io) he weight of dime vated
14 15
coognenmaanimomnasryeiosensndswhgehp.opA).vSerrasma,,paniroitadpmsilkirnidiwiannopai,os
16
17
wdeertemcianlceudlatiendgwithrSoASG9L.1(SAANSOIVnsAti,tuiteh;CarDy,iNC)t. Stastitstiocaslsciogmnpifairciasnocne5wads.
18 if vassts005
n
n
20mm [RP
p17
.
2
[ER 2 3.1 Biological Outcomes 3 `This thefirststdytoreport ingle dosedisposition ofPFOA inpregnantand. 4 lactatingmiceandtheioffspring.Thedoseschosenwerebasedonprevious reportsin 5 CP-1mice 3, 14,16] demonstrating developmental beakthoutcomesfollowingmultiple 6 gestationalPFOAexposures. Asingle PFOA exposure on GDI7didnotaffect the: 7 mamberoffivefetuses (an GDI),implantationsites,or live-bompups (on NDI),or 8 dam body weights(daanotshown).Unlikestudi usingmalipl gestational PFOA 9 exposures [13, 25)therewasnochaagein pupbodyweight,dam liverweight, anddam 10. liver:BW ratios,withinthe PFOAdoserange administered in thisstudy(Figure1). The 13 rise indam liver:BWratiobetween GDI endPNDI,whichpersisted until weaning,was: 12. duetothedramaticdecrease in bodyweighta parturition, as tis singlehtegestation 13 PFOA exposurefiled ochangemean iverweight i exposeddams,compared control 14 values,at anytimeevaluated. 15 16 3.2 PFOAConcentrPraitoritooBinrtsh " `Themeanconcentration ofPFOA inthe amiotic fluidandserumoftheexposed 18 dams24hr afrexposure is shown (Figure2;amiotic uidcontrolsaverage3.8ng/mi). 19 Theaverageconoentation ofPFOAdetectedindamserumwasabou twicethe amniotic: 20 fiidconcentrationatcachdose evaluated (amniotic lidwas 68.,51.8,a0d 40% of 21 dam serumlevelsat 0.1,1,and S og PFOA/Kg BW,respectively). Acomparisonofthe 22 amountof PFOA inencotire GIDI fetus (bodyburden/pupstandarderrorofthemean 23 [SEM]; Figure 5)the1GDoIS PFOA concenitnarmnaiottiic oind (ng/ml; assuming 1
2202009
Page 120132
pis
| ove) val 2.3.1, nd 274d ceed PFOAin heppvs. the id.
2 in iciva coi ner fr 01,1, 3mg oegraepee
3 4
3.
PFOAConcerinttheoDonss
s Theera aad inePFOAconecsrions weeeval i umdst wre
6 ning trafpessimaly10pup PNDIcai;minima op osavrie).
7 Aexpected,da senconsindte ighstPFOAconcttons ofanymarx
5 att, egodss (igs; sr cont <Q).Teri in rnin
5 era PROAwitocesingdumexposesvaspropor othe chao in dose:
10 delivered,realsofsage ofhin. en 9-04nd 5.1 ese
1 between01-0 migand 1.050mphexposesrpectivh).
12 AooomePFOA exposof0. mgsproducedsnavngedam scum PFOA
13
14
concentration (Figure
which vas eed 0
3A) of
nave
14
of4-22
6
mgd ng/mlat
24 and 48 hrafter exposure,respectively,
rhekof Rion(PDS), odd
15. risnto mesmo 123ng byPNDIS, imewhentepps prayclrnk
16 came fo edtchowad os ilkThe U-apdseuconcn uve obi
17 inthe.mgPRON dos rovpwsa prescain he | dSmf xpos
3% porn
19
20
bougAhsbsehocwonnicneFnigsuures3of(PA-RCO;cAocntnronlurbienceaonmdpmraemmdairygylabnedePeFnOAser<aLOQ)i,oe,
21 ndmammary sue, dosto he iffrnc ntvas cident ches PFOA
22 wasbeingexcii dum inthanvas presen nda scum,ndth array
25 ieconned consider amon of PFOA.Whi shaped sponse am
220m009 [Rp
pis (oSTE TTTS oHRn |
1 excrionfPROA roe) as ota proouncd1 ifeu, amyGs
2 mons ongUnhped ese, ith lowestoxenmead ar.
3 ep ofcon,and sift e nconscomiaprtasia PRDIS
eons,
5 6a
UshWpheedncaaviero ed milv k PFOAe ats em rAvdaee id (iFnTn gle315,t hecopntcol. LrOe)o,f
7
5
PFOAinmilk (compared toserum)was substantial.Comparing the milk concentrations
toecoset iced dams concen ye), untof PFOA in
5 ik conten nga rom 1101 2 tf der OAsos dose adie
10 esperodyofction onwich ilk PFOAwas rdbd3 port
1 nfo oni esos.The sumPPOA twas rst cayad
12 cain PND? andPDS), agin from 15.56% ns of 396 yd26%1).
15 vhlcsar he ekof ion(NDSsd 11), heFROArill do gedfom
16 10.250on 1779). Twn possibleto smely man vl of ilk
15
16
obtained staspiration,butprecise weights were compared. On PNDs2,8,
avengewiht ikondvi spinofcos miewasO72,
11,and
01906,
18,the
17 0.2547,and0.0457g, respectively, demonstratingover a 3.5-foldincreasein weightfrom
18 FNDZ1a 1and 5.646 dpSomPADI 01,
w 20
3.4PPONConcenrtons
hePgs
3 pen PRO cocinnvas votedonPND 14,6, 18.1
22 compuing heversPFOAconan aPND!pup. irpcivdes
23 (ipa44; wholcool up ndoti rm<LOQ), peedht ccuing
20mm pom thet
p20
R STTT EE Re san
:
15
1 popseramPPOAcocoa erspin igh then hosemessrdi us,
2 regardlessof dose(<0.05).Althoughpupspossessed asubstantiallyhigherserum PFOA.
3 concer thandas, he ifsinp nddam lodvl hose asof 4 updevelaospcommiedrnblte Regofahors ifdieclese,besghesnd 5 clout PFOAinp srsefleced ncn exons,proportional due 6 ought actin (Lc,men104dsd43-dnreses wen 01-0mg
7 and 1.0-5.0mg/kgexposures,respectively).
8
Unliketheir dams, pups did notdemonstrate U-shaped serum PFOA
9 concntaion ives Figur 45. Popsr POA snosatios conned 0send
10 thesvgca semPFOAconestrtion vem,ul NDISwh thpupand
11 damconcentrationsapproached1:1. When the PFOAconcentration(ng/g)wasevaluated
12 in wel ie(upsnd Fire asl) deine in PFOAconnie vas 13 dtctove ime,cos los. However benthe ply increasingbodywight 14. of he opswes ken to consider to alt het atof PFOA inh 15. ectshownin Fir 1), complydiffevendvas nod Fige right
16 pancls). Regardlessofexposuredose,PFOAbodyburden (adjustedforweight)rose
17 throughthe peakoflactation andhadbegun 10declinebyPND18,demonstrating an
18 inverseU-shapedcurve.Whentheadministered PFOAdoseandmeasuredbodyburden
15. imwhoops odywight keto lfc)wrcompared oe distr 20 PROAmesure PFOA io wes 0 ong propor tonghont cain, sod nike 21 temo epor fortmsdpu sn PFOA. Mes byben sof 132-4 Zang 11078) sd 43-00 (age 32.1) ses between 0.110 hgmd L.0-
P)23 5.0mgkgexposures,respecwteriedveteerlmiyne,d. 2202000
[
p21
16
1 4.Discussion 2 "Thesedataconfirm thaton aconcentration-basedcomparison,gestatonally 3 PFOA-exposed pupscibite asigificantylargersemPFOAloadtha thir aan. 4 Thatsubstantial scrumPFOAloadinpupswasevident 24 hrafte asingleexposure,aad 5 wasapparently due oblood-boroe (imasplaccotal)transfer.Anotherimporantdiscovery 6 istheU-shaped PFOAconcentrationove time,regardlessofdoe,iathedammammary 7 tissue,milk, andserum.Thisunique PFOAresponsewasook delctedin pupsof pup 8 serum,andwasevident1a less extca inthedams"urinaryexcretioncurves. However, 9 whenPFOAbodyburden inwhol pupswestheustofmeasure, an inverse U-shaped 10 curvewasapparct, an the PFOAburdenofpupsisproposed increase due 0 ilk 11 bomePFOAintake. 2 "Thedeclineinconccaraionsecainthemilk,mammaryandserum U-shaped 13 curves isbypothesized 1be ue obydro-dilution associated with increased bloodand 14 milkvolumes. Severalphysiologicalconditionsarcchangedduring cation thathave. 15 beenwelldocumentedinrasanddiceyrelae 0mice 8 heirlactationperiodis ofthe 16 same eogth. Adecreas i otal plasmaproteiosdu to increasedblood vohune,cardiac 17 ouput,andbloodflow focetintissues,suchs themammaryglandbasbeen reported 18 inrat 26, 27).Elevatodblood volome idue toincreasedplasmavohume [27].Milk 19 yield(he) in aswasreported 0reachitspeakby PND 10 (27)andtherat mamamary 20 glandreaches itsmaximumsize(ss% bodyweight) byPNDIS(26),withastepis in 21 sizefomPNDS-15. Ratmammary lendbloodflowandvolumeofmilkproduce re 22 dirctyrelated, whenmeasuredonPNDIS [26], Totalserumproteinsaelowerin 23 Ictaing rats thtthosemeasured in on-lciating us (27), andin humans,serum
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:
"
1 albuminconcentrationdecreasesduringpregnancyandcarly lactation 28),Further,at 14 2d postpartum,th cardia outputoflactatingrabbiswas30%higherthanthatin on3 lactatinganimals, andthemammaryglandwastheolyorganshown 0increasein 4 weight,relive obodyweight 29). 5 Although completstofdatathatcouldadressthe cxactrezsonfortheUs 6 shapedcurvesduring acationwasnotcollectedinthisstudy,the aspiredmilkweights 7 didreveal adramaticincroasefomilkvolume (assumedduc tweightchange) rom 8 PND2uptothepeakof action(PND).Thisdramaticchangeinvolume (weigh) 9 mayexplainthedecreaseinmilk PFOAcanceatrationseenbetweenPND?andPNDI | 10 PFOAalsoappears 10conocotrate iserumandmk ne the odof tation(PNDIS, 11 forexample)whenpupsarecatingmorechowandsacle less fin.Mammarygland 12 bloodflowbasbeen reporid deceaseby alin 24hrperiod,whensuckling at 13. offspringar removedfromthedam (26),and hisfllinmammarybloodflowis directly 14 asocisicdwithdecreasedcardiooutputnd94 bloodflowusedbythemammaryglen. 15. nth stdy aprecipitousdropjnweightofmilkcollectedbetweenthepeakoflacaion 16 andPNDISwas noted,indicating arapiddecreaseinmilkvolume.Therefore, theUs 17. shapeofthedam PFOAcurvesarcproposed tbedrivenbyphysiological dilution and 18 conocaiation ofthe PFOAloudover th periodofcation,reachingthegreatestdition 19 atornearthepeakoflacuationwhenthemilk volumeproducedbythedamand 20 consumedbythe upsisth grstst.Increasedconsumptionof milk upto PND! ikl 2) dirtycontributedtothesccumultionofbodyburdeninthepupovertis iestage. 2 Asignificantcontribution ofmilk-bomePFOA ansfe inCD-1micewas 23 detectedinthes suds.Prvious reports rt 22)andhumans(18) ave stimaied
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TCH TCCNs
:
18
1 thatthedamPFOAmilliserum distribution atowas0.1and0.01, respectively. Inthe 2 presentsay,thedisrbutonratorange omslightymor then 0510.0. inmi, 3 dependingondos,with he vestdocetestddemonstratingthe highest tio ver
4 time. IfthemilkPFOAconcentrationshedbeenmeasurednearthepeakoflactationonly.
5 (days8-11),the0.1milkseradistributionestimatepreviouslyreportedforrasinmid-
6 location 22]mayhavealsobeenpresumedtru inmice.However,attwopodsduring 7 lactation (caryandIte)spikes of increasedwillserumratiosappeared,egadiesof
:
8 dose,with asubstantialpeakinmilkPFOAconcentrationsonPND2.Althoughvolumes
9 ofmilklargecaough operformsoa measore prosto PNDZwerenotabletobe:
10 obained,wesuspect,bsedo thesignificantPFOAconccatratons ithePNDI
11 mammarylandthtsubstantialmilk PFOAcopocaraioswouldbavebee evident
12 PND,aswel,prayde obeingcondensedinsllmilkvolumes.
1B
InpreviousreportsbyLau (13), Wolf(16],White [14)andco-workers,decreased
14 bodyweigh gainandaconstamoralitywere evidentonseveraldysjustafterbirth
15 CD-1mouseliters gestational exposed 0 3mpgPFOAaodhigher.Inc,ina
16 cros fosterstudy (16) demonstratingdecreasedbodyweightgana 3mg/gfrom in
17 weroexposure any,significantdecreases inbodyweightganwere detctodinte 3
18 makdosegrouponly when neroexposedmicewer aloallowed 0 urefrom a
19 PFOAexposeddam, Even stmgs,terewaspoevidenceofdecreasedpupbody
20 weightorneonatalmortalityinthecurrentstudy,following asinglegestationalPFOA
21 eaposur.OurPFOAmeasurements inwholepopsindicatethatthePFOAbodyburden 22 accumlates incary Ife,3dbegins adeclinea pups usr,opentei yes,andbegin
23 toeatchowanddrinkwater.Ourdatsandthosedemonstrating deleterious health.
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1"
1 outssgthemilkofgana PFOA-capose mic ws jorsomes 2 ofconinedexpose otiscompoundfr hedevelopingis. 3 Asexpected,rediffrac indamsndpupsemPFOAconctios om
4 thosepreviously reported [14, 16]werenoticed,andthosedifferencesbringtolightthe
5 issueof singlevs. multipledosekinetics.Asnotedfor PFOS, singledosekineticsmay
6 ifrbanal om hoseinvolving pet does 10), once dependent 7 hingesinclernccaneindiscepaciesbeensigesnd peste dose + Kosi. 9 Alimiedumberofpdemilgial sts ev veldseiadnsbwesn 10 heathote ithweight hdfc)and ond oodorment en 11 PFOAcocentaionin mans[20, 21), whictesis iletodetectsoins
12 with laterdevelopmentalmilestonesininfants [31]. Severalstudieshavenowmeasured
13 PRAASin hnml [17:15, 12, 3,however olyonestd as en beto 14 spasm themilsr relics of PFOApast[1], Thepred 0.01
15 (1/100")relationship was determined from s singlevoluntarily contributed sample at 3
16 weekspopu Acotiog ohmow ilkserumPROAditbutionaveri tat 17 wereportherin,theves porto on human (15 nd i [2] ayn be
18 representativeofthePFOAdistributiontomilkthroughoutlectationinthosespecies.
19 ncooduion,these sisconfmedsodSher definedconsidersPRO
20 exposuresto mouse offspringfollowing asingle gestationalexposure. They also
21 demons tsscum heal avertininwhlepps,which ilyeas 2 rom lorePFOA, xpos hathdpeiuslybn cpl assedin 25 aberspcin.Asale0.1mpg PFOA xpos pga msened
2n0n09 [Tr
p25
1 circulatingserum PFOAconccotaion of44-216 nf indamsand 117-326npnin 2 pups valuessila oorlower hanserumPFOAconcentrationsofchikdcathat were 3 scsidetaly posedvia DuPoutproductionpactemission (34). Becaseofevidence 4 115,35)demonsrtiogneonataland cothealtheffectsfollowingdevelopmental 5 exposure o PFOAjomice,sociatedwithhighercirculatingPFOAlevelsthanthose 6 reportedhere,continuedstoiccvalutin exposure-ffoctetonsipsarcamo in
7 chien.
8
5
10
n
2 13 Adaeidgements 14 Theauthorswould like othakDrs.Barbora Abbott(USEPA,ReproductiveTuxiology 15 Division)andChester Rdigoez(NationalCenterforComputations Toxicology, US 16 EPA)for thei constractive criciamsofthismanuscript. Weacknowledgethexcelent 17 careoftheseamimalsbyNow Year Tech,loc(Rest, VA).The esearchin isaril 16 basboc reviewedbythe NationalHealthandEnvironmentalEffectsResearch 19 Laboratory,USEaviroamentalProtection Agency(EPA), odapproved(orpublication.
20 Finding inthisreportar thoseoftheauthorsndapproval docsnoii isreport
21 22
reeflenctsdEPAopoorlrirceycs.oTmhmeeeunsdmeatoiefonrfnaoderutasem.esorcommercial produc
doesnoconsiaie
zn
2
2102009
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21
1 References
233 SS(b1p)varUtiSi.ppEPnurvoiogoavnmimeoopAtpdiPnreopstocsbibooneAglSeanpocy,sAL noiounnncm.en2At0k0of6r)hceasv2a0l1ib0El1Oe5SP.FOA
75 L(a2 WMiEAnndersn,ad11.BuKtBs.hWoitl,lS.aC,.CPheansgt,Do.nG.Fawrrs, GnLd.Keewvodyh,Jri, C.n
150
onionsand odesofsion, ToeSe. 103 AREY. D1 C.LanKC.Ano,C.Hodes,D.Li, A liteHuchessod.Sd,
11 Peforsallyacids arevi ofmoaiog nd colon dings,To 51,99
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(2007),366-394.
D(8u1chotGfWa.sdOlLen.,Z1ov.eB,aRrisf,D..ofsrsemn,mLVi. FirooeflpircherAeMs.sacnaclefo,1n.tc,
i11s67 Vpeteer,EomirornHeos bPwerdspoefo1ar5sGonOcaNmst1e29a9e1r30ne5dhioroochmnipodtucieon
3F1il0l51H5i)ngrbilTiro,dBl,aL Hiorcoown,mMu.ntWoxrpth,1.0PSHcOhSeiie,PFLOT.AC,oRwik raand2K8. 2008),
2354 V(6amKsSi,SGupmegye,pPaMs.eMacnoanget,aN.iYnosmaonfapiesf,sSroMtiioyt am.aTysossndrmN.and
5%55
pens i uCp romos3GhHOBeSr10.2. (1 GV.Olan, LY. Huang,KJ.HelouK,.. Harn,1. Buienboffa1n1d
23258. SVaensdeDl,riaorcahleSophaumanobflpoec,rrvopwncmHnellloPaeerpeecsf1t3s0s0o0%c,a5m39nv.3,d45
333152 sT[o8ot,s,eP1ngToieon,,KrnKdapinonlsarsnh.seKeofoamvoadrsbl,eiSMenMhd.eDCetonrsontcheGe.ainrF,iBicflloianona,i5Sm.ntrTToaskaaceh,alslthisa0entd.
M 336190 ) LrWe.nYoeun.g MX.So,G, Jang, Tanya,N.Yamshite M.S,.Wo,
33F76 rDDue1o.rycGbieon,sKionbuarsgevmoidPmX.lLasm,oPmeCmhiee,sEsmtraesToaocldato,nd8t2106),
2 [R1A0L] HoGrWo.,O2M lD.Ce.Mai in,TR.Chuh rcbh,tMLE,Ba JlAltioion,Wi X1..BRuenegl,. lTaMo.dLBote,
5453 ZAoembaetlc,saDnecRliendeCinrpeebrufiloeudoornsoo0a0nc0d.3ot0t0hae6r,npEotveyrfshounourSoloalkfTyelcohcnhenetm,isc4a2tls(2ei0n06),
220009
Papo 210152
ET TR Sl es
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2
, LL ER 2 [11] JL.Butenhoff,D.W.Gaylor, J.A. Moore,G.W. Olsen,J. Rodricks, J.H. Mandel Odopeo.oo 4 perfluReogulrToo xico olPc hart maca ol,n39o (20a 04)t ,36e 3-3, 80.
:i L(S E1) to 11.ti abla 2 epnem e tent e t 9 [13] C.Lau, JR.Thibodeaux,R.G.Hanson, M.G.Narotsky,JM.Rogers,AB. $B SinTen ie ne ry eto nn 11 inthemouse, ToxicolSci,90(2006), 510-518.
i2 if U8M , SSvi,Aae cans2tbioetS nEVliTemnktD.H inotre, 16 andfemaleoffspring,ToxicolSci,96 (2007), 133-144.
3E ziE3xR B2i3I3I:E$28p"URW0lR, lEUre m A UB ge E oC0m,omtmMES I nI 0rh0mnnalbE te iAn rhcKeto,eeemrr aB E a Cini di rs,niCr TmR nnr enbosKKfT ErrT n e r m ena ontrepAr3ae,dmt tCce 0e e hft. eot ilncnte BemeeCtppodernes im1arts5ots 23 [16] C.J. Wolf,SE.Fenton,J.E.Schmid,AM.Calafat,Z.Kukleoyik,X.A. BryantJ,.
sn ron
A NS A is
|||; 0h) CCmrht tain Temes ort eli
h :} oE y D21m evetm , i 1e Cr gn ec Te 5 (22) PM.HindeslitrE,.Mylchreest,S.A. GaJn L.Bn uteno boffn and, G.L..Kennedy,
5y ltl
m E a e moi n1 : E n 8iC S0 e e AL
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223xEBm Sim m) n me m ott etom i --
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2 [33] O.S. vonEhsenstein,Fenton, Suzanne E.,Kato, Kayoko, Kuklenyik,Zsuzsanna,
3 Calafat,AntoniaM.,Hines,ErinP. , PolyfluoroalkylChemicalsintheSerumandMilkof
45&
BreaWos ment Repf rode Toxie col,d In Pi ressn (20g 09).
(3) EAEmmet, FS,Shot, .Zhang,D.Freeman,C.DisdLM,Sha,
1705
ant corresores eyEviron Me 43000, 755.70 Communityexposure(0perfluorooctanoate:relationshipsbetweenserumconcentrations [35] EP.Hes,Whi,Sal,Sako,Jon P,Gibbs Floumoy,EvgocA,Lo,
111123 CBaexrpvtoaospwoeS1rsr,eaFomecoosp,otScsoasnsdnoeelA.inPk(enFndRarO wDFcehmdaoleaMGy.FAoIllM,oiwciHenogLlDoeCwvDiloE scinaollse
1ii4 TnPress(2009).
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1 Figurelegends:
2 memeeso toeA taosnrescottog0t 1in,s Figur1e.Damtissueweightsandaverage pupweightsfollowing asinglegavagePFOA.
5
7
eecoemat--ys--s rrOTNm--n--t D--o --an rtt--m--rSirn20 (GD)I8 (notshown). (A)Damliverweight,(B)liver:body weightratio,and (C)pup
I 5 moeCompton
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eon t ron eet anrnm0o9,ootnete rieo dom5n
I
13 indamserum (A; g/m),urine(B;ng/gcreatinine),and mammary tissue (C; ng/gtissue.
14 wre Sant n reeds weight) onpostataldays (PND)1,4, 8and 18. PFOAconceatrationsweremeasuredin
1716 ten oes tom sori bo i's A-Cand B-D cannotbedirectlycompared(duetodifferentunits), the U-shaped
e o aoreoaannmeroHn asltdtnseftmtTeTooo nnct9stkspttte5yetr1tSeOygr Aoi 18 `mammarytissueandaspiratedmilk.Dataareshownas Mean + SEM. "Denotes asingle.
se rm
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1 declinedove time,presumablydeto ition ofdosebyincreasedgrowth relied blood 2 volume,Dataaeshown as Mean SEM. 3 Figures. WholepupPFOAconcentrations.PFOAconocommatonsweremeasuredia 8
4 representative wholepup(pupandblood;ng/g;leftpanels)fromeachlitter.Although
5 ther is aconsistentdownwardtrendinPFOAconcentrationove tie, the apy 6 increasing bloodvolume 0dbodyweightchangesmustbetakeninoconsideration when 7 interpreting hes dae.Bodyweightadjusidvahoes(ightpools (oggPFOA 8 measures bodyweight =bodyburden]demonstrate an accumulationofexposureui 9 latinthelacaonalperiod.Daaare shownas Mean +SEM. 10 n2
202009
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Figuress1. 50
S5EHI2lH5 lii7
(A) DLam%Liver Weight
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PFOA Exposure (mglkg)
.
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Figure3.
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ELSEVIER
temic
Molecular and Cellular Endocrinology
Journal homepsas: wwwslsavior.com/igsateimee
Phenotypic dichotomy following developmental exposure to perfluorooctanoic acid (PFOA) in female CD-1 mice: Low doses induce elevated serum leptin
and insulin, and overweight in mid-life*
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