Document N2V55zQqYgymEXDv26QREaE5y
3M MedicalDepartment Study:T-6295.7
Report No. FACT TOX-030 LaboratoryRequest Number-U2279
ANALYTICAL LABORATORY REPORT
FROM THE
26-Week Capsule ToxicityStudy with PerfluorooctanesulfoniAccid Potassium Salt
(T-6295)inCynomolgus Monkeys
ON THE
Determinationof the Presence and Concentration of Perfluorooctanesulfonat(ePFOS) in Liverand Serum Samples
Projectldentification 3M MedicalDepartment Study:T-6295.7
Covance In-LifSetudy:#6329-223 AnalyticaSltudy:FACT TOX-030 3M LaboratoryRequest No. U2279
Study Completion Date At signing
TotalNumber of Pages 2-33
3M EnvironmentalLaboratory
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3m Medical Department Study: T-6295.7 3M MedicaDlepartmenSttudyT:-6295.7
GLP COMPLIANCE
STATEMENT
Report No. FACT TOX-030 laboratory Request Number-U2279
ReportNo. FACT TOX-030 LaboratoryRequest Number-U2279
Study T-ide:
AnalyficaLlaboratoryReportfromthe26-Week Capsule ToxicitSytudywith PerfluorooctanesulfoAnciicd PotassiumSalt(T-6295)inCynomolgus Monkeys on the DeterminationofthePresence and ConcentratioonfPerflucrooctanesulfon(aPtFeOS) inLiverand Serum Samples
Study IdentificatiNounmber: FACT TOX-030, T-6295.7,Covance #6329-223
Thisstudywas conductedincompliancewithUnitedStatesEnvironmentalProtectioAngency Good LaboratoryPractice(GLP) Standards40 CFR Part792,withtheexceptionsinthebulletedlisbtelow.AJI raw data and samples forthisstudyareretainedinarchivesatthe3M Lab and wilble retainedfora periodof atleasttenyears.The analyticaplhase completedatthe3M Lab was performedin accordance with3M ET&SS StandardOperatingProcedures.
ExceptionstoGLP compliance:
There were two studydirectorisnthisstudy.Thisstudywas designedas two separatestudies. The in-lipfhease studywas consideredtoend atthegenerationand shipmentofspecimens. The analyticasltudywas consideredtostarattthereceipotfthesespecimens foranalysis. This resultedinhavingtwo separatestudydirectorosn,e foreach phase ofthesame study, However, sincethetechnicalperformanceofeach phase was entirelsyeparate,no effectis expectedfrom thisexception.
On a few occasions,datawere notrecordedor correctedexacflyas requiredby theGLPS.
The 3M TOX 030 protocolstatesintheRegulatoryCompliance sectionthat'7hisstudywillbe conducted inaccordancewiththeUnitedStatesEnvironmentalProtectioAngency Good LaboratoryPracticesStandards,40 CFR 792,withtheexceptionthatanalysisofthetest materialmixtureforconcentrations,olubilithyo,mogeneity,and stabiliwtiyllnotbe conducted, and istheresponsibiliotfytheSponsor."Analyseswere,however,completedon the concentratioannd homogeneity ofthetestmaterialmixture,accordingtonon-GLP validated methods, and are incjudedinthisreportA.s pertheprotocols,olubiliatnyd stability determinationwsere notconducted.
Study Director
Date
Study Sponsor
Date
3M EnvironmentalLaboratory 3M Env4-ronmental 1T@aboratory
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3m Medical DepartmenL- Study: T-629S.7 3M MedicalDepartment Study:T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
ReportNo. FACT TOX-030 LaboratoryRequest Number-U2279
GLP STUDY-QUALiTy
AssuRANCE STATEMENT
Study Tite:
AnalyticaLlaboratoryReportfrom the26-Week Capsule ToxicityStudywith PerfluorooctanesulfoAnciicdPotassiumSalt(T-6295)inCynomoigus Monkeys on the Determinationofthe Presence and ConcentratioonfPerfluorooctanesulfon(aPtFeOS) inLiverand Serum Samples
Study IdentificatiNounmber-. FACT TOX-030, T-6295.7,Covance #6329-223
The analyticaplhase ofthisstudyhas been inspectedby the3M Lab QualityAssurance Unit(QAU) as indicatedintheblowing table.The findingwsere reportedtothestudydirectoarnd management.
INSPLCTION DATES
DecemberOlM
PHASE
Sample receipt
DATE REPORTED TO
MAtJAGEI.7EIVr
STUOYDIRECTOR
1/17100
1/17/00
March 19,22,23199
Analysis
3/25/99
3/25/99
October 14/99
Extraction i
May 3,8-12,15-19,22-26,29-31100,
June 1,2,5,7,8/00
Data
June 1,5,7,12-16/00
Draftreport
10/20/99 6/14/00 6/16/00
10/20/99 6/14/00 6/16/GO
September 14/00
Draftreport
9/14/00
9114/00
QAU Represo@tative
Date
3M Environmental Laboratory 3M Environme---i-@alLaboratory
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3m Medical Department Study: T-6295.7 3M MedicalDepartment Study:T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
ReportNo. FACT TOX-030 LaboratoryRequest Number-U2279
STUDY PERSONNEL AND CONTRIBUTORS
Study Director Andrew M. Seacat Ph.D. 3M MedicalDepartment 3M Center,Building220-2E-02
PO Box 33220 St.Paul,MN 55133-3220 (651)575-3161
Sponsor 3M ToxicologyServices- MedicalDepartment 3M Center,Building220-2E-02 St.Paul,MN 55133-3220
John L.ButenhoffP,h.D.,SponsorRepresentative
Analytical Chemistry Laboratory Liverand Serum Analyses 3M EnvironmentalTechnology and SafetyServices(3M ET&SS) 3M EnvironmentalLaboratory(3M Lab) FluorineAnalyticaClhemistryTeam (FACT) 2-3E-09 935 Bush Avenue St.Paul,MN 55106
KristenJ.Hansen, Ph.D.,PrincipaAlnalyticaIlnvestigator
Contributing Personnel David R. Bamidge LisaA. Clemen
KellyJ.Dorweiler Mark E. Ellefson Sara E. Estes
Barb A. Gramenz Sarah A. Heimdal CariS. Hewitt Marlene M. Heyirg
Harold0. Johnson KellyJ.Kuehlwein SallyA. Linda MichaelD. Livingston Joseph C. Pilon ScottR. Post [anA. Smith Anh-Dao Vo Bob W. Wynne
In-lifeTesting Laboratory Covance LaboratoriesI,nc. 3301 Kinsman Boulevard Madison,Wi 53704-2595
PeterJ.Thomford,Ph.D.,in-LifPehase StudyDirector
3M EnvironmentalLaboratory 3M Env@-ronme---tal Laboratory
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3m Medical Department Study: T-6295.7 3M MedicalDepatnent Study:T-6295.7 TABLE OF CONTENTS
Report No. FACT TOX-030 laboratory Request Number-U2279
ReportNo. FACT TOX-030 LaboratoryRequest Number-U2279
GLP Compliance Staterr*nt..............................................................................2......... GLP Study-GualityAssuranceStatement...................................................3...................... StudyPersonneland Contributor.s..........................................................4...................... Introductioand Purpose .................................................................6......................
TestSystem ........................................................................6...................... Specimen Collectioannd Analysis......................................................................7.......................... Specimen Receipt.......................................................................7...................... Dose ConfirmationAnalyses.............................................................................8................................... Materialasnd Methods ......................................................................................8....................................... Chemical Characterizabo.n..............................................................8...................... Method SummOes ..........................................................................8................ AnaNbcal Equipment.................................................................9....................... Deviabons .........................................................................1.0...................... Data QualityObjectivesand Data Integrit.y.................................................1.0....................... Data Summary, Analyses,and Results......................................................11....................... Summary ofQual@y ControlAnalyses Results............................................11....................... Summary ofSample Resufts..........................................................1.2................... Statsbr-aMlethods and Calculabons........................................................1.2...................... Statement ofConclusion.........................................................................................@..1.2................. ListofAttachments.........................................................................................1..2........................... AttachmentA: ControlMatrixCharacterizabonand Dose ConfirmationAnalyses..................1.3............... AttachmentB:Protocoland Deviabon Summary .........................................................15................ AttachmentC: Extractioannd AnalyticaMlethods .............................................4.3...................... AttachmentD: Data Summary Tables......................................................1.7.9...................... Attachment E-.Data Spreadsheets...........................................................................1..8..8........................... Attachment F.-Example Calculabons..........................................................2.2.5......... AttachmentG: InterimCerbficatoefAnalyses...............................................2.2.6....................... AttachmentH: ReportSignaturePage ........................................................2.3.3.............
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INTRODUCTION
AND PURPOSE
Report No. FACT TOX-030 laboratory Request Number-U2279
ReportNo. FACT TOX-030 LaboratoryRequest Number-U2279
C8Fl7-S
-0-
11 0
Perfluorooctanesuff(oPnFaOtSe) CASNumbe2r759-39-3
Chemical Formula: C,,Fl7SO.3-
MolecularWeight-4.98.98
The purpose oftheanalyticaplhase ofthisstudyistodeterminethepresenceand concentratioonf PFOS (CBF17S03-) inlivearnd serum specimens collectedduringthestudyofCynomclgus monkeys oralldyosed withperfluorooctanseulfoniaccidpotassiumsalt(T-6295).
Test System
The testsystem speciesand strainselectedwas theCynomclgus monkey from Covance Research Products,Inc.i,dentifiuesdinga collatrag.At theinitationftreatmentt,heCynomolgus monkeys were young adulttoadult,and weighed appmximately3-5 kg.
Twenty-twomale and 22 female Cynomolgus monkeys were used as the testsystem inthe present study.Four groups oftestanimalswere establisheadccordingtodosage levelsG.roup 1 consistedof controlCynomolgus monkeys thatdidnotreceivethetestsubstance,butreceivedtheequivalent amount oflactoseingelatncapsulesas thatadministeredtotheGroup 4 animals.Groups 2,3,and 4 were administeredailywith0.03(lowdose),0.15 (middose),and 0.75 (highdose)mg respectiveloyf, T-6295 perkg ofbody weight/day(mgikg/day)trituratweidthlactoseingelaticnapsules(seeTable I for Dosage and Group Characteristics).
Table 1. Dosage and Group CharacteristicosfTest System inStudy T-6295.7
STUDY GROUP
NUMBER OF ANIMALS TOTAL DOSAGE LEVEL DOSAGE RATIO (mgfkglday) (W:W)a
Total:Test System
22 males 22 females
Group I (Control) 66 mfaelmeasles 12 0 -
Group 2 (Low Dose) 44 fmeamlaelses 8 0.03 1@499
Group 3 (MidDose) 66 fmeamlaelses 12 0-15 1i39
Group 4 (HighDose) 66 fmeamlaelses 12 0-75 139
a Testsubstancetrituratweidthlactose . 48 animalswere inrjudedinthebaselineseracollectiobnu,t44 animalswere assignedfortreatment
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Alltreatmentgroups were dosed fora minimum periodof26 weeks. Sera specimens were collected from alltestanimalsatvar;oustimepointsduringthein-lipfhease ofthe26-week studyand senttothe 3M Lab foranalysis(seeAttachmentD, Tables D-1a,D-1b).
Four animalseach from Groups 1,3,and 4 were designatedas recoverygroup animals.Treatment was discontinuedand the animalswere monitoredforeliminationfcompounds forone year posttreatmentT.he recoverygroups were observedafterthecessationoftreatmentuntiFlebruary25,2000 (Week 79)forGroup 1 and Group 4 recoveryanimals,and untiMlarch 7,2000 (Week 80)forGroup 3 recoveryanimals.
Specimen Collection and Analysis
Inthe analyticaplhase reportedhere,livearnd seraspecimens collectefdrom alltestanimalswere sent to the3M Lab and analyzedforthepresenceofPFOS (some samples were analyzedtodeterminethe presence ofETFOSE, PFOSA, POAA, PFOSEA, M556, PFOSAA, and themonoester-h,owever,these datawere collectefdorinformationaplurposesonly,and arenotreported)S.pecimens otherthanserum and livetrissueswere collecteadnd receivedfrom Covance Laboratorie(s6329-223),butwere notpart ofthecurrentscope ofanalysisdeterminedby thestudydirectoarnd sponsor.Additionaalnalysesof fecesare beingcompletedand willbe issuedas an amendment tothisfinarleport.
Bloodspecimens were centrffugewdithinone hourofcollectioTnh.e serum was thenharvestedand storedina freezersettomaintainspecimens at-60to-80*C untislhippedtothe3M Lab.Liver specimens collectefdrom each animalwere flashfrozeninliquinditrogenand thenstoredina freezer settomaintainspecimens at-60to-80'Cuntislhippedtothe3M Lab.Liverand seraspecimens were shippedtothe3M Lab frozenand on dryice.Liverspecimens from Group 3 (3/01/00)and Group 4 (9/22199)recoveryanimalswere collectevdiabiopsy.
Sera and livesramples were extractedusingan ion-pairinrgeagentand methyl-tert-buettyhler(MtBE). Liversamples were homogenized priortotheextractiopnrocedure.Sample extractwsere analyzed usinghigh-pressurleiquicdhromatography-electrospray/tandmeamss spectrometry(HPLCES/MS/MS) inthe multiplreesponse mode. PFOS levelswere quantitatebdy externalstandard calibratioAnn.alyticadletailasre includedinthisreport.
Specimens Collectedfrom Study Groups I through 4 (through 2J25/99): Serum Specimens-550 specimens:9--14specimensianimal LiverSpecimens--30 specimens
Specimens Collectedfrom the Recovery Group from 2127199to 3107100-. Serum Specimens-224 specimens:18-20 specimenslanimal LiverSpecimens-1 2 specimens from Group 3 and Group 4 animals(8viabiopsy)
SPECIMEN RECEIPT
Specimens were receivedfromCovance Laboratoriepseriodicaldluyr,ingthe in-lipfhease ofthisstudy, from August 1998 throughMarch 2000.Specimens receivedwere frozenand on dryice.Specimens were loggedinwiththe3M Lab and transferretdofreezersforstorageateither-55'ClG-20'C or -20*C 10*C.
Controlmatricesused inlivearnd seraanalysesperformedduringTOX-030 were obtainedfrom commercialsourcesand arepresentedinAttachmentA (seeTableA-1).Samples analyzedatthe3M Lab willbe maintainedfor2 periodof 10 yearsand willbe storedatthelaboratorayt-20'C 1O'C.
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Dme Corfflrmation Analyses
Dose confirmatioannalyseswere performedon lactosedose samples (1:39and 1:499)collecteodn 8/11/98duringthe in-ifpfhease ofthestudy:theresultasrepresentedinAttachmentA (seeTable A-2, A-3).The dose confirmatiodnatawere collecteadccordingtoa method thatwas notfullvyalidated.
Dose confirmatiownas performedby dilutintghelactosedose samples (1:39- 1,000xand 1:4991,000x)withMilli-wOater,then extracteudsingtheion-paiprrocedure,diluted1:50and 1:5respectively intothe linearange oftheinstrumentF.oreach sample (top,middle,bottom),a matrixspikewas prepared(appmximately5000 pg/gand 400 pg/g)by spikintghedose solutioannd thendilutinagnd extracbngas describedabove. Inallcases,samples were analyzedversusan unextractedcurveusing HPLC-ESIMS/MS. The instrumentaplarametersand analyticaClonditiondsescribedinETS-8-5.1were used fordose solutioannalyses.The averagedose levelmeasured was confirmedtobe 99 27% of thetargetconcentrationM.atrixspikeswere recoveredat>60%.
MATERIALS AND METHODS
Chemical Characterization
Table2 presentsinformatiroengardincgharacterizatoiftohnetestsubstancuesed inthein-lipfhease of thisstudy,and the analyticarleferencesubstanceused intheanalyticaplhase ofthisstudy.
Table 2. Characterizationof Test and AnalyticalReference Substances inStudy FACT TOX-030
CHEwcAL NAME SOURCE ExpiFzA-noNDATE STORAGE CONE)MONS CHEmicAL LOT NumBER PHysicAL DESCRPNON PURITY
TEST SUBSTANCE
ANALYTICAL REFERENCE SUBSTANCES
KPFOS Potassium
KPFOS Potassium
Perfluorooctanesuffonate Perfluorooctanesulfonate
3M SpecialtCyhemicalsDiv. 3M Special@CyhemicalsDiv.
THPFOS IH.lH,2H,2Hperflucrooctanesulfaodndic
ICN BiomedicsI,nc.
8131/2001
8/3112C)01
1/01/2020
Frozen<-10*C
Frozen:s-lo'C
Ambienttemperature
217
FC-95.Miitecrystalline er
86.90/a
171 Whitecrystallpionweder
86.4%
59909 Brown powder
N/A
53406 Brownwaxy sdid
N/A
Reserve samples oftheanalyticarleferencesubstancewillbe storedatthe3M Lab fora periodof 10 years,as willany reservesamples oftestsubstancereturnedfromthein-lipfhease ofthestudy.
Method Summ2ries
Followingisa briefdescriptioonfthelatesmtethods used duringtheanalyticaplhase of thisstudyby the3M Lab.Detaileddescriptionosfthemethods used inthisanalyticaplhase arelocatedin AttachmentC. As thepresentanalyticaplhase ofthisstudyprogressed,more advanced methods evolvedand eariiemrethods were used withdeviabonsuntialmendments totheprotocolwere written. Changes tothemethods includedtheuse ofmethyl-tert-buettyhler(MTBE) insteadofethylacetate, curves plottedby linearegressionweightedI/xinsteadofunweightedcurves,a reductioninthe sizeof theanalyticaclolumn from 100mm to50mm, gradientchanges,and fasteHrPLC cycletimes.A summary ofprotocoland method deviationisspresentedinAttachmentB (seeTableB-1)ofthisreport.
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Preparatory Methods:
ETS-8-6.0,"ExtractionofPotassium Perfluorooctanesulfonatoer otherFluorochemicalCompounds from LiverforAnalysisusingHPLC-Electrospray/MassSpectrometr/'
Liversamples were homc>genized inwater.An aliquotof each homogenate was spikedwith THPFOS and extractedusing an ion-pairinegxtractiopnrocedure.An ion-pairinrgeagentwas added tothe sample and the analyteionpairwas partitioneidntoMTBE. The extractwas transferredtoa centrifugetube and put onto a nitrogenevaporatoruntidlry.Each extractwas reconstituteidn1.0mL ofmethanol and passed througha 0.2 pm nylonfilteurs,inga 3 CM3 disposable plasticsyringeintoglassautosampler vials.
ETS-84.1, "ExtractionofPotassium PerfluorooctanesulfonatoerOther Fluorochemical Compounds from Serum forAnalysisUsing HPLC-Electrospray/Mass Spectrometr,/'
Sera samples were spiked withTHPFOS and extractedusing an ion-pairinegxtractiopnrocedure. An ion-pai@ngreagentwas added tothe sample and the analyteionpairwas partitioneidntoMTBE. The MTBE extractwas removed and put onto a nitrogenevaporatoruntidlry.Each extractwas reconstituteidn1.0mL of methanol and passed througha 0.2 pm nylonfilteurs,ing a 3 cm-, disposable plastiscydnge intoglassautosampler vials.
Analytir-alMethods:
ETS-8-7.0, "AnalysisofPotassium PerfluorooctanesulfonatoerotherFluorochemicalsinLiver ExtractsUsing HPLC-Electrospray/Mass Spectrometr/'
ETS-8-5.1, "AnalysisofPotassium Perfluorooctanesulfonatoer Other FluorochemicalinSerum ExtractsUsing HPLC-Electrospray/Mass Spectrometry"
The analyses were performed by monitoringone ormore productionsselectedfrom a single primaryioncharacteristiocfa particulafrluaror-hemicaulsing HPLC/ESIMSIMS. For example, molecularion499, selectedas the primaryionforPFOS (C,F,,SO,-)analysisw,as fragmented to produce ion99 (FSO,-).Tne characte@stiicon99 was monitoredforquantitativaenalysis.
An2WcW
Equipment
The actualanalyticaelquipment settingsused inthe presentanalyticaplhase ofthisstudy variedslightly duringactualdata collectionT.he followingisrepresentativoefthe settingussed during',heanalytical phase ofthisstudy.
Liquid Chromatograph: Hewlett-PackardoSeries1100 LiquidChromatograph Analyticaclolumn: KeystoneD Betasil'C"ie 2x5O mm (5pm) Column temperature:Ambient Mobile phase components@
Component A: 2mM ammonium acetateinwater Component B: methanol Flow rate:300 pumin Injectiovnolume: 10 pL SolventGradient:10 minutes
system
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Startat 1O%B Hold at10%B for1.0minute Increaseto95%B over4.5minutes Hold at95%B for2.0minutes Return to 1O%B over 0.5minutes Hold at 10%B for2.0minutes
Mass Spectrometer MicromassO API/Mass SpectrometerQuattro11"TriplQeuadrupole system Software:Mass Lynx' 3.2 Cone Voltage:60V CollisioGnas Energy:40-6OeV Mode: ElectrospraNyegaWe Source BlockTemperature:1500C lOOC ElectrodeZ:-spray AnalysisType: MultiplReeactionMonitorin(gMRM)
Table 3. NegativeIons Monitored inFACT TOX-030
TARGETANALYRE
PPJMARYION(amu) PRODUCT [ON (amu)
PFOS
499.0
99.0
THPFOS
427.0
80.0
Devi2tiorLs
Itshould be noted thatas the analyticaplhase ofthisstudyprogressed,method parameters were evaluatedto improve ana@/ses.Eadiermethods were used withdeviationsuntialmendments tothe protocolwere writtenD.eviationsfromtheoriginaplrotocoland methods aredocumented inthe AttachmentB (seeTableB-1).
DATA QUALITY OBJECTIVES AND DATA INTEGRITY
The followindgata qualitoybjecbves(DQOS) were indicateidntheprotocolforthisstudy:
LinearityT:he coefficieonftdeterminatio(n@)equaltoor greaterthan0.98 Limitsof Quantitation(LOQ): The Method DetectioLnimit(MDL) forPFOS is12 ppb forserum
and 15 ppb forliverT.he LOQ isequaltothelowestacceptablestandardinthecalibratiocnurve. Duplicate/AcceptablePrecision:Precisiownas reproduciblteowithin30% Spike/Ar-ceptablReecoveries:70-130% Confirmatory Methods: Indeterminatseamples may be re-@nalyzedusinga confirmatormyethod.
Ifa confirmatorymethod isused,an amendment tothisprotocolshouldbe written. Demonstration of SpecificityS:pecificittoybe demonstratedby chromatographicretentiotnime
and mass spectraldaughterioncharacterization.
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DATA SUMMARY, ANALYSES, AND RESULTS
Dataqualitoybjectivefsortheanalyticpahlase ofthistudyouflineidnthe3M Lab protocoflorFACT TOX-030 (seeAttachmentB)were metwiththeexceptionnsotedinthisreport.
Summary of Quality Control Analyses Results
LinearityT:he coefficieonftdeterminatio(n@)ofthestandardcurvewas @!0.985.
CalibrationStandards: Quartitatioonfthetargetanalyteswas based on linearegression analysis(unweighted- priotro3/5/99u,nweightedorI/xweighted-3/5/9t9o3/19/99a,nd 1/x weighted-3/19/9t9oend ofthestudy)oftwoextractemdatrixcurvesbracketinegach groupof samples,exceptas notedinthedeviatiosnummary, Highor lowpointson thecurvemay have been deactivatetdoprovidea bettelrineafriotverthecurverangemost appropriatteo thedata. Low curvepointswithpeak areaslessthantwo timesthatoftheextractiobnlankswere deactivated todisqualifaydatarangethatmay have been significanatflfyectebdy backgroundlevelsofthe analyteO.ccasionallya,singlemid-rangecurvepointthatwas an obviousoutliewras deactivated. Quantitatioonfeach analytewas based on theresponseofone specifipcroductionusingthe multiplreesponse-monitorimnogde oftheinstnimen(tseeAttachmentC).
Limitsof Quantltation(LOQ):The LOQ isequaltothelowestacceptablestandardinthe calibraticounrve(defineads a standardwithin30% ofthetheoreticvaallue)a,nd isatleastwo timestheanalytepeak areadetectedintheextractiobnlanks.Thisvaluedoes notexceed the validatedLOQ ofthemethod fordatathatisaccepted(seeAttachmentD, TableD-6).
Table 4. Determinationof PFOS LOQ inTOX-030 Analyses
ANALYTE-MATRLX
LOQ
PFOS-Sera PFOS-Liver
4.39-15.n2g/mL 26.9---60n.g1/g
Blanks: AJIblankswere below thelowerlimiotfquantitatifoonrthecompounds ofinteresTto. simplifaynalysesthatwere complicatedby endogenous levelsoffluorochemicailnsunexposed monkey sera,rabbaserawas selectedas a suitablseurrogatematrix.
Duplicate/AcceptablPerecision:Precisiownas determinedby analysiosfMS/MSD and was reproduciblteowithin30%.
MatrixSpikes: Matrixspikesand matrixspikeduplicatewsere extractewditheach setofsamples and analyzedduringanalyticarlunsatthe3M Lab.AJIseramatrixspikeswere within30% ofthe theoreticacloncentratioMna.trixspikespreparedinlivewrere compliantwithin30%, withthe exceptionofone spikethatwas preparedwithDay-393 samples and had a lowrecovery.The matrixspikewas reextrac*,aendd therecoverywas within30% ofthetheoreticcaolncentration.
Spike/AcceptableRecoveries:Spikerecoverieosf30% ofexpectedvalueswereachievedfor allmatrixspikespreparedinsera.Withone exception(notedearlierm)a,trixspikespreparedinliver were within30%.
Use ofSurrogates:The surrogate(THPFOS) was added toallsamplesand standardsT.HPFOS was notused forquantitatiobnu,twas used tomonitorforgrossinstrumenftailurAef.ter11/04/99, thesurrogateresponseofeach analyticarlunwas verifietdodeterminethatitdidnotvarymore than:t5O% fromthemean withineach analyticarlun.No problemswere observedwiththesedata.
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Assuming spikerecoverystudiesforma suitabliendicatiofnendogenous analyterecoveryd,ata are quantitatitvoe30%. The validitoyfthisassumptionhas notbeen verifiebdy othertechniques.
Summary of Sample Results
Samples from ControlAnimals:Low levelosfPFOS wereoftendetectedintheseraand liveorf thecontrolanimals.These levelwsere significanluoywerthanthosefoundinthelow dose test animals.
Samples from Dosed Animals:IngeneralP,FOS levelfsoundintheseraand liveorfthetest animalsincreasedwithdose group.PFOS levelsincreasedas dosage increaseds;ignificant dfferencesbetween male and femalePFOS levelwsere notobservedinsera.However,Group 4 males had notablyhigherPFOS levelsinlivesramples thanGroup 4 females.Detailedsample dataispresentedinAttachmentsD and E.
STATISTICAL METHODS AND CALCULATIONS
Stadsticamlethods were limitetdothecalculatiofnmeans and standarddeviationsS.ee AttachmentF forexample calculationused togeneratethelivearnd serum sample datainTOX-030.
STATEMENT OF CONCLUSION
Under theconditionosfthepresentanalyticpahlase ofthisstudy,PFOS was detectedintheseraand livesramples of Groups 2,3,and 4 animals.The ControlGroup 1 animalsshowed minimalamounts of PFOS. PFOS levelsincreasedas dosage increaseds;ignificadnitfferencebsetween male and female PFOS levelwsere notobservedinsera.However,Group 4 (highdose)males had notablyhigherPFOS levelsinlivesramples thanGrou@4 females. Data qualitoybjectivefsortheanalyticpahlase ofthisstudyoutlineidnthe 3M Lab protocoflorFACT TOX-030 (seeAttachmentB) were met withtheexceptionnsotedinthisreport.
LIST OF ATTACHMENTS AttachmentA: ControlMatrixCharacterizatiaonnd Dose ConfirmatioAnnalyses Attachment B: Protocoland DeviationSummary AttachmentC: Extractioannd AnalyticaMlethods AttachmentD: Data Summary Tables AttachmentE: Data Spreadsheets AttachmentF: Example Calculations Attachment G: InteriCmertificaotfeAnalyses Attachment H: Report SignaturePage
3M EnvironmentalLaboratory 3M Environme7,L--alLaboratory
Page 12 Page 12
3m Medical Department Study: T-6295.7 3M MedicaDlepartmenSttudyT:-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
ReportNo. FACT TOX-030 LaboratoryRequest Number-U2279
ATTACHMENT
A
CONTROL MATRIX
CHARACTERIZATION
AND DOSE CONFIRMATION ANALYSES
TableA-1.Characterizatioonfthe ControlMatricesUsed forLiverand Sera AnalysesInStudy FACT TOX-030
CONTROL MATRD( FZABBrrSERum FZABBrrSERUM MONKEY SERUM MONKEY SERUM MONKEY SERUM
Sourr,e ExpiratioDnate StorageConditions Chemical Lot Physical Descdpflon
Sigma Chemir-als 01/01/2010 Frozen-20'C 118H8418
RabbitSerum
Sigma Chemicals 01/01/2010 Frozen-20'C 47H4641
RabbitSerum
LampireBiological SierraBiomedical
N/R
01/01/2010
Frozen-50*C
Frozen-20*C
111022515
' #LY2NO
Monkey Serum Monkey Serum
NIR 01/01/2010 Frozen-20'C
N/R
Monkey Serum
CONTROL MATRIX RABBRT LNER
RABBRT LNER
PABi3rTLrvER RABBRT LIVER MONKEY LIVER
Source ExpiratioDnate
StorageConditions Chomir-alLot Physical Description
N/R-not recorded
Coming Hazleton 12/01/1999 Frozen-20'C F00007
RabbitLiver
N/R 12/01/1999 Frozen-20oc
N/R
RabbitLiver
Coming Hazleton 01/01/2010 Frozen-20'C F00005
RabbitLiver
Coming Hazleton 01101/2010 Frozen-20*C F00009
RabbitLiver
SierraBiomedical 01/01/2010 Frozen-50*C N/R
Monkey Liver
3M EnvironmentalL-aboratory 3M Environmental -@aboratory
Page A-1 Page 13
3m Medical Department Study: T-6295.7 3M MedicalDepartment Study:T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
ReportNo. FACT TOX-030 LaboratoryRequest Number-U2279
TableA-2.LactoseDose Verificati(oPnFOS) forStudy6329-223-8/21/99
EXPECTED
CONC.
(ng/mL)
MEASURED
C40NC.
(ng/mL)
%REC.
FOR
ng/mL
EXPECTED
CALC.
CONC. (Pwg)
MEASURED
CALC. CoNr-
(Pwg)
AVERAGE
Sm DEVLAT$ON
%REC. FOR pglg
1:39DOSE(25000Ppm PFOS)
Top
580
479
Middle 500
650
Boftom 500
422
1:499DosE (2000Ppm PFOS)
Top
411)
305
Middle 404
287
Boftom 400
272
83% 25000 2D647
83%
130% 25000 32537
130%
84% 25000 21108 24764 6736 27%
84%
average/std.deviabon= 99% 27%
74%
2000
1490
74%
71%
2000
1425
71%
68%
2000
1361
1425 64.55%
68%
average/std.deviaton= 71% 3%
ActualMS Concentration-Actuablackgroundconcentrabond,ividedbyexpected,times100 (Spikedtoolow which accountsforthewidedifferenciensrecovery)
TableA-3.Lactose Dose Verifir-ati(oPnFOS-Matrix Spikes)forStudy 6329-223--a/21199
EXPECTED
ACTUAL
%PEC.
CONC.
CONC.
FOR
(ng/mL) I (ng/mL) I ng/mL
CALCULATED CONC.
(pg/g)
EXPECTED CONC.
(Pgtg)
ACTUAL CALC. CONC.
(pg/g)
AVERAGE
sm DEVTATION
%REc.
FOR
pgtg
1:39DOSE (25000 Ppm PFOS) MS
Top
604
507 84-/. 21858
10.8
12.1
Middle 524
485 92-/. 24252
12.5
-82.8
112% -664*
Bottom 524
438 83%
21889
12.5
7.82
22666 1374 6% 63%
1:499DOSE (2000Ppm PFOS) MS
Top
606
475 78%
2320
9.77
8.30
85%
Middle 600
447 75%
2217
9.92
7.93
80%
Boftom 596
440 74%
2202
10.0
8.41
2246 64.53-/.4 84%
Thisvaleuisan outiearndwas notusedinanycalculatons
AVERAGE
87%
3M Environmental Laboratory 3M Environmental Laboratory
Page A-2 Page 14
3m Medical Department Study: T-6295.7 3M MedicaDlepartmenSttudyT.-6295.7
ATTACHMENT B PROTOCOL AND DEVIATION
SUMMARY
Reucrt No. FAC-1 TOX-030 laboratcry Request Number-U2279
ReportNo.FACT TOX-030 LaboratoryRequest Number-U2279
Table B-1.DeviationSummary forFACT TOX-030
DEviATioN
MTBE was usedas an extacfim solvent insteadofethylacetate.
F@pettewas used insteadof Oxford dispenser.
Curves plottedby linearegression weightedltxrathetrhanby linear
regressionas specifiedinte pmtoool.
A second extractedmatrixcurve was not used tobracketsamples.
Recorded extractcn method FACT-M-1.0 ratherthan FACT-M-1. 1. Folkwed extractionmethod ETS43-6.0 ratherthan FACT-M- 1.1. Folla.vedanalyticalmethod ETS-8-7.0 ratherthan FACT-M-2. 1. Follov.,aendaly@l ff)etiwETS-&5.0 ratherthanFACT-". 1. Samples extractedusing 0.5 mL rather than 1.0 mL due toinsufficiesnatmple. Folloveedextractionmethod ETS43-4.0 ratherthan FACT-M-3.1. Matrixspikeswere not spiked with st3ndard (Used as blanks).
Contruing calibratiosntandards were not spiked wth standard due toanalysterror.
Samples extractedus4ng <0.5 mL due to insufficieinntitisaalmple volurm.
DATES OF OCCURRENCE 2/5/99,219m,5/18m, 6/11/99
10/14199
2/13/99,3/5%,3/12199,3119/99, 3/20/99,3/21/99,3/233M/.24199,
3/25%. 4r7t99,4111199,4/12199, 4117/99,5/191%, 5r22/99,&S%. 6/14/99
3/5/99,3/gM. 3/1&99. 3/16/99, 5/19/99,5/22199,10126199.1121/00.
3t24/00,4/27100
6/11/99
10/14199,10/25/99.1/191DO.ar22J()O 7/29199,10120/99,lOr22/99.10/26/-09,
10127199, 1128100.3124/00, 3128/00 3io5l99,N0599
10/25/99
3YO2/99, 3103/99
11/3/99
11/3/99
Z-5199,2/9M. Y2/99,MM, 3/10/99, 3/12/99,3/15/99,3/16199,4/6M, 4/8/99,
812599, 11/3/99,4/21/00
IMPACT ON STUDY
No negativiempacton the StK"tBE
impmved the absolute
recoverieasnd shortenedextm(tontime.
No negadve impact on the study.
No negativiempacton thestxty-l/xweightedcurvesimproved
the precisionand accuracy ofanalysis.
No negativeimpact on thestudy--The accuracy ofcalibration
checks analyzedevery fivetoten samples wasmonitoretdo
ensure contnued accuracy oftheanalysis.The OC providedby the calibrabonchecks issufflcienatnd &* data quality@Mllnot be adversely affected.
No negativeimpact on the study-New method was followed. even though oldmethod was recorded.
No negativeimpacton the sbidy---New validatednied)od providesimprovements in precisionand extractiontime.
No negativeimpacton the study--New validatedrnetiod providesimprovements inprecision,accuracy and analysistime.
No negativeimpacton the study--New validatedmethod Providesimprovements inprecision.accuracy and analysistime.
No negativeimpacton the study-Studies indicatethatdata qualityisnotjeopardizedusing 0.5 mL of sera. No negativeimpacton the sbidy-New validatedmethod providesimprovements inprecisionand extra(:bcntime.
Adequate QC was preparedwth thesample set unspiked samp;es pose no negabve impact c)nthe study. Nlid-leveclurve standardswere substituteads QC forthe nonspiked calibraboncheck standards;the unspiked calibration standardspose no negativeimpact to the sbudy.
Studies indicatethatdata accuracy and precisionmay be affectedwhen serasamples lessthan0.5 mL were extracted. Data reportedfrom extractioonfsamples lew than 0.5 mL is noted inthedata tables.
3M Environmental Laboratory 3M Er.-v4-ronme--italLabora!:ory
Page B-1 Page 15
3m Medical
Department Study:
3,1*E1nvironmentalTechnology and Services
T-6295.7
Report No. FACT TOX-030
PO Box 33331
laboratory
St.Paul,%IN 55133-3331
6127786442
Request Number-U2279 Protocol #FACT-TOX-030
Study Title 26-Week Capsule Toxicity Study with PerfluorooctaneSulfonicAcid Potassium Salt(T-6295)in
Cynomolgus Monkeys
PROTOCOL
Author
Lisa Clemen
Date:
January 25, 1999
Performing Laboratory
3M Environmental Technology & Safety Services 3M Environmental Laboratory 935 Bush Avenue St.Paul,MN 55106
LaboratoryProjectIdentification
FACT-TOX-030
3M EnvironmentaLlaboratory
3M Environmental
Laboratory
Page1of9 Page 16
3m Medical Department Study: T-6295.7
ReDort No. FACT TOX-030 laboratory Request Number-U2279
Protoco#lFACT-TOX-030
StudyIdentification
26-Week CapsuleToxicityStudywith PerfluorooctanSeulfoniAccid PotassiumSalt(T-6295)in
Cynomoigus Monkeys
TestMaterial
Perfluoroocstualnfeonaiccidpotassisuamlt (T-6295)
Sponsor
3M ToxicologSyervice-sMedicalDepartment 3M Center,Building220-2E-02 St.Paul,MN 55144-1000
Sponsor Representative
Andrew Seacat,Ph.D. 3M ToxicologyServices Telephone:612-575-3161 Facsimile:612-733-1773
Study Director
KristenHansen,Ph.D. 3M EnvironmentalTechnologyand Safety Services Building2-3E-09 651-778-6018
Study Location(s) In vivo TestingFacility
AnalyticalTestingLaboratory
Covance LaboratoriesI,nc. 3301 Kinsman Boulevard Madison,Wisconsin 53704
3M EnvironmentalLaboratory Buildinc2,-3E-09 935 Busah Avenue St.Paul,MN 55106
Proposed Study Timetable Study InitiatiDoante Study Completion Date
January25,1999 January25,2000
3M EnvironmentaLlaboratory 3M Environmental Laboratory
Page 2 of9 Pacie 17
3m Medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
Protoco#lFACT-TOX-030
1. STUD Y
Twenty-sixweek capsuletoxicitsytudywithpotassiumperfluorooctasnuelfoniaccid(T-6295)in cynomolgus monkeys.
2. PuRposE
This analyticalstudy isdesigned to determinelevelsof potassiumperfluorooctanesulfonate (PFOS) in theliverand serum of cynomoigus monkeys. Additionaltissuesor fluidsmay be analyzed. The in-lifpeortionof thisstudywas conducted atCovance Laboratoriess,tudy #6329223.
3. REGuLAToRyCompLiANcE
This study willbe conducted in accordance with the United StatesEnvironmental Protection Agency Good Laboratory PracticesStandards,40 CFR 792, with the exceptionthatanalysisof the testmaterialmixture forconcentrations,olubilityh,omogeneity,and stabilitwyillnot be conducted, and isthe responsibilitoyf the Sponsor.
4. QUALITY ASSURANCE
The 3M Environmental LaboratoryQualityAssurance Unit willreview the protocoland audit study conduct,data, and finalreportto determinecompliance with Good LaboratoryPractice Standards and with 3M Environmental LaboratoryStandard Operating Procedures.
5. TESTMATERIAL 5.1 Refer to Covance Laboratoryprotocolforstudy#6329-223.
6. COIVTROL MATRICES
6.1 Identification Monkey liverand serum and/orrabbitliverand serum, traceability numbers willbe recorded in the raw data and includedin the finalreport
6.2 Source Covance Research and/orSigma Chemical 6.3 Physical Description Monkey liverand serum and/orrabbitliverand serum
6.4 Purify and Stability Not applicable
6.5 Storage Conditions Frozen at -20 'C 10 OC or-55 OC 10 OC
6.6 Reserve Matrix A portionof the controlmatrix willbe retainedinthe archivesfor as long as the qualityof the preparationaffordsevaluation,but not longerthan ten years followingtheeffectivdeateof thefinaltestrule(ifapplicable).
6.7 Disposition Matriceswillbe retainedper GLP regulation.Certainmatrices(feces, urine,and blood)may be disposedafterQAU verification.
3M EnvironmentalLaboratory 3M Env@-ronmental Laboratory
Page 3 of9 Page 18
3m Medical Department St---udy:T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
Protoco#lFACT-TOX-030
6.8 SafetyPrecautionsRefetroMSDS forchemicaulssedW.earappropriate laboratoryattirea,nd followadequateprecautionfsorhandlingbiologicamlaterialsand
preparing samples foranalysis.
7. REFERENC-E MATERIAL
7.1 IdentificatioPnotassiupmerfluorooctanfeosnautle(PFOS),lot#s 171,215,or217 (equivalenltots)
7.2 Source 3M SpecialtCyhemicals
7.3 Physical Description Whitepowder
7.4 Purityand StabilityResponsibiliotfytheSponsor
7.5 Storage Conditions Room temperature
7.6 Reserve Material A reservseamplefromeachbatchofPFOS usedinthisstudywill be retainedas longasthequalityofthepreparatioanffordsevaluationb,utnotlonger thantenyearsfollowingtheeffectivdeateof thefinatlestrule(ifapplicable).
7.7 Disposition Unused referencmeateriawlillbe retainefdoruseby the3M EnvironmentalLaboratoryand willbe discardedwhen thequalitoyf preparationno longeraffordsevaluation.
7.8 Safety Precautions RefertoMSDS forchemicalsused.Wear appropriate
laboratoryattirea,nd followadequate precautionsforhandling biologicalmaterialsand
preparingsamples foranalysis.
S. TEST SYSTEM
Cynomolgus monkeys were used as the testsystem, and were maintained and dosed as described
inCovance protocol#6329-223. Group I controlanimalsdidnotreceivethetestsubstance. Groups 2,3,and 4 receivedthetestsubstancedailyfor26 weeks,atconcentrationosf0.02,0.5, and 2.0mgfkg/day,respectivelyR.efertoCovance protocol#6329-223 fortabularpresentation of data.Two animalseach from Groups 1,3,and 4 were designatedasrecoveryanimalsand were allowedatleasta 13 week, which may be extended,recoveryperiodaftercessationof treatment.
9. SPECIMEN AND SAMPLE RECEIPT
The 3M EnvironmentalLaboratorywillreceivehomogeneitysamplesfordoseanalysisand specimensof thefollowingbody tissueasnd fluidfsrom theindicatepdointsinthestudy.All specimenswillbe packedon dry iceforshipping.
3M EnvironmentaLlaboratory 3M Environmental Laboratory
Page 4 of9 Page 19
3m Medi-cal Depar-"men'- Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Numher-U2279
Protoco#lFACT-Tox-030
Body tissue/fluid
Collected
Expected# of specimens
Serum - allanimals Urine and feces- recoveryanimals Liver- allanimals
7 days priorto treatment 7 days posttreatment everytwo weeks duringtreatment and recovery Day zero of recovery 6,30,and 90 (witha potentia1l80) daysof overy Afterterminatioonfthestudy
616 from main study 24 additionaflrom recovery 24 urine 24 feces
Totalnumber oftestanimals:32 Totalnumber ofcontrolanimals:12
Specimens sentto3M EnvironmentalLaboratoriewsillbe receivedand trackedaccordingto applicableStandard OperatingProcedures.
10.PREPARATORY METHODS
10.1 FACT-M-1.0, ExtractionofPotassiumPerfluorooctanesulfonaotreOther Anionic FluorochemicalSurfactanftrom LiverforAnalysisUsing HPLC-Electrospray/M ass Spectrometry
10.2 FACT-M-3. 1,Extractionof Potassium Perfluorooctanesulfonaotre Other FluorochemicalCompounds from Serum or Other FluidforAnalysisUsing HPLCElectrospray/MassSpectrometry
10.3 Ifpreparatorymethods otherthan thoselistedabove areused,an amendment to this protocolwillbe written.Any deviationsfrom thesemethods willbe documented and includedwiththestudydata.
11.ANAL Y77CAL METHODS
11.1 FACT-M-2.0, AnalysisofFluorochemicalsinLiverExtractsUsing HPLCElectrospray/MassSpectrometry
11.2 FACT-M-4. 1,Analysisof Potassium Perfluorcoctanesulfonaotre Other FluorochemicalsinSerum orOther FluidExtractsUsing HPLC-Electrospray/M ass Spectrometry
11.3 Ifanalyticamlethods otherthanthoselistedabove areused,an amendment to this protocolwillbe written.Any deviationfsrom thesemethods willbe documented and includedwiththestudydata.
3M EnvironmentaLlaboratofy 3M Env'-ronmental Laboratory
Page 5 of9 LDage 20
3m Medical Department Szudy: T-629S.7
Report No. FACT TOX-C30 laboratory Request Number-U2279
Protoco#lFACT-TOX-030
12.DATA QUALITY OBJEC77VES
The number of spikes/duplicatuesse,of surrogatesa,nd informationon otherdataquality indicatorsare included in the analyticalmethods. In addition,the followingcriteriawillbe met:
12.1 Linearityr2 >-0.98
12.2 Limits of detection/ quantitation
12.2.1
Method Detection Limit (N4]DL) for PFOS
a)
Serum: 12 ppb
b) Liver: 15 ppb
12.2.2 PracticalQuantitationLimit (PQL) - Equal tothe lowest standardin the calibrationcurve
12.3 Duplicate acceptable precision < 30% for the method
12.4 Spike acceptable recoveries 70% - 130%
12.5
Use of confirmatory methods Indeterminatesamples willbe re-analyzedusing a confirmatory method. Ifa confirmatory method isused,an amendment to this protocol willbe written.
12.6
Demonstration of specificity Chromatographic retentiontime,mass spectral daughter ion characterization.
13. SuB-CoNTRAcTED
ANALYSIS
13.1
All analyses as detailedin thisprotocol will be performed at 3M Environmental Laboratories,Building 2-3E-09, 935 Bush Avenue, St.Paul,MN 55106.
13.2
An amendment to thisprotocolwill be writtenifanalysesare performed at laboratoriesother tha' n the 3M Environmental Laboratory.
14. STATISTICAL ANALYSIS
Averages and standard deviationswill be calculated.The statisticamlethods thatwill be used are described below:
14.1 14.2
Data transformations and analysis Data willbe reportedas the concentration (weictprht/weightor weight/vol)of PFOS or metaboliteper tissueor fluid.
Statistical analysis
Statistics used may include regression analysis of
concentrations over time, and standard deviations calculatedfor the concentrations
within each dose group. If necessary,simple statisticatlests,such as Student's t test,
may be applied to evaluate statisticadlifference.
3M EnvironmentalLaboratory
3M Environmental
Laboratory
Page 6 of 9 Page 21
3m Medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
Protoco#lFACT-TOX-03o
15.REPORT
A reportoftheresultosfthestudywillbepreparedby 3M EnvironmentaLlaboratoryT.he report willinclude,but not be limitedto,thefollowing,when applicable:
15.1 Name and addressof thefacilitpyerformingthestudy
15.2 Dates upon which the studywas initiateadnd completed
15.3 15.4
A statementof compliance by theStudy Directoraddressingany exceptionsto Good Laboratory PracticeStandards
Objectivesand procedures as statedin the approved protocol,includin-any changes in theoriginalprotocol
15.5
The testsubstanceidentificatiboyn name, chemical abstractsnumber or code number, strength,purity,and compositionor otherappropriatecharacteristicisf,provided by the Sponsor
15.6 Stabilityand the solubilityof the testsubstancesunder the conditionsof administrationi,fprovided by the Sponsor
15.7 A descriptionof the methods used toconduct the test(s)
15.8 A descriptionof the testsystem
15.9 A descriptionof any circumstancesthatmay have affectedthequalityor the integrity of the data
15.10 The name of the Study Directorand the names of otherscientistsp,rofessionalsa,nd supervisorypersonnel involved in the study
15.11 A descriptionof the transformationsc,alculationso,r operationsperformed on the data,a summary and analysisof the analyticaclhemistry data,and a statement of the conclusionsdrawn from the analyses
15.12 Statisticamlethods used to evaluatethedata,ifapplicable
15.13 The signed and dated reportsof each of the individualscientistosr otherprofessionals involved inthestudy,ifapplicable
15.14 The locationwhere raw dataand thefinalreportareto be stored
15.15 A statementpreparedby the QualityAssurance Unit listintghedatesthatstudy inspectionsand auditswere made, and the datesof any findingsreportedto the Study Directorand Management
Ifitisnecessaryto make correctionsor additionsto a finadreportafterithas been accepted,the changes willbe made inthe form of an amendment issuedby the Study Director.The amendment willclearlyidentifythe partof thefinalreportthatisbeing amended, the reasons for the amendment, and willbe signed by the Study Director.
3M EnvironmentalLaboratory
3M Environmenzal
Laboratory
Page 7 of9 Page 22
3m Medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
Protoco#lFACT-TOX-030
16.LocATION OF RAwDArA, RECORDS, AND FiNALREponT Originadlata,orcopiesthereofw,illbeavailablaet3M EnvironmentaLlaboratortyofacilitate auditsof the study during itsprogressand beforeacceptanceof the finalreport.When the final reportiscompleted, alloriginalpaperdata,includingthoseitems listedbelow, willbe retainedin the archivesof 3M Environmental Laboratoryforatleasta periodof time as specifiedby regulation,and as establishedby 3M Environmental LaboratoryStandard Operating Procedures.
16.1 The following raw data and recordswillbe retainedinthe studyfolderin the study/projectarchivesaccordingto3M Environmental LaboratoryStandard Operatinc, Procedures: 16.1.1 Approved protocoland amendments 16.1.2 Study correspondence 16.1.3 Shipping records 16.1.4 Raw data 16.1.5 Approved finalreport(originalsigned copy) 16.1.6 Electroniccopies of data
16.2 The following supporting recordswillbe retainedseparatelyfrom the study folderin the archivesaccording to 3M Environmental LaboratoryStandard Operating Procedures: 16.2.1 Trainin- records 16.2.2 Calibrationrecords 16.2.3 Instrument maintenance logs 16.2.4 Standard Operating Procedures,Equipment Procedures,and Methods
17.SPEctmEN RETENTION
Specimens willbe maintained in thelaboratoryspecimen archivesfora periodof time as specifiedby regulationor as long as thequalityof the preparationaffordsevaluation,but not longerthan ten yearsfollowingthe effectivdeateof the finaltestrule(ifapplicable)a,nd as establishedby 3M Environmental LaboratoryStandard Operating Procedures.
18. PROTOCOL AMENDMEIVTS AND DEVIATIONS
Planned changes to theprotocolwillbe inthe form of writtenamendments signed by the Stud'Y Directorand the Sponsor's RepresentativeA.mendments willbe consideredas partof the protocoland willbe attachedto the finalprotocol.All changes to the protocolwillbe indicatedin the finalreport.Any otherchanges willbe in the form of writtendeviationss,igned by the Study Directorand filedwith the raw data.
3M EnvironmentalLaboratory 3M E-.ivironmer@--al Laboratory
Page 8 of9 Page 23
3m Medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
Protoco#lFACT-TOX-030
19.ATTAcHmENTs 19.1 AttachmentA
Preparatorayndanalyticmaelthods
20.SIGNATuREs
z@z@
Andrew Seacat,Ph.D., Sponsor Representative
@7,
Date
KristenHansen, Ph.D.,3M EnvironmentalLaboratoryStudy Director Date
3M EnvironmentalLaboratory
3M Envi-ronmental
Laboratory
Page 9 of9 Page 24
3m Medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
GLP Study ProtocoAlmendment
StudyNumber: FAC-T-TOY,-D3D Lvcnu- (p@aq-2@l
StudyTitle@:L L@@u-k
Toxici@S6@@
?FOS i,,C@,'%Dr^clts
StudyDirector:krijAi2nia Amendment Date: 03)oq)qq
Amendment Number:
This amendment modifiesthe followingportionof theprotocol:
10
Mpl@.As anA
iiA.I@@-ci@u@@.As
F,@CT-Yn-3-t aiJ FACT-m-q.) rAs 4]u, s<fjitfnex-@aAoA
-ihe. Yrtl@ods ha,,- 1,>ttr, tApdaQ @D Ers- 8-@.o
arLc4
C4r\@-ETS- 3-5.b.
@erurn tx4rc-@'onT
upjalf-i4r-e@@oAs w-,ii@, LA@e3 (4nA CAnal@ses,
@hp- r-p-rna,ri,-Vl
Approved by: Stuhy Director
Date
3M En-vironmental Laborato--y
Page 25
3m Medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
StudyTitle
26-Week CapsuleToxicitSytudywithPerfluorooctaSnuelfonicAcid Potassium Salt(PFOS, T-6295) inCynomolgus Monkeys
PROTOCOL AMENDMENT NO. 2
Amendment Date:
April29, 1999
PerformingLaboratory
3M EnvirorunentalTechnology & SafetyServices 3M EnviroromentalLaboratory 935 Bush Avenue St.Paul,MN 55106
Laboratory Project ldentirication ET&SS FACT-TOX-030 LIRN U2279
3M EnvironmentaLlaboratory
3M Environmental
Laboratory
Page 26
3m Medical Department Study: T-629S.7
Report No. FACT TOX-030
laboratory Request Number-U2279
PrOtOcOFlACT-TOX-030 Amendment 2
This amendment modifiesthe followingpartion(so)f the protocol:
1. PROTOCOL READS: Inamendment1,sectio1n0PreparatoMreythodsand SectionII
AnalyticalMethods were updatedto ETS-8-4.0 and ETS-8-5.0 as therevisedserum
extractionand analyticamlethods.
ll.siql
AMEND TO READ: These methods were revisedon 41XI99 to ETS-8-4.1 and ETS-8-5.1 which willbe used forallfutureanalyses.
REASON., The methods were revisedforclarificatiaonnd toincludelinearegression1,/x weightingforinitiaclurves.
Amendment Approval
Andrew SeacatPh.D.S,ponsorRepresentative
7130 Date
K.risJ.Hansen Pfi.D.S,tudy Director
3M EnvironmentalLaboratory
3M Environmental
Laboratory
Date Page 27
3m Medical Department Study: T-629S.7
Report No. FACT TOX--130 laboratory Request Number-U2279
StudyTitle
26-Week CapsuleToxicitSytudywithPerfluorooctaSnuelfoniAccid Potassium Salt(PFOS, T-6295) in Cynomolgus Monkeys
PROTOCOL AMENDMENT NO. 3
Amendment Date:
June 03, 1999
PerformingLaboratory 3M EnvirorunentTaelchnolog&y SafetyServices
3M EnviromnentalLaboratory 935 Bush Avenue St.Paul,MN 55106
Laboratory Project ldentirication ET&SS FACT-TOX-030 LIRN U2279
3M EnvironmentaLlaboratory
3M Environmental
Laboratory
Page 28
3m Medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
ProtocolFACT-TOX-030 Amendment 3
Thisamendment modifietshefollowinpgortion(osf)theprotocol:
1. PROTOCOL. READS: Section10PreparatorMyethodsand SectionIIAnalyticaMlethods list FACT-M-1.0 and FACT-M-2.0 as the liverextractionand analyticamlethods.
AMEND TO READ: These methodswere revisedon 06/03/99 toFACT-M- 1.1 and FACT-M-
2.1 which willbe used forallfutureanalyses.
REASON: The methods were revisedforclarificatiaond to expand on the listof target aiialytes.
Amendment Approval
J-4@@
2:@ol@t
Andrew Seacat Ph.D., Sponsor Representative
-713D /Ilq
Date
411",,
KrisJ.Ha@nsenPh.D.,StudyDire--tor
3M Environmental Laboratory
3M Environmental
Laboratory
Date
Page 29
3m Medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Recruest Number-U2279
StudyTitle 26-WeekCapsulTeoxiciSttyudywithPerfluorooctane SulfonicAcid PotassiumSalt(T-6295)inCynomolgus Monkeys
PROTOCOL AMENDMENT NO. 4
Amendment Date: April25,2000
Performing Laboratory
3M Environmental Technology & Safety Services 3M Environmental laboratory
935 Bush Avenue St.Paul,MN 55106
Laboratory Project Identification FACR Tox-030
ET&SS LRN-U2279
3M EnvironmentaLlaboratory 3M Environmertal Laboratory
Page 30
3m Medical DepartTrent Study: T-6295.7
Report No. FACT TOX-030 laboratory Request NuTnber-U2279
ProtocolLRN-U2279
Amendment Number 4
This amendment modifies the followingportion(s)of the protocol:
1. PROTOCOL READS: The sponsor forthe presentstudywas identifieads Andrew Seacat, Ph.D. AMEND TO READ: The roleof sponsor forthe presentstudywas reassignedto John L. Butenhoff, Ph.D. as of the date of signatureapproval ofthisprotocolamendment. REASON: To ensure thatthe study directordoes not also carrythe dutiesof study sponsor, the sponsor rolewas reassigned. Inthismanner, personnel responsibilitiaensd workload are more evenly balanced.
2. PROTOCOL READS: On page 2 of the protocol,KrisHansen isidentifieads the study directorforthe analyticalphase of the study.Peter Thomford isalso identifieads a study director, but forthe in-lifpehase of the study (see Covance LaboratoriesProtocol6329-223).
AMEND TO READ: On page 2 of the protocol,Andrew Seacat willbe identifieads the study director, KrisHansen willperform the dutiesof the principalanalyticalinvestigatora,nd Peter Thomford willbe identifieidnthe finalreportas the principalin-lifienvestigatoras of the date of signatureapproval of thisprotocolamendment.
REASON: The originalstudy design identifietdwo study directors;one forthe in-lifpehase of the study and one forthe analyticalphase ofthe study.The roleof study director has been reassigned inan effortto ensure compliance with Good Laboratory PracticeStandards thatoutlinestudy personnel requirements.
3. PROTOCOL READS: 10. Preparatory Methods: 10.1 FACT-M-1.1, "Extractionof Potassium Perfluorooctanesulfonateor Other
Fluorochemical Compounds from LiverforAnalysis Using HPLCElectrospray/Mass Spectrometry" AMEND TO READ: 10. Preparatory Methods:
10.1 REASON:
ETS-8-6.0, "Extractionof Potassium Perfluorooctanesulfonateor Other Fluorochemical Compounds from LiverforAnalysisUsing HPLCElectrospray/Mass Spectrometry"
The method was revisedto includeextractionsof other tissuetypes and the use of
methyl-tert-butyelther (MTBE) instead ofethylacetate inthe extractionprocess.
4. PROTOCOL READS: 11. Analytical Methods:
3M EnvironmentaLlaboratory 3M Env4-rcnmental Laboratory
Page 31
3m Medical Departmen-@, Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
ProtocolLRN-U227,9 Amendment Number 4
11.1 FACT-M-2. 1,"Analysisof FluorochemicalsinLiverExtractsUsing H PLCElectrospray/Mass Spectrometry'
AMEND TO READ: 11. Analytical Methods:
11.1 ETS-8-7.0, "Analysisof Potassium Perfluorooctanesulfonateor Other Fluorochemical Compounds inLiverExtractsUsing HPLCElectrospray/Mass Spectrometr/'
REASON: The method was revisedto includecurves plottedby linearregressionweighted 1/x and a reduced cycle time from 13.5 minutes to 9.0 minutes.
5. PROTOCOL READS: 8. Test System Refer to the Covance protocol#6329-223 fortabularpresentationof data.Two animals each from Groups 1,3,and 4 were designated as recovery animals and were allowed atleasta 13 week, which may be extended, recovery period after cessation oftreatment. AMEND TO READ: 8. Test System A tabular presentationof the testsystem data willbe included inthe finalreport forthisproject(FACT Tox-030). Four animals each (two/gender)from Groups 1, 3, and 4 were designated as recovery animals and were observed fora recovery period aftercessation of treatment untilstudy cut-offon March 7, 2000 (Week 80).The observation and analysisofthe recovery group IIIanimals beyond the cut-offdate of thisstudy willbe reported ina new long-term_recovery study. REASON: Additionalanimals were assigned to the recovery group followingapproval of the protocolfor FACT Tox-030. A new study willreportthe long-term recovery of the remaining animals from recovery group III(mid-dose group).
6. PROTOCOL READS: 9. Specimen and Sample Receipt: (Sample Receipt Table] Expected # of Specimens: Serum-all animals:616 from main study,24 additionalfrom recovery Urine and feces-recovery animals:24 urine,24 feces Liver-allanimals:44 Collected: Urine and feces-recovery animals: Day 0, 6,30, 90 (potentia1l80) Total number of test animals: 32
3M EnvironmentaLlaboratory 3M Erivironmen--al Laboratory
Page 32
3m Medical Department Study: T-6295.7
Report No. FACT TOX-C30 laboratory Request Nurnber-U2279
ProtocolLRN-U2279 Amendment Number 4
AMEND TO READ: 9. Specimen and Sample Receipt: [Sample Receipt Table]
# of Specimens: Serum-all animals:516 from main study,280 additionalspecimens from recovery Liver-allanimals: 42 (eightspecimens via biopsy from recovery group) Total number of test animals: 32 Total number of animals: 48 (12 animals incontrolgroup) Note: 4 animals were not assigned to a study group. Day 0 serum specimens were collected.Specimens ofbody tissuesand fluidsother than serum and liver specimens willbe collectedand receivedfrom Covance Laboratories(6329-223, Study T-6295.7). REAsoN: Additionalanimals were assigned tothe recoverygroup followingapproval of the protocolfor FACT Tox-030. The recovery period has been extended for the recovery group. Specimen collectionfiguresshown are through the end of the study 3/07/00.
Amendment Approval
John L. Butenhoff,Ph.D.,Sponsor Representative
C@@
) //@;- z@Z,4@
Andrew Seacat,Ph.D., Incoming Study Director
#2 f
KristenJ.Hansen, Ph.D., Outgoing Study Director
Date
7.z@z,@ Date
IJDate
Date L. Bacon, Lal5'oratorMyanager
Date
3M EnvironmentalLaboratory
3M Environmental
T@aboratory
Page 33
3m Medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
StudyTitle 26-WeekCapsulTeoxicitSytudywithPerfluoroocStualnfeoniAcidPotassiuSmalt(T-6295)in
Cynomolgus Monkeys
PROTOCOL AMENDMENT
NO. 5
Amendment Date: August 14, 2000
Performing Laboratory 3'vfEnvirorunentaTlechnology & SafetyServices-
3M EnvironmentalLaboratory 935 Bush Avenue
St.Paul,MN 55106
Laboratory Project Identification ET&SS FACT-TOX-030 Covance #6329-223 LIMS gU2279
3M EnvironmentaLlaboratorl 3M Environmental Laboratory
LDage 34
3m Medical Department Szady: T-6295.7
Report No. FACT TOX-030 labora+@-o@-y Request Nurnber-U2279
Protocol TOX-030 Amendment 5
This amendment modifiesthe followingportion(so)f the protocol:
1. PROTOCOL READS: 2. PURPOSE: This analyticalstudy is designed to determine levelsof potassium perfluoroocianesulfonate(PFOS) in the liverand serum of cynomoli-zusmonkeys. Additional tissuesor fuids may be analyzed.
AMEND To READ: Add thatselectfecessamples willbe analyzed forPFOS atCentre.
REASON: Feces samples were added afterthe originalprotocolwas wn'tten.
2. PROTOCOL
READS: STUDY
Environmental Laboratory
LocATIONS(PAGE
2): Analytical Testing Laboratory:. 3M
AMEND TO READ: 3',IvEtnvironmental Laboratory and Centre Analytical Laboraton*es Inc. (Centre),3048 Research Drive, StateCollege,PA 16801
REASON: Analyses of feces are assigned to Centre, in addition to the analyses of other tissuesat the 3@vlEnvircnmental Laboratory.
3. PROTOCOL. READS: SECTIONS 10. PREPARATORY AND 12. DATA QUALITY Oi3JECTIVES
METHODS, 11. ANALYTICAL METHODS
AMEND TO READ: Add to these sections-the most current version of "Determination of Flucrochemical Residues in Monkey/Rat Feces by LC/.,IvISI.MS,C"entre method number OONI-O?-3-003, with ar. LOQ in feces of 10 ng/g. The method w;lllincorporatean initial homogenization step i-nmediatelyafter adding the extractionsolvent,using a microhomo,zeniz.-r,to allow fcr complete dispersionof the specimen in the solvent.
REASON: To specify -,.hevalidated method to be used for feces analyses along .,,Ithits analyticallimits.NOTE: LC/MS/iMS is an abbreviation for "liquidch-romatograph y/mass spectrometry/mass spec--ometry."
4. PROTOCOL METHODS
READS: SECT70N 10. PREPARATORY
METHODS AND 11. 3M ANALYTICAL-
AMEND TO READ: Cha.-,ceto specify that the most current version of the methods listed should be used.
REASON: To specify that the most appropriate version of the preparatory and analvtlcal rr,ethcdsshould be used during the course of the study.
3M EnvironmentaiLaboratory 3M Env4-ronmenl--al Laboral-o--y
Page 35
3m Medical Department Study: T-6295.7
Report No. FAC--, TOX-C30 laboratory Request Number-U2279
Protocol TOX-030 Amendment 5
5. PROTOCOL READS: The amended protocol(Amendment #4) statesthatK-risJ.Hansen, Ph.D. isthe PrincipalAnalyticalInvestigatorforthe entirestudy.
AMEND TO READ: Add Enaksha Wickremesinhe, Ph.D. as the PrincipalLq-@@,lnvestigatorat 6-r1'. Centre for feces analyses.
REASON: To specify the PAI at Centre for fecesanalysis.
6. PROTOCOL REPORTS
READS: SECTION 16. LOCATION OF RAw DATA, RECORDS
AND FINAL
AMEND TO READ: Add that Centre will forward alloriginalstudy-specificraw data to 3Nf Environmental Laboratories,togetherwith copies of appropriatefacility-specifircaw data applicable to thisstudy. Centre will maintain a copy of the applicablestudy-specificraw data, protocol and analyticalreportin the Centre archives,as well as all originalfacility records.
REASON: Centre.
To specify the archival requirement for the portion of the data developed by
7. PROTOCOL READS: SECTION 17. SPECIMEN RETENTION
AMEND TO READ: Add that after the analyticalreport on feces is signed by the study director,allfeces specimens of thisstudy will be returnedto 3,N4Environmental Laboratory. These specimens may then be discardedby writtendirectionof the study director.Specimens of serum and urine may also be discardedby writtendirectionof the study directorafterthe analyticalreport for the 3M Environmental Laboratory analyses is signed by the study director.
REASON: To specify the handling of allbiologicalfluids,and to definewhen ver1"ficat'ion IisconsiIdered complete.
the quality assurance
-,M Environmental Laboratory
3M Env-'-ronmental
Laboratory
Page 36
3m MEW@o@.Dep@gtiiSerit
SEP,15,20M ll:33qM
WIS49
UG: 31
f
eczw-UL9@g:
17
Report No.
2'5---@;9@ 410 894 91?2aboratory
cafm FTMYTICAL LA
ReWde@i4
EW LA 2-M--Gg -6el4 231 L5W
FACI@3.n, NuF.L@er3:-@YU2279
NO. 338
M2
Amendment Approval
Ptutocol Tox-cao I Amendment 5
2z
JohnI- BUaLbogFbly., SPOMOT'IAMMIUNdve
Andow asam MD., Study Dimtw Widamefthe, Pbl).,Pri=iPAIIn-lilfnOv64Ptw
Date
rl(2 C) Date
3W IMW@mmaM Lspba*c@y
3M Env@-ronmental Laboratory
1 .10
Page 37
3m Medical Department sz:udy: T-6295.7
Report No. FAC'-7TOX-03C laboratory Request Number-U2279
StudyTitle 26-WeekCapsulTeoxiciSttyudywithPerfluoroocStualnfeonAiccidPotassiSuaml(tT-6295i)n
Cynomotgus Monkeys
PROTOCOL AMENDMENT NO. 6
Amendment Date: September 11,2000
Performing Laboratory 3NI EnvironmentalTechnology& SafetyServices
3M EnvirorunentaLlaboratory 935 Bush Avenue St.Paul,MN 55106
Laboratory Project Identification ET&SS FACT TOX 030 Covance #6329-223 LIMS #U2279
3M EnvironmentaLlaboratory 3M E@-ivironme-ntal Laboratory
Page 38
3m Medical Department Study: T-629S.7
Report No. FACT TOX-030 laboratory Request Number-U2279
ProtocoTlOX 030
Amendment 6
Thisamendment modifiesthefollowinpgortion(so)ftheprotocol:
PROTOCOL READS: 8. TEST SYSTEM: Groups 2,3,and 4 receivedthetestsubstancedailyfor26 weeks,at concentrations of 0.02, 0.5,and 2.0 mg/kg/day, respectively.
AMEND TO READ: Groups 2, 3, and 4 received the testsubstance daily for26 weeks, at concentrationsof 0.03, 0.15, and 0.75 mg/kg/day.
REASON: Test substance doses were changed afterprotocol was written.The Covance protocol reflects the actual doses of testsubstance thatwere given.
PROTOCOL READS: The amended protocol (Amendment Number 4, section2.)states:On page 2 of the protocol, Andrew Seacat will be identifiedas the study director,Kris Hansen willperform the dutiesof the principalanalyticalinvestigatora,nd PeterThomford willbe identifiedin the Finalreport as the pr-incipatin-lifeinvestigatoras of the date of signatureapproval of thisprotocol amendment. AMEND TO READ: Peter Thomford will remain as the Covance Study Director for the purpose of issuing the Covance finalreport for the in-lifephase of the study. REASON: Study directorshipwas not relinquishedby Covance for the in-lifephase of the study, since the animal experimental phase was completed before Amendment Number 4 was issued.
Amendment Approval
John L. Butenhoff PH.D., Sponsor Representative
Date
Andrew Seacat, Ph.D., Study Director
Date
3M EnvironmentalLaboratory
3M Environmental
Laboratory
Page 39
3m Meddwa!l-eoeparo5p&-
t S bOyi@B @-:ft2-d9-5471 410 E384 1122
Report No. FACT TOX-030
anoratory Request Numb@U---:U2279P%
Study Title
Pmtowl TOX-030 Amencheiit7
26-weak Capsule ToxicityStudy with PerfluorooetaneSiilfoniAccid Potassium Salt (T-6295) inCynomoigus Monkey3
ProtocolAmendinent No. 7 Amendment Date-.
September 14, 2000
PerformingLaboratory
3M Environmental Technology and Safety Services
3M Fnvironmen.W Laboratory 93 5 Bush Avenuc
St.Paul, MN 55106
LaboratoryProjectIdentification
F-r&S,9YACT-TOX-030
Covance #6329-223 LIMS #U2279
3M Environmental Laboratory son
3m, medi@@dlis@parvnEs4t
stsWrA;qBT2--g-c@._.71 410
Report No. FACT TOX-030
E3841TIRratory Request Numbe@-aTn79POe
Amendinent Approval
ProtocolTOX-030 Amendmeilt 7
John L. Butenhoff,Ph.D.,Spotiso?sRepresentative
Date
AndreL'w'-@e@tPh.D., Study Director
Date
@P4
3M Env-'@ronme@ntal
Laboratory
3m Medical Department Study: T-6295.7 3M Medir-alDepartment Study:T-6295.7
ATTACHMENT EXTRACTION
C AND ANALYTICAL
METHODS
Report No. FACT TOX-030 laboratory Request Number-U2279
Report No. FACT TOX-030 LaboratoryRequest Number-U2279
3M EnvironmentaLlaboratory 3M Environmental Laboratory
Page C-1 Page 43
3m Med@-cal Department Study: T-629S.7
Report No. FACT TOX-030 laboratory Request Number-U2279
3M ENVIRONMENTAL
LABORATORY
METHOD
EXTRACTION
OF POTASSIUM PERFLUOROOCTANESULFONATE
FLUOROCHE,NIICAL
COMPOUNDS
FROM LIVER FOR AINALYSIS
ELF-CTROSPRAYFMASS
SPECTROMETRY
OR OTHER
USING HPLC-
Metfiod Number: ETS-8-6.0
Author: Lisa Clemen, Rober-tWynne Approved By:
Adoption Date: 0 Revision Date:
Laboratory Nianager
&. /-I./-@.Group Leader
a,'A @, LL Technical Reviewer
Date
--?/-/-@ Datc
c ill@ lil Date
1.0 SCOPE AND APPLICATION 1.1 Scope: This method is for the extraction of potassium perfluorooctanesulfonate (PFOS) or
other fluorochemical compounds from liver.
1.2 Applicable Compounds: Fluorochemical surfactantsor other fluorinatedcompounds.
1.3 Nlatrices: Rabbit, rat,bovine, and monkey liversor other tissuesas designated in the validationreport.
Word 6.0,195 3M Environmencal Laboratory
ETS-8-6.0 Exmction ofPFOS from Liver
Page I of 14 Page 44
3m Med@-cal Department Study: T-6295.7
-.Report No. FAC- TOX-030 laboratory Request Number-U2279
2.0 SUNINLARY OF METHOD
2.1 This method describesthe procedure for extractingpotassium perfluorooctanesulfonate (PFOS) or other fluorochemicalsurfactantsfrom liver,or othertissues,using an ion painng reagent and methyl-tert-butylether(MtBE). In thismethod, seven fluorochemicalscan be extracted:PFOS, PFOSA, PFOSAA, ETFOSE-OH, PFOSEA, M556, and surrogate standard.An ion pain'ng reagent isadded to the sample and the analyte ion pair is partitionedintoMTBE. The MTBE extractis transferredto a centrifugetube and put onto a nitrogenevaporator untildry. Each extractisreconstitutedin 1.0 mL methanol then Filteredthrough a 3 cc plasticsyringeattachedto a 0.2 um nylon filterintoglass autovials.
2.2 These sample extractsare analyzed following method ETS-8-7.0 or other appropriate methods.
3.0 DEFINITIONS 3.1 PFOS: perfluorooctanesulfonate(anion of potassium salt)C,F,,SO, 3.2 PFOSA: perfluorooctane sulfonylamide C,F,,So2NHI3.3 PFOSAA: perfluorooctane sulfonylamido (ethyl)acetateC,F1,SO,N(CH,CH,)CH,CO, 3.4 ETFOSE-OH: 2(N-ethylperfluorooctanesulfonamido)-ethylalcohol
C,F,,SO,N(CH,CH,)CH,CH,OH 3.5 PFOSEA: perfluorooctanesulfonylethylamide C,F,,SO,N(CH,CH3)H 3.6 M556: C,F,,SO,N(H)(CH,COOH) 3.7 Surrogate standard: IH- IH-'@H'-2H perfluorcoctane sulfonic acid
4.0 WARNINGS AND CAUTIONS 4.1 Health and Safety Warnings:
4.1.1 Use universalprecautions,especiallylaboratorycoats,gocp-ies,and gloves when handling animal tissue,which may contain pathogens.
5.0 INTERFERENCFS 5.1 There are no interferences',-,nowant thistime.
6.0 E()UIPMENT 6.1 The following equipment isused while performing thismethod. Equivalentequipment is
acceptable.
6.1.1 Ultra-TurraxT25 Grinder forgrinding liversamples 6.1.2 Vortex mixer,VWR, Vortex Genie 2 6.1.3 Centrifuge,Mistral 1000 or IEC 6.1.4 Sliaker,Eberbach or VWR
ETS-8-6.0 Extractionof PFOS from l.i%-er
Page 2 of 14
3M Environmental Laboratory
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3m Medical Departmen-- Szudy: T-6295.7
Report No. FAC- TOX-030 laboratory Request Number-U2279
6.1.5 Nitrogen Evaporator,Organomation 6.1.6 Balance (sensitivittyo 0.100 g)
7.0 SUPPLIES AND MATERIALS
7.1 Gloves 7.2 Dissecting scalpels
7.3 Eppendorf or disposable pipettes 7.4 Nalgene bottles,capa@oleof holding 250 mL and I L 7.5 Volurnetn'cflasks,glass,type A
7.6 I-CHEM vials,40 mL glass
7.7 Plasticsampule vials,Wheaton, 6 mL (or appropriatesize)
7.8 Centrifuge tubes7,pol.vpropylene, 15 mL
7.9 Labels 7.10 Oxford Dispensor - -'.0 to 10.0 ml
7.11 Syringes, capable of measuring 5 pLL to 50 @iL
7.12 Graduated pipettes 7.13 Syringes, disposable plastic,3 cc
7.14 7.15 7.16
Syringe filtersn,ylon, 0.2 gm, 25 mm Timer Crimp cap autovialsand caps
7.17 Crimpers
Note: Priorto using glassware and bottles,rinse3 times with methanol and 3 times with Milli-
Q I'mwater. Rinse s@,liincliesa minimum of 9 times with methanol, 3 rinses from 3 separate
vials.
8.0 REAGENTS AND STAND.4RDS 8.1 Type I reagent gade water, Milli-QTIlor equivalent;allwater used in thismethod should
be Mi lll_QT.wMater and be provided by a Milli-Q TOC plUSTIISystem
8.2 Sodium hydroxide (N'aOH), J.T Baker or equivalent 8.3 Tetrabutylammonium hydrogen sulfate(TBA),Kodak or equivalent 8.4 Sodium carbonate C-Na@CO,),J.T.Baker or equivalent 8.5 Sodium bicarbonate (,NaHCO,), J.T.Baker or equivalent 8.6 Methyl-tert-butylether,Omnisolv, glassdistilleodr HPLC grade 8.7 Methanol, Omnisolv, glassdistilleodr HPLC grade 8.8 Liver,frozen from supplier 8.9 Dry ice from supplier 8.10 Fluorocbemical standards
8.10.1 PFOS (3N[ SpecialtyChemical Division),molecular wei(,'ht 538
3M Envirormental Laboratory
ETS-8-6.0 ExtractionofPFOS froniLivcr
Pa-c of 1-4 Page 46
3m Medical Department Sz@udy: T-6295.7
Renort No. FAC-@ TOX-030 laboratcry Request Number-U2279
8.11
8.12
8.10.2 PFOSA (3,,lSpecialtyChemical Division),molecular weight = 499
8.10.3 PFOSAA
SpecialtyChemical Division),molecular wclcht = 585
8.10.4 ETFOSE-OH (3M SpecialtyChemical Division),molecular weight = 570
8.10.5 PFOSEA (3M SpecialtyChemical Division),molecular weight = 527
8.10.6 M556 (3M SpecialtyChemical Division),molecular weight = 557
8.10.7 Surrogate standard:4-H, perfluorooctanesulfonicacid (I-H,I-H, 2-H, 2-H C,F,,SO,H) molecular weight = 428
8.10.8 Other fluotochemicals, as appropriate
Reagent preparation
NOTE: When preparing largervolumes than listedin reagent,standard,or sur-rogate preparation, ad@ustaccordingly.
8.11.1 10 N sodium hydroxide (NaOH): Weigh approximately 200 g NAOH. Pour intoa
1000 mL beaker containing500 mL Milli-Q"w'aterm,ix untialllsolidasre dissolved.Storeina I L Nalgene bottle.
8.11.2 1 N sodium hydroxide(NaOH): Dilute10 N NAOH 1:10. Measure 10 mL of
10 N NAOH solutionintoa 100 mL volumetricflaskand dilutetovolume using Milli_QTIwIater. Storeina 125 mL Nalgene bottle.
8.11.3 0.5 M tetrabutylammonium hydrogen sulfate(TBA): Weigh approximately169 g of TBA intoa I L volumetriccontaining500 mL Milll_Q71water.Adjustto pH 10 usingapproximately44 to54 mL of 10 N NaOF1 (While adding the lastML of NAOH, add slowlybecausethepH changes abruptly).Dilutetovolume with Milli-Q" water.Storeina I L Nalgene bottle.
8.11.3.1TBA requiresa check priortoeach use toensurepH = 10. Adjust as needed using 1 N NAOH solution.
8.11.4 0.25 M sodium carbonate/sodiubmicarbonatebuffer(NaCO,/NaHCO,): Welc,,h approximately26.5g ofsodium carbonate(Na,CO,) and 2 1.0g ofsodium bicarbonate(NaHCO,) intoa I L volumetricflaska-nd brinlt,ovolume with Milli-
Q T,%i water.Sloreina I L Nalgene bottle.
Standards preparation
8.12.1 PreparePFOS standardsforthestandardcurve.
8.12.2 Prepareotherfluorochemicalstandards,as appropriate.Nluiticomponent fluorochemicalstandardsareacceptable(forexample,one working standard solutioncontaining1.00ppm PFOS, 1.02ppm PFOSA, 0.987ppm PFOSAA, and 1.10 ppm Et.70SE-OH.)
8.12.3 Weigh approximately100 mg of PFOS intoa 100 mL volumetricflaskand record the actualw--Ight.
8.12.4 Bring tovolume withmethanol fora stockstandardofapproximately1000 ppm (4g/mL).
8.12.5 Dilutethestocksolutionwithmethanol fora working standardI solutionof approximately50 ppm.
3M Env4-ronmental Laboratory
ETS-8-6.0 ExtractionofPFOS from Livci
Page 4 of 14
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3m Medi-cal De@Dartment Study: T-6295.7
Report No. FAC-@ TOX-C30 laboratory Request Number-U2279
8.13
8.12.6 Dilute the s-,ocksolutionwith methanol for a working standard2 solutionof approx. 5.0 ppm.
8.12.7 Dilutethe stock solutionwith methanol fora working standard ')solutionof approx. O..@Oppm.
Surrogate stock standard preparation
8.13.1 Weigh approximately 50-60mg of surrogate standard 1-H,I-H, 2-H, 2-H, C,F,,S0,H intoa 50 ml volumetric flaskand recordthe actualweight.
8.13.2 Bring to volume with methanol for a sur-rogatsetock of approximately 1000-1200 PPM-
8.13.3 Prepare a surrogateworking standard. Transferapproximately 1.0 ml of surrogate stock to a 10 ml volumetn'c flaskand bring to volume with methanol for a work'uig standard of 10-20 ppm. Record the actualvolume transferred.
9.0 SANIPLE HANDLING 9.1 All samples are received frozen and must be kept frozen untilthe extractionisperformed.
10.0 ()UALITY CONTROL 10.1 Matrix blanks and method blanks
10.1.1 An aliquotof 1.0 mL methanol is used as a solventblank.
10.1.2 Extract two 1.0 mL
aliquotsOfMi
lli_QTII water following thisprocedure
and
use
as method blanks.
10.1.3 Extracttwo 1.0 mL aliquotsof liverhomogenate followitigthisprocedure and use as matrix blanks. Refer to 11.1.6.
10.2 Matrix spikes
10.2.1 Prepare and analyze matrix spike and matrix spike duplicatesamples to determine the accuracy of the extraction.
10.2.2 Prepare each spike using a sample chosen by the analyst,usuallya control liver received with each sample set.
10.2.3 Expected concentrationswill fallin the mid-range of the initiaclalibrationcurve. Additional spikes may be includedand may fallin the low-range of the initial calibrationcurve.
10.2.4 Prepare one matrix spike and matrix spike duplicateper 40 samples, with a minimum o C 2 matn*x spikes per batch.
10.3 Continuing calibration verirications
10.3.1 Prepare continuing calibrationverificationsamples to ensure the accuracy of the initiaclalibrationcurve.
10.3.2 Prepare,at a minimum, one continuing calibrationverificationsample per group of 10 samples. For example, ifa sample set= 34, folirverificationasre prepared and extracted.
3M Environmental Laboratory
ETS-8-6.0 Extractioonf PFOS from Livcr
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Re-@@ort No. FAC'I' TOX-030 laboratory Request Numbe---U2279
10.3.3 Prepare each continuing calibrationverificationfrom the same matnx used to prepare the initialcur-ve.
10.3.4 The expected concentrationswill fallwithinthe mid-ranizeofthe initial calibrationcur-ve.Additionalspikesmay be included thatfallin the low-rang-.of the initiaclalibrationcurve. This isnecessary ifthe analvstmust quantitateusinc, only the low end of the calibrationcurve (forexample, 5 ppb - 100 ppb, rather than 5_ppb - 1000 ppb).
11.0 CALIBRATION AND STANDARDIZATION 11.1 Prepare matrix calibration standards
11.1.1 Weigh approximately 40 g of liverintoa 250 mL Nalgene bottlecontaining 200 mLs Mi lll_QT*wlalter.Grind toa homogeneous solution.
11.1.2 If40 g isnot available,use appropriateamounts of liverand water to ensure a 1:5 ratio.
11.1.3 Refer to 13.0 to calculatethe actualdensity of liverhomogenate and the concentration of solidlivertissuedisoersed in 1.0 mL of homogenate solution.
11.1.5 Add I mL of homogenate to a 15 mL centrifugetube.Re-suspend solutionby shaking between aliquotswhile preparing a totalof eighteen I mL aliquotsof homogeneous solutionin 15 mL centrifugetubes.
11.1.6 Two I mL aliquots,or otherappropriatevolume, ser-veas matrix blanks.
11.1.7 Typically use the standard concentrationsand spiking amounts listedin Table 1,at the end of thissection,to spike,in duplicate,two standard curves,for a totalof eighteen samples, two matrix blanks,and two method blanks.
11.1.8 Refer to validationreportsETS-8-6.0 and ETS-8-7.0-V-1 or Attachment B, which liststhe working ranges and the Linear CalibrationRange (LCR) for calibrationcurves.
11.1.9 Use Attachment C as an aid in calculatingthe concentrations of the working standards. Refer to 13.0 to calculateactualconcentrationsof PFOS in calibration standards.
11.2 To each working standard,blank,or continuing verificationa,dd appropriateamount of surrogate working standard forthe concentrationto fallwithin the calibrationcurve range 5 ppb -1000ppb.
3M Environme-tal Laboratory
ETS-8-6.0 Extractionof PFOS from Liver
Page 6 of 14 Page 49
3m Medical Department S+--udy: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
11.3 Extractspiked liverhomogenates following12.14-12.25of thismethod. Us-.these standardsto establisheach initiaclur-veon themass spectrometer.
Table I Approximate Spiking Amounts forCalibration Standards
Working Standard (Approx.Conc.)
0.50 ppm 0.50 ppm 0.50 ppm 0.50 ppm 0.50 ppm 5.0ppm 5.0 ppm 5.0 ppm 50 ppm
@ll
Approx. finalconc.of
PFOS inliver
-
Blank
2
0.005 ppm
4
0.010 ppm
10
0.025 ppm
20
0.050 ppm
40
0.100 ppm
10
0.250 ppm
20
0.500 ppm
30
0.750 ppm
4
1.00ppm
12.0 PROCEDURE
12.1 Obtain frozenliversamples. 12.2 Cut approximatelyI c,of liverusinga dissectinsgcalpel.This partoftheprocedureisbest
performed quickly,not allowingthelivertothaw. 12.3 Weigh the sample directlyintoa taredplastic sampule vial. 12.4 Record theliverweight inthestudynotebook.
12.5 Return unused liverportionsto freezer.
12.6 Add 2.5 mLs ofwater tosampule vial.
12.7 Grind the sample.Put thegrinderprobein thesample and grindforadout2 minutes,or untilthesample ishomogeneous.
1'-1.8 Rinse theprobe intothesample with 2.5mLs waterusinga pipette. 12.9 Take thegrinderapartand cleanitwith methanol aftereach sample.Referto A-iMDT-EP-
22.
12.10 Cap thesample and vortexfor15 seconds.Label thesampule vialwith thestudynumber, weight,liverID, dateand analystinitials.
3M Environmental Laboratory
ETS-8-6.0 Extractionof PFOS from Li@,er
Page 7 of 14
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3m Medical Department Study: T-6295.7
Report No. FA--- TOX-030 laboratory Pecruest Number-U2279
12.11 Pipette 1.0 mL, or other appropr-iatveolume, of homogenate into a 15 mL polypropylene centrifugetube. Label the centrifugetube with the identicalinfortnationas the sampule via].Refer to attached worksheet fordocumenting the remaining steps.
12.12 Pipette two I mL aliquotsof Milli-Qw'atetrocentn'futguebesT.hesweilslervaes
method blanks.
12.13 Spike all samples, including blanks and standards readv for extraction with surrogate standard as described in section 11.2.
12.14 Spike each matirx with the appropriate amount of standard as described in 11. 1, or Table I of thatsection,forthe calibrationcurve standards. Also prepare matn*x spikes and continuin@:,c,alibration standards.
12.15 Vortex mix the standard curve samples, matrix spike samples, and continuing calibration samples for 15 seconds.
12.16 Check to ensure 0.5 M TBA reagent isat pH 10. Ifnot,adjustaccordingly,
12.17 To each sample, add I mL 0.5 M TBA and 2 mL of the 0.25 M sodium carbonate/sodium bicarbonate buffer.
12.18 Using an Oxford Dispenser, add 5 mL methyl-tert-butylether.
12.19 Cap each sample and put on the shaker at a settingof 300 rpm, for20 minutes.
12.20 Centrifuge for 20 to 25 minutes at a settinco,f 3500 rpm, or untillaycrsare wcll separated. 12.21 Label a fresh 15 mL centrifugetube with the same information as in 12.10.
12.22 Remove 4.0 mL of the organic layerto the fresh 15 mL centrifugetube.
12.23 Put each sample on the analyticalnitrogenevaporator untildry,approximately I to 2 hours.
12.24 Add 1.0 mL to each centrifugetube using a graduated pi@)ette.
12.25 Vortex mix for 30 seconds. 12.26 Attach a 0.2 @im nylon mesh filtetro a 3 cc syn'nge and transferthe sample to thissyrinee.
Filterinto a 1.5 mL glassautovialor low-volume autovialwhen necessary.
12.27 Label the autovialwith the study number, animal number and gender, sample timepoint, matrix, finalsolvent,extractiondate,and analyst(s)performing the extraction.
12.28 Cap and storeextractsat room temperature or at approximately 4 'C untilanalysis.
12.29 Complete the extractionworksheet, attached to thisdocument, and tape in study notebook or include in study binder,as appropn'ate.
3M Environmental Laboratory
ETS-8-6.0 ExtractionofPFOS from Liver
Page 8 OF 1,4
Page 51
3m Medical Department Study: T-629S.7
Pe-@ort No. FACT TOX-030 laboratory Pequest Numbe---U2279
13.0 DATA ANALYSIS 13.1 Calculations:
AND CALCULATIONS
13.1.1 Calculate the average density of the liverhomozenate bv recording each mass of ten separate 1.0 mL aliquotsof homogenate.
Average density (mg/mL) = Average mass (mg) of the aliquots
1.0mL aliquot
13.1.2 Calculatethe amount of liver(mg) per 1.0mL homogenate (orconcentrationof dispersed solidtissueper mL of homogenate suspension) using the following equation:
g of Li@er x Averae:edensity*of homogenatelmg/mL) (g of Liver + g of Water)
referto 13.1.1 for details.
13.1.3 Calculateactualconcentrationsof PFOS and other fluorochemicalsin calibration standards using the following equation:
@iL of Standard x Concentration (@ig/mL) = Final Concentration (4g!g or rng!kg)
mg Liver/ I mL homogenate*
of PFOS in Liver
*referto 13.1.2 for details.
14.0 METHOD PERFORNTA*QCE
14.1 The method detectionlimit(MDL) isanalyte and matrix specific.Refer to MDL report for
spec'ificN/IDLandlimiotfquantitation(LOvQa) lu(ersetfoeArttachmeanntdscB).
14.2 The followinqgualictoyntrsoalmpleasrextracwtietdehachbatcohfsampletsoevaluate the qualityof theextractionand analysis.
14.2.1 Method blanksand matrixblanks.
14.2.2 Matrix spikeand matrixspikeduplicatesamplestodeterrninaeccuracyand precisionof theextraction.
14.2.3 Continuingcalibratiovnerificatiosnamples todeterminethecontinuedaccuracy ofthe initiaclalibratiocnurve.
14.3 Refer tosection14 of ETS-8-7.0 formethod performancecriteria.
15.0 POLLUTION PREVENTION AND WASTE MANAGErvIENT
15.1 Sample waste isdisposedinbiohazardcontainersf,lammable solventwaste isdisposedin high BTU containersa,nd used glasspipettewaste isdisposedinbroken glasscontainers locatedin thelaboratory.
3M Environmental
Laboratory-
ETS-8-6.0 Exrractionof PFOS from L'iver
Page 9 of 1-4
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3m Med@-cal Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
16.0 RECORDS
16.1 Complete the extractionworksheetattachedto thismethod, and tapein thestudynotebook or includein the3-rin-s,tudybinder,as appropriate.
17.0 TABLES, DIAGRAms, FLOWCHARTS, AND VALIDATIo,*4 DATA 17.1 Attachment A, F-xtractiownorksheet 17.2 Attachment B, MDLILOQ valuesand summary 17.3 Attachment C, Calibratiosntandardcalculatioannd concentrationworkshect
18.0 REFERENCES 18.1 The validationre-poratssociatedwith thismethod isETS-8-6.0 & 7.0-V-1.
18.2 AMDT-EP-22, "RoutineMaintenanceofUltra-TurraTx-25" 18.3 FACT-M- 1.1,"ExtractionofPFOS orOther AnionicFltiorochemicaSlurfactantfsrom
LiverforAnalysisUsing HPLC -ElectrsoprayfmassSpectrometry"
19.0 AFFECTED DocUNIENTS
19.1 ETS-8-7.0, "Analysisof LiverExtractsforFluorochemicalsusin-IHPLC-Electrospray Mass Spectrometry"
20.0 REVTSIONS
Revision Number.
Reason For Revision
Revision Date
3M Env4@--onmental Laboratory
ETS-8-6.0 Extractionof PFOS from I-i,,-er
Page 10 of 14
Page 53
3m Med@-cal Department S:@-ddy: T-6295.7
Report No. FA-7 TOX-030 laboratory Request @4umber-U2279
Study
Matrix Box Vv'k/Day
Date Spiked/Analyst ccv
Surrogatz Std approx. ppm actual ppm
MSD
FC Nlix Std
approx. (D.5ppm
actual
ppiii 1
FC,"vllxStd approx. 5 ppm actual PPM
FC Nlix Std approx. 50 ppm actual PPM
Comments
Blank
LiverHomo_genate: Sd
LiverExtractionMethod
Liveramount
Spike surrogateand Standardmix, Vortex 15 sec-
PipetteImL of LiverSolution
PipetleImL of tO.5,M TBA, pH 10. pH
Std.
Pipett2e mL of0.25Na-)C03/0.25M NaHC03 3uffer
Std.
Dispense5m[ of Methyl-t-ButyElther Shake 20 min. Ccntrifuge20-25 min. Remove a 4 mL aliquotof organiclaver Puton NitrogenEvaporatortodrvness Add 1.0mL of Methanol
TN-AShaker Speed CcntrifugeSpeed
EvaporatorTemperature TN-A-
5artex 30 sec.
I Filteursinea 3cc B-D svrin@2wcith a0.2um SRI f-iftienrtoautosamplevial Cont. Cal.Verificationsused thesame matT--Iaxs forthestandardcut-ve.
AtiactimentB: MDLi'LOQ Values 3M Env@-ronmen-@al Laboratory
ETS-8-6.0 Extractionof PFOS from Li%-er
Date & In tials
Page II of 16 Page S4
3m Medical Department Szady: T-629S.7
Report No. FAC-@ TOX-C30 laboratory Request Number-U2279
MDLILOQ Compound
PFOS PFOSA PFOSAA ETFOSE-OH M55 PFOSEA
values for rabbit liver
NIDL
LOQ Linear CalibrationRange (LCR)
(p pb)
(ppb) Approximate concentrationtsobe used forpreparingthe Standard Calibration Curve
8.45
26.9 30 ppb - 1200 ppb
3.50
11.1 12 ppb - 1200 ppb
24.6
78.3 30 ppb - 1200 ppb
108
345 60 ppb - 900 ppb*
82.3
262 60 ppb - 1200 ppb
33.9
108 30 ppb- 1200 ppb
MDL/LOQ values in rat,bovine, and monkey liverwere not statisticalldyetermined. Two curves in each of these-matriceswere extractedand analyzed with the rabbitlivercurves to determine equivalence. Responses in the rat,bovine, and monkey livercurves were equivalent to the rabbitresponses, therefore,their'i\,IDaLnd LOQ will be assumed to be equivalentto those values as determined for the rabbitliver.
Refer to LOQ Summary and MDL studyin ETS-8-6.0 & 7.0-V-1forfurtherinformazion
* ETFOSE-OH estimatesonly forMDL and LOQ. Did not meet criterifaorvalidation.
Compound: PFO S
Liver matrix
I Prepared
Range of LCR from
I range of
average (pave curve
standards
curve
(ppb)(ng.,-L)(ppb)(ng/mL) pb
Range of LCR from Ranizrof
I w std
low std
'@iighstd
curve
curve
(ppb)(ngiml) (pr)(bn)g/mL) (ppbC)U(rn'gv/eLm)
Rabbit
6 19 1137 -
12 - 1200
12- 1200
6-300
12-300
60- 1200
LCR from high std
(ppcurve b) (ng/mL)
60- 1200
Compound: PFOSA
Liver matrix
Prepared
Range of LCR from Range of I.CR from Range of LCR from
range of
average
ave curve
low std
low std
high std
high std
standards
curve
curve
curve
carve
curve
(pob)(ng/-L) (ppb)(ngi'rnL()ppb)(ng/mL)(ppb)(ng.,'mL()Dpb)(ng/mL) (;)c)(bn)g!mL) (ppb)(ngiml)
[Rabbit
6.19 - 1237 12 - 1200 1
12- 1200
12 - 300
12-300
60- 1200 60- 1200
Compound: PFOSAA
Liver matrix
Prepared
Range of LCR from Range of LCR from Range of LCR from
range of
average
ave curve
low std
low std
high std
high std
standards
curve
curve
curve
cur-ve
curve
(ppb()rig/-L)(ppb()ng/-L)(ppb)(ng/mL)(ppb)(ng/mL)(P:)(oi)lgiml)@ppb)(ng,'-L) (ppb)(ng/mL)
i Rabbit
6.16 - 1232 12 - 1200 30- 1200
30-900
60-900
NI'A
NIA
L
-1
1
Attachment B: I@IDL,LOQ Values 3M Environmental Laboratory
ETS-8-6.0 ExtractionofPFOS from Liver
Page 12 of 16 Page 55
3m Medical Department Study: T-6295.7
Recort No. FAC7 TCX-030 laboratory Request Number-U2279
Compound: ETFOSE-OH
FLiver
Prepared range of
Range of average
matrix
standards
curve
(ppb)(ng/-L) (ppb)(ngiml)
LCR from ave curve
(ppb)(ng/mL)
Range of LCR from
low std
low std
curve
curve
(ppb)(ng,'mL) (ppb) (ng@mL)
F@,b7bit
6.17- 1235
31 -900
31 -900
NiA
N/A
.1
1
Range of high sid
curve
(ppb)(ng'mL)
N/A
LCR from high std
curve
b) (ng/,@rL)
N,A
Compound: PFOSEA
Liver matrix
I Prepared range of standards
(ppb)(ng/TnL)
Range of LCR from Range of LCR from
average
ave curve
low std
low std
curve
curve
curve
(ppb)(ng/TnL) (ppb)(ng/rnL) (ppb)(ng,'M[.)(ppb) (ng/mL,l
Range of high std
curve
(ppb)(ngi-L)
LCR from high std
curve
(ppb)(ng/mL)
Rabbit
6.17-1235 31 - 1200 31 - 1200
N/A
N/A
I
NI'A
N/A
Compound: M556
Prepared
Liver
range of
matrix standards
(ppb)(ng/-L)
Range of averace curve
(ppb)(ng/mL)
LCR from ave curve
(ppb)(ng/mL)
Range of LCR from
low std curve
low std curve
(ppb)(ng/mi-) (p,@,
Rabbit
6.17 - 1235 31 - 1200 60- 1200
N/A
N,/A
Range of LCR from
high std
high std
curve
curve
p,b)(ng/ml,) (ppb)(ng/-L)
Nl,'A
N/A
Attachmen- C: StandardCalculations
ETS-8-6.0
Extraction ofPFOS from Li,.,er
3M Environmental Laboratory
Pave 13 of 14 Page S6
3m me--@@-cal Departrrent Study: T-6295.7
Report No. FA----TOX-030
la]DoraL'ory
Request Number-U2279
Ion PairStandard Curves - Tissue
Prep date(s): Analyte(s): S2mple matrix:
Method/revision: Target analyte(s): FC mix std approx. 0.500 ppm: FC mix std approx. 5.00 ppm: FC mix std approx. 50.0 ppm: Surrogate std approx. 100 ppm:
Standard number: Equipment number: Finalsolventand TN: Blank liver/identirier:
Actual concentrations of standards in the FC mix
I PFOS
PFOSA PFOSAA ETFOSE PFOSEA
Std conc Std conc Std conc Std conc Std conc
ug/mL
ug/mL
ug/mL
ug/n-LL ug/niL
0.500
0.500
0,500
0.500 1 0.500
0.50
0.50
0.50
0.50
0.50
0.500
0.500
0.500
0.500
0.500
0.500
0.500
0.500
0.500
0.-500
0.500
0.500
0.500
0.500 1 0.50
5.00
5.00
5,00
500
5.00
5-00
5.00
5.00
5.00
5.00
5.00 1 5.00
5.00
5.00
500
50.0 i 50.0
50.0
50.0
.0
N1556 Std conc ug/mL
0.500 0.50 0.500 0.500 0.50
5.00. 5.00 5.00 50.0
Std conc
All Am't spiked
mL 0.002 0.04 o@oto 0,020 0.40 0.010 0.020 0.030 0.004
AifDensity
9 0.167 1 0.167 0.167 0.167 0.167 0.167
0.167 i
Calculated concentrations of standards in the sample matrix
PFOS Final conc ng,,g 5.99 12.0
PFOSA Final
I conc ng/g 5.99 12.0
PFOSAA Finalconc
ng/g
5-99 12.0
ETFOSE Final conc nglg 5.99 12.0
PFOSFA
M556
Final
Final Std conc
conc I conc
ng/a
ngjg
ng,,c,
5.99
5.99 1
12.0
12.0
29.9
29.9
29.9
29.9
29.9
29.9
59.9
59.9
59.9
59.9
59.9
59-9
120
120
120
120 1 120
120
299
299
299
299 1 299
299
599
599
599
898
898
898
1198
1198
119-8
599 1 599
898
1198
1198
599 898_ 1198
Surrogate Std conc np-/riil.
i 100
All A m't spik-ed ML 0,(J05
Surrogate Finalconc
ng/mL 0.500
Validated ranges - approximate concentrations
I
Liver
Rabbit
ovine
Rat
PFOS
PFOSA
5-1000 ppb
5-1000 ppb
Estimatesonly,use rabbitvalues.
Estimatesonly,use rabbitvalues.
@AA@ 5-1000 ppb
Nionkey
Fstimatesonly.use rabbitvalues.
ETFOSE-OH 1 5-1000 ppb
POAA
PFOSE,K
5-1000 ppb 1 5-10
pb
A,tachment C: StandardCalculations
ETS-8-6.0 Extractionof PFOS froniLi%-er
3M Enii4-ronmental Laboratcry
Page 14 of 14 Page 57
3m Medical Department Study: T-629S.7
Report No. FACT TOX-C30 laboratory Request Number-U2279
3M ENVIRONMENTAL
LABORATORY
METHOD
A-NALYSIS
OF POTASSIUM PERFLUOROOCTAINESULFONATE
OR OTHER
FLUOROCIMMICALS
IN LIVER EXTRACTS USING
HPLC-ELF,CTROSPRAY/MASS
SPECTROMETRY
Nlethod Number: ETS-8-7.0
Author: Lisa Clemen, Glenn Langenburg Approved By:
AdoptionDate: 07)Z2-li@
Revision Date: NA
Laboratory N@anager - i@@ Group Leader
Technical Reviewer
Date
-@/ Ili Date
o(Il. Date
1.0 SCOPE AND APPLICATION
I -I Scope: This method is for the analysisof liverextractsfor fluarochemicalsurfactantsusing HPLC-electrospray/mass spectrometry.
1.2 Applicable Compounds: Fluorochemical surfactantsor other fluorinatedcompounds, or other ionizablecompounds.
1.3 Matrices: Rabbit,rat,bovine, monkey liver,or other tisslieass designated in the ','alidatiori report.
Word 6,'9-5 3M Environmental
ETS-8-7.0 Analvsisof LiverExtractUsiii,E-S,/'vlS
Laboratory
Page I of 10 Page 58
3m Medical DeiDartment S@,-,dy: T-6295.7
Report No. FACT TOX-030 laboratc--y Request Number-U2279
2.0 SUM@',IARYOF NIETHOD
2.1 This method descr-ibesthe analysisof fluorochemical surfactantsextractedfrom liverusing HPLC-electrospray/mass spectrometry,or similarsystem as appropriate.The analysisis performed by monitoring a singleion characten*stiocf a particularfluorochemical,such as the per fluorooc tanesuI-,"onat(ePFOS) anion,m/z = 499. Additionally,samples may be analyzed using a tandem mass spectrometer to furtherverifythe identityof a compound by detecting dau2fiterions of the selectedparent ion.
3.0 DFFINITIONS
3.1 Atmospheric Pressure Ionization (A.Pl):The Micromass Quattro 11triplequadr-upole systems allow for variousmethods of ionizationby utilizingvarioussources,probes,and interfaces.These include but arenot limitedto:ElectrosprayIonization(ESI),Atmospheric Pressure chemical ronization(A.Pcl),Thermospray, etc. The ionizationprocess in these techniques occurs at atmospheric pressure(i.e.not under a vacuum).
3.2 Electrospray Ionization (ES, ESI): a method of ionizationperformed at atmospheric pressure,whereby ions in solutionare transferredto the gas phase via tiny charged droplets. These charged droplets are produced by the applicationof a strong electricalfield.
3.3 Mass Spectrometrv, Mass Spectrometer (iMS),Tandem Mass Spectrometer (MS/MS): The API Quattro 11 triplequadrupole mass spectrometer isequipped with two quadrupole mass selectivedetectorsand a collisioncell. Ions are selectivelydiscriminatedby mass to charge ratio(mlz) and subsequently detected.A singleMS may be employed forion detectionor an ion may be selectedin the firstquadrupole, fragmented in the collisioncell, and these fragments may be analyzed in the second quadrupole.
3.4 Conventional vs.Z-spray probe interface:Th'e'latesmtodels of Micromass Quattro Il triplequadrupole (post 1998) utilizea "Z-spray" conformation. The spray emitted from a probe is orthogonal to the cone aperture.In the conventional conformation itisaimed directlvat the cone aperture,afterpassin,,t,hrough a tortuouspathway in the counter electrode.Though the configurationisdifferentt,he methods of operation,clcaning,and maintenance are the same. However, Z-spray components and conventional components arc not compatible with one another,but only with similarsystems (i.e.Z-spray components are compatible with other Z-spray systems,etc.)
3.5 Mass Lynx Software: System software desiped forthe specificoperationof theseQuattro 11triplequadrupole systems. Currently MassLynx has Windows 95 and WindowsNT 4.0 versions. All versions are similar.For more detailsreferto the manual specificto the instrument (Micromass Quattro Iltriplequadrupole NlassLynx or MassLynx NT User's Guide).
4.0 WARNINGS AND CAUTIONS 4.1 Health and Safety Warnings:
4.1.1 Use caution with the volta0ge cables for the probe. 1,@'heenngIa'@g1e1:d1 , the probe employs a voltage of approximately 5000 Volts.
ETS-8-7.0 Aiial),soifsLiverExtractUsing,ES/i'vlS
3M Env-'@rc)nment@al Laborato--y
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Report No. FAC- TOX-030 laboratory Request Number-U2279
4.1.2 Vvlhenhandling samples or solventswear appropriateprotective-,lovese,yewear, and clothinz.
4.2 Cautions: 4.2.1 Operate the solventpumps below a back pressureof 400 bar (5800 psi).Ifthe back pressureexceeds 400 bar,theHPI 100 willinitiataeutomatic shutdown. 4.2.2 Do not run solventpumps to dryness.
5.0 INTERFERENCES
5.1 To minimize interferencewshen analyzingsamples, Teflon shallnot be used forsample storageor any p4rtof instrumentatiotnhatcomes in contactwith the sample or extract.
6.0 EouiPMENT 6.1 Equipment listedbelow may be modifiedin ordertooptimizethe system.Document
modificationsin the raw data as method deviations.
ally
6.1.1 6.1.2
Micromass Quattro 11triplqeuadrupoleMass Spectrometerequipped with an electrosprayionizationsource.
HPI 100 low pulsesolventpumping system, solventdegasser,column compartment, and autosampler
7.0 SUPPLIES AND MATERIALS
7.1 Supplies-
7.1.1 7.1.2
High purityZ-radeairregulatedto approximately 100 psi(house airsystem)
HPLC analyticalcolumn, specificsto be determined by the analystand documented in the raw data
7.1.3 Capped autovialsor capped 15 ml centrifugetubes
8.0 REAGENTS AND STAINDARDS 8.1 Reagents
8.1.1 Methanol, HPLC grade or equivalent
8.1.2
Milll_QTIwater (ASTM type1),allwater used in thismethod shouldbe ATSM type 1,or equivalent,and be providedby a Milli-QTOC Plussystem or other vendor
8.1.3 Ammonium acetate,reagentgrade or equivalent
8.1.3.1 When preparingdifferenatmounts than thoselisteda,djustaccordingly.
8.1.3.2 2.0 mM ammonium acetatesolution:Weigh approximately0.300 g animonium acetateP.our intoa 2000 mL @,olumetriccontainercontaiiiicny 2000 mL Milli-Q" water,mix untilallsolidsaredissolved.Store atroo* m temperature.
ETS-8-7.0 AnalysisofLiverExtractUsing ES/'YIS
Page 3 of 10
3M Environmen+.-al Laboratory
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3m Medical Department Study: T-6295.7
ReTDort No. FACT TOX-030 laboratory @Request Number-U2279
8.2 Standards
8.2.1 Typically two method blanks,two matrix blanks, and eighteen matrix standards are prepared du@ing the extractionprocedure. Ref,-rto ETS-8-6.0.
9.0 SAMPLE HA,4DLING 9.1 Fresh matrix standards are prepared with each analysis. Extractedstandards and samples
are stored in capped autovialsor capped 15 ml centrifugetubes untilanalysis.
9.2 Ifanalysis willbe delayed, extractedstandardsand samples may be stored at room temperature, or refrZiP-cratedatapproximately 4' C, untilanalysiscan be performed.
10.0
()UALITY
10.1 Method
CONTROL
Blanksand
Matrix Blanks
10.1.1 Solvent blanks, method blanks, and matrix blanks are prepared
and analyzed
with
each batch to determine contamination or carryover.
10.1.2 Analyze a method blank and a matrix blank priorto each calibrationcurve.
10.2 imatrix Spikes
10.2.1 Matrix spikes are prepared and analyzed to determine the matrix effecton the recovery efficiency.
10.2.2 Matrix spike duplicatesare prepared and analyzed to measure the precisionand the recovery for each analyte.
10.2.3 Analyze a matrix spikeand matrix spikeduplicateper fortysamples. With a minimum of 2 spikes per batch.
10.2.4 Matrix spike and matrix spikeduplicateconcentrationswillfallinthe mid-range of the initiaclalibrationcurve. Additionalspike concentrationsmay fallin the lowrange of the initiaclalibrationcurve.
10.3 Continuing Calibration Checks
10.3.1 Continuing calibrationverificationasre analyzed to verifythe continued accuracy of the calibrationcurve.
10.3.2 Analyze a mid-rangc calibrationstandardevery tenthsample, with a minimum of one per batch.
11.0 CALIBRATION
AND STANDARDIZATION
11.1 A-nalyze the extractedmatrix standardspriorto and following each set of sample extracts. The average of two standardcurves willbe plottedby linearregression(y = mx - b), weighted I/x,not forcedthrough the origin,using MassLynx or other suitablesoftware.
11.2 Ifthe curve does not meet requirements perforrtrioutine maintenance or reextractthe standard cur-ve(ifnecessary) and reanalyze.
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11.3 For purposes of accuracy when quantitatinlgow levelsof analyte,itmay be necessaryto use the low end of thecalibratiocnurve ratherthan the fullrange of the standardcur-ve. Example: when attemptingto quantitateapproximately 10 ppb of analyte,generatea calibrationcurve consistingof thestandardsfrom 5 ppb to 100 ppb ratherthan the full range of the cur-ve(5 ppb to 1000 ppb). This willreduce inaccuracyattributetdo linear regressionweighting of high concentrationstandards.
12.0 PROCEDURES 12.1 Acquisition Setup
12.1.1 Set up the sample list.
12.1.1.1 AssIL7na sample listfilename using MO-DAY-last digitof year-increasinc, letterof the alphabet startingwith a
12.1.1.2@Lssign a method (MS file)for acquiring 12.1.1.3 Assign an HPLC program (Inletfile) 12.1.1.4Type in sample descriptionsand vialpositionnumbers
12.1.2 To createa method clickon method inthe Acquisitioncontrolpanelthen mass spectrometerheadingsand selectSIR (SingleIon Recording) or MT;LM (Multiple Reaction Monitoring).Set IonizationMode as appropriateand mass to 499 or other appropriatemasses. A fullscan isusuallycollectedalong with the SIRS. Save acquisitionmethod. IfMS/MS instrumentsare employed, additionalproduct ion fragmentationinformationmay be collected.Refer toMicromass MassLynx GUIDE TO DATA ACQUISITION foradditionalinfor-matioannd MRI@VI.
12.1.3 Typically the analyticablatch run sequence begins and ends with a setof extracted matrix standards.
12.1.4 Samples are analyzedwith a continuingcalibratiovnerificatioinnjectedstandard afterevery tenthsample. Solventblanks should be analyzed periodicalltvo monitor possibleanalytecarryoverand arenot consideredsamples but may be included as such.
12.2 Using the Autosampler
12.2.1 Set up sample trayaccordingto the sample listprepared in Section12.1.1.
12.2.2 Set-up the HP II00/autosampleratthe followingconditionsor atconditionsthe analystconsidersappropriateforoptimal response.Record actualconditionsin the instrument logbook:
12.2.2.1Sample size= 10 @iL injection
12.2.2.2Inj'ect/sampl=e 1
12.2.2.3Cycle time = 9 minutes
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12.2.2.4Solvent ramp conditions
Time
MEOH
0.00 min.
40%
1.0 min.
40%
4.5 min.
95%
6.5 min.
95%
7.0min.
40%
9.0 mi.
40%
2.0 mNI Ammonium acetate
60% 60% 5% 5% 60% 60%
12.2.2.5Press the"Start"button.
12.3 Instrument Set--up
12.3.1 Refer to ETS-9-24.0, "Operationand Maintenance of the Micromass Quattro Ii TripleQuadrupole Mass SpectrometerFittedwith an Atmospheric Pressure IonizationSource,"formore details.-
12.3.2 Check the solventlevelinreservoirsand refililfnecessary.
12.3.3 Check thestainlessteelcapillaryatthe end of the probe. Use an eyepiece tocheck thetip.The tipshouldbe flatwith no jagced ed-es. Ifthetipisfound to be unsatisfactor-v,disassemble the probe and replacethestainlesssteelcapillar@'.
12.3.4 Turn on the nitrogen.
12.3.5 Open the tune page. Clicks on operateto initiatseource block and desolvation heaters.
12.3.6 Open the InletEditor.
12.3.6.1Set HPLC pump to "On" 12.3.6.2 Set the flow to 10 -500 uL/min or as appropriate 12.3.6.3 Observe dropletscoming out of the tipof the probe. A finemist should be
expelledwithno nitrogenleakingaround thetipof theprobe. Readjust the tipof the probe ifno mist isobserved 12.3.6.4Allow to equilibratfeorapproximately 10 minutes.
12.3.7 The instrumentuses theseparameters atthe followingsettings.These settingsma,, change inorder tooptimize theresponse:
12.3.7.1 Drying gas 250-400 liters/hour 12.3.7.2 ESI nebulizinC>ggas 10-15 liters/hour 12.3.7.3HPLC constantflow mode flow rate10 - 500 @iL/min 12.3.7.4 Pressure<400 bar (Thisparameter isnot set,itisa guide to ensure the
HPLC isoperatingcorrectly.)
12.3.7.5Source block temperature150"
12.3.7.6Desolvation temperature2500
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12.3.8 Printthe tur;epage, with itsparameters,and storeitin the study binder ,vitha copy taped into the instrument log.
12.3.9 Click on startbutton inthe AcquisitionControl Panel (thismay vary among MassLynx versions,referto appropriateMassLynx User's Guide). Ensure startand end sample number includesallsamples to be analyzed.
13.0 DATA ANALYSFS 13.1 Calculations:
AND CALCULATIONS
13.1.4 Calculate matn*x spike percent recoveries using the following equation:
% Recovery
Observed Result - Background Result x 100 Expected Result
13.1.5 Calculatepercent differenceusing the following equation:
% Difference
Exi)ectedConc. -Calculated Conc. x 100 Expected Conc.
13.1.6 Calculateactualconcentrationsin matn'x (@tg0/-):
(nizof PFOS calc.from std.Curve.x DilutionFactor) x I ag
(InitiaWleight of Liver
1000 ng
FinalVolume (mL)
14.0 METHOD PERFORMA.NCE
14.1
Method Detection Limit (MDL) and Limit of Quantitation(LOQ) aremethod, analyte,and matrix specific.Refer to ETS-8-6.0, Attachment B fora liiingof currentvalidatedMDL and LOQ values.
14.2 Solvent Blanks, Method Blanks and Matrix Blanks
14.2.1 Solvent blanks, method blanks,and matrix blanks must be below the lowest standard in the calibrationcurve.
14.3 Calibration Curves
14.3.1 The r2value for the calibrationmust be 0.980 or better.
14.4 Matrix Spikes
14.4.1 Matrix spike percentrecoveriesmust be within 30% of the spiked concentration.
14.5 Continuing Calibration Verification
14.5.1 Continuing calibrationverificatiopnercentrecoveriesmust be within +-300/'oof the spiked concentration.
14.6 If cn'terialistedin the method performance sectionare not met, maintenance may be performed on the system and samples reanalyzed or other actions as determined by the analyst.Document allactionsin the appropriatelogbook.
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14.7 Ifdata areto be reportedwhen performance criterihaave not been met, the data must be footnotedon tablesand discussedinthetextof thereporl.
15.0 POLLUTION PREVENTION AND WASTE MANAGENIENT
15.1 Samole extractwaste and flammable solventisdisposed inhigh BTU containers,and glass pipettewaste isdisposed inbroken glasscontainerslocatedin the laboratory.
16.0 RECORDS
16.1 Each page generated fora studymust have the followinginformationincludedeitherin the header or hand writtenon the page: studyor projectnumber, acquisitiomnethod, integratiomnethod, sample name, extractiodnate,dilutionfactor(Ifapplicable)a,nd analyst.
16.2 Print the tune page, sample lista,nd acquisitionmethod from MassLynx to include in the appropriatestudy folder.Copy thesepages and tape intothe instrumentrunlog.
16.3 Plot the calibratiocnurve by linearregressionw,eighted l,'xt,hen printthesegraphs and storein the study folder.
16.4 Printdata integrationsummary, integratiomnethod, and chiomatograms from MassLynx and storein the study folder.
16.5 Summarize datausinC,)-suitablesoftware(Excel 5.0+)and storeinthe study folder,referto Attachment A for an example ofa summary spreadsheet.
16.6 Back up electronicdata to appropriatemedium. Record in studynotebook the filename and locationof backup electronicdata.
1'10' TABLEs DIAGRAMS, FLOWCHARTS, AND VALIDATION DATA I'iI. Attachment A: ETS-8-7.0 Data summary spreadsheet
18.0 REFERENCES
18.1 FACT-M-2. Compounds
1,"Extractionof Potassium Perfluorooctanesulfonatoer Other Fluorochemical ftom Live,-forAnalysisUsing HPLC-Electrospray/Mass Spectrometry"
18.2 ETS-9-24.0, "Operation and Maintenance of the Micrc)massAtmospheric Pressure Ionization/MassSpectrometer QuattroIItriplequadrupole Systems"
18.3 The validationreportassociatedwith thismethod isETS-8-6.0 & 7.0-V-1
19.0 AFFECTED DOCIJMENTS
19.1 ETS-8-6.0, "Extractionof Potassium Perfluorooctanesulfonatoer Other Fluorochemical Compounds from Liver or Fluid forAnalysisUsing HPLC-Electrospray/Mass Spectrometry"
ETS-8-7.0 Analysisof LiverExtractt:,sinEuSii%[S
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20.0 REVISIONS
Revision Number
Reason For Revision
Revision Date
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Laboratory Study
Study: Test Material: Matrix,'FinaSlolvent: Method/Revision: AnalyticalEquipment System Number: InstrumentSoftware/Version: Filename: R-Squared Value: Slope: Y Intercept-. Date of Extraction/Analyst@. Date ofAnalysis/Analyst:
Group Dose
s2mpie#
concentration ng/g
lniti2Wlt. 9-
Dilution Factor
FinalConc. ug/g
-STo-p-v-.-ra-@-ie-ni-nTeraorm regressionequation. Group/Dose: Taken from thestudyfolder. Sample#: Taken from thestudyfolder. Concentration (ngig):Taken from theMassLynx integratiosnummary. InitiaWlt. (g):Taken from thestudyfolder. DilutionFactor: Taken from thestudyfolder. FinalConc. (tig/g):Calculatedby dividingtheinitiavlolume from theconcentration
Attachment A: Sunurary Spreadsheet
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Analysisof LiverExtractUsing ES"%IS
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3M ENVIRONME-N'TAL
LABORATORY
METHOD
EXTRACTIOISL FLUOROCHEMICAL
OF POTASSIUM PERFLUOROOCTANIESULFONATE
COMPOUNDS
FROM SERUi'vl FOR ANALYSIS
ELECTROSPRAY/MASS
SPECTRONIETRY
OR OTHER
USING HPLC-
Method Number: ETS-8-4.1
Adoption Date: 031'01/99
Author: Lisa Clemen, Glenn Langenburg
Revision Date:
Approved By:
Laboratory Manager
Datc
Group Leader Technical Reviewer
Date Date
1.0 SCOPE AND APPLICATION 1.1 Scope: This method isforthe extractionof potassium perfluorooctanesulfonate(PFOS)
or other fluorochemical compounds from serum. 1.2 Applicable compounds: Fluorochemical surfactants or other fluorinated compounds.
1.3 Matrices: Rabbit, rat,bovine, monkey, and human serum or other fluids as designated in the validationreport.
Word 6/95 3M Environmental Laboratory
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2.0SUNINIARY OF METHOD
2.1 This method descr-ibetsheprocedureforextractingpotassiumpertluorooctanesulfonate (PFOS) or otherfluorochemicaslurfactantfsrom serum,or otherfluidsu,singan ion pairingreagentand methyl-tert-buteytlher(MtBE). Inthismethod,seven fluorochemicalswere extractedP:FOS, PFOSA, PFOSAA, ETFOSE-OH, PFOSEA, M556, and surrogatestandard(see3.0Definitions).An ionpairingreagentisadded to the sample and theanalyteion pairispartitioneidntoMTBE. The MTBE extractis removed and put onto a nitrogenevaporatoruntildry. Each extractisreconstituteidn 1.0 mL of methanol,then filteretdhrougha 3 cc plastiscyn'n,-aettachedtoa 0.2 lAm nylon filteirntoglassautovials.
2.2 These sample extractsareanalyzedfollowingmethod ETS-8-5.1 or otherappropn'ate methods.
3.0 DEFINITIONS 3.1 PFOS: perfluorooctanesulfonat(eanionof potassiumsalt)C,F,IS033.2 PFOSA: perfluorooctanesulfonylamideC,F,.,SO.NE,,
3.3 PFOSAA: perfluorooctanseulfonylamido(ethyl)acetaCt,eF,,SO,N(CH,CH3)CH,CO,-
3.4 ETFOSE-OH: 2(N-ethylperfluorooctasnuelfanamido)-ethyallcohol C,F,IS02N(CH2CH3)CH,CH,OH
3.5 PFOSEA-. perfluorooctanseulfonytethylamideCIF,7SO,N(CH,CH,)H
3.6 M556: C,F,,SO,N(H)(CH,COOH)
3.7 Surrogatestandard:IH-IH-2H-2H perfluorooctanseulfonicacid
4.0 WARNINGS
AND CAUTIONS
4.1 Health and safetywarnings
4.1.1 Use universalprecautionse,specialllyaboratorycoats,-oggles,and gloves when handlinganimal tissuew,hich may containpathogens.
5.0 INTERFERENCES
5.1 There areno interferenceksnown at thistime.
6.0 EouipNIE,14T 6.1 The followingequipment isusedwhileperformingthismethod. Equivalentequipment is
acceptable. 6.1.1 Vortex mixer,VV@R, Vortex Genie 2 6.1.2 CentrifugeM,istral1000 orIEC
6.1.3 Shaker,Eberbach or VWR
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6.1.4 Nitrogen evaporator,Organomation 6.1.5 Balance ( 0.100 g)
7.0 SUPPLIES AND MATERIALS 7.1 Gloves 7.2 Eppendorf ordisposable pipettes 7.3 Nalgene bottles,capable of holding 250 mL and I L 7.4 Volumetn'c flasks,class,type A 7.5 I-CHEM vials,glass,40 mL glass 7.6 Centrifuge tubes,polypropylene, 15 mL 7.7 Labels 7.8 Oxford Dispenser - 3.0 to 10.0 mL 7.9 Syringes, capable of measuring 5 4L to 50 pLL 7.10 Graduated pipettes 7.11 Syringes, disposable plastic,3 cc 7.12 Syringe filtersn,ylon, 0.2 pm, 25 mm 7.13 Timer 7.14 Crimp cap autovialsand caps 7.15 Crimpers Note: Prior to using glassware and bottles,rinse3 times with methanol and 3 times with
Milli_QTM water. Rinse syringesa minimum of 9 times with methanol, 3 rinsesfrom 3 separate vials.
8.0 REAGENTS AND STANDARDS 8.1 Type I reagent grade water, Milli-QTIAor equivalent;all,,vateursed in t.@ilmsethod should
be Milll_QT',wlater and may be provided by a Milli-Q TOC plUSTm System 8.2 Sodium hydroxide (iNaOH), J.T Baker or equivalent 8.3 Tetrabutylammonium hydrogen sulfate(TBA),Kodak or equivalent 8.4 Sodium carbonate (Na@CO,), J.T.Baker or equivalent 8.5 Sodium bicarbonate (NaHCO,), J.T.Baker or equivalent 8.6 Methyl-T-Butyl Ether,Omnisolv, glassdistilleodr HPLC crade 8.7 Methanol, Omnisolv, glassdistilleodr HPLC grade 8.8 Serum or blood, frozen from supplier 8.9 Fluorochemical standards
8.9.1 PFOS (3M SpecialtyChemical Division),molecular weight= 539 8.9.2 PFOSA (3M SpecialtyChemical Division),riioleculawreight = 499
ETS-8-4.1 Ex=ction ofPFOS from Scrum
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8.10 8.11
8.9.3 8.9.4
PFOSAA (3M SpecialtyChemical Division),molecular weight = 585 ETFOSE-OH (3M SpecialtyChemical Division),molecular wel,-ht= 5'10
8.9.5 8.9.6 8.9.7
PFOSEA (3M SpecialtyChemical Division),molecular we@-,.h=t 527
M556 (3M SpecialtyChemical Division),molecular weight = 55 /' Surrogate standard:4-H, perfluorooctanesulfonicacid (I-H, I-H, 2-H, 2-H C,F,,SO,H) molecular weight = 428
8.9.8 Other fluorochemicals,as appropn'ate
Reagent preparation
NOTE:
When preparing largervolumes than listedin reagent,standard,or surrogate preparation,adjustaccordingly.
8.10.1 10 N sqdium hydroxide (NaOH): Weigh approximately 200 g NAOH. Pour into a 1000 mL beaker containing500 mL Milli-Q" water,mix untilallsolidsare dissolved. Store in a I L Nalgene bottle.
8.10.2 1 N sodium hydroxide (NaOH): Dilute 10 N NAOH 1:10. Measure 10 mL of 10 N NAOH solutionintoa 100 mL vol'umetricflaskand diluteto volume using Milli-Q" water. Store in a 125 mL Nalgene bottle.
8.10.3
0.5 M tetrabutylammonium hydrogen sulfate(TBA): Weigh approximately 169 g
of TBA intoa I L volumetriccontaining 500 mL MilliT.-1 Qwater.Adjust to pH
1.0using approximately 44 to 54 mL of 10 N NAOH (While adding the lastmL of
NAOH, add slowly because the pH changes abru-otly)D.iluteto volume with MillI_QTM water. Store in a 1 L Nalgene bottle.
8.10.3.1 TBA requiresa check pn'orto each use to ensure pH = 10. Adjust as needed using I N NAOH solution.
8.10.4 0.25 M sodium carbonate/sodium bicarbonatebuffer(Na,CO,,'NaHC03): Weigh approximately 26.5 g of sodium carbonate (NaCO,) and 2 1.0- of sodium bicarbonate(NaHC03) intoa I L volumetric flaskand bring to volume with MilliQTm water. Store in a I L Nalgene bottle.
Standards preparation
8.11.1 Prepare PFOS standards for the standard curve.
8.11.2 Prepare other fluorochemical standards,as appropriate.Multicomponent fluorochemical standards are acceptable (forexample, one working standard
solutioncontaining 1.00ppm PFOS, 1.02 ppm PFOSA, 0.987 ppm PFOSAA, and
1.10 ppm EtFOSE-OH.)
8.11.3 Weigh approximately 100 mg of PFOS into a 100 mL volurfletn'fclaskand record the actualweight.
8.11.4 Bring to volume with methanol for a stock standardof approximately 1000 ppm (4g/mL).
8.11.5 Dilute the stock solutionwith methanol fora working standard I solutionof approximately 50 ppm.
8.11.6 Diluteworking standard I with methanol fora working standard2 solutionof approx. 5.0 ppm.
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8.12
8.11.7 Dilute working standard I with methanol fora working standard3 solutionof approx. 0.50 ppm.
Surrogate stock standard preparation
8.12.1 Weigh approximately 50-60 mg of surrogatestandard I-H,I-H, 2-H, 2-H, C,F,3SO,H into a 50 mL volumetric flaskand record the actualweight.
8.12.2 Bn'ng to volume with methanol fora surrogatestock of approximately 1000- 1200 PPM. '
8.12.3 Prepare a surrogateworking standard. Transferapproximately I mL of surrogate stock to a 10 mL volumetric flaskand bn*ng to volume with methanol for a working standard of 100 ppm. Record the actualvolume transferred.
9.0 SAMPLE HANDLING 9.1 All samples are received frozen and must be kept frozen untilthe extractionis performed. 9.2 Allow samples to thaw to room temperature pn*orto extraction.
10.0 OUALITY
CONTROI,
10.1 Solvent Blanks, Method blanks and matrix blanks
10.1.1 An aliquotof 1.0mL methanol isused as a solvent blank.
of Milli_QTII
10.1.2 Extracttwo 1.0mL aliquots
water followine thisprocedure and use
as method blanks.
10.1.3 Extract two 1.0 mL aliquotsof the serum following thisprocedure and use as matrix blanks. See 11.1.4.
10.2 Matrix spikes
10.2.1 Prepare and analyze matn'x spike and matrix spike duplicatesamples to determine the accuracy of the extraction.
10.2.2 Prepare each spike using a sample chosen by the analyst,usuallythe control matrix received with each sample set.
10.2.3 Expected concentrationswillfallin the mid-range of the initiaclalibrationcurve. Additional spikes may be includedand may fallin the low-range of the initial calibrationcurve.
10.2.4 Prepare one matn'x spike and matrix spike duplicateper 40 samples, with a minimum of 2 matrix spikesper batch.
10.3 Continuing calibration checks
10.3.1 Prepare continuing calibrationcheck samples to ensure the accuracy of the initial calibrationcurve.
10.3.2 Prepare, at a minimum, one continuing check per group o@'10 samples. For example, ifa sample set= 34, four checks are prepared and extracted.
10.3.3 Prepare each continuing calibrationcheck from the same rnatrixused to prepare the initiaclur-ve.
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Extraction ofPFOS from Serum
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10.3.4
The expected concentrationswillfallwithin the mid-range of the initial calibrationcurve. Additionalspikesmay be included thatfallinthe low-range of the initiaclalibrationcurve. This isnecessary ifthe analystmust quantitateusing only the low end of thecalibrationcurve (forexample, 5 ppb - 100 ppb, rather than 5 ppb - 1000 ppb).
11.0 CALIBPATION AND STANDARDIZATION
11.1 Prepare matrix calibrationstandards
11.1.1 Transfer I mL of serum to a 15 mL centrifugetube.
11.1.2 If most sample volumes are lessthan 1.0 mL, extractstandards with matrix volumes equal to the sample volumes. Do not extractlessthan 0.50 mL of matrix. Rec-ord each sample volume on the extractionsheet.
11.1.3 While preparing a totalof twenty aliquotsin 15 mL centrifugetubes,mix or shake between aliquots.
11.1.4
Two I mL aliquots,or other appropn'atevolume, serve as matrix blanks. Typically use the standard concentrdtionsand spiking amounts listedin Table 1, at the end of thissection,to spike,in duplicate,two standard cur-ves,for a totalof eighteen standards,two matrix blanks,and two method blanks.
11.1.5 Refer to validationreportETS-8-4.0 & ETS-8-5.0-V-1, which liststhe working ranges and the Linear CalibrationRange (LCR) forcalibrationcurves.
11.1.6 Use Attachment D as an aid in calculatingthe concentrationsof the working standards. See Section 13.0 to calculateactual concentrationsof PFOS in calibrationstandards.
11.2
To each standard,blank, or continuing check, add appropriateamount of surrogate working standard for the concentrationto fallwithin the calibrationcurve ran2e 5 ppb 1000 ppb.
11.3
Extract spiked matn*x standards following 12.6-12.16 of thismethod. Use these standards to establisheach initialcurve on the mass spectrometer.
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Table I
Approximate spiking amounts for standards and spikes
Using 1.0 mL of matrix
Working standard
(approx.conc.) --
4L
Approx. finalconc. of
analytein matrix
-
Blank
0.500 ppm
10
0.005 ppm
0.500 ppm
20
0.010 ppm
5.00 ppm
5
0.025 ppm
5.00 ppm
10
0.050 ppm
5.00 ppm
20
0.100 ppm
5Cr.0ppm
5
0.250 ppm
50.0 ppm
10
0.500 ppm
50.0 ppm
15
0.750 ppm
50.0 ppm
20
1.00 ppm
12.0 PROCEDURE
12.1
Obtain frozen samples and allow to thaw atroom temperature or in a lukewan-n waterbath.
12.2 12.3
Vortex mix for 15 seconds,then transfer1.0 mL or other appropriatevolume to a 15 mL polypropylene centrifugetube.
Return unused samples to freezerafterextractionamounts have been removed.
12.4 Record the initiavlolume on the extractionworkshect.
12.5
Label the tube with the study number, sample ID, date and analystinitials.See attached worksheet fordocumenting the remaining steps.
12.6
Spike allsamples, includingblanks and standards,ready forextractionwith surrogate standard as described in 11.2.
12.7 12.8
Spike each matrix with the appropriateamount of standard as described in 11.1,or Table I in that section,forthe calibrationcurve standards.Also prepare matrix spikes and continuing calibrationstandards.
Vortex mix the standardcurve samples, matrix spikesamples, and continuing calibration samples for 15 seconds.
12.9 Check to ersure the 0.5 M TBA reagentis at pH 10. Ifnot,adjustaccordingly.
12.10 To each sample, add I mL 0.5 M TBA and 2 mL of 0.25M sodium carbonate/sodium bicarbonate buffer.
12.11 Using an Oxford Dlsr)enser,add 5 mL methyl-tert-butylether.
12.12 Cap each sample and put on the shaker at a settingof 300 rpm, for 20 minutes.
12.13 Centrifuge for 20 to 25 minutes at a settingof 3500 rpm, or untillayersare well separated.
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12.14 Label a fresh 15 mL centrifugetube with the same information as in 12.5. 12.15 Remove 4.0 mL o'-@,.hoerganic layerto thisclean 15 mL centrifugetube. 12.16 Put each sample on the analyticalnitrogen e@,,aporatourntildry, approximately I to
hours. 12.17 Add 1.0 mL of methanol to each centrifugetube using a graduated pipette. 12.18 Vortex mix for 30 seconds.
12.19 Attach a 0.2 Am nylon mesh filterto a 3 cc syringe and transferthe sample to this syringe. Filterinto a 1.5 mL glassautovialor low-volume autovialwhen necessar-v.
12.20 Label the autovialwith the study number, animal number and gender, sample timepoint, matrix, finalsolvent,extractiondate,and analyst(s)performing the extraction.
12.21 Cap and store extractsat room temperature or at approximately 4 'C untilanalysis. 12.22 Complete the extractionworksheet, attached to thisdocument, and tape in the study
notebook or include in study binder,as appropr-iate.
13.0 DATA ANALYSIS AND CALCULATIONS
13.1 Calculations 13.1.1 Calculate actual concentrationsof PFOS, or other applicablefluorochemical, 'in calibrationstandards using the following equation:
mL of standard x concentrationof standard /mL) mL of standard + mL of surrogatestandard+ initiamlatrix volume (mL)
Final Concentration (@ig/mL)_of PFOS in matrix
14.0 METHOD PERFORMANCE
14.1
The method detectionlimit(NIDL) isanalyteand matrix specific.Refer toMDL report
forspecificMDL and limitof quantitation(LOQ) values(seeAttachmentsB and C).
14.2 The followingqualitycontroslamplesareextractewditheachbatchof samplesto evaluatethequalityof theextractionand analysis.
14.2.1 Method blanks and matrixblanks.
14.2.2 Matrix spikeand matrixspikeduplicatesamples to determineaccuracyand precisionof theextraction.
14.2.3 Continuingcalibratiocnheck samples to deter-mintehecontinuedaccuracyof the initiaclalibratiocnurve.
14.3 Refer tosection14 of ETS-8-5.1 formethod performancecriteria.
15.0 POLLUTION PREVENTION AND WASTE MANAGEME14T
15.1 Sample waste isdisposedinbiohazardcontainersf,lammable solventwaste isdisposedin high BTU containersa,nd used glasspipettewaste isdisposedinbroken glasscontainers locatedinthelaboratory.
ETS-8-4.1 Extractionof PFOS from Serum
Page 8 of 14
3M Environmental Laboratory
Page 75
3m Medical Department Study: T-6295.7
Reporz No. FACT TOX-C30 laboratory ReQ-uest Number-U2279
16.0 RECORDS
16.1
Complete the extractionworksheet attachedto thismethod, and tape in the study notebook or include in the 3-rin-study binder,as appropriate.
17.0 ATTACHMENTS 17.1 Attachment @, Extractionworksheet 17.2 Attachment B, MDL/LOQ values and summary 17.3 Attachment C, Calibrationstandard concentrationworksheet
18.0 RIEFERENCES
18.1 The validation -reportassociated with thismethod is ETS-8-4.0 & 5.0-V-1. 18.2. FACT-M-3. 1, "Analysis of Serum or Other Fluid Extractsfor Flucrochemicals using
HPLC-Electrospray Mass Spectrometry"
19.0 AFFECTED DOCUMENTS
19.1
ETS-8-5. 1, "Analysis of Serum or Other Fluid Extractsfor Fluorochemicals usincy HPLC-Electro spray Mass Spectrometry"
20.0 REviSIONS
Revision Number
I
Reason For Revision Section 12.21 Changed to include sample storage atroom temperature. Section 12.13 Added the shaker speed. Section 12.17 Final volume is 1.0mL; not adjustedfor initiavlolumes less than 1.0 mL.
Revision Date
04/02/99
3M Environmental Laboratory
ETS-9-4.1 Extractionof PFOS from Senini
Page 9 of 14 Page 76
3m Med4-cal Department
study: T-6295.7
Report No.
laboratorv Reauest
ExtractioWnorkshect ETS-8-4.1
FACT TOX-030 Number-U2279
Studv Matrix Box
@Vk/Day
DateSpiked/Analyst ccv \,IS MSD
surtogateStd approx. ppm actual ppm
FC-Mix approx.0.5 pm actual PPM
FC-Mix
approx.5 ppm actual ppm
F C:@@@ixt-approx.50 ppm actual PPM
I Blank
Std
amount
Serum Extr2ctionMethod Vortex IS see.
PipetteMatrix
Volume
mL
PipcttIe mL of 0.5M TBA, pH 10. pH
Std@ #
Pipctic2 mL of0.25Na2CO3/0.25M NaHC03 buffer
Std.4
Dispense5 mL of methyl-t-butyelther
TN-A-
Shake 20 min.
Shaker speed:
Ccntrifu_g2c0-25 min. Remove a 4 mL aliquotoforganiclaver
Ccntrifu_gsedced:
Put on Nitro,ycnEvaDoratortodrvncss
TempeTature:
Add methanol
Volume
mL
T-,N-A-
Vortex30 sec.
Filteursin,ga 3ec B-D svringewith a 0.24m f-litCTintoa 1.5mL autosamdievial Cont. Cal.Verificationsused same matrixas forstdcurve.
mL D2te& Initials
Attachment A 3M E-iv-Lronmen-@al Laboratory
ETS-8-4.1 Extractionof PFOS from Serum
Page 10 of 14 Page 77
3m Medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
MDL[LOQ values forrabbitserum
Compound
MDL
LOQ Linear CalibrationRange (LCR)
(ppb) (ppb) Approximate concentrationstobe used forpreparing the
Standard CalibrationCurve
PFOS
1.74
5.55 5 ppb - 1000 ppb
PFOSA
1.51
4.79 5 ppb - 1000 ppb
PFOSAA
3.46
20.5 5 ppb - 1000 ppb
ETFOSE-OH
11.4
36.2 5 ppb - 1000 ppb
M556
6.03
19.2 5 ppb - 1000 ppb
PFOSEA
5.71
18.2 1 5 ppb - 1000 ppb
MDULOQ
values in rat,bovine,monkey, and human serum, and monkey plasma were not statistically
determined. Two curves in each of thesematriceswere extractedand analyzed with therabbitserum
curves to determine equivalence. Responses inthe rat,bovine,monkey, and human were equivalentto
the rabbitresponses,therefore,theirMDL and LOQ willbe the same valuesas determined in rabbit serum.
Please see LOQ Summary and MDL study inETS-8-4.0 & 5.0-V-I forfurtherinformation.
Attachment B: iviDL/LOQ Sununary 3M Env@-ronmen*@-al Laboratory
F-TS-8-4.1 Extractionof PFOS from Serum
Page II of 14 Page 78
3m Medical Department Sz:udy: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
Compound: PFOS Prepared range
LCR from
Rabbit Serum of standards
curve
(ppb)(ng/r.,-L) (ppb)
(ng/mL)
FullRange
0.995-973
24.8-978
Low Curve
4.94-248
4.94-248
High curve
97.8-978
97.8-978
I/X
0.995-978
4.94-978
% Recoverv Range
83-108 85-104 85-106 94-111
Compound: PFOSA Prepared range
Rabbit Serum of standards (ppb)(ng/mJ-)
FullRange
0.993-976
LCR from curve (ppb) (ng/mL)
4.93-976
Low Curve
4.93-97.6
4.93-97.6
High cur-ve 1/X
24.8-976 0.993-976
24.8-978 4.93-976
% Recovery Range
88-103 87-105 93-102 94-103
Compound: PFOSAA Prepared range
Rabbit Serum of standards (ppb)(ng/mL)
FullRange
0.991-974
LCR from curve (ppb)
(ng/mL)
24.7-974
Low Curve High curve
4 92 -247 -
49.2-974
9.74-247 97.4-974
0.991-974
9.74-974
% Recovery Range
81-111 97-107 85-108 95-115
RSD Range
4.67-11.0 5.34-12.0 4.84-9.80 4.60-10.5
RSD Range
5.10-14.7 9.85-14.7 5.08-13.9 5.10-14..
RSD Range
4.18-10.6 6.38-21.8 4.33-12.5 4.11-23.2
A-,tachmenBt: MDLil-OQ Summary 3M Environmental Laboratory
ETS-8-4.1 Extractioonf PFOS from Serum
Page 12 of 14 Page 79
3m Medi-cal Department S--udy: T-629S.7
Report No. FACT TOX-030 laboratory Request Number-U2279
Compound: ETFOSE-OH
Prepared range
Rabbit Serum
of standards (ppb) (ng/mL)
Full Range Low Curve High curve 1/X
0.993 -976 4.93-97.6 49.3-976 0.993 -493
LCR from curve (ppb)
(ng/mL) 49.3 -976
9.76-97.6
97.6-976
9.76-976
% Recovery Range
77-110 97-107 90-109 86-111
Compound: PFOSEA
Prepared range
Rabbit Serum
of standards
(ppb) (ng/mL)
Full Range Low Curve High curve I/X
0.993-976 4.93-248 49.3-976 0.993-976
LCR- from curve (ppb)
(ng/mL) 24.8-976
9.76-248
49.3-976
9.76-976
% Recovery Range
96-106 91-110 86-106 95-117
Compound: M556
I Prepared range
Rabbit Serum
of standards
(ppb) (ng/mL)
Full Range Low Curve High curve i,ix
0.993 -976 4.93-97.6 97,6-976 0.993 -976
LCR from curve (ppb)
(ng/mL) 24.8-976
9.76-97.6
97.6-976
9.76-976
% Recovery Range
88-106 100-105 81-111 97-110
RSD Range
11.2-25.5 14.1-21.3 11.5-19.6 11.1-21.2
RSD Range
10.1-16.2 11.8-19.5 10.2-18.2 10.1-19.1
RSD Range
4.82-17.9 5.95-18.2 5.11-9.74 4.77-19.5
Attachrr.e,B-:iMtDL,'LOQ Sun=ry 3M Environmental Laboratory
ETS-8-4.1 Extractionof PFOS from Senim
Paue 13 of 14 Page 80
3m Medical Departrrent Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
Ion PairStandard Curves - Fluids
Prep date(s):
Standard number:
Analyte(s):
Equipment number:
Sample matrix:
Finalsolventand TN:
Blank fluid/identirier:
Method/revision:
Target analyte(s):
FC mix std approx. 0.500 ppm:
FC mix std approx. 5.00ppm:
FC mix std approx. 50.0ppm:
Surrogate std approx. 100 ppm:
Actual concentrations of standards in the FC mix
PFOS
PFOSA PEOSAA ETFOSE PFOSEA
Std conc Std conc Std conc Std conc Std conc
ug/n-LL ug/mL
ug/rnL ug/mL
ug/mL
0.500
0.507 i 0.532
0.501
0.521 1
0
0.507
0.532
0.501
05-21
5.00
5.07
532
5.01
5.21
50
5.07 ---
5.01 5.21
5.00
5.07
5.32
5.01
5.21
50.0
50.1
53.2
50.1
52.1
50.0
50.1
53.2
50.1
52.1 i
[__50.
50.1
53.2
50.1
52.1
50.0
50.1
53.2
50.1
52.1 1
M556 Std conc ug/mL
0.501
61 5.01 5.01 50.1 50.1----
5 0. 1
All Am't
All Finalvol
spikedmL
ML
0.010
0.020
1.025
0.005
o-oi,o 1.015
0.020
1.025
0.005
1.010
-6.@-0 if-d
1.020 1.025
Calculated concentrations of standards in the sample matrix
PFOS -,-,PFOSA PFOSAA
ETFOSE PFOSEA
M556
Surrogate
Finalconc Finalconc Finalconc Finalconc Finalconc Finalconc Stdconc
ng/mL
ng/mL
ng/mL
ng/mL
ng/mL
ng/mL
ng/mL
4.93
5.00 1 5.24
4.94
5.01
5.13
100 1
9.76
9.89
101.4
9.78 '-T9-93
1-d2-----
-@4- 8 49.3
25.1
26@3
50.0 -7---@@
24.8
25.2
49.4 1 50.1
5.8
51.S ------TSiunr@raolc-og@-tnccll
97.8 i 99.3
102
ng/mL
----i---4@--
251
263
f4-8
252
258
500
493
500
524
494
501
513
735
746
782
737
749
6
976
989
1038
978
993 i 1017
All
Am't spiked mL 0.005
Validated ranges - approximate concentrations
Serum
PFOS
PFOSA
PFOSAA
ETFOSE-OH
Rabbit
5.00-1000 1 5.00-1000
5.00-1000 1 5.00-1000 1
Bovine
Estimatesonly. Use valuesforrabbit.
Rat
Estimatesonly. Use valuesforrabbit.
Monkey & Plasma Estimatesonly. Use valuesforrabbit.
Human
Estimatesonly. Use valuesforrabbit.
PFOSEA 5.00-1000
M556 5.00-1000
Attachment C: Ion PairStandardCurves
ETS-8-4.1
Extractionof PFOS from Serum
3M En-v4-ronmental Laboratory
Page 14 of 14 Page 81
3m Medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
3M ENVIRONN4ENTAL
LABORATORY
METHOD
A-NALYSIS QF POTASSILTM PERFLUOROOCTANESLILFONATE
OR
FLUOROCHEMICALS
IN SERUiNt EXTRACTS USING
HPLC-ELECTROSPRAY/MASS
SPECTROMETRY
OTHER
Method Number: ETS-8-5.1
Author: LisaClemen,RobertWynne Approved By: LaboratoryManager
Adoption Date: 03/01/99 Revision Date:
2 Date
Group Leader
,@& A
Technical
Reviewer
Date
. cvz .2@.1
Date
1.0 SCOPE AND APPLICATION
1.1 Scope: This method descn*besthe analysisof serum extractsfor fluorochemicalsurfactants usingHPLC-electrospray/massspectrometry.
1.2ApplicableCompounds: Fluorochemicalsurfactantosrotherfluorl*natceodmpounds, or otherionizablecompounds.
1.3Matrices: Rabbit,ratb,ovine,monkey, and human serum,or otherfluidsasdesignatedin thevalidatiorneport.
Word 6i95
ETS-8-5.1 AnalysisofSerum ExtractUsinp,ES/NIS
Paec I of 9
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2.0 SUNL@MARY OF METHOD
2.1 This method descn*bes the analysisof fluorochemical surfactantsextractedfrom serum or other fluids,using HPLC-electrospray/mass spectrometry, or similarsystem as appropriate. The analysisisperformed by monitoring a singleion characten'stiocf a particular fluorochemical, such as the perfluorooctanesulfonate(PFOS) anion, n-L/z=499. Additionally,samples may be analyzed using a tandem mass spectrometer to furtherverify the identityof a compound by detectingdaughter ions of the parent ion.
3.0 DEFINITIONS
3.1 Atmospheric Pressure Ionization (API); The Micromass Quattro 11tn'plequadrupole systems allow for various methods of ionizationby utilizingvan*ous sources,probes, and interfaces.These include but arenot limitedto:ElectrosprayIonization(ESI),Atmospheric Pressure chemical Ionization(APcl),Thermospray, etc. The ionizationprocess in these techniques occurs at atmospheric pressure (i.e.n,ot under a vacuum).
3.2 Electrospray Ionization (ES, ESI): a method of ionizationperformed at atmospheric pressure,whereby ions in solutionare transferredto the gas phase via tinycharged droplets. These charged droplets are produced by the applicationof a strong electn'calfield.
3.3 Mass Spectrometry, Mass Spectrometer (MS), Tandem Mass Spectrometer (MS/MS): The API Quattro 11 triplequadrupole systems are equipped with quadrupole mass selective detectors.Ions arc selectivelydiscriminatedby mass to charge ratio(Mjz) and subsequently detected. A singleMS may be employed forion detectionor a series(MS/MS) formore speci icfragmentat'on information.
3.4 Conventional vs.Z-spray probe interface:The latestmodels of MicromaQsusatt1r1o
tnplequadr-upaslyestems(post1998)utiliaze"Z-sprayc"onformationT.he sprayemitted from a probe isorthogonaltothecone aperture.Intheconventionalconformationitisaimed directlyatthecone aperture,afterpassingthrougha tortuouspathway inthecounter electrode.Though theconfiguratioinsdifferentt,hemethods of operationc,leaning,and maintenance arcthesame. However, Z-spraycomponents and conventionalcomponents are not compatiblewithone another,butonlywith similarsystems(i.e.Z,-spraycomponents are compatiblewith some otherZ-spraysystems,etc.)
3.5 Mass Lynx Software: System softwaredesignedforthespecifiocperationoftheseQuattro IItriplequadrupolesystems.CurrentlyMassLynx has Windows 95 and WindowsNT 4.0 versions.Allversionsaresimilar.For more detailseethemanual specifitcotheinstrument (N41cromassQuattroIItriplequadrupoleMassLynx or MassLynx NT User'sGuide).
4.0 WARNINGS AND CAUTIONS
4.1 Health and SafetyWarnings:
4.1.1 Use cautionwith thevoltagecablesfortheprobe. When engaged,theprobe employs a voltageof approximately5000 Volts.
4.1.2 When handlingsamples or solventswear appropriatperotectivegloves,eyewear, and clothing.
ETS-8-5.1 Analysis of Serum ExtractUsing ES,@@IS
3M Env4-ronmenta 1 T aboratory
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4.2 Cautions:
4.2.1 Do not operate solventpumps above capacity of 400 bar (5800 psi)back pressure. Ifthe back pressure exceeds 400 bar,the HP I 100 willinitiateautomatic shutdown.
4.2.2 Do not run solventpumps todryness.
5.0 INTERFERENCES-
5.1 To minimize interferenceswhen analyzing samples, teflonshould not be used for sample storage or any part of instrumentationthatcomes in contact with the sample or extract.
6.0 EouIPMENT
6.1 Equipment listedbelow may be modified in order to optimize the system. Document any modifications in-theraw data as method deviations.
6.1.1 6.1.2
Micromass Quattro IItriplequadrupole Mass Spectrometer equipped with an electrosprayionizationsource
HPI 100 low pulse solventpumping system, solventdegasser,column compartment, and autosampler
7.0 SUPPLIES AND MATERIALS
7.1 Supplies 7.1.1 High pur-itgyrade nitrogengas regulatedto approximately 100 psi (House air system) 7.1.2 HPLC analyticalcolumn, specificsto be determined by the analyst and documented in the raw data. 7.1.3 Capped autovialsor capped 15 mL centrifugetubes
8.0 REAGENTS AND STANDARDS 8.1 Reagents
8.1.1 8.1.2
Methanol, HPLC grade or equivalent Mi Il_lQTIL water, allwater used in thismethod should be M 1 11 1 _QTI'water or equivalent,and may be provided by a Milli-Q TOC Plus system or other vendor
8.1.3 Ammonium acetate,reagentgrade or equivalent
8.2 Standards
8.2.1 Typically two method blanks,two matrix blanks, and eighteenmatrix standards are prepared dun'ng the extractionprocedure. See ETS-84.1.
9.0 SAIIPLE HANDLIN'G
9.1 Fresh matn'x standards are prepared with each analysis. Extracted standards and samples are stored in capped autovialsor capped 15 mL centrifugetubes untilanalysis.
3M Environmental
ETS-8-5.1 Analysisof Serum ExtractUsing ES/i@(IS
Laboratory
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Rer)ort No. FACT TOX-030 laboratory Request Number-U2279
9.2 If analysis will be delayed, extractedstandards and samples can be refr-igerateadt approximately 4' C, or at room temperature,untilanalysiscan be performed.
10.0 ()UALITY CONTROL 10.1 Solvent Blanks, Method
Blanks and Matrix Blanks
10.1.1 Solvent blanks, method blanks and matrix blanks are prepared and analyzed with each bat-ch to determine contamination or carryover.
10.1.2 Analyze a method blank and a matrix blank pn'orto each calibrationcurve.
10.2 Matrix Spikes
10.2.1 Matr-ixspikes are prepared and analyzed to determine the matrix effecton the recovery efficiency.
10.2.2 Matn'x spike duplicatesare prepared and analyzed to measure the precisionand the recovery for each analyte.
10.2.3 Analyze a matrix spike and matrix spikeduplicateper fortysamples, with a minimum of 2 spikes per batch.
10.2.4 Matrix spikeand matrix spike duplicateconcentrationswillfallin themid-range of the initiaclalibrationcurve. Additional spikeconcentrationsmay fallinthe lowrange of the initiaclalibrationcurve.
10.3 Continuing CalibrationVerifications
10.3.1 Continuing calibrationverificationsare analyzed to verifythe continued accuracy of the calibrationcurve.
10.3.2 Analyze a mid-range calibrationstandardafterevery tenthsample, with a minimum of one per batch.
11.0 CALIBRATION AND STANDARDIZATION
11.1
Analyze the extractedmatrix standardspriorto and following each setof extracts.The average of two standardcurves willbe plottedby linearregression(y = my + b),weighted I/x,not forced through zero, using MassLynx or other suitablesoftware.
11.2 If the curve does not meet requirements,perform routinemaintenance or reextractthe standard curve (ifnecessary)and reanalyze.
11.3
For purposes of accuracy when quantitatinglow levelsof analyte,itmay be necessary to use the low end of the calibrationcurve ratherthan the fullrange of the standard curve. Example: when attempting to quantitateapproximately 10 ppb of analyte,generate a calibrationcurve consistingof the standards from 5 ppb to 100 ppb ratherthan the full range of the curve (5ppb to 1000 ppb). This willreduce inaccuracy attributedto linear regession weighting of high concentrationstandards.
3M Environmental
ETS-8-5.1 Analysisof Serum ExtractUsing ES@'MS
Laboratory
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12.0 PROCEDURES 12.1 Acquisition Setup
12.1.1 Click on staxibutton in the AcquisitionControl Panel. Set up a sample list.Assicyn a filename using MO-DAY-last digitof year-sample number, assign a method (i@,IS) for acquiring,and type in sample descriptions.
12.1.2
To create a method clickon scan button in the Acquisition controlpanel and select SIR (SingleIon Recording) or MRM. Set IonizationMode as appropr-iataend mass to 499 or other appropr-iatmeasses. A fullscan Is usually collectedalong with the SIRS. Save acquisitionmethod. IfMS/MS instruments are employed, additional product ion fragmentation informationmay be collected.See Micromass MassLynx GUIDE TO DATA ACQUISITION foradditionalinformationand ,\4RM (MultipleReaction Monitoring).
12.1.3 Typicallythe analyticablatchrun sequence begins with a setof extractedmatrix standards and ends with a set of extractedmatrix standards.
12.1.4 Samples are analyzed with a continuing calibrationcheck injectedafterevery tenth sample. Solvent blanks should be analyzed periodicallyto monitor possibleanalvte carr-yoverand are not considered samples but may be included as such.
12.2 Using the Autosampler
12.2.1 Set up sample tray according to the sample listprepared in Section 12.1.1.
12.2.2 Set-up the HP I I00/autosampler atthe following conditions or atconditions the analystconsiders appropriatefor optimal response. Record actualconditions in the instrument logbook:
12.2.2.1 Sample size= 10 @iLinj*ection
12.2.2.2 Inj'ect'sample= 1
12.2.2.3 Cycle time = 13.5 minutes
12.2.2.4 Solvent ramp =
Time
0.00 min. 8.50 min. 11.0 min. 12.0 min.
MEOH
40% 90% 90% 40%
2.0 mM Ammonium acetate
60% 10% 10% 60%
12.2.2.5 Pr-@ssthe "Start"button. 12.3 Instrument Set-up
12.3.1 Refer to ETS-9-24.0 for more details. 12.3.2 Check the solve-.iltevelin reservoirsand refillifnecessary
ETS-8-5.1 Analysisof Serum ExtractUsing ES/i%,IS
3M Environme--ital- Laboratory
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ReDorL-- No. FACT TOX-n@3C laboratory Request Number-U2279
12.3.3 Check the stainlessteelcapillaryattheend of theprobe. Use an eyepiece to check the tip.The tipshould be flatwith no jagged edges. Ifthe tipisfound tobe uns atisfactor-vd,isassemble theprobe and replacethestainlesssteelcapillarv.
12.3.4 Set HPLC pump to"On". Set the flow to 10 - 500 uL/min or as appropriate. Obser-vedropletscoming out of the tipof the probe. Allow to equilibratfeor approximately 10 minutes.
12.3.5 Turn ortthe nitrogen.A finemist should be expelledwith no nitrogenleaking around the tipof the probe. Readjustthe tipof the probe ifno mist isobserved.
12.3.6 The instrumentuses theseparametersatthe following settings.These settingsmay change in order to optimizethe response:
12.3.6.1Drying gas 250-400 liters/hour 12.3.6.2FSl nebulizinggas 10-15 liters/hour 12.3.6.3HPLC constantflow mode, flow rate 10 - 500 pL/min 12.3.6.4Pressure<400 bar (This parameter isnot set,itisa guide to ensure the
HPLC isoperatingcorrectly.)
12.3.7 Carefullyguide theprobe intotheopening. Insertprobe untilitwillnot go any furtherC.onnect the voltagecables to theprobe.
12.3.8 Printthe tune page, with itsparameters,and storeitin the studybinderwith a copy taped intothe instrumentlog.
12.3.9 Using the cross-flowcounterelectrodeinthe ES/iMS source isrecommended for the analysisof biologicalmatn*ces.
12.3.10CIickon startbutton inthe AcquisitionControl Panel (thismay vary among MassLynx versions,see appropriateMassLynx USER'S GUIDE). Pressthe start button. Ensure startand end sample number includesallsamples to be analyzed.
13.0 DATA ANALYSIS AND CALCULATIONS 13.1 Calculations:
13.1.4 Calculatema,,nx spikepercentrecoveriesusing the followingequation:
% Recovery
Obser-vedResult-Background Result x 100 Expected Result
13.1.5 Calculatepercentdifferenceusing the followingequation:
Difference
Exi)ectedConc. -CalculatedConc. x 100 Expected Conc.
13.1.6 Calculateactualconcentrationof PFOS, or otherfluorochemical,inmatrix (pg/mL):
(ng,of PFOS calc.from std.Curve x DilutionFactor) x (InitiaVlolume ofmatrix(mL) + mL of Surro,izateStandard
FinalVolume (mL)
I uv 1000 nu
3M Environmenr-al
Laboratory
ETS-8-5.1 Analysisof Serum ExtractUsing ES/NIS
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Report No. FACT TOX-030 laboratory Request Number-U2279
14.0 METHOD PERFORMA4CE
14.1 Method Detection Limit (MDL) and Limit of Quantitation (LOQ) are method, anal@qe,and
matrixspecific.Pleasesee ETS-84.1, Attachment B, fora listinogfcurrentvalidated MDL and LOQ values.
14.2 SolventBlanks,Method Blanks,and Matrix Blanks
14.2.1 Solvent blaaks,method blanks,and matrixblanksvaluesaremust be below the loweststandardinthecalibratiocnurve
14.3CalibratiCounrves
14.3.1 The r2 value forthecalibratiocnurvemust be 0.980 or better.
14.4 Matrix Spikes
14.4.1 Matn*x spikepercentrecoveriesaremust be within 30% of thespiked concentration.
14.5 Continuing CalibrationVerifleations
14.5.1 Continuingcalibratiovnerificatiopnercentrecoveriesmust be 30% ofthespiked concentration.
14.6 Ifcriterilaistedinthismethod performancesectionisn'tmet, maintenancemay be performed on thesystem and samples reanalyzedor otheractionsas determinedby the analyst.Document allactionsintheappropriatleogbook.
14.7 Ifdata areto be reportedwhen performance criten'haave notbeen met, thedatamust be footnotedon tablesand discussedinthetextof thereport.
15.0 POLLUTION
PREVENTION
AND WASTE MANAGEMENT
15.1 Sample extractwaste and flammable solventisdisposedinhiz-n hBTU containersa,nd C-,lass pipettewaste isdisposedinbroken glasscontainerslocatedin thelaboratory.
16.0 REcoRDs
16.1 Each page generatedfora studymust have thefollowinginformationincludedeitherinthe header or hand w-ritteonn thepage: studyor projectnumber, acquisitiomnethod, integratiomnethod, sample name, extractiodnate,dilutionfactor(ifapplicable)a,nd analyst.
16.2 Pr-intthe tunepage,sample lista,nd acquisitiomnethod from MassLynx toincludeinthe appropriatestudy folder.Copy thesepages and tapeintotheinstrumentr-untog.
16.3 Plotthecalibratiocnur-veby linearegressionw,eighted I/x,thenprintthesegraphs and storeinthestudy folder.
16.4 Printdata integratiosnummary, integratiomnethod, and chromatop-rams,from MassLynx, and storeinthestudy folder.
ETS-8-5.1 AnalysisofSerum ExtractUsingESi"vlS
3M Environmental Laboratory
Page 7 of 9 Page 86
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16.5 Summarize datausing suitablesoftware(Excel5.0)and storeinthe study folder,see Attachment A foran example of a summary spreadsheet.
16.6 Back up electronicdata to appropriatemedium. Record in study notebook the filename and locationof backup electronicdata.
17.0 TABLES, DIAGRAms. FLOWCHARTS, AND VALIDATION DATA 17.1 Attachment A: ETS-8-5.1 Data summary spreadsheet.
18.0 PEFERENCES
18.1 FACT-M-4. compounds
1,"Extractionof Potassium Perfluorooctanesulfonatoer Other Fluorochemical from Serum forAnalysisUsing HPLC-E lectrospray/,MassSpectrometry
18.2 ETS-9-24.0, "Operation and Maintenance of the Micromass Atmospheric Pressure Ionization/MassSpectrometerQuattroIItriplequadrupole Systems"
18.3 The validationreportassociatedwith thismethod is ETS-8-4.0 & 5.0-V-1.
19.0 AFFECRED DOCUMENTS 19.1 ETS-8-4. 1,"Extractionof Potassium Perfluorooctanesulfonatoer Other Fluorochemical
Compounds from Serum forAnalysis Using HPLC-Electrospray/.%,IasSspectrometry"
20.0 REVISIONS
Revision Number.
1
Reason For Revision
Section 6.1.2 Clan'Ecationof HPI 100 system components. Section 11.1 Average of two curves,not standardvalues,are used for
plottinglinearregressionand added the I/x weightincg:lof thecurve. Section 12.2.2.4Clarificatioonf solventramp. Section 17.1 Changed from attachmentB to A.
Revision Date
04/02/199
ETS-8-5.1 AnalysisofSerum ExtTactUsing ES/',MS
3M Environme--ital Laboratory
Page 8 of9 Page 89
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Report No. FACT TOX-030 laboratory Request Number-U2279
Laboratory Study
Study: Test Material: Matrix/FinalSolvent: ,Nfethod/Revision: AnalyticalEquipment System Number: InstrumentSoftwarefVersion: Filename: R-Squared Value: Slope: Y Intercept: Date ofExtractiori/AnalystDate ofAnalysis/Analyst:
Group Dose
S2MP]e#
Concentration ug/mL
InitiaVlol. mL -
Dilution Factor
FinalCone. ug/mL
Slope: Taken from linearregressionequation. Group/Dose: Taken from thestudyfolder. Sample#: Taken from thestudyfolder. Concentration (ug/mL): Taken from theMassLynx integratiosnummary. InitiaVlolume (mL): Taken from thestudyfolder. DilutionFactor: Taken from thestudyfolder. FinalConc. (ug/mL): Calculatedby dividingtheinitiavlolume from theconcentration
Ac-.achmentA: Summary Spreadsheet
ETS-8-5.1
Analysisof Serum ExtractU-sin,E,S,'MS
3M Env-'@ronmental Laboratory
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Report No. FACF TOX-030 laboratory Request Nun@cer-U2279
3M ENVIRONMENTAL
LABORATORY
EXTRACTION-OF FLUOROCHEMICAL
METHOD
POTASSIUM ]?ERFLUOROOCTANESULFONATE
COMPOUNDS
FROM SERUM FOR ANALYSIS
ELECTROSPRAY/MASS
SPECTROMETRY
OR OTHER
USING HPLC-
Method Number: ETS-8-4.0
Adoption Date:
I/"'I"
Author: Lisa Clemen, Glenn Langenburg
Revision Date:
Approved By: Laboratory Mana-er/
c Date
Gro/up Leader
4 T e@c@nical Review-er
Date Date
1.0 SCOPE AND APPLICATION 1.1 Scope: This method isforthe extractionof potassium perfluorooctanesulfonate(PFOS)
or other fluorochemical compounds from serum.
1.2 Applicable compounds: Fluorochemical surfactants or other fluorinatedcompounds.
1.3 Ntatrices: Rabbit,rat,bovine, monkey, and human serum or otherfluidsas designated in the validationreport.
Word 97 SR- I 3M Environmental Laboratory
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2.0SUNIMARY OF METHOD
2.1 This method describes the procedure for extractingpotassium perfluorooetanesulfonate (PFOS) or other fluorochemical surfactantsfrom serum using an ion pairingreagent and 5.0 niL of methyl-tert-butyelther(MtBE). In thismethod, seven fluorochemicalswere extracted:PFOS, PFOSA, PFOSAA, ETFOSE-OH, PFOSEA, M556, and surrogate standard (see @7.0Deflnitions).An ion pairing reagent isadded to the sample and the analyte ion pair ispartitionedintoMTBE. The MTBE extractisremoved and put onto a
nitrogen evaporator untildry. Each extractisreconstitutedin 1.0ml of methanol, then
filteredthrough a 3 cc plasticsyringeattached to a 0.2 @im nylon filterinto class autovials.
3.0 DEFINITIONS 3.1 PFOS: pert-luorooctanesulfonat(eanion of potassium salt)CgFl7SO33.2 PFOSA: perfluorooctane sulfonylamide C8Fl7SO2NH,
3.3 PFOSAA: perfluorooctane sulfonylamido (dthyl)acetateC8Fl7SO-,N(CH,CH3)CH2CO'--
3.4 ETFOSE-OH: 2(N-ethylperfluorooctanesulfonam ido)-ethylalcohol CsF17SO2N(CH2CH3)CH2CH20H
3.5 PFOSEA: perfluorooctanesulfonylethylamide C8Fl7SO,N(CHICH3)H
3.6 M556: C8Fl7SO2N(H)(CH2COOH)
3.7 Surrogate standard: IH- IH-2H-2H perfluorooctanesulfonicacid
4.0 WAR@NINGS
AND CAUTIONS
4.1 Health and safety warnings
4.1.1 Use universalprecautions,especiallylaboratorycoats,goggles, and gloves whcn handling animal tissue,which may contain pathogens.
5.0 INTERFERENCES
5.1 There are no interferencesknown at thistime.
6.0 EQUIPMENT 6.1 The following equipment isused while performing thismethod. Equivalent equipment is
acceptable. 6.1.1 Vortex mixer, VWR, Vortex Genie 2 6.1.2 Centrifuge,Mistral 1000 or IEC 6.1.3 Shaker, Eberbach or VWR 6.1.4 Nitrogen evaporator,Organomation 6.1.5 Bala-nce( 0.100 c,)
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Extractionof PFOS from Serum
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7.0 SUPPLIES AND MATERIALS
7.1 Gloves 7.2 Eppendorf or disposablepipettes 7.3 Nalgene bottlesc,apableofholding250 mL and I L 7.4 Volumetric flasks,glass,typeA 7.5 I-CHEM vialsg,lass,40 mL glass 7.6 Centrifugetubes,polypropylene,15 mL 7.7 Labels 7.8 Oxford Dispenser- 3.0to 10.0ml 7.9 Syringes, capable of measuring 5 pL to50 pL 7.10 Graduated pipettes 7.11 Syringes,disposableplastic3,cc 7.12 Syringefilternsy,lon,0.2 pm, 25 mm 7.13 Timer 7.14 Crimp cap autovialsand caps 7.15 Crimpers Note: Priortousingglasswareand bottlesr,inse3 timeswithmethanol and 3 timeswith
Milli_QTM water. Rinse syringesa minimum of 9 times with methanol, 3 rinsefsrom 3 separatevials.
8.0 REAGENTS AND STANDARDS 8.1 Type Ireagnt grade water,Milli-QTM or equivalent,allwater used inthismethod should
be Milli-(@TIMwater and may be provided by a Milli-Q TOC PlusTNi system 8.2 Sodium hydroxide(NaOH), J.TBaker orequivalent 8.3 Tetrabutyalmmonium hydrogen sulfate(TBA)K,odak orequivalent 8.4 Sodium carbonate (Na2CO3), J.T.Baker or equivalent 8.5 Sodium bicarbonate(NaHC03), J.T. Baker or equivalent 8.6 rvtethyl-T-ButEytlher,Omnisolv, glassdistilleodr HPLC grade 8.7 Methanol,Omnisolv, glassdistilleodrHPLC grade 8.8 Serum or blood,frozenfrom supplier 8.9 Fluorochemicalstandards
8.9.1 PFOS (3M SpecialtCyhemical Division)m,olecularweight= 538 8.9.2 PFOSA (3M SpecialtyChemicalDivision)m,olecularweight= 499 8.9.3 PFOSAA (3M SpecialtyChemicalDivision)m,olecularweight= 585 8.9.4 ETFOSE-OH (3M SpecialtCyhemical Division)m,olecularweight= 570
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8.10 8.11
8.9.5 PFOSEA (3M SpecialtyChemical Division),molecularweight= 527
8.9.6 M556 (3M SpecialtyChemical Division),molecularweight = 557
8.9.7 Surrogate standard:4-H, perfluorooctanesulfonicacid (I-H,I-H, 7--H,2-H C8Fl3SO3H) molecular weight = 428
8.9.8 Other fluorochemicals,as appropriate
Reagent preparation
8.10.1 10 N sodium hydroxide (NaOH): Weigh approximately 200 g NAOH. Pour intoa 1000 mL beaker containing500 niL MillI_QTM water,mix untilallsolidsare dissolved.Store ina I L Nalgene bottle.
8.10.2 1 N sodium hydroxide(NaOH): Dilute10 N NAOH 1:10. Measure 10 mL of 10 N NAOH solutionintoa 100 mL volumetricflaskand diluteto volume using Milli-QTm water. Storeina 125 mL Nalgene bottle.
8.10.3 0.5 M tetrabutyalmmonium hydrogen sulfate(TBA): Wei&@ approximately 169 g of TBA intoa I L volumetriccontaining500 mL Milli-Q' water.Adjustto pH 10 using approximately44 to 54 mL of 10 N NAOH (While adding the lastmL of NAOH, add slowly because thepH changes abruptly).Diluteto volume with
Milli-QwTaMter. Storein a I L Nalgene bottle.
8.10.3.1TBA requiresa check priorto each use to ensure pH = 10. Adjust as needed using I N NAOH solution.
8.10.4 0.25 i'vstodium carbonate/sodiumbiIcarbonatebuffer(NA,CO ,/NallC03):Weigh approximately26.5 g of sodium carbonate(Nal-C03)and -2 1.0 of sodium bicarbonate(NaHC03) intoa IL volumetricflaskand brinc,tovolume with MilliQTm water. Storein a I L Nalgene bottle.
Standards preparation
8.11.1 Prepare PFOS standardsforthestandard curve.
8.11.2 Prepare otherfluorochemicalstandards,as appropriate.Multicomponent fluorochemicalstandardsare acceptable(forexample, one working standard solutioncontaining1.00 ppm PFOS, 1.02 ppm PFOSA, 0.987 ppm PFOSAA, and 1.10 ppm EtFOSE-OH.)
8.11.3 Weigh approximately 100 mg of PFOS intoa 100 ml volumetricflaskand record the actualweight.
8.11.4 Bring to volume with methanol for a stock standardof approximately 1000 ppm (@iglml).
8.11.5 Dilutethe stocksolutionwith methanol fora working standard I solutionof approximately 50 ppm.
8.11.6 Diluteworking standardI with methanol fora working standard2 solutionof approx. 5.0 ppm.
8.11.7 Diluteworking standardI with methanol fora working standard3 solutionof approx. 0.50 ppm.
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8.12 Surrogate stockstandard preparation
8.12.1Weigc@h approximately50-60mg of surrogatsetandardI-H,I-H, 2-H, 2-H, C8Fl3SO3H intoa 50 ml volumetric flaskand record the actualweight.
8.12.2 Bring to volume with methanol for a surrogatestock of approximately 1000- 1200 PPM.-
8.12.3 Prepare a surrogateworking standard. Transfer approximately I ml of surrogate stock to a 10 ml volumetric flaskand brinc,to volume with methanol for a working standard of 100 ppm. Record the actualvolume transferred.
9.0 SAMPLE HANDLING 9.1 All samples are-receivedfrozen and must be kept frozen untilthe extractionisperformed.
10.0 OUALITY CONTROL
10.1
Method blanks and matrix blanks 10.1.1 Extracttwo 1.0ml aliquotsof Milli_QTM water following thisprocedure and use
as method blanks.
10.2
10.1.2 Extract two 1.0mL aliquotsof the serum following thisprocedure and use as matrix blanks. See 11.1.4.
Matrix spikes
10.2.1 Prepare and analyze matrix spike and matrix spike duplicatesamples to determine the accuracy of the extraction.
10.2.2 Prepare each spike using a sample chosen by the analyst,usually the control matrix received with each sample set.
10.2.3 Expected concentrationswillfallin the mid-ran0ae of the initiaclalibrationcurve. Additional spikes may be included and may fallin the low-ran-e of the initial
calibrationcurve.
10.2.4 Prepare one matrix spike and matrix spike duplicateper 40 samples, with a minimum of 2 matrix spikes per batch.
10.3 Continuing calibrationchecks
10.3.1 Prepare and analyze continuing calibrationcheck samples to ensure the accuracy of the initiaclalibrationcurve. Ifthe percent differencebetween the initiaclurve
and the continuinCg) check differby >30%, re-analyzesamples analyzed afterthe lastacceptable check.
10.3.2 Prepare one continuing check per group of 10 samples. For example, ifa sample set= 34, four checks are prepared and extracted.
10.3.3 Prepare each continuing calibrationcheck from the same matrix used to prepare the initiaclurve.
10.3.4 The expected concentrationsfallwithin the mid-ranc0e of the initiaclalibration curve, Additionalspikes may be included thatfallin thelow-range of the initial
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ETS-8-4.0 Extractionof PFOS from Serum
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calibrationcurve. This isnecessaryifthe analystmust quantitateusing only the low end of the calibratiocnurve (forexample, 5 ppb - 100 ppb, ratherthan 5 ppb - 1000 ppb).
11.0 CALIBRATION AND STANDARDIZATION
11.1 Prepare matrix calibrationstandards
11.1.1 TransferI mL of serum toa 15 mL centrifugetube.
11.1.2 Ifmost sample volumes are lessthan 1.0mL, extractstandardswith matrix volumes equal to the sample volumes. Do not extractlessthan 0.50 mL of matrix. Record each sample volume on theextractionsheet.
11.1.3 While preparinga totalof twenty aliquotsin 15 ml centrifugetubes,mix or shake between aliquots.
11.1.4 Two I mL aliquotso,r otherappropriatevolume, serveas matrix blanks. Typicallyuse the standardconcentrationsand spikingamounts listed'inTable 1,at the end of thissection,to spike,in duplicate,two standardcurves,fora totalof eighteenstandards,two matrixblanks,and two method blanks.
11.1.5 Refer to validationreportETS-84.0 & ETS-8-5.0-V-1, which liststhe working ranges and the LinearCalibrationRange (LCR) for calibratiocnurves.
11.1.6 Use Attachment D as an aid incalculati0ngtheconcentrationsof the workingt, standards.See Section13.0 to calculateactualconcentrationsof PFOS in calibrationstandards.
11.2
To each standard,blank,or continuingcheck, add appropriateamount of surrogate working standardfor the concentrationto fallwithin thecalibratiocnurve range 5 ppb 1000 ppb.
11.3 Extractspiked matrixstandardsfollowing 12.6-12.16of thismethod. Use thesestandards toestablisheach initiaclurve on the mass spectrometer.
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Table1
Approximate spikingamounts forstandardsand spikes
Usi g 1.0ml ofmatrix
Working standard
Approx. finalconc. of
(approx.conc.)
analyteinmatrix
Blank
0.500 ppm
10
0.005 ppm
0.500 ppm
20
0.010 ppm
5.00 ppm
5
0.025 ppm
5.00 ppm
10
0.050 ppm
5.00 ppm
20
0.100 ppm
5(70 ppm
0.250 ppm
50.0 ppm
10
0.500 ppm
50.0 ppm
15
0.750 ppm
F- 50.p0pm
20
1.00 ppm
12.0 PROCEDURE
12.1 Obtain frozensamples and allow to thaw.
12.2
Vortex mix for 15 seconds,thentransfer1.0mL or otherappropriatevolume to a 15 mL polypropylene centrifugetube.
12.3 Return samples to freezerafterextractionamount has been removed.
12.4 Record the volume on the extractionworksheet.
12.5 Label the tube with the studynumber, sample ED, date and analystinitialsS.ee attached worksheet fordocumenting the remaining steps.
12.6 Spike allsamples, includingblanksand standards,ready forextractionwith surrogate standard as describedin 11.2.
12.7
Spike each matrix with the appropriateamount of standard as described in 11.1,or Table I in thatsection,forthe calibrationcurve standards. Also prepare matrix spikes and continuing calibratiosntandards.
12.8 Vortex mix thestandardcurve samples, matrixspike samples, and continuingcalibration samples for 15 seconds.
12.9 To each sample, add I mL 0.5 M TBA and 2 mL of 0.25,M sodium carbonate/soduim bicarbonatebuffer.
12.10 Using an Oxford Dispenser,add 5 mL methyl-tert-butyelther.
12.11 Cap each sample and put on the shaker for20 minutes.
12.12 Centrifugefor20 to 25 minutes atapproximately3500 rpm, untillayersare well separated.
12.13 Remove 4.0 mL of the or0uaniclayerto a clean 15 mL centrifugetube.Label thisfresh tube with the same informationas in12.5.
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12.14 Put each sample on the analyticanlitrogenevaporatoruntildry,approximately I to 2 hours.
12.15
Add 1.0mL or otherappropriatevolume of methanol to each centrifugetube usinZgD a graduated pipette.Methanol volume toadd equalsthe initiavlolume of sample used for
the extraction.
Note: Ifthe initiavlolume islessthan0.500 mL thefinalmethanol volume willequal 1.0mL.
12.16 Vortex mix for30 seconds.
12.17 Attach a 0.2 pm nylon mesh filtetroa 3 cc syringeand transferthe sample to thissyringe. Filterintoa 1.5mL glassautovialor low-volume autovialwhen necessary.
12.18 Label the autovialwith the studynumber, animal number and gender,sample timepoint, matrix,finalsolvent,extractiondate,and analyst(s)performing.t,h.eextraction.
12.19 Cap and store=tracts atapproximately4 *C untilanalysis.
12.20 Complete the extractionworksheet,attachedtothisdocument, and tape inthe study notebook or includein studybinder,as appropriate.
13.0 DATA ANALYSIS AND CALCULATIONS
13.1 Calculations
13.1.1 Calculateactualconcentrationsof PFOS, or other applicablefluorochemical,in calibratiosntandardsusing thefollowingequation:
mL of standardx concentrationof standard(uLy/mL) mL of standard+ mL of surrogatestandard+ initiamlatrixvolume (rnL)
FinalConcentration(@tg/mL)of PFOS inmatrix
14.0 METHOD PERFORMA.NCE
14.1 The method detectionlimit(MDL) isanalyteand matrixspecific.Refer to N4DL report forspecificMDL and limitof quantitatio(nLOQ) values(seeAttachments B and C).
14.2 The followingqualitycontrolsamples areextractedwith each batchof samples to evaluatethe qualityof theextractionand analysis.
14.2.1 Method blanks and matrixblanks.
14.2.2 Matrix spikeand matrixspikeduplicatesamples to determine accuracy and precisionof theextraction.
14.2.3 Continuing calibratiocnheck samples to determine the continued accuracy of the initiaclalibratiocnurve.
15.0 POLLUTION PREVENTION AND WASTE MANAGEMENT
15.1
Sampie waste isdisposed inblohazard containers,flammable solventwaste isdisposed in
hi1g. h BTU containersa,nd used glasspipettewaste isdisposed in broken glasscontainers locatedinthe laboratory.
3M Environmental Laboratory
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16.0 RECORDS
16.1
Complete the extractionworksheet attachedto thismethod, and tape in the study
notebook or include in the 3-ring study binder, as appropriate.
17.0 ATTACHNIENTS
17.1 Attachment A. Extraction worksheet
17.2 Attachment B, MDLJLOQ
values and summary
17.3 Attachment C, Calibration standard concentration worksheet
18.0 REFERENCES 18.1 The validation report associated with thismethod is ETS-8-4.0 & 5.0-V-1.
19.0 AFFECTED DOCUMENTS
19.1
ETS-8-5.0, "Analysis of Serum or Other Fluid Extracts for Fluorochemicals using HPLC-EL ec trospray Mass Spectrometry"
20.0 RF-VISIONS
Revision Number
Reason For Revision
Revision Date
3M Environmental
Laboratory
ETS-8-4.0 Extractionof PFOS from Scruni
Pa-e 9 of*13 Page 99
3m Medical Department
S@udy: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
ExtractionWorksheet ETS-8-4.0
Studv #/matrix SurrogateStd approx. ppm actual PPM
FC-Mix approx.0.5 ppm actual PPM
FC-@Mix approx.5 ppm actual PPM
FC-Nlix approx.50 ppm actual PPM
Date and Initialis*or
Std.or Comments
'.Studyntimherwhere thenriginnwlorkghe,.fi-gl.ntciteri
B13nk
Std
Serum ExtractionNlethod
3mount
mL Date & Initials
Vortex 155ec.
Pipette.MatriN
Volume
mi
PipettIernlof 0.5M TBA, pH 10.
Std.#
Pir)ett2emlof0.25Na,CO,/0.25MNAHCO, buffer Std,$t
Dispense5 ml of methyl-t-buteytlher
TN-A-
Shake 20 min.
Centrifuiz2e0-25 min.
Centrifueser)ced:
Remove a 4 mL aliquot of oreanic laver Puton NicroeenEvaporatotrodryness Evaporator#:
T-.mverature:
Add methanol
Volume
mi
7,N-A--
Vortex30 sec.
Filteursin2a 3ccB-D syrinizweitha 0.2Limfilteirntoa 1.5ml autosamr)lveial .MSIMSD/- Cont. Checks: Spiked - uL of a --- ppm std(
.)fora finalconcentratioonf-
ppm. NIS/MSD used sample
. Cont.Checks used same matri.a-s forsidcurve.
S,,jrrogSattaendardS:piked- uL ofa- ppm std(
)to allsamples,standards.indbl@inks
AttachmentA 3M Environmental Laboratory
ETS-8-4.0 Extractioonf PFOS from Scruiii
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Report No. FACT TOX-030 laboratory Request Number-U2279
MDLFLOQ
alues for rabbitserum
Compound
MDL (ppb)
LO,Qpb, Linear CalibrationRange (LCR)
(p
Approximate concentrationsto be used forpre@ppaarriitn7ghethe
I
Standard CalibrationCurve
PFOS
4.76
15.2 5 ppb - 1000 ppb
P FO SA
2.89
9.1 5 ppb - 10 00 ppb
PFOSAA
2.94
9.33 5 ppb - I000_ppb
ETFOSE-OH
13.2 41.9 5 ppb - 1000 ppb
M556 PFOSEA
12.6 11.1
40.2 5 ppb - 1000 ppb 35.4-"F5-@-pb--1000 ppb
MDL/LOQ valuesinrat,bovine,monkey, and human serum were notstatisticaldleytermined.Two
curvesin each of thesethreematriceswere extractedand analyzedwith the rabbitserum curves to determine equivalence.Responses intherat,bovine,and monkey were equivalentto therabbit responses,therefore,thei!M.DrL and LOQ willbe the same valuesas determined inrabbitserum.
Pleasesee Attachment C (LOQ Summary) and MDL studyinETS-8-4.0 & 5.0-V-I forfurther information.
[on Pairing Extraction of Fluorochemicalsfrom Serum and Analysis by APIfL'VIS(MS) Summary Table:Limitsof Quantitation
Compound PFOS PFOSA PFOSAA ETFOSE-OH* PFOSEA @M556
NFDL and LOQ
I Matrix
NIDL
All
4.76
All
2.89
All
2.94
All
13.2*
All
12.6
All
11.1
areestimatesonly forETFOSE-OH.
LOQ
Low std
15.2
25.1
1
9.19
25.0
9.33---@
25.0
41.9* 1
50.0
40.2
25.0
35.4-----F-25.0
itd 1002 1000 998 10 0 1000 10()0
AttachmentB: MDL/LOQ 3M Environmental Laboratory
ETS-8-4.0 ExtractioonfPFOS from Seruin
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Compou d:PFOS
Prepared
3erum
rangeof
matrix standards (pb) (ne/mL)
@R,bb,t 1 1.00-1002
Range of LCR from Range of LCR from Range of LCR from
averaue ave curve low std
low std
highsid
hieyhsid
curve
curve
curve
curve
curve I
(ppb)(ng/mL) (Ppb)(ng/rnL)(ppb)(niz/mL)@pob)(nL/mL) @ppb)(na/mL)..(pob)(nL/inL)
].DO- 1002 25.1- 1002 5.01-250 5.01-250 100-1002 100- 1002
Compound: PFOSA
Prepared
Serum
rangeof
matrix standards (i)t()nbW)mL)
Range of LCR from Range of LCR from Range of LCR from
average ave curve low std
low std
high std
highstd
curve
curve
CUTVE
curve
curve
(ppb)(ng/mL) (ppb)(ng/mL) (oc)b()ne/mL) (Ppb)(ng/mL) (Ppb)(ne/mL) (ppb)(ne/iTiL)
Rabbit 1.00-10()0 1.00- 1000 10.0-1000 5.00- 100 5.00- 100 25.0-10()0 25.0 - 1000
Compound: PFOSAA
I Prepared Range of LCR from Range of LCR from Range of LCR from
Serum
rangeof
average ave curve low std
low std
high std
high std
matrix standards
curve
curve
curve
curve
curve
(ppb)(ng/mL) (ppb)(ngjml) (pob)(nWmL) _(_Mb)(n-g@mL)(ppb)(ng/mL) (pi)(bn)g/mL) @p pb)(nYL/mL)
I.C)-O 998 1.()0-998 25.0-998 4.99-250 9.99-250 49.9-998 99.8-998
Compound: ETFOSE-OH
Prepared Range of
Serum
rangeof
average
matrix
standards
curve
(ppb)(np/mL) (pDb)(ng/mL)
Rabbit I 1.00- 1000 1.00- 1000 1
LCR from ave curve
(pDb)(ng/mL)
50.0- 1000
Range of low std
Curve
(ppb)(ng/ML)
5.00- 100
LCR from low std curve
(p b) (ne/mL
10.0-loo ' 1
Range of
hi-hstd
c@-Irve
(ppb@ (ne/rnL) I
50.0- 100
-
LCR from high std curve
(ppb)(nWinL)
10- 100
Compound: PFOSEA
Prepared
Serum
rangeof
matrix standards 1 (ppb)(np/mL)
Range of LCR from average ave curve curve
(ppb)(np,/mL) (ppb)(ng/mL)
Rabbit 1.00-loco 1.00-10()0 25.0-1000
Range of LCR from Rancyeof LCR from
low std
low std
high std
high std
curve
curve
curve
curve
2pb) (ne/TnL) (ppb)(np-,/tnL(),,)p(bn)g/rTiL) b n1me0@L0),0L)
5.00-250 5.00-250 50- 1000 50-
Compound: N[556
Prepared
Serum
rangeof
matrix standards
(Ppb@ (neJmL)
Rabbit 1.00- 1000
Range of average
curve
(pob)(nz/mL)
LCR from ave curve
(pob)(nz/mL)
Range of LCR from
low std
low std
curve
curve
(2ph)(nv-/mL) (ppb)(np/mL)
Ran-e of hieh std curve
fppb)(ng@mL)
1.00- 1000 25.0- 1000 5,00- 100 5.00- 100 foo- 1000
LCR from highstd curve
(ppb)(ng/mL)
100- 1000
AttachmentB: %IDL-fLOQ 3M Env@Lronme.-ita7-,Laboratory
ETS-8-4.0 Extractioonf PFOS from Serum
Pi,-,1c2 of 13 Page 102
3m Medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
Ion PairStandard Curves - Fluids
Prep date(s):
Standard number:
Analyte(s):
Equipment number:
Sample matrix:
Finalsolventand TN:
Blank fluid/identifier:
Method/revision:
Targetanalyte(s):
FC mix std approx. 0.500ppm:
FC mix std approx. 5.00ppm:
FC mix stdapprox. 50.0ppm:
Surrogate std approx. 100 ppm:
Actual concentrationsofstandards inthe FC mix
PFOS
PFOSA PFOSAA ETFOSE PFOSEA
Std cone Std conc S@d conc Std conc Std conc
ug/mL ug/mL
ug/mL
ug/mL ug/niL
0.500 0.507
0.532
0.501
0.521
0.5()0 0.507
0.532
0.501 0.521
5.00
5.07
5.32
5.01
5.21
5.00
5.07
5 .32
5.01
5.21
5--.-0--0--------5--.07
5.32
5.01
5.21
50.0
50.1
53.2
50.1 -5'2-1.
50.0
50.1
53.)
50.1
52.1
-.7
50.0
50.1 - ---5-3-.-2---- 50.1
52.1
50.0
50.1
53.2
50.1 1 52.1 1
M556 Std conc ug/mL 0,501 0.501
5.01 5.01 5.01 50.1 50.1 50. 1_ 50.1
All Aml spikedmL 0.010 0.020 0.005--0.010 0-.-0-2-0---0.005 0.010 0.015 0.020
All Finalvol
ML 1.015 1.025
1.015 1-..@0-I2.5.--.-@ 1.010 1.015 1.020 1.025
Calculated concentrationsof standards in the sample matrix
PFOS
PFOSA
Finalconc Finalconc
ng/mL
ng/mL
PFOSAA Finalconc
nLJmL
ETFOSE PFOSEA
N1556 Surrogate
Finalconc Finalconc Finalconc Sidconc
ng/mL
ng/mL
ne/rn-L niz/mL
4-.-9-3--------5-.-00 9.76 1 9.89 24.8 1 25.1 49 .3
5.24 1 4.94
5.01
10.4 1 9.78
9.93
5.13
100
F-
26.3 1 24.8
25.2
25.8 Surrogate
49.4
50.1
Finalconc
97.6
98.9
104
97.8
99.3
248
251 1 263
248
252
493
500
524 i 494
501
102
ng/mL
258
500
513
735
746
749
98 9
1038
978
993
1017
All Am'[ spiked
ML
0.005
Validatedranges approximate concentrations
Serum
PFOS
PFOSA
PFOSAA
Rabbit
25.1-1002 1 25.0-tOOO 1 25.0-998
1
Bovine
Estimatesoniv.Use valuesforrabbie.
Rat
Estimatesonly.Use valuesforrabbit,
\4onkev
Estimatesonlv.Use valuesforrabbit.
;
Human
Estimatesonly.Use valuesforrabbit.
ETFOSE-OH 1 50.0-1000 1
PFOSEA 25 0-1000
N1556 -25@0-1000
AttachmentC: IonPairStandardCurves
ETS-8-4.0
ExtractioonfPFOS from Serum
3M Environmental Laboratory
Page 13 of 13 Page 103
3m Medical Departmer-t Study: T-6295.7
Repor@-- No. FAC-L TOX-030 laboratory Request Number-U2279
3M ENVIRONMENTAL
LABORATORY
METHOD
ANALYSIS
OF POTASSIUM PERFLUOROOCTANESULFONATE
OR
FLUOROCHEMICALS
IN SERUM EXTRACTS USING
HPLC-ELECTROSPRAY/MASS
SPECTROMETRY
OTHER
Method Number: ETS-8-5.0
Author: Lisa Clemen, RobertWynne Approved By:
Adoption Date: Revision Date:
Lab&t@t@ry',Man@o,er
Date
Group Leader
. .3-@fi, CLr,,@,
Technical Reviewer
Date
31
Date
1.0 SCOPE AND APPLICATION 1.1 Scope: This method isforthe analysisof extractsfrom serum forfluorochemicalsurfactants
usin0-HPLC-electrospray/mass spectrometry.
1.2 Applicable Compounds: Fluorochemical surfactants or other fluorinated compounds, or other ionizablecompounds.
1.3 Matrices: Rabbit,rat,bovine,monkey, and human serum, or otherfluidsas designatedin the validationreport.
Word 97 SR-t 3M Environmental
ETS-8-5.0 AnalysisofSerum ExtractUsin- ESA,IS
Laboratory
Page I of'9 Page 104
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Report No. FACT TOX-030 laboratory Request Number-U2279
2.0 SumMARY OF METHOD
2.1 This method describesthe analysisof fluorochemicalsurfactantsextractedfrom serum, using HPLC-electrospray/mass spectrometry,or similarsystem as appropriate.The analysisisperformed by monitoringa singleion characteristiocf a particular fluorochemical,such as the potassiumperfluorooctanesulfonat(ePFOS) anion,M/z= 499. Samples may a]so be analyzed usingan API-ESIMS/'IvISsystem tofurtherverify compound iden'tification.
3.0 DFFINITIONS
3.1Atmospheric Pressure Ionization(API):The Micromass QuattroIIsystems allow for variousmethods of ionizationby utilizinvgarioussources,probes,and interfaces.These includebut are not limitedto:ElectrosprayIonization(ESI),Atmospheric Pressurechemical Ionization(APcl),thermospray, etc.The ionizatiopnrocessin thesetechniquesoccursat atmospheric pressure(i.en.ot under a vacuum).
3.2 Electrospray Ionization(ES, ESI): a method of ionizationperformed at atmospheric pressure,whereby ionizationoccursthrough theproductionof tinychar-ed dropletsina strongelectricaflield.
3.3Mass Spectrometry, Mass Spectrometer (MS), Tandem Mass Spectrometer (MS/INIS): The API Quattro Ilsystems areequipped with quadrupole mass selectivedetectors.Ions are selectivelydiscriminatedby mass tocharge ratio(nl/z)and subsequentlydetected.A single MS may be employed forion detectionor a series(MS/i'vlSf)ormore specificfracmentation information.
3.4Conventional vs.Z-spray probe interface:The latestmodels of Micromass QuattroH systems (post1998) utilizae "Z-spray"conformation.The spray emittedfrom a probe is orthogonalto the cone aperture.In theconventionalconformation itisaimed directlyat the cone aperture,afterpassingthrough a tortuouspathway in thecounter electrode.Though the configurationisdifferentt,he methods of operation,cleaning,and maintenance are the same. However, Z-spray components and conventionalcomponents are not compatible with one another,but only with similarsystems (i.eZ.-spray components arecompatible with some otherZ-spray systems,etc.)
3.5 Mass Lynx Software: System softwaredesiCg)ned forthe specificoperationof theseQuattro Ilsystems. CurrentlyNlassLynx has Windows 95 and WindowsNT 4.0 versions.All versionsare similar.For more detailsee the manual specificto the instrument(imicromass Quattro H MassLynx or MassLynx NT USER'S GUDDE).
4.0 WAPNINGS AND CAUTIONS 4.1 Health and Safety Warnings:
4.1.1 Use cautionwith the voltagecablesforthe probe. The probe employs a voltageof approximately5000 Volts.
4.1.2 When handling samples or solventswear appropriateprotectivegloves,eyewear, and clothing.
3M Environmental
ETS-8-5.0 AnalysiosfSerum ExtracUtsingES/@'vlS
Laboratory
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4.2 Cautions: 4.2.1 Do not operatesolventpumps above capacityof 400 bar (5800 psi)back pressure. Ifthe back pressureexceeds 400 bar,the HP I100 willinitiataeutomatic shutdown.
4.2.2 Do not run solventpumps todryness.
5.0 INTERFERENCES
5.1 To minimize interferenceswhen analyzingsamples, teflonshould not be used forsample storageor any partof instrumentationthatcomes incontactwith the sample or extract.
6.0 EOUIPMENT 6.1 Equipment listedbelow may be modified in orderto optimizethe system.
6.1.1 Micromass ElectrosprayMass Spectrometer 6.1.2 HPI 100 low pulse solventpumping system and autosampler
7.0 SUPPLIES AND MATEMALS
7.1 Supplies 7.1.1 High puritygrade nitrogengas regulatedtoapproximately 100 psi(House air system) 7.1.2 HPLC analyticalcolumn, specificstobe deteri-ninebdv the analyst 7.1.3 Capped autovialsor capped 15 ml centrifugetubes
8.0 REAGENTS AND STANDARDS 8.1 Reagents
8.1.1 Methanol, HPLC gradeor equivalent
Mill_iQ Tm
8.1.2 Milli-QT"'wAater,allwaterused in thismethod should be
" water or
equivalent,and may be providedby a Milli-Q TOC Plussystem or othervendor
8.1.3 Ammonium acetate,reagentgrade or equivalent
8.2 Standards
8.2.1 Typicallytwo method blanks,two matrixblanks,and eighteenmatrix standardsare prepared during theextractionprocedure. See ETS-8-4.0.
9.0 SAMPLE HANDLING
9.1 Fresh matrix standardsare preparedwith each analysis.Extracted standardsand samples are storedincapped autovialsor capped 15 mi centrifugetubesuntilanalysis.
9.2 Ifanalysiswillbe dela1yed,extractedstandardsand samples can be refr0igerateadt approximately 4' C untilanalysiscan be performed.
3M Environmental
ETS-8-5.0 Analysisof Serum ExtractUsing ESIMS
Laboratory
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10.0 OUALITY CONTROL 10.1 Method Blanks and Matrix Blanks
10.1.1 Analyze a rrethod blank and a matrix blank priorto each calibrationcurve.
10.2 Matrix Spikes
10.2.1 Analyze'a matrix spikeand matrix spikeduplicateper fortysamples. With a minimum of 2 spikesper batch.
10.2.2 Expected spikeconcentrationswillfallin the mid-range of the initiaclalibration curve. Additionalspikeconcentrationmsay fallin thelow-rangeof the initial calibratiocnurve.
10.2.3 See Secti-on13 tocalculatepercentrecovery.
10.3 Continuing Calibration Checks
10.3.1 Analyze a mid-range calibratiosntandardafterevery tenthsample. Ifa significant change ( 30%) in peak areaoccurs,relativeto the initiasltandardcurve,stop the run.Only those samples analyzed before the lastacceptablecalibrationstandard willbe used. The remaining samples must be reanalyzed.
10.3.2 See Section13 to calculatepercentdifference.
11.0 CALIBPATION A.ND STANDARDIZATION
11.1 Analyze the extractedmatrix standardspriorto and followingeach setof extracts.The
mean of two standardvalues,ateach standardconcentration,willbe plottedby linear regression(r2)forthe calibratiocnurve usingMassLynx or othersuitablesoftware.
11.2
The
2
r value forthe data should be 0.990 or greater.Lower
valuesmay
be acceptableatthe
discretionof the analystand approvalof the Pr01jectLead.
11.3 Ifthe curve does not meet requirements,perform routinemaintenance or reextractthe standardcurve (ifnecessary)and reanalyze.
11.4
For purposes of accuracy when quantitatinglow levelsof analyte,itmay be necessary to use the low end of the calibratiocnurve ratherthan the fullrange of the standardcurve. Example: when attemptingtoquantitateapproximately 10 ppb of analyte,generatea calibrationcurve consistingof thestandardsfrom 5 ppb to 100 ppb ratherthan the fulI range of thecurve (5 ppb to 1000 ppb). This willreduce inaccuracyattributetdo linear regressionwellyhtingof high concentrationstandards.
12.0 PROCEDURES
12.1 Acquisition Setup
12.1.1 Click on startbutton in the Acquisition Control Panel. Set up a sample list.Assign a filenameusing MO-DAY-last digitof year-sample number, assigna method (MS) foracquirlnc,a,nd typein sample descriptions.
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Labcratory
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12.1.2 To createa method clickon scan buttonin the Acquisitioncontrolpanel and select SIR (SingleIon Recording)or MRM. Set IonizationMode as appropriateand mass to 499 or other appropriatemasses. A fullscan isusuallycollectedalong with the SIRS. Save acquisitionmethod. IfMS/'YIS instrumentsareemployed, additional product ion fr-agmentatioinnformationmav be collected.See Micromass MassLynx GUIDE TO DATA ACQUISIT@ON foradditionalinformationand MR.M (MultipleReactionMonitoring).
12.1.3 Typicallythe analyticablatchrun sequence beginswith a setof extractedmatrix standardsand ends with a setof extractedmatrix standards.
12.1.4 Samples are analyzed with a continuingcalibratiocnheck injectedafterevery tenth sample. Solvent blanksshould be analyzed periodicalltyo monitor possibleanalyte carryoverand are not consideredsamples but mav be included as such.
12.2 Using the Autosampler
12.2.1 Set up sample trayaccordingto the sample listprepared in Section12.1.1.
12.2.2 Set-up the HPI 100/autosampleratthefollowinCg, conditionsor atconditionsthe analystconsidersappropriatefor optim'alresponse.Record actualconditionsin the instrur-nenltogbook:
12.2.2.1Sarrplesize= 10 gL injectionwith a sample wash
12.2.2.2Inject/sample= 1
12.2.2.3Cycle time = 13.5 minutes
12.2.2.4Solvent ramp
Time
0.00 min. 7.5 min. 11.0 min. 11.5 min.
MEOH
40% 90% 90% 40%
2.0 mM Ammonium acetate
60% 1017c 10% 60%
12.2.2.5Pressthe "Start"button.
12.3 Instrument Set-up
12.3.1 Refer toETS-9-24.0 formore details.
12.3.2 Check the solventlevelin reservoirsand refililfnecessary.
12.3.3 Check the stainlessteelcapillaryatthe end of the probe. Use an eyepiece tocheck the tip.The tipshould be flatwith no jagged edges. Ifthe tipisfound to be unsatisfactoryd,isassemblethe probe and replacethe stainlessteelcapillary.
12.3.4 Set HPLC Pump to "On". Set the flow to 10 - 500 uLJmin or as appropriate. Observe dropletscomingZ2 outof thetipof theprobe. Allow toequilibratfeor approximately 10 minutes.
ETS-8-5.0 AnalvsisofSerum ExtractUsine ES/NIS
3M Env4-ronmental Laboratory
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Report No. FACT TOX-030 laboratory Request Number-U2279
12.3.5 Turn on the nitrogen.A finemistshould be expelledwith no nitrogenleakino, around the tipof the probe.
12.3.6 The instrumentuses theseparametersatthe followingsettinas.These settincymsay change in order to optimize theresponse:
12.3.6.1Drying gas 250-400 liters/hour 12.3.6.ZESI nebulizinggas 10-15 liters/hour 12.3.6.3HPLC constantflow mode flow rate 10 - 500 @il-/m'in 12.3.6.4Pressure<4GO bar (Thisparameter isnot set,itisa guide to ensure the
HPLC isoperatingcorrectly.)
12.3.7 Carefullyguide the probe intotheopenina. Insertprobe untilitwillnot go any furtherC.onnect the voltagecablesto the0probe.
12.3.8 Record tune parameters in the instrumentloogl
12.3.9 Using the cross-flowcounterelectrodeinthe ES/MS source isrecommended for theanalysisof biologicalmatrices.
12.3.10CIickon startbutton in theAcquisitionControl Panel (thismay vary among MassLynx versions,see appropriateMassLynx USER'S GUDDE). Pressthe start button. Ensure startand end sample number includesallsamples to be analyzed.
13.0 DATA ANALYSIS AND CALCULATIONS 13.1 Calculations:
13.1.4 Calculatematrix spike percentrecoveriesusing the followingequation:
% Recovery
Observed Result-Background Result x 100 Expected Result
13.1.5 Calculatepercentdifferenceusing thefollowingequation:
7c Difference
ExQected Conc. - CalculatedConc. x 100 Expected Conc.
13.1.6 Calculateactualconcentrationof PFOS, or otherfluorochemical,inmatrix (pg/ml):
(ng of PFOS calc.from std.Curve.x.DilutionFactor) x (InitiaVlolume of matrix(ml)+ mi of SurrogateStandard)
FinalVolume (mL)
I g@!Z 1000 n-
14.0 METHOD PERFOR@MANCE
14.1 Method DetectionLimit(MDL) and Limitof Quantitation(LOQ) aremethod, analyte,and matrixspecific.PleaseseeETS-8-4.0,Attachment B, fora listino,f-currentvalidated MDL and LOQ values.
3M Env4@ronmental
ETS-8-5.0 Analysis of Serum Extract Using ES/NIS
Laboratory
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3m medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
14.2 Method Blanksand MatrixBlanks
14.2.1Method blanksandmatrixblankswillbe analyzedwitheachsamplesetfor possiblecontaminationorcarryover.Values are expected tofallbelow the lowest standard inthe calibratiocnurve.
14.3 Matrix Spikes
14.3.1 Matrix spikes areanalyzedwith each sample setand the percentrecoveriesare expected to fallwithin 30% of the spiked concentration.
14.4 Continuing CalibrationChecks
14.4.1 Continuing calibratiocnhecks are analyzedata minimum of afterevery 10 samples with each sample set.The percentrecoveriesare expected tofallwithin 30% of the spiked concentration.
14.5 Ifany criterialistedin the method performance sectionisn'tmet, maintenance may be per-formedon thesystem and samples reanalyzedor otheractionsas determined by the analyst.All actionswillbe documented in the instrumentrunlog,the maintenance log,or on the summary sheet with the sample results..
15.0 POLLUTION PREVENTION AND WASTE MANAGEMENT 15.1 Sample extractwaste and flammable solventisdisposed in high BTU containers,and glass
pipettewaste isdisposed in broken glasscontainerslocatedinthe laboratory.
16.0 RECORDS 16.1 Store chromatograms in the studyor projectfolder.Each chromatogCr)am must have the
followinginformationincludedeitherin the header or hand writtenon the chromatogram: study or projectnumber, acquisitiomnethod, integrationmethod, sample name, extraction date,dilutionfactor(ifapplicable)a,nd analyst.
16.2 Plot calibratiocnurve by linearregressionand storein the studyfolder. 16.3 Printsample listfrom MassLynx and tape intothe instrumentruiilolg.
16.4 Printdata integrationsummary from MassLynx and tape intothe instrumentrunlog.
16.5 Copy instrumentrunlogpaaes,includinginstrumentparametersand sample resultsa,nd storein appropriatestudy folder.
16.6 Summarize data usin- suitable software and store in the study folder. 4
16.7 Back up electronicdatatoappropriatemedium. Record instudy notebook the filename and locationof backup electronicdata.
17.0 TABLES, DIAGRAms, FLOWCHARTS, AND VALIDATION DATA 17.1 Attachment B: ETS-8-5.0 Data reportingspreadsheet. 17.2 The validationreportassociatedwith thismethod isETS-8-4.0 & 5.0-V-1.
3M Environmental
ETS-8-5.0 AnalysisofSerum ExtractUsiny ES/'%.IS
Laboratory
Pi-e 7 of 9 Page 110
3m Medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
18.0 REFERENCES
18.1 ETS-9-24.0, "Operation and Maintenance of theMicromass Atmospheric Pressure Ionization/NlasSspectrometer QuattroU Systems"
19.0 AFFECTED DOCUMENTS 19.1 ETS-8-4.0, "Extractionof Potassium Perfluorooctanesulfonateor Other Fluorochemical
Compounds from Serum forAnalysisUsing HPLC-Electrospray/Mass Spectrometry"
20.0 REvisiONS
Revision Number.
Reason For Revision
Revision Date
3M Environmental
ETS-8-5.0 Analysisof Serum ExtractUsin- ES/NIS
Laboratory
Page 8 of 9 Page 111
3m Medical
Departmen@-- S--udy: T-6295.7 Attachment A
Report No. laboratory Request
FACT TOX-030 Nurnber-U2279
Laboratory Study
Study: TestMaterial: Matrix/FinaSlolvent; iMeLhod/Revision: AnalyticalEquipment System Number: InstrumentSoftware[Version: Filename: R-Squared Value: Slope: Y Intercept: Date ofExtraction/Analys@ Date ofAnaivsis/Anaivst:
Group Dose
Sample#
Concentration ue/mL
InitiaVlol. mL
Dilution Factor
FinalCone. UL,/Ml,
SIOI)E:Taken from lineareeressioenquation. Grout)/Dose:Taken from thestudyfolder. Samv]L-#: Taken from thestudyfolder. Concentration(up-/mL):Taken fromtheMassLvnx intelratisounmmarv. InitiaVlolume (rnL):Taken from thestudyfolder. DilutionFactor: Taken fromthestudyfoldcr. FinalConc. (upJmL): Calculatebdy dividintlh,einitivaollume fromtheconcentration
3M Environmental
ETS-8-5.0 AnalysisofSerum ExtractUsin- ES/NIS
Laboratory
Page 9 of9 Page 112
3m Med@-cal Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Numbe---U2279
3M ENVIRONMENTAL
LABORATORY
METHOD
EXTRACTION OF POTASSIUM PERFLUOROOCTANESULFONATE
OR OTHER A-,NIONIC
FLUOROCHF,MICAL
SURFACTANTS FROM LIVER FOR ANALYSIS USING
HPLC-ELECTROSPRAY/MASS
SPECTROMETRY
Method Number: FACT-M-1.0
Author: Lisa Clemen Approved By:
Adoption Date: 5'1.C2. Revision Date: k)
Laboratory Manager
Date
Group Leader
Date
Technical Reviewer
Date
1.0 SCOPE AND APPLICATION 1.1 Scope: This method is for the extractionof Potassium Perfluorooctanesulfonate(PFOS) or
otherfluorochemicalsurfactantsfrom liver.
1.2Applicable Compounds: Fluorochemicalsurfactantosr otherfluorinatedcompounds.
1.3Matrices: Rabbit,-at,bovine, and monkey liversor otherliversas designatedinthe validationreport.
Microsoft 7.0.1/95
FACT-M-1.0 Extractionof PFOS from Liver
3M Env@@ronmental Laboratory
Page I of 8 Page 113
3m Medical E)epartment Study: T-6295.7
Report No. FACT TOX-C30 laboratory Request Number-U2279
2.0 SUMMARY OF NIETHOD
2.1 This method describeshow to extractpotassiumperfluorooctanesulfonat(ePFOS) or other fluorochemicalsurfactantsfrom liverusingion pairingreagentand 5.0 mLs of ethyl acetate.An ion pair-inrgeagentisadded to each sample and partitionedintoethylacetate. Four mLs of extractisremoved toa centrifugetube and put onto a nitrogenevaporator untildry. Each extractisreconstituteidn 1.0mL methanol then filteretdhrough a 3 cc plasticsyringeattachedto a 0.2 @im filteirntoglassautovials.
3.0 DEFINITIONS 3.1 None.
4.0 WARNINGS AND CAUTIONS 4.1 Health and Safety Warnings:
4.1.1 Use universalprecautionswhen handlinganimal liverst,hey may contain pathogens.
5.0 INTFRFERENCES 5.1 There are no known interferenceastthistime.
6.0 EQU[PMENT 6.1 The followingequipment isused whilecarryingout thismethod. Equivalentequipment is
acceptable.
6.1.1 Ultra-TurraxT25 Grinderforgrindingliversamples 6.1.2 Vortex mixer,VWR, Vortex Genie 2 6.1.3 Centrifuge,Mistral 1000 or IEC 6.1.4 Shaker, Eber*oach or VVY'R 6.1.5 Nitrogen Evaporator,Organomation 6.1.6 Balance
7.0 SUPPLIES AND MATERIALS 7.1 Gloves 7.2 Dissectingscalpels 7.3 Eppendorf or disposablepipettes 7.4 Nalgene bottlesc,apable of holding250 mL and I L 7.5 Glass,type A, volumetricflasks 7.6 40 mL glass I-CHE,@vtvials 7.7 Plasticsampule vials,Wheaton, 6 mL 7.8 Polypropylene centrifugetubes,15 mL 7.9 '-abeIs
FACT-M-1.0 Extractionof PFOS from Liver
Page 2 of 8
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7.10 Syringes, capable of measuring 10 @iL to 50 pL 7.11 Glass, type A, volumetric pipettes 7.12 Graduated pipettes 7.13 Electronicpipettor,Eppendorf or equivalent 7.14 Timer 7.15 Disposable plastic3 cc syringes 7.16 Filters,nylon syn'nge filters0,.2 pm, 25 mm 7.17 Cr-imp cap autovials Note: Pr-iorto using glassware and bottles,rinse3 times with methanol and 3 times with Milli-
Q' water. Rinse syringesa minimum of 9 times with methanol, 3 rinsesfrom 3 separate vials.
8.0 REAGENTS AND S@TANDAPDS
8.1 Reagents
8.1.1
Sodium Hydroxide (J.TBaker or equivalent),(NAOH) ION: weigh approximately 200 grams NAOH. Pour intoa 1000 mL beaker containing500 liter(sL) Nlilll_QTM
water,mix untilallsolidsare dissolved.Store in a I L nalgene bottle.
8.1.2
Sodium Hydroxide (J.TBaker or equivalent),(NAOH) IN. Dilute ION 1:10. Measure 10 mL of the ION NAOH solutioninto a 100 mL volumetric flaskand diluteto volume using Milli-Q"mwater. Store in a 125 mL nalgene bottle.
8.1.3
Tetrabutylammonium hydrogen sulfate(Kodak or equivalent),('FBA) 0.5M: Weigh approximately 169 grams of TBA intoa I L volumetric containing500 L Milli-Q,-" water. Adjust to pH 10 using approximately 64 mL ION NAOH and diluteto volume with Milli-Q'-"water. Add NAOH slowly while adding the lastI mL of NAOH because the pH changes abruptly. Store in a I L nalgene bottle.
8.1.3.1 TBA requiresa check priorto each use to ensure pH = 10. Adjust as needed using IN NAOH solution.
8.1.4
Sodium carbonate/Sodium Bicarbonate Buffer (J.T.Baker or equivalent), (Na,C03NaHC03) 0.25M: Weigh approximately 26.5 g of sodium carbonate (Na2CO3) and 21.0 g of sodium bicarbonate(,NaHCO,) intoa I L volumetric flask and diluteto volume with Milli-Q' water. Store ina I L nalgene bottle.
8.1.5 PFOS (3M SpecialtyChemical Division),molecular weiizht= 538.
8.1.6 Ethyl Acetate,Omnisolv, glassdistilleodr HPLC grade. 8.1.7 Methanol, Omnisolv, glassdistilleodr HPLC grade.
8.1.8 8.1.9
Liver and controlliver,receivedfrozen from testin,l,aboratory. Milli-QT4 water, allwater used in thismethod should be rvl1 111 _QTII water and ma@, be provided by a Milli-Q TOC Plus system.
8.2 Standards
8.2.1 Prepare PFOS standards forthe standard curve.
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8.2.2 Weigh approximately 100 mg of PFOS intoa 100 mL volumetricflaskand record the actualweight.
8.2.3 Bring to volume with methanol fora stockstandardof approximatelv 1000 ppm (gg/mL).
8.2.4 Dilutethestocksolutionwith methanol fora working standardI solutionof approximately 50 ppm.
8.2.5 Dilutethe stocksolutionwith methanol fora working standard2 solutionof approx.5.0 ppm.
8.2.6 Dilutethe stocksolutionwith methanol fora working standard3 solutionof approx. 0.50 ppm.
9.0 SAMPLE HANDLIIN(; 9.1 All liversarereceivedfrozenand must be kept frozenuntilthe extractionisperformed.
10.0 QUALITY CONTROL 10.1 Matrix Spikes
10.1.1 Prepare and analyzematrix spike and matrix spike duplicatesamples to deter,-nine the accuracy of the extraction.
10.1.2 Prepare each spikeusingliverchosen by theanalyst,usuallya controlliver.
10.1.3 Expected concentrationswillfallinthe mid-range of the initiaclalibratiocnurve.
10.2 Continuing CalibrationChecks
10.2.1 Prepare and analyzecontinuingcalibrationcheck samples to determine the continuedlinearitoyf the i,-litciaallibratiocnurve.
10.2.2 One check isprepared per group of ten samples. For example, ifa sample set= 34, four checks are prepared and extracted.
10.2.3 Prepare each continuingcalibrationcheck from the same liverhomogeriate used to prep the initiaclur-ve.
10.2.4 The expectedconcentrationwillfallwithin the mid-range of the initiaclalibration curve.
11.0 CALIBRATION AND STANDARDIZATION 11.1 Prepare Liver Homogenate to Use for Standards
11.1.1 Weigh approximately 40 g of liverintoa 250 mL Nalgene bottlecontaining200 mLs Milli-QT'water.Grind to a homogeneous solution.
11.1.2 If40 g isnot availableu,se appropriateamounts of liverand water in keeping with a 1:5ratio.
11.1.3 See section1').0to calculatethe actualdensityof liver.
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11.1.4 Add I mL of homogeneous solutionto a 15 mL centrifugetube.Re-suspend homogeneous solutionby shaking between aliquotswhile preparinga totalof sixteenI mL aliquotsof homogeneous solutionin 15 mL centrifugetubes.
11.1.5 Two I mL aliquotsserveas matrixblanks. Use the standardconcentrationsand spikingamounts listedintable1 to spike,in duplicate,two standardcurves fora totalof fourteensamples.
Table 1 Approximate Spiking Amounts for Calibration Standards
Working Standard (Approx.Conc.)
0.50 ppm 0.50 ppm 0.50 ppm 5.0 ppm 5.0 ppm 5.0 ppm 50ppm
@iL
Approx. finalconc.of
PFOS in liver
Blank
4
0.0 10 ppm
20
0.050 ppm
40
0.100 ppm
-1-0
0.250 ppm
20
0.500 ppm
30
0.750 ppm
4
1.000 ppm
11.1.1 See section13.0 to calculateactualconcentrationsof PFOS in calibrationstandards. 11.2 Extractspiked liverhomogenates following 12.14-12.24of thismethod. Use these
standardsto establisheach initiaclurve on the mass spectrometer.
12.0 PROCEDURES 12.1 Obtain frozenliversamples. In spenttissue,note thatthe liverhas not been packaged with
other tissues. 12.2 Cut approximately I g of liverusinga dissectingscalpel. 12.3 Weigh the sample directlyintoa taredplasticsampule vial. 12.4 Record the liverweight in the studynotebook. 12.5 Label the sampule via]with thestudynumber, weight,liverID, dateand analystinitials. 12.6 Add 2.5 mLs of water to sampule vial. 12.7 Grind the sample.Put the grinderprobe in thesample and grindforabout 2 minutes,or
untilthe sample ishomogeneous. 12.8 Rinse the probe intothe sample with 2.5 mLs water using a pipette. 12.9 Take the grinderapartand cleanitwith methanol aftereach sample. Follow AMDT-EP-22. 12.10 Cap the sample and vortex for 15 seconds.
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3M Envi-ronmental Laboratory
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12.11PipetteI mL homoizenate intoa 15 mL polypropylene centrifugetube.Label the centrifuge tube with the identicailnformationas thesampule vial.(See Worksheet fordocumenting the remaining steps.)
12.12Spike liverhomogenates with the appropfiateamount of PFOS standardas describedin section11.1 or Table 1.
12.13 Pipettetwo I mL aliquotsof Milli-Q' water to centrifugetubes. These willserve as instrument blanks.
12.14Add I mL 0.5 M TBA and 2 mL of the 0.25 M sodium carbonate/sodium bicarbonate buffer.
12.15Using a volumetricpipette,add 5 mLs ethylacetate.
12.16Cap each sample and put on the shakerfor20 minutes.
12.17Centrifugefor26 to 25 minutes,untillayersare well separated.Set power on the centrifuge to approximately -'1500rpm.
12.18Remove 4 mLs of organiclayer,usinga 5 mL graduated glasspipette,to a clean 15 mL centr-ifugteube.Label thisfreshtube with th6 same informationas in 12.5.
12.19 Put each sample on the analyticalnitrogenevaporatoruntildry,approximately 2 to 3 hours.
12.20Add 1.0mL of methanol toeach centrifugetube using a graduated pipette,
12.21Vortex mix for30 seconds. 12.22Attach a 0.2 pm nylon mesh filtetroa 3 cc syringeand transferthe sample tothissyringe.
Filterintoa 1.5mL glassautovial.
12.23 Label the autovialwith the studynumber, animal number and gender,sample tirrepoint, matrix,finalsolvent,extractiondate,and analyst(sw)ho performed the extraction.
12.24Cap and hold forelectrospraymass spectrometry analysis. 12.25 Complete the worksheet and tapeto page of study notebook.
13.0 DATA ANALYSIS AND CALCULATIONS 13.1 Calculations:
13.1.1 Calculatethedensityof liver(mg) in 1.0mL homogenate using thefollowing equation: g of Liver x Average weight of ten I mL aliquots(mp(g of Liver+ g of Water)
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13.1.2CalculataectualconcentratioonfsPFOS incalibratisotnandardussingthe followingequation:
@iL of Standard x Concentration(jig/TnL)= FinalConcentration(@Lg/gor mg/'kg)
mg Liver'/I mL homogenate
of PFOS in Liver
*Average weight of liverin solutionas determined in 13.1.1,by weighing ten I mL homogenates of approximately40 mg liverin200 mL of Milli-Qwater.
14.0 METHOD
PERFORMANCE
14.1 The method detection limitis equal to half the lowest standard in the calibrationcurve.
15.0 POLLUTION PREVENT TON AND WASTE MANAGEMENT
15.1
Sample waste isdisposed in biohs7.q d containers, flammable solvent waste isdisposed in high BTU containers, and used glass pipette waste isdisposed in broken glass containers located in the laboratory.
16.0 RECORDS 16.1 Complete
the extraction worksheet and tape into the study notebook.
17.0 TABLES, DIAGRAms, FLOWCHARTS,
AND VALIDATION DATA
17.1 The validation report associated with this-method isFACT-M-1.0
& 2.0-V-1.
18.0 REFERENCES
18.1 AMDT-EP-22,
"Routine Maintenance of Ultra-Turrax T-25"
19.0 AFFECTED DocuMENTS
19.1 FACT--,'vf-2,"Analysis of Liver Extracts for Fluorochemicals using HPLC-Electrospray Mass Spectrometry"
20.0 REVISIONS Revision Number.
Reason For Revision
Revision Date
3M Environmental
Laboratory
FACT-M-1.0 Extraction of PFOS from Liver
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Der)artmert
Study: T-629S.7
Report No.
'T
-Laboratory Request
ExtractionWorksheet for FACT-M- I
FACT TOX-030 Number-U2279
Study,;
Sample Number set 4
H,O-Blank LiverBlank
PFOS approx.0.5 ppm actual ppm 9w
-
PFOS approx.5 ppm actual ppm 9w
PFOS approx. 50 ppm actual ppm 9w
-ffac-tan d Initials for Std.
Studv number where theori2inawlorksheetislocated,
Blank
LiverHomogenate: Std
Liver Extr2ction Method
Vorlex 15 sec.
Ltvcramount
p Date & lnit;als
PipeiteImL ofLiverSolution
PipettIemL oftO.5M TBA, pH 10.
Std.
Pipette2 mL of0.25Na2CO310.25M NaHCO3 Buffer Std.
Pipett5e mL ofEthylAcetate
TN-A-
Shake 20 min.
Centrifue2e0-25min. Centrifuee
Speed
Remove a4 mL aliquootforganiclaver
Puton NitrogenEvaporatortodrvness Evaporator Add 1.0mL ofMethanol
TN-A-
Temperature
Vortex30 sec.
Filteursinga 3cc B-D svrinlewitha 0.2um SRI filteirntoa 1.5mL autosamplevial
NISi'MSD/- Cont.Checks:Spiked- uL ofa
ppm std
fora finalconcentratioonf
ppm. MS/ivISD usedsample
Cont.Checks used same homogenate as forstdcurve,
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3M ENVIRONMENTAL LABORATORY
METHOD
ANALYSIS OF FLUOROCHEMICALS IN LIVER EXTRACTS USING
HPLC-ELF,CTROSPRAY/MASS
SPECTROMETRY
Method Number: FACT-M-2.0
Author: Lisa Clemen Approved By:
AdoptionDate:5/)L.,/qy RevisionDate: A@;i.i
LaboratoryManager
Date
Group Leader
A
TechnicalReviewer
Date
,@-1271(le
Date
1.0 SCOPE AND APPLICATION
1.1 Scope: This method isfortheanalysiosf extractosfliverorothertissuefsorfluorochemical surfactantussingHPLC-electrospray/masspectrometry.
1.2ApplicableCompounds: Potassiumperfluorooctanesulfonantieo,nicfluorochemical surfactantosr,otherionizablceompounds.
1.3Matrices: Rabbit,ratb,ovine,and monkey liverosr otherliverassdesignatedinthe validatiorneport.
Word 7.0.1/95
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2.0 SUM,-YIARY OF INIETHOD
2.1 This method describesthe analysisof fluorochemical surfactantsextractedfrom liverusing HPLC-electrospray/mass spectrometry.The analysisisperformed by monitoring a sI*n,cle ion characteristicof a particularfluoro'chemical;,uchlas the potassium perfluorooctanesulfonate(PFOS) anion,M/Z= 499. Samples may also be screened to verif@ compound identification.
3.0 DEFINITIONS 3.1 None.
4.0 WARNINGS AND CAUTIONS 4.1 Health and Safety Warnings:
4.1.1 Use caution with the voltagecable for the probe. When the voltage cable isplugged into the probe DO NOT TOUCH THE PROBE, thereisriskof electricaslhock.
4.2 Cautions:
4.2.1 Do not run solventpumps above capacityof 400 bar (5800 psi).Ifpressuregoes over 400 bar,the HP I 100 will initiataeutomatic shutdown.
4.2.2 Do not rlinsolvent pumps to dryness.
5.0 INTERFERENCES
5.1 Teflon should not be used forsample storage or any part of instrumentationthatcomes in contact with the sample or extract.
6.0 EQUIPMENT 6.1 Equipment listedbelow may be changed in order to optimize the system.
6.1.1 Micromass ElectrosprayMass Spectrometer 6.1.2 HPI 100 low pulse solventpumping system and autosampler.
7.0 SUPPLIES AND MATERIALS 7.1 Supplies
7.1.1 Nitrogen gas,refrigeratedliquid,regulatedto approximately 100 psi. 7.1.2 HPLC column, specificsto be determined by the analyst. 7.1.3 Capped autovialsor capped 15 mL centrifugetubes.
8.0 REAC;ENTS AND STANDARDS 8.1 Reagents
8.1.1 Methanol,HPLC gradeorequivalent.
Word 7.0.1/95
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3M Envi---onmental Laboratory
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8.1.2Milli-QwTat-emr,allwaterused inthismethod shouldbe N11111 _QT"l water and may
be provided by a Milli-Q TOC Plus system.
8.1.3 Ammonium acetate,HPLC grade or equivalent.
8.2 Standards
8.2.1 Typically one H20 blank,one liverblank,and seven liverstandardsare prepared during the extractionprocedure. See FACT-M- I
9.0 SAMPLE HANDLING
9.1 Fresh liverstandards are prepared with each analysis.Extracted standards and samples are stored in capped autovialsor capped 15 mL centrifugetubes untilanalysis.
9.2 If analysiswill be delayed, extractedstandardsand samples may be refrigerateduntil analysis can be @erformed.
10.0_ QUALITY CONTROL 10.1 Matrix Blanks and Method
Blanks
10.1.1 Analyze a method blank and matrix blank prior to each calibrationcun,e. 10.2 Matrix Spikes
10.2.1 Analyze a matrix spike and matrix spike duplicatewith each analysis.
10.2.2 Expected concentrationswillfallinthe mid-range of the initiaclalibrationcurve. Additional spike concentrationsmay fallin the low-range of the initiaclalibration curve.
10.2.3 See section 13 to calculatepercent recovery. 10.3 Continuing Calibration Checks
10.3.1 Analyze a mid-range calibrationstandard afterevery tenth sample. Ifa significant change ( 30%) in peak area occurs,relativeto the initiasltandard curve,stop the run. Only those samples analyzed before the lastacceptable calibrationstandard will be used. The remaining samples must be reanalyzed.
10.3.2 See section 13 to calculatepercent difference. 10.4 System Suitability
10.4.1 System suitabilit(y-..gp.eak area,retentiontime and peak shape, etc.)@villbe assessed for each run.
11.0 CAL113RATION AND STANDARDIZATION
11.1 Analyze the extractedliverstandardspriorto and following each setof extracts.The mean of two standard values,at each standard concentration,will be plottedby linearregression forthe calibrationcurve using MassLynx or othersuitablesoftware.
3M Environmental
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Laboratory
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11.2 The r-v'alue forthe data should be 0,98 or greater.Lower valuesmay be acceptableatthe discretionof the analyst.
11.3 Ifthe curve does not meet requirements,perform routinemaintenance or reextractthe standard curve (ifnecessary)and reanalyze.
12.0 PROCEDURES
12.1 Acquisition Set up
12.1.1 Click on startbuttonintheAcquisitionControl Panel.Set up a sample list.Assign a filenameusing letter-MO-DAY-lastdigitof year-samplenumber, assigna method (MS) foracquiring,and typein sample descriptions.
12.1.2 To createa method clickon scan buttonin theAcquisitioncontrolpanel and select SIR. SetlonizationMode as app:ropriataend mass to 499 or otherappropriate masses. A scan isusuallycollectedalong with the SIRS. Save method.
12.1.3 Typicallythe sample listbeginswith the firstsetof liverstandardsand ends with the second setof standards.
12.1.4 Samples are analyzed with a continuingcalibrationcheck injectedafterevery tenth sample. Solvent blanksshould be analyzed periodicalltyo monitor possibleanalyte carryoverand are not consideredsamples but may be includedas such.
12.2 Using the Autosampler
12.2.1 Set up sample trayaccordingtothesample lisptreparedinsection12.1.1.
12.2.2 Set-up the HP II00/autosampleratthe followingcon'ditionsor atconditionsthe analystconsidersappropriateforoptimal response.Record actualconditionsinthe instrumentlogbook:
12.2.2.1Sample size= 10 @tLinjectionwith a sample wash
12.2.2.2Inj'ect/sampl=e 1
12.2.2.3Cycle time = 15 minutes
12.2.2.4Solvent ramp =
Time I
0.00 min. 7.5 min. 11.0 min. 1 11.5 min.
MEOH
45% 90% 90% 45%
2.0 mM Ammonium acetate
55% 10% 10% 55%
Note: In thisinstrumentconfigurationt,he run must be setup on the clectrosprav softwarewith a "Waiting forinletstart"message beforethe"Start"button is pressed on the HP Workstation.
12.2.2.5Press the"Start"button.
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12.3InstrumenStep-up
12.3.R1efetroA,@,flDT-EfPo-rm3o1redetails. 12.3.C2heckthesolvelnetveilnreservoainrdrseflilfnecessary.
12.3.3 Check the stainlesssteelcapillaryatthe end of the probe. Use an eye piece to check the tip. The tipshould be flatwith nojagged edges. If the tipisfound to be unsatisfactory,disassemble the probe and replace the stainlesssteelcapillary.
12.3.4 Set HPLC pump to "On". Set the flow to 10 - 500 uL/min or as appropn-ate. Observe dropletscoming out of the tipof the probe. Allow to equilibratefor approximately 10 minutes.
12.3.5 Turn on the nitrogen.A finemist should be expelledwith no nitrogenleaking around the tip of the probe.
l@.3.6 The instrument uses these parameters at the following settings.These settingsmay change in order to optimize the response:
12.3.6.1Drying gas 250-400 liters/hour 12.3.6.2ESI nebulizinggas 10-15 litersihour 12.3.6.3LC constantflow mode flow rate 10 - 500 uL/min 12.3.6.4Pressure <400 bar (This parameter isnot set,itisa guide to ensure the
instrument is operatingcorrectly.)
12.3.7 Carefullyguide theprobe intothe opening. Insertprobe untilitwillnot go any further.Connect the voltage cables to the probe.
12.3.8 Record tune -parametersin the instrument loiz.
12.3.9 Using the cross-flow counter electrodein the ES INIS source isrecommended for the analysisof biologicalmatrices.
12.3.10 Click on startbutton in the Acquisition Control Panel. Press the startbutton at top of sample list.Ensure startand end sarnple number includes allsamples to be analyzed.
13.0 DATA ANALYSIS 13.1 Calculations:
AND CALCULATIONS
13.1.1 Calculate matrix spike percent recoveries using the following equation:
% Recovery
Observed Result-Background Result x 100 Expected Result
13.1.2 Calculatepercent differenceusing the following equation:
% Difference
Expected Conc. -Calculated Conc. x 100 Expected Conc.
3M Environmental
FACT-M-2.0 Analysis of Liver Extract Usini2 ES/N/IS
Laboratory
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13.1.3 CalculateactualconcentratioonfPFOS anionintotaliver(mg):
ug PFOS anion calc.from std curve g of liverused formialysis 1000 ugl I mg
x Total mass of liver
14.0 IMETHOD PERI@OP@MANCE 14.1 The method detectionlimitis equal to at leastthreetimes the baselinenoise in the matrix
blank.
14.2 The practicalquantitationlimitisequal to the lowest standard in the calibrationcurve.
15.0 POLLUTION PRF!RVENTION AND WASTE MANAGEMENT
15.1 Sample waste is disposed in biohazard containers,flammable solventwaste is disposed in high BTU containers,and glasspipettewaste isdisposed in broken glass containers. All containers are located in the laboratory.
16.0 RECORDS 16.1 Store chromatograms in the study folder.Each chromatogram should have the following
information included eitherin the header or hand writtenon the chromatogram: study number, sample narne,extractiondate,and dilutionfactor(ifapplicable).
16.2 Plot calibrationcurve by linearregressionand store in the study folder.
16.3 Printsample listfrom MassLynx and tape intothe instrumentrunlog.
16.4 Printdata integrationsummary from MassLynx and tape intothe instrument runlog. 16.5 Copy instrument runlog pages, includinginstrument parameters and sample results,and
tape intoappropriate study notebook.
16.6 Summarize data using suitablesoftware and storein the study folder.
16.7 Back up electronicdata to appropriatemedia. Record in study notebook the filename and locationof backup electronicdata.
17.0 TABLES, DIAGRAms, FLOWCHARTS, AND VALIDATION DATA 17.1 Attachment A: FACT-M-2 Data reportingspreadsheet 17.2 The validationreportassociatedwith thismethod is FACT-M- 1.0 & 2.0-V-1.
18.0 REFERENCES 18.1 ANIDT-EP-3
1,"Operation of VG Platform ElectrosprayMass Spectrometer"
3M Environmental
FACT-M-2.0 Analysis of Liver ExtractUsing ES;'MS
Laboratory
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Report No. FACT TOX-030 laboratory Request Number-U2'L79
19.0 AFFECTED DOCUMENTS
19.1 FACT-M-1.0, "Extractioonf PotassiumPerfluorooctanesulfonfartoem LiverforAnalysis Using HPLC-Electrospray/MassSpectrometry"
20.0 REVISIONS
Revision
Number.
Rmon For Revision
Revision
Date
FACT-M-2.0
Analysisof LiverExtractUsing ES/MS
3M Environmental Laboratory
PagC7e 7 of 8
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Laboratory Study
Study: Test Material: Matrix/FinaSlolvent: Method/Revision: AnalyticalEquipment System Number-. InstrumentSoftwareNersion: Filename: R-Squared Value: Slope: Y Intercept: Dateof Extraction/Analy5t: Dateof Analysis/Analyst:
Group Dose
Sample#
Concentration ug/mL
InitiaVlol. mL
Dilution Factor
FinalConc. ug/mL
Slope: Taken ftom linearegressioenquation. Group/Dose: Taken from thestudyfolder. Samplei$:Taken fromthestudyfolder. Concentration(ug/mL): Taken from theMassLynx integratisounmmary. InitiaVlolume (mL): Taken fromthestudyfolder. DilutionFactor:Taken fromthestudyfolder. FinalConc. (ug/mL): Calculatebdy dividintgheinitiavlolume from theconcentration
FACT-M-2.0 Analysisof LiverExtractUsing ES/MS
3M Environmental Laboratory
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Report No. FACT TOX-030 laboratory Request Number-U2279
3M ENVIRONMENTAL
LABORATORY
METHOD
EXTRACTIOP4-OF
POTASSIUM PERFLUOROOCRA.NESULFONATE
OR OTHER
FLUOROCHEMICAL
COMPOUNDS
FROM Lll,'ER FOR ANALYSIS USING
HPLC-ELECTROSPRAY/MASS
SPECTROMETRY
Method Number: FACT-M-1.1
Author: LisaClemen, Glenn Langenburg
Approved By:
-7 1)1"14
LaboratoryManager
-ILI',v @E7ro@UPLeader
@@, ,A
Technical Reviewer
AdoptionDate:05/26/98
RevisionDate: 06),))Ill
Date 6/1 /14@ Date
li),i55
Date
1.0 SCOPE AND APPLICATION
1.1Scope: Thismethod isfortheextractionf potassiumperfluorooctanesulfo(nPaFtOeS) or otherfluorochemicalcompounds from liver.
1.2Applicable Compounds: Fluorochemicalsurfactantosr otherfluon*natecdompounds.
1.3Matrices: Rabbit,rat,bovine,andmonkeyliveorrotherlivearsdesignateidnthevalidation
report.
N,ficroso6f.t0/95
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FACT-M- 1.1
ExtractionofPFOS from Liver
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2.0SUMMARY OF METHOD
2.1 This method describestheprocedureforextractinpgotassiumperfluorooctanesulfonate
(PFOS) or other fluorochemicalsfrom liverhomogenate using an Ion pairingreagent and
5.0ml of ethvlacetate.Inthismethod,seven fluorochemicalwsere extractedP:FOS, PFOSA,PF6sAA, ETFOSE-OH, POAA, PFOSEA, and FC-807 monoester (see3.0 Definitions).An ionpairingreagentisadded tothesample and theanalyteIon pairis partitioneidntoethylacetate.Four ml ofextractareremoved and putonto a nitrogen evaporatorunt@ldry. Each extractisreconstituteidn 1.0ml of methanol,then filtered through a 3 cc plasticsyringeattachedtoa 0.2 @Lm nylon filteirntoglassautovials.
3.0 DEFINITIONS
3.1 PFOS: perfluorooctanesulfonate(anion of potassium salt)CF17SOl3.2 PFOSA: perfluorooctanseulfonylamideC,F,7SO,NH, 3.3 PFOSAA: perfluorooctanseulfonylamido(ethyl)acetaCt@eF,,SO,N(CH,CH,)CH,CO,3.4 ETFOSE-OH: 2(,N-ethylper-fluorcoestualnfeonwnido)-ethylalcohol
C,F17So2N(CH2CH3)CH,CH20H 3.5 POAA: perfluorooctanoat(eanionofammonium salt)C,F,,COO' 3.6 PFOSEA: perfluorooctanseulfonylethylamideC,F,7SO,N(CH,CH3)H 3.7 FC-807 monoesterC,F,,SO,N(CH,CH,)CH2CH,O-PO,H) 3.8 SurrogatestandardIH, IH,2H,2H perfluorooctanseulfonicacid
4.0 WARNINGS AND CAUTIONS 4.1 Health and safetywarnings:
4.1.1 Use universalprecautionse,speciallylaboratorycoats,goggles,and gloveswhen handlinganimal tissuei,tmay containpathogens.
5.0 INTERFERE14CES 5.1 There areno known interferenceastthistime.
6.0 EOUIPMENT
6.1 The followingequipment isusedwhilecarryingout thismethod. Equivalentequipment is acceptable.
6.1.1 6.1.2 6.1.3 6.1.4
Ultra-Turraxwith T25 grinderattachmentforgrinding/dispersing/emulsifying Vortex mixer,VV@'R,Vortex Genie 2 CentrifugeM,istral1000 orIEC Shaker,Eberbach or VWR
6.1.5 NitrogenevaporatorO,rganomation 6.1.6 Balance,( 0.100 g)
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7.0 SUPPLIES A,*,*MDATERIALS 7.1 Gloves 7.2 Eppendorf or disposablepipettes 7.3 Nalgene bottlesc,apable of holding250 ml and I L 7.4 Wheaton 6 ml PlasticSampule Vials 7.5 Glass,type A, volumetricflasks 7.6 40 ml glassI-CHENF vials 7.7 Polypropylene centrifugetubes,15 ml 7.8 Labels 7.9 Syringes,capable of measuring 5 @iLto50 gL 7.10 Glass,type A, volumetricpipettes 7.11 Graduated pipettes 7.12 ElectronicpipettorE,ppendorf or equivalent 7.13 Timer 7.14 Disposable plastic3 cc syringes 7.15 Filtersn,ylon syringefilters0,.2 um, 25 mm 7.16 Crimp cap autovials Note: Priorto using glasswareand bottlesr,inse3 timeswith methanol and 3 timeswith Milli-
Q TM water. Rinse syringesa minimum of 9 timeswith methanol, 3 rinsesfrom 3 separate
vials.
8.0 REAGENTS AND STANDARDS 8.1 ASTM Type Ireagentgade water,Milli_QTM or equivalent;allwater used inthismethod
should be Milli_QTMwater and may be provided by a Milli-Q TOC plUST,'Slystem.
8.2 Sodium hydroxide (NaOH), J.TBaker or equivalent 8.3 Tetrabutylammonium hydrogen sulfate(TBA), Kodak or equivalent
8.4 Sodium carbonate(NaC03), J.T.Baker or equivalent
8.5 Sodium bicarbonate(NaHC03), J.T.Baker or equivalent 8.6 Ethyl acetate,Omnisolv, glassdistilleodr HPLC grade
8.7 Methanol, Omnisolv, glassdistilleodr HPLC gade 8.8 Liver tissue,frozenfrom supplier
8.9 Control matrix or blank matrix forstandards,QC checks,blanks,etc. 8.10 Fluorochemical standards
8.10.1 PFOS (3M SpecialtyChemical Division),molecular weight= 538
8.10.2 PFOSA (3M SpecialtyChemical Division),molecularweight = 499
8.10.3 PFOS.-@-A(3M SpecialtyChemical Division),molecular weight = 585
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8.10.4 ETFOSE-OH (3M SpecialtyChemical Division),molecularweight= 571
8.10.5 POAA (3M SpecialtyChemical Division),molecularweight = 431
8.10.6 PFOSEA (3NI SpecialtyChemical Division),molecularweight = 527
8.10.7 FC-807 monoester (3M SpecialtyChemical Division).FC-807 isa mixture of triesterd,iestera,nd monoester fluorochemicalcomponents. The monoester molecular weight = 650
8.10.8 SurrogateStandard:4-H, perfluorooctanesulfonicacid (1-H,I-H, 2-H,2-H C,F,,SO3H) molecularweight = 428
8.10.9 Other fluorochemicalsa,s appropriate
8.11 Reagent preparation
8.11.1 10 N sodium hydroxide(NaOH): Weigh approximately200g NAOH. Pour intoa 1000 ml beakercontaining500 ml Milli-Q"'water,mix untilallsolidsare dissolved.Storeina I L Nalgene bottle.
8.11.2 1 N sodium hydroxide (NaOH): Dilute ION NAOH 1:10. Measure 10 mi of 1ON
NAOH solutionintoa 100 ml volumetricflaskand diluteto volume using Milli-Q"'
water. Storein a 125 ml Nalgene bottle.
8.11.3 0.5M tetrabutylammonium hydrogen sulfate(TBA): Weigh approximately169 grams of TBA intoa I L volumetriccontaining500 MI Milll_QTIwIater.Adjust to pH 10 using approximately44 to 54 ml of ION NAOH and diluteto volume with Milll_QTIwater. While adding the lastfew ml's of NAOH, add slowly because the pH changes abruptly.Storein a I L Nalgene bottle.
8.11.3.1TBA requiresa check priorto each use to ensurepH = 10. Adjust as needed using IN NAOH solution.
8.11.4 0.25M Sodium carbonate/sodiumbicarbonatebuffer(Na@CO,/NaHCO,): Weigh approximately26.5g of sodium carbonate(Na.CO,) and 21.0 g of sodium bicarbonate(,N'aHCO,)intoa I L volumetricflaskand bringtovolume with Milli-
Q TM water. Storein a I L nalgene bottle.
8.12 Standards
8.12.1 Prepare PFOS standardsforthe standardcurve.
8.12.2 Prepare otherfluorochemicalstandards,as appropriate.Multicomponent fluorochemicalstandardsareacceptable(e.g.one working standardsolution containing1.00 ppm PFOS, 1.02ppm PFOSA, 0.987 ppm PFOSAA, and 1.10 ppm EtFOSE-OH.)
8.12.3 Weigh approximately100 mg of PFOS intoa 100 ml volumetricflaskand record the actualweight.
8.12.4 Bring to volume with methanol fora stockstandardof approximately1000 ppm (@ig/ml).
8.12.5 Dilutcthestocksolutionwith methanol fora working standardI solutionof approximately 50 ppm.
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8.12.6 Dilutethestock solutionwith methanol fora working standard2 solutionof approx. 5.0 ppm.
8.12.7 Dilutethestock solutionwith methanol fora working standard3 solutionof approx. 0.50 ppm.
8.13 Surrogate stock standard preparation
8.13.1 Prepare-asurrogatestockstandard.Weigh approximately 50-60 mg of surrogate
standard 1-H,I-H, 2-H,2-H, C,F,3SO3H
intoa 50 ml volumetricflaskand record the
actualweight.
8.13.2 Br-ingto volume with methanol fora surrogatestockof approximately 1000- 1200 PPM.
8.13.3 Prepare a surrogate working standard. Transfer approximately 0.5 mi of surrogate stockto i 50 ml volumetricflaskand bringto volume with methanol fora working standardof 10-20 ppm. Record theactualvolume transferred.
8.14 Liver homogenate preparation Note.-The followingprocedure willbe much easiertoperform withfrozen liver tissue.Prevent tissuefromthawing; keep storedon iceuntileccisingaportion of it.-
8.14.1 Weigh 40 g of blank or controlliverintoa 250 ml Nalgene bottlecontaining100 mls Milli-Q'Tw"ater. Record theactualweight of liverand totalvolume of water used. Grind the liverintoa finelydispersedhomogenate with an Ultra-TurraxT25 grinder(highspeed forapproximately3 minutes or untilsufficiently homogenized). Rinse grinderwith an additional100 MI Of MilllQTIIwater,to bring the totalvolume of water added to 200 ml.
8.14.2 To determine theconcentrationof the blank liverhomogenate, transferten 1.0 ml aliquotsof the homogenate totaredpolypropylene tubes,and weigh each aliquot on a balance. The averagedensityof thesealiquotsisdetermined and then the concentration(g of liver/mlof homogenate) can be calculatedas follows:
8.14.3 [,zrams(g)of liver]x favizw.eight of 1.0ml of homogenate (density)(,sz/ml)l f[grams (g)of liver]+ [grams (g)of water]@
8.14.3
Preparesample liversas describedin8.3.1,butweigh out I g of liverh,omogenize with 2.5 ml of MilliQ" water,and n'nsewith another2.5MI Of MIIIIQTI water. Use Wheaton 6 ml plasticsampule vialsor appropriatereceptacle.Rinse grinder unitafterevery sample with water and thenwith methanol. Label vials appropnately includingstudynumber, sample ID, liverweight,date,and analyst. Record allweights and volumes used. (Do notperform 8.3.2forthe sample liver homogenates).
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9.0 SANIPLE HANDLING 9.1 All liversare received frozenand must be kept frozen untilthe extractionisperformed.
10.0 ()UALITY CONTROL 10.1 Matrix blanks and method
blanks
10.1.1 Extract two 1.0 ml aliquots of the liver homogenate (prepared in 8.14.1-2) following thisprocedure and use as matrix blanks. See Section 11.1.2.
10.1.2 Extracttwo 1.0ml aliquotsof Milli-Q' water followingthisprocedure and use as method blanks.
10.2 Matrix spikes
10.2.1 Prepare dnd analyze matrix spike and matrix spike duplicatesamples to determine the accuracy of the extraction.
10.2.2 Prepare each spike using liverchosen by the analyst,usually the control liver received with each sample set.
10.2.3 Expected concentrationsfallin the mid-range of the initiaclalibrationcurve. Additional spikesmay be includedand may fallin the low-range of the initial calibrationcurve.
10.2.4 Prepare one matrix spike and one matrix spike duplicateper 40 samples, with a minimum of 2 matrix spikes per batch.
10.3 Continuing calibrationchecks
10.3.1
Prepare and analyze continuingcalibrationcheck samples to ensure the accuracy of the initiaclalibrationcurve. Ifthe percentdifferencebetween the initiaclurve and the continuing check differby >30%, reanalyze samples analyzed afterthe last acceptable check.
10.3.2 Prepare one check per group of ten samples. For example, ifa sample set = 34, prepare and extractfour checks.
10.3.3 Prepare each continuing calibrationcheck from the same blank liverhomogenate used to prepare the initiaclurve.
10.3.4 The expected concentrationsfallwithin the mid-range of the initiaclalibration curve. Additional spikesmay be included thatfallin the low-range of the initial calibrationcurve. This isnecessary ifthe analystmust quantitateusing only the low end of the calibrationcurve (e.g.10 ppb - 100 ppb, ratherthan 10 ppb - 1000 ppb).
11.0 CALIBRATION AND STANDARDIZATION 11.1 Prepare liverhomogen ate standards
11.1.1 Transfer I ml aliquotsof blank/controlliverhomogenate prepared in 8.14.1-2 to 15 mi centrifugetubes.
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11.1.2 Ifthe volumes of sample liverhomogenates are limited,extractstandardswith liver homogenate volumes equalto the sample volumes. Do not extractbelow 0.50 ml of liverhomogenate. Record thesample volume on the extractionsheet.
11.1.3 V;hllepreparinga totalof twenty aliquotsof liverhomogenate in 15 ml centrifuge tubes,mix or shake between aliquots.
11.1.4 Two I mi, or appropriatealiquotss,erveas matrix blanks. Typicallyuse the standaraconcentrationsand spikingamounts listedinTable I (atthe end of this section)to spike,in duplicatet,wo standardcur-ves,fora totalof eighteenstandards and two matrix blanks.
11.1.5 Refer to the validationreportsFACT-M-1.1-V-1 and FACT-M-2.1-V-1 which list theworking rangesand LinearCalibrationRan-0e (LCR) forcalibratiocnurves.
11.1.6 Use Attachment D as an aid in calculatingthe concentrations of the working standards. See SectIon 13.0to calculateactualconcentrationsof PFOS in calibrationstandards.
11.2 To each standard,blank,or QC check,add appropriateamount of surrogateworking standardforthe concentrationto fallwithintfiecalibratiocnurve range 10 ppb - 1000 ppb.
11.3 Extractspiked liverhomogenate standardsfollowing12.6-12.16of thismethod. Use these standardsto establisheach initiaclurve on themass spectrometer.
Table I
Approximate Spiking Amounts for Standards and Spikes
Using 1.0ml of Liver
Working Standard
@tL
Approx. finalconc. of
(Approx.Cone.)
-
-
PFOS in liver Blank
0.500 PPM
4
0.012 ppm
0.500 ppm
10
0.030 ppm
0.500 ppm
20
0.060 ppm
0.500 ppm
40
0.120 ppm
5.00 ppm
10
0.300 ppm
5.00 ppm
20
0.600 ppm
5.00 ppm
30
0.900 ppm
50.0 ppm
4
1.20 ppm
50.0 ppm
6
1.80 PPM
12.0 PROCEDURES 12.1 Obtain frozenliversamples and homogenize as describedin 8.14.3.
12.2 Vortex mix homogenate for 15 seconds,then transfe.1-.0ml or otherappropriatevolume to a 15 ml polypropylene centrifugetube.
12.3 Return liverhomogenate samples to freezerafterextractionamount has been removed.
3M Environmental Laboratory
FACT-M- 1.1 Extractioonf PFOS froniLiver
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12.4 Record the liverhomogenate volume on the extractionworksheet. The finalmethanol volume willequal theinitiahlomogenate volume. For example, ifI ml of homogenate is transferredforextractiont,henthe finalreconstitutiomnethanol volume equals I ml.
12.5 Label the tube with *he study number, liverID, date,and analystinitialsS.ee attached worksheet fordocumenting the remaining steps.
12.6 Spike blank liverhomogenate aliquotswith the appropriateamount of standardas described in Section11.1 or Table I in thatsectionforthe calibratiocnurve standards. Also preparematrix spikesand continuingcalibrationstandards.
12.7 Spike allsamples, includingblanksand standards,ready forextractionwith surrogate standardas describedin Section11.2.
12.8 Vortex mix the standardcurve samples,matrix spikesamples,and continuingcalibration samples for15 seconds.
12.9 To each sample, add I ml 0.5 M TBA and 2 ml of the 0.25 M sodium carbonate/sodium bicarbonatebuffer.
12.10Using a volumetricpipette,add 5 ml ethylacttate.
12.11 Cap each sample and put on theshaker for20 minutes.
12.12 Centrifuge for20 to 25 minutes atapproximately 3500 rpm, untillayersare well separated.
12.13Transfer4 ml of organiclayer,usinga 5 ml graduated glasspipettet,o a clean 15 ml centrifugetube.Label thisfreshtube with the same informationas in 12.5.
12.14Put each sample on the analyticanlitrogenevaporatoruntildry,approximately 2 to 3 hours.
12.15Add 1.0ml or appropriatevolume of methanol to each centrifugetube usinga graduated pipette.Methanol volume equalsthe initiavlolume of liverhomocenate used forthe extraction.
12-16Vortex mix for30 seconds.
12.17 Attach a 0.2 @im nylon mesh filtetro a 3 cc syringeand transferthesample to thissyringe. Filterintoa 1.5ml glassautovial(orlow-volume autovialwhen necessary).
12.18Label theautovialwith thestudynumber, animal number and gender,sample timepoint, matrix,finalsolvent,extractiondate,and analyst(sw)ho performed the extraction.
12.19Cap and storeextractsatapproximately4' C untilanalysis.
12.20 Complete the extractionworksheet, attachedto thisdocument, and tape topage of study notebook or includein studybinder,as appropriate.
13.0 DATA ANALYSIS AND CALCULATIONS 13.1 Calculations:
13.1.1 Calculateactualconcentrationsof PFOS, or other appropriatefluorochemical,in calibratiosntandardsusingthe followingequation:
3M Environmental Laboratory
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Report No. FAC-L TOX-030 laboratory Request Number-U2279
ml of Standard x Concentrationof Standard(4-g/ml) ConcentrationofBlank LiverHomogenate (g/ml)(see8.14.2)
FinalConcentration(@ig/g)of PFOS
in L,-.ver
See Attachment D fora sample form to calculatethe concentrationsof standards.
14.0 METHOD PERFORMANCE 14.1 The method detectionlimit(MDL) isanalyteand matrixspecific.Refer to MDL reportfor
spee'lficMDL andlimiotfquantitat(iLoOnQ)value(sseeAttachmentBs and C).
14.2 The followingqualitycontrolsamples are extractedwith each batch of samples to evaluate the qualityof the extractionand analysis.
14.2.1 Method blanks and matrixblanks
14.2.2 Matrix spikeand matrixspikeduplicatesamples to determine accuracy and precisionof the extraction
14.2.3 Continuing calibratiocnheck samples to detentilnethe continued accuracy of the initiaclalibratiocnurve.
15.0 POLLUTION PREVENTION AND WASTE MANAGEMENT
15.1 Sample waste isdisposedinbiohazardcontainersf,lammable solventwaste isdisposed in high BTU containers,and used glasspipettewaste isdisposed in broken glasscontainers locatedin the laboratory.
16.0 REcoRDs
16.1 Complete the extractionworksheet attachedtothismethod, and tape intothe study notebook or includeintostudy binder,as appropriate.
17.0 ATTACHMENTS 17.1 Attachment A, Extractionworksheet 17.2 Attachment B, MDL/LOQ values 17.3 Attachment C, LOQ summary 17.4 Attachment D, Calibrationstandardconcentrationworkshect
18.0 REFERENCES 18.1 The validationreportsassociatedwith thismethod are FACT-M-1.1
and 2.1-V-1.
19.0 AFFECTED DOCUTVIENTS
19.1 FACT-M-2. 1, "Analysisof Liver ExtractsforFluorochemicalsusing HPLC-Electro spray Mass Spectrometry"
3M Environmental Laboratory
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20.0 REVISIONS
Revision Number.
1
Validation systems, e.-ctraction, etc.
of method monkey liver
MDL study,
Reason For Re-visio to include 7fluorochemicals, cross validation, improvements
updates in record keeping
new APIIMS(MS) ..
to ion pai ring and storing policies,
Revision Date
08/01/98
3M Environmental Laboratory
FACT-M-
1. 1
ExtractioonfPFOS from Liver
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Report No. FAC-- TOX-030 laboratory Request Number-U2279
Study# Matrix Boxg
Surroga,.eStd. approx. ppm actual PPM
FC Mix Std approx.0.5 ppm actual PPM
AnalysUDate H,O Blank Blank
FC Mix Std approx.5 ppm actual PPM '"W
FC Mix Std approx. 50 ppm actual PPM
Comments
Blank
Std
ExtractioMnethod/Revision:
amount
Date& lniti2is
Add SurrogateV,ortex ISsec.
PipettSeample
Volume
ml
PipettIemi of 0.5M TBA, pH 10. PH
Std.
Pipett2emi of0.25Na2CO3/0.25M NaHC03 buffer
Std.
Pipett5emi of ethylacetate
Shake 20 min.
Centrifu.g2e0-25min.
Remove a 4 mi aliquotof organiclayer
Puton Nitro_geEnvaporatortodryness
Add methanol
Volume
TN-AShaker Speed -Centrifugsepeed:
Temperature:
ml
TN-A-
Vortex30 sec.
_Filterusinga 3ccB-D syrineewitha 0.2pm SRI filteirntoa 1.5ml autosamplevial
MSfMSD/- Cont.Checks:Spiked- uL ofa
ppm std(
) fora finacloncentratioonf
ppm. IvISi'NISuDsedsample
Cont,Checks used same matrixas forstdciir-@e.
AttachmentA: Extractiownorkshect 3M Environmental Laboratory
FACT-M- 1.1 ExtractioonfPFOS from Liver
PacycII of 15 Page 139
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Report No. FAC'@" TOX-030 laboratory Request Number-U2279
MDL/LOQCompound
@PF-OS PFOSA PFOSAA ETFOSE-OH POAA PFOSEA Monoester
values for Rabbit Liver:
MDL
LOQ Linear CalibrationRan-e (LCR)
(ppb) (ppb) Approximate Concentrations to be used for preparing the
Standard Calibration Curve
11.8
37.4 38 ppb - 1000 ppb
6.06
19.3 120 ppb - 1200 ppb
55.7
177 180 ppb - 1000 ppb
58.7
187 190 ppb - 1800 ppb
23.7
75.5 76 ppb - 1800 ppb
16.2 n/v
51.7 62 ppb - 1200 ppb n/v I Monoester was not detectable/quantifiabaltethespiked concentrations.
MDL/LOQ Compound
PFOS PFOSA PFOSAA ETFOSE-OH POAA PFOSEA Monoester
values for Rat Liver:
MDL
LOQ LinearCalibratioRnange (LCR)
(ppb) @(ppoppbQb))IAALStpipapnIroximate Concentrationstobe used forpreparingthe
Standard CalibrationCurve
24.7 78.7 62 ppb - 1200 ppb
20@7
65.8 20 ppb - 1200 ppb
n/v
n/v _62ppb - 1200 ppb
n/v
n/v 120 ppb - 1200 ppb
n/v
n/v 62 ppb - 1200 ppb
n/v
n/v 120 ppb - 1200 ppb
n/v
n/v Monoester was not detectable!quantifiaabtlethespikedconcentrations.
i'vIDLILOQ valuesforMonkey Liver:
Compound
MDL
LOQ LinearCalibrationRange (LCR)
(ppb) (ppb) Approximate Concentrationsto be used forpreparingthe
Standard CalibrationCurve
PFOS
n/v
rVv 59 ppb - 1200 ppb
PFOSA
27.4 87.1 28 ppb - 1200 ppb
PFOSAA
nJv
n/v 120 ppb - 1200 ppb
ETFOSE-OH
n/v I n/v 58 ppb - 1200 ppb
POAA
n/v
n/v 120 ppb - 1200 ppb
PFOSEA
n/v
n/v 120 ppb - 1200 ppb
Nlonoester
niv
n/v Monoester was not detectableq,uantifiablaet thespikedconcentrations.
niv = Not valid.Upon analyzingthedata,valuedidnotpassthecriterisaetforthischaracterization. Untilfur-thearnalysisiscompleted,use theLCR todeterminetherange ofstandard concentrationfsorcalibratiocnurvepreparation.
AttachmentB:MDL/LOQ Values 3M Environmental Laboratory
FAC7-M- 1,1 ExtractioonfPFOS from Ll%,er
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Report No. FACT TOX-030
labcratory Request Number-U2279
Compound PFOS
Matrix
Rabbit Bovine
NIDL
LOQ
11.8 ppb
37.4 ppb
n/d= not detenttined'
Approximate Linear Rang@@
Low Standard
38 ppb i 60 ppb
High Standard
1000 ppb 0 ppb
PFOSA
i
Rat
--m 0 rikey
Rabbit
24.7 ppb 1 78.7ppb
n/v= not valid'
1
1
6.06 ppb
19.3ppb
62 ppb 59 ppb
20 ppb
1200 ppb 1200 ppb 1200 ppb
Bovine Rat
n/d 20.7 ppb
a/d 65.8 ppb
30 ppb 6 ppb
1200 ppb 1200 ppb
PFOSAA
Monkey i Rabbit
Bovine
27.4 ppb
87.1 ppb
6 ppb
1200 ppb
55.7 ppb i 177 ppb 1 180 ppb 1 1900 ppb
n/d
ri/d
120 ppb
1200 ppb
ETFOSE-OH
Rat Monkey Rabbit
n/v
n/v
riiv I
n/v
58.7ppb
187 ppb
---62ppb 120 ppb
190 ppb-
1200 ppb 1200 ppb 1800 ppb
nJd
n/d
120 ppb
1200 ppb
Rat
n/v
n/v
120 ppb
1200 ppb
Monkey
n/v
n/v
58 ppb
1200 ppb
POAA
Rabbit Bovine
Rat
23.7 pp b n/d
niv
75.5ppb n/d n/v
76 ppb 120 ppb 62 ppb
1800 ppb 1206-ppb1200 ppb
Monkey
YV'V
n/v
120 ppb
1200 ppb
PFOSEA
Rabbit
16.2 ppb
51.7 ppb
62 ppb
1200 ppb
Bovine
n/d
n/d
30 ppb
1200 ppb
Rat
n/v
nJv
120 ppb
1200 ppb
Monkey
n/v
n/v
120 ppb
1200 ppb
Monoester
Rabbit
n/d
ri/d
n/a
nia
Bovine
ri/d
ri/d
rt.a,
n@a
Rat
ib'd
n/d
ri/a
n/a
Monkey
n/d
n/d
n)a
n/a
I -Upper Limitchosenwhere thevaduewas withintheLinearCalibratioRnange (LCR) butdid not excessivelwyeight thestandardcurveoraffectRepeatabilit&yReproducibilitvyalues.
2 -Not determinedrefertso no samplewas analyzedforthisdata.
3 -Not validreferstodatafrom the analysisfailetdomeet specificcriterifaora valid@MDL/LOQ determination.
Compound Liver intatrix
Rabbit Bovine Rat lvlonek..v
PFOS
Prepared
Rangeof Standards
Rangeof Average Curve
Range of Low Std.
Curve
LCR from,,,.-Range of -L-o-@w' td. flighStd.
Curve
(ppb)(ng/g) (ppb)(ngTg)-,.-.
(Ppb)(ng/g)
5.95- 1790
1790 @ir4_-ALqCk, 5.95-298 fl-5@@-299
(ppb)(ng/g) 119 - 1790
600. 200 6.00- 1200
n/a
1240 6.2'-- 1240 04-,;.1'24
nia
11 5 93 - I190 5.9--,1-190
nia
nla@4,. nia nla
nYa
iv
nla
nia i nla
Attachment C: LOQ summary 3M Environmental Laboratory
FACT-M- 1.1 ExtractioonfPFOS from Liver
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3m Medical Decartment- Sz,-d,/:---0'295.7
Report No. FA---L TOX-030 lahoratory -Request Number-U2279
!Compound@
I PFOSA
Liver
Prepared
Rangeof -.14CR-,frdin"R.a,ngeof 1. LCR from@-@ Range of LCR,-from
Matrix
Rangeof
Average
Low Std. LonSid High Std
Std"
Standards
Curve
Curve
Curve I -vat"
(ppb)(ng/g) (ppb)@ngig)
(ppb)(ng/g) (PP,@)(4e&"(@PP6-)-(n-g/g)
Rabbit
6.04-1810 6-04- 1210
6.04-301.
121- 1210
J7,-
Bovine
5.95-1190 @.95 1190
n/a
n/a
Rat
6.17-1240- 5.17- 1214900
n/a
n/a
Nion ey
5.88-1180 5.38-1180
n/a
n/a
@Compound@ Liver Matrix
Rabbit Bovine R2t Monkey
PFOSAA
1
Prepared
Rangeof
Range of Standards
Average Curv
(ppb)(ng/g)(ppb)(ng/g)
6.33 - 1900 12-/-1900
5.99- 1200 120- 1200
6.21 - 1240 62.1-1240
5@92 - I ISO 59.2-1180 IWlt
Rangeof Low Std.
Curve (ppb)(ng/g)
n/a n/a nla n/a
Range of High Std.
Curve (ppb)(ng/@gf)t-
n/a
n/a n/a n/a
Compound Liver Matrix
Rabbit Bovine Rat Monkey
ETFOSE-OH
Prepared
Range f
Rangeof Standards
Average Cur-ve0
(ppb)(ng/g)(ppb)(ng/g)
5.96- 1790 1]9-1790
5 87- 1170 58.7-1170
6.09- 1220 5.80- II60
122-1220 294-1160
Range of L Low Std.
Curve (ppb)(nWg)
n/a n/a
n/a n/a
Rangeof 1 High Std.
Curve ;j (ppb)(nWg)
n/a
n/a
M...,
n/a n/a
Compound Liver Matrix
Rabbit Bovine Rat Monkev
I
POKA
Prepared Range of
Range of Average
Standards
Curv
(ppb)(ng/g)(ppb)(ng/g)
6.06- 1820 30.3- 1820
5.93 -1190 59.3 -1190
6.15- 1230 61.5- t230
5.86 - I I"@O II-,- 1170
Range of @LC
Low Std.
Curve
e
(ppb)(ng/"@)
30.3-606
nla
n/a
n/a
R2ngeof High Std.
Curve (ppb)(ng/g)
303 - 1820
n/a
n,a nia
,Compound Liver Matrix
Rabbit Bovine Rat Monkey
PFOSEA
Prepared
Rangeof
R2ngeof Standards
ANera,,e Curve
(ppb)(ng/g)(ppb)(ng/g)
6.20- 1860 62.0- 1240 i:,
Range of Li.@0RLrgm4@t Rangeof L
hi@,
Low Std-
High Std.
Curve
Curve
'.4
(ppb)(ngfgI),(-@pb)(79/-(,p-pObz)r(ng/g)
nla
nia@
nia
5.92- 1180 6,14- 1230
29,6 -1180 123 - 1230
n/a
-!;@Wa
n/a
r@a-
n/a
-wi;
n/a
iVa
5.85 - ll-,O 58 1170 1)7-"l170L- n/a
nia
n@a
n/a
kioncester%vasnot detectabic!quantifiaibnl@e,iver.Tatrfioxrthecgncentrat@cnrangeoC4 94 - 14@10ppb
Artachment C: LOQ summary 3M Environme.-ital Laboratory
FACT-,Nvf-1.1 Extractionof PFOS from
Page 14 of 15 Page 142
3m Medical ]Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
,PrepDate(s): 11112/98
lAnalyst(s): IRWW-IAS
ISampleMatrix: Monkey L_ iver I
@Method[Revision FACT-M 1.0
Target
FC-,Mix
lAnalyte(s):
Ion Pair Standard Curves--Tissues
;StudyNumber:
@CrossValidation
Equipment Number:
FinalSolvent& TN Number:;,MeOH TN-A-20"76
i
Blank Tissue/d]entifier*. 'Liver
FC Mix Std Approx.0.500ppm: IW398-1004
@FC Mix Std Approx. 5.00ppm-.' JW399-1003 i
IFC Mix Std Approx.50.0ppm: IW398-1002
i
ISurrog2teStdApprox. 16.5ppm:
IW398-989
!ActualConcentrationosf StandardsintheFC Mix
PFOS
PFOSA
PFOSAA i
StdConc.
Std Conc. Std Conc. 1
ETFOSE StdConc.
ug/mL
ug/mL
ug/mL I ug/mL
0.501
0.497
0.500 1 0.490
0.501 0.501
0.497 0.497
0.500 0.500
0.490 0.490
0.501 -F-0.497
0.500
0.490
0.501 5.01
1 0.497 1 0.500
4.97
5.00
0.490 4.90
5.01
4.97
5.00
4.90
5.01
4.9-7
5.00
4.90
50.1
49.7
50.0
49.0
POAA
PFOSEA
StdConc. I Std Conc.
ug/mL
ug/mL
0.495
0.494
0.495 1 0.494 0.495 1 0.494
0.495 1 0.494
0.495
0.49
4.95
4.94
4.95
4.94
4.95
4.94
49.5
49.4
All Am't Spiked mL 0.002 0.004 0.010 0.020 0.040
0.020 1 0.030 1 0.00.4
All Li coner,7 g/ml 0.169 0.169 0.169 0.169 0 169 o@ 169
0-169 169
C21culated Concentrations of Standards in the S2mple Matrix.
PFOS
PFOSA
PFOSAA
ETFOSE
FinalConc. FinalConc. FinalConc. FinalConc.
POAA I PFOSEA FinalConc. FinalConc.
ng/9
ng/g
ng/g
ng/g
ng/g i ng/g
5.93
5.88
5.92
5.80
5.86
5.85
11.9
11.8
11.8
11.6
11.7
11.7
29.6
29.4
29.6
29.0
29.3
29.2
59.3
58,8
59.2
58.0
58.6
58.5
119
118
118
116
11i
117
296
294
296
290
293
292
593
588
592
580
586
585
889
882
888
870 i 879
877
1186
1176
1183
11 0
1172 1 1169
Surrog2tel All Std Conc. Am't
Spiked ug/mL rnL 16.50 0.005
Surrogate' FinalConc. ng/g
488 2
ValidatedR2nzes- ApproximateConcentrations
Liver
PFOS
PFOSA
PFOSAA
Rabbit
40 - 1000ppb 20 - 1200ppb 180 - 1900ppb
Bovine
60 - 1200ppb 30 - 1200ppb 120 - 1200ppb
Rat
60 - 1200ppb 170 - 1200ppb 60 - 1200ppb
Nionkev 60 - 1200ppb 190 - 1200ppb 120 - 1200ppb
ETFOSE-OH 190 - 1800ppb 120 - 1200ppb 120 - 1200ppb 60 - 1200 opb
POAA 80 - 1800ppb 80 - 1200 ppb 60 - 1200 ppD 120 - 1200 ppb
-PFOSEA 60 - 1200 ppb 30 - 1200 ppb 120- 1200 ppb 120- 1250 ppb
Attachment D@ Calibratiosntandard concentratio\nvorksheet
3M Env4-ronmental Laboratory
FACT-M- t.I ExtractioonfPFOS from Liver
Page 15 of 15 Page 143
3m Medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
3M ENVIRONMENTAL
LABORATORY
METHOD
ANALYSIS OF FLUOROCHEMICALS HPLC-ELECTROSPRAYMASS
IN LIVER EXTRACTS SPECTROMETRY
USING
Method Number: FACT-M-2.1
Author: Lisa Clemen Approved By:
Adoption Date: 05/26/98
Revision Date: 0& lo3 Ick
Laboratory Manager
Date
Group Leader
Date
Technical Reviewer
Date
1.0 SCOPE AND APPLICATION 1.1 Scope: This method is for the analysisof extractsof liveror othertissuesfor flUOTochemical
surfactantsusing HPLC-electrospray/mass spectrometry.
1.2 Applicable Compounds: Potassium perfluorooctanesulfonate,anionic fluorochemical surfactants,or other ionizablecompounds.
1.3 Matrices: Rabbit,rat,bovine, and monkey liversor other liversas designated in the validationreport.
Word 7.0.1!95 3M Environmental
FACT-M-2.1 Analysisof LiverExtractUsing ES/,MS
Laboratory
Page I of 9 Page 144
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2.0 SUMNIARY OF METHOD
2.1 This method describesthe analysisof fluorochemicalsurfactantesxtractedfrom liverusing HPLC-electrospray/tmass spectrometry.The analysisisperformed by monitoringa single ion characteristiocf a particulafrluorochemical,such as the potassium perfluorooctanesulfonat(ePFOS) anion,M/Z= 499. Samples may alsobe screenedto verifycompound identification.
3.0 DEFINITIONS
3.1 Atmospheric Pressure Ionization(API): The Micromass platform systems allow for variousmethods of ionizationby utilizinvgarioussources,probes,and interfaces.These includebut arenot limitedto:ElectrosprayIonization(ESI),Atmospheric Pressurechemical Ionization(A-Pcl),,Thermospray,etc.The ionizationprocess inthesetechniquesoccurs at atmospheric pressure(i.en.ot under a vacuum).
3.2 Electrospray Ionization(ES, ESI): a method of ionizationperfon-nedatatmospheric pressure,whereby ionizationoccursthrough thq productionof tinycharged dropletsin a strongelectricaflield.
3.3 Mass Spectrometry, @NlassSpectrometer (MS), Tandem Mass Spectrometer (MS/MS): The API platformsare equipped with quadrupole mass selectivedetectors.Ions are selectivelydiscriminatedby mass tocharge ratio(m/z) and subsequentlydetected.A single MS may be employed for ion detectionor a series(MSNTS) formore specificftagmentation information.
3.4 Conventional vs.Z-spray probe interface:The latestmodels of Micromass platfon-n svstems (post1998) utilizae "Z-spray"conformation.The sprayemittedfrom a probe is orthogonalto the cone aperture.In theconventionalconformationitisaimed directlyat the cone aperture,afterpassing througha tortuouspathway in the counterelectrode.Though the configurationisdifferentt,he methods of operation,cleaning,and maintenance are the same. However, Z-spray components and conventionalcomponents arenot compatiblewith one another,but only with similarsystems Z-spray components are compatiblewith otherZspray systems, etc.)
3.5 Mass Lynx Software: System softwaredesigned forthe specificoperationof theseplatform systems. CurrentlyMassLynx has Windows 95 and WindowsNT 3.1 versions.All versions are similar.For more detailssee themanual specificto the instrument(Micromass Platform IIor Quattro11MassLynx or MassLynx NT USER'S GUIDE).
4.0 WARNINGS AND CAUTIONS
4.1 Health and Safety Warnings:
4.1.1 Use cautionwith the voltagecablesforthe probe. The probe employs a voltageof approximately5000 Volts.
4.1.2 When handlina samples or solventswear appropriateprotectivegloves,eyewear, and clothing.
1.@*or-d.0.1/95
FACT-M-2.1 Anatysisof LiverExtractUsing ES/'IvIS
3M Env-@ronmen-Lal Laboratory
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4.2 Cautions: 4.2.1 Do not ran solventpumps above capacityof 400 bar (5800 psi).Ifpressuregoes over 400 bar,the HP I100 willinitiataeutomatic shutdown. 4.2.2 Do not run solventpumps todryness.
5.0 INTERFERENCE& 5.1 To minimize interferencewshen analyzingsamples forperfluorooctanoate(POAA),teflon
should not be used forsample storageor any partof instrumentationthatcomes in contact with the sample or extract.
6.0 EouiPMENT 6.1 Equipment listecbrelow may be modified in orderto optimize thesystem.
6.1.1 Micromass ElectrosprayMass Spectrometer 6.1.2 HPI 100 low pulse solventpumping system and autosampler.
7.0 SUPPLIF-S AND MATERIALS 7.1 Supplies
7.1.1 High puritygrade nitrogengas regulatedto approximately 100 psi 7.1.2 HPLC column, specifictsobe detenninedby theanalyst. 7.1.3 Capped autovialsor capped 15 mL centrifugetubes.
8.0 RFAGFNTS AND STANDARDS 8.1 Reagents
8.1.1 Methanol,HPLC grade or equivalent. 8.1.2 ASTM, Type Iwater,Milll_QTMwater,allwater used inthismethod should be
Milli-Q' waterand may be providedby a Milli-QTOC Plus system. 8.1.3 Ar=onium acetate,reagentgradeor equivalent. 8.2 Standards 8.2.1 Typically one method blank, one matrix blank, and ten matrix standards are
preparedduring the extractionprocedure. See FACT-M-1.1.
9.0 SAMPLE HANDLING 9.1 Fresh matn*x standardsareprepared with each analysis.Extractedstandardsand samples
are storedin capped autovialsor capped 15 mL centrifugetubesuntilanalysis. 9.2 Ifanalysiswillbe delayed,extractedstandardsand samples may be storedatroom
temperatureor refrigerateadt4' C untilanalysiscan be performed.
FACT-M-2.1 Analysisof LiverExtractUsing ES/MS
3M Env4@ronmental Laboratory
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10.0 OUALITY CONTROL 10.1 Matrix Blanks and Method Blanks
10.1.1 Anaiyze a method blank and matrixblank pn*ortoeach calibratiocnurve.
10.2 Matrix Spikes
10.2.1 Analyze a matrix spikeand matrixspikeduplicatewith each analysis.With a minimum of 2 spikesper batch.
10.2.2 Expected concentrationswillfallin themid-range of theinitiaclalibratiocnurve. Additionalspikeconcentrationmsay fallinthelow-rangeof theinitiaclalibration curve.
10.2.3 See section13 to calculatepercentrecovery.
10.3 Continuing Cafi@brationChecks
10.3.1 Analyze a mid-range calibratiosntandardafterevery tenthsample. Ifa significant change ( 30%) inpeak areaoccurs,relativeto the initiasltandardcurve,stop the run. Only those samples analyzedbefore the lastacceptablecalibrationstandard willbe used. The remaining samples must be reanalyzed.
10.3.2 See section13 to calculatepercentdifference.
11.0 CALIBRATION AND STANDARDIZATION
11.1 Analyze the extractedmatrix standardspriorto and followingeach setof extracts.The average of two standardcurveswillbe plottedby linearregression(y = my b),not forced through zero,usingMassLynx or othersuitablesoftware.
11.2 Ifthe curve does not meet requirements,perform routinemaintenance or reextractthe standardcurve (ifnecessary)and reanalyze.
11.3
For purposes of accuracywhen quantitatinlgow levelsof analyte,itmay be necessaryto use the low end of the calibratiocnurve ratherthan the fullrange of the standardcurve. Example: when attemptingto quantitateapproximately 10 ppb of analyte,generatea calibrationcurve consistingof the standardsfrom 5 ppb to 100 ppb ratherthan the full range of thecurve (5 ppb to 1000 ppb). This willreduce inaccuracyattributetdo linear regressionweighting of high concentrationstandards.
12.0 PROCEDURES
12.1 Acquisition Setup
12.1.1 Click on startbuttonin the AcquisitionControl Panel.Set up a sample list.Assign a filenameusing MO-DAY-last digitof year-samplenumber, assigna method (MS) for acquiring,and type in sample descriptions.
12.1.2 To createa method clickon scan button inthe Acquisitioncontrolpanel and select SIR (SingleIon Recording)or MRM. Set IonizationMode as appropriateand mass to 499 or otherappropriatemasses. A fullscan isusuallycollectedalong with the SIRS. Save acquisitionmethod. IfMS/MS instrumentsare employed, additional product ion fragmentationinformationmay be collected.See i'vflcromass
FACT-M-2.1 AnalysisofLiverExtractUsing ES/NIS
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3M Ervironmental Laboratory
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MassLynx GT7-'IDETO DATA ACQUISITION MR.M (MultipleReactionMonitoring).
foradditionalinformationand
12.1.3 Typicallythe sample listbegins with the firsstetof liverstandardsand ends with the second setof standards.
12.1.4 Samples are analyzed with a continuingcalibratiocnheck injectedafterevery tenth sample.-Solvent blanksshould be analyzed pen'odicalltyo monitor possibleanalyte carryoverand are not consideredsamples but may be includedas such.
12.2 Using the Autosampler
12.2.1 Set up sample trayaccordingtothe sample listpreparedin section12.1.1.
12.2.2 Set-up theHP II00/autosampleratthe followingconditionsor atconditionsthe analystconsidersappropriateforoptimal response.Record actualconditionsin the instrumehtlogbook:
12.2.2.1Sample size= 10 pL injectiownith a sample wash
12.2.2.2Inject,sample= I
12.2.2.3Cycle time = 13.5minutes
12.2.2.4Solvent ramp
Time
ivfeOH
0.00 min.
40%
8.0 min.
90%
71-1.0 min.
90%
12.0 m-in. @-40%
2.0 mM Ammonium acetate
60% 10% 10% 60%
12.2.2.5Press the"Start"button.
12.3 Instrument Sep-up
12.3.1 Refer to ETS-9-24.0 formore details.
12.3.2 Check the solventlevelinreservoirsand refililfnecessary.
12.3.3 Check the stainlessteelcapillaryatthe end of theprobe. Use an eye piece to check the tip.The tipshould be flatwith no jagged edges.Ifthetipisfound to be unsatisfactoryd,isassemblethe probe and replacethestainlessteelcapillary.
12.3.4 Set HPLC pump to"On". Set the flow to 10 - 500 uL/min or as appropnate. Obser-vedropletscoming out of the tipof theprobe. Allow to equilibratfeor approximately 10 minutes.
12.3.5 Turn on thenitrogen.A finemist should be expelledwith no nitrogenleaking around the tipof the probe.Readjust the tipof theprobe iI'no mist isobserved.
12.3.6 The instrumentuses theseparametersatthe followingsettings.These settingsmay change inorder to optimizethe response:
FACT-M-2.1 A.nalysiosf LiverExtractUsing ES/NIS
PaLe 5 o[9
3M Envi-ronmenL-al Laboratory
Page 148
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12.3.6.1Drying gas 250-400 litersihour 12.3.6.2 ESI nebulizinggas 10-15 liters/hour 12.3.6.3 LC constantflow mode flow rate10 - 500 uL/min 12.3.6.4Pressure<400 bar (Thisparameter isnot set,itisa guide to ensure the
instr.imenitsoperatingcorrectly.)
12.3.7 Carefullyguide the probe intothe opening. Insertprobe untilitwillnot go any further.Connect the voltagecables to theprobe.
12.3.8 Printthe tune page,with itsparameters,and storeitinthe study binderwith a copy taped intothe instrumentlog.
12.3.9 Usinc,,thecross-flowcounterelectrodeinthe ES/MS source isrecommended for the analysisof biologicalmatrices.
12.3.10 Click on startbuttonin theAcquisitionControl Panel. Pressthe startbutton at top of sample list.Ensure startand end sample number includesallsamples to be analyzed.
13.0 DATA ANALYSIS AND CALCULATIONS 13.1 Calculations:
13.1.1 Calculatematrix spikepercentrecoveriesusingthe followingequation:
% Recovery
Observed Result-Background Result x 100 Expected Result
13.1-.2Calculatepercentdifferenceusing the followingequation:
% Difference= Ext)ectedConc. - CalculatedConc. x 100 Expected Conc.
13.1.3 Calculateactualconcentratioonf PFOS anion intotalliver(mg):
ug PFOS aruo*n calc.from stdcurve g of liverused foranalysis 1" ug mg
x Totalniassofliver(g)
14.0 METHOD PERFORNIANCE 14.1 Method DetectionLimit(MDL) and Limit of Quantitation(LOQ) aremethod, analyte,and
matrix specific.Pleasesee ETS-8-1.1,Attachment B, fora listinogf currentvalidated MDL and LOQ values.
14.1 14.2 Solvent Blanks, Method Blanks, and Matrix Blanks
14.1.1 Solvent blanks,method blanks,and matrix blanks values are must be below the lowest standardinthe calibratiocnurve.
14.2 Calibration Curves 14.2.1 The r-v'aluefo,-the calibratiocnurve must be 0.980 or better.
FACT-M-2.1 AnalysisofLiverExtractUsing ES/MS
Page 6 of 9
3M Environmental '@.Jaboratory
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Report No. FACT TOX-@V30 laboratory Reauest Number-U2279
14.3 Matrix Spikes
14.3.1 Matrix spikepercentrecoveriesaremust be within 30% of the spiked concentration.
14.4 Continuing Calibration Verirications
14.4.1 Continuing calibrationverificatiopnercent recoven'esmust be-+ 30% of the spiked concentration.
14.5 If criterialistedin thismethod performance sectionisn'tmet, maintenance may be performed on the system and samples reanalyzed or other actions as determined by the analyst.Document allactionsin the appropriatelogbook.
14.6 If data are to be reported when performance criteriahave not been met, the data must be footnoted on tablesand discussed in the textof the report.
15.0 POLLUTION PREVENTION AND WASTE MANAGEMENT
15.1 Sample waste is disposed in biohazard containers,flammable solvent waste isdisposed in hitc@,hBTU containers,and glasspipettewaste'isdisposed in broken glasscontainers. All containers are located in the laboratory.
16.0 RECORDS
16.1
Each pac7egenerated for a study must have the following information included eitherin the header ocr' hand writtenon the page: study or projectnumber, acquisitionmethod, integrationmethod, sample name, extractiondate,dilutionfactor(ifapplicable),and analyst.
16.2 Printthe tune page, sample lista,nd acquisitionmethod from MassLynx to include in the appropriate study folder. Copy these pages and tape into the instrument runlog.
16.3 Plot the calibrationcur-veby linearregression,weighted I/x,then printthese graphs and store in the study folder.
16.4 Printdata integrationsummary, integrationmethod, and chromatograms, ftom MassLynx, and store in the study folder.
16.5 Summar-ize data using suitablesoftware (Excel 5.0) and store in the study folder,see Attachment A for an example of a summary spreadsheet.
16.6 Back up electronicdata to appropriatemedium. Record in study notebook the filename and locationof backup electronicdata.
17.0 TABLES, DIAGRAms. FLOWCHARTS, AND VALIDATION DATA 17.1 Attachment A: FACT-,M-2.1 Data reportingspreadsheet
FACT-M-2.1 Analysis of Liver ExtT-acUtsing ES/MS
3M Env4-ronmental Laboratory
Pa,,e7 of 9 Page 150
3m Medical Departmert Study: T-6295.7
ReDcrt No. FACT TOX-030 laboratory Request Number-U2279
18.0REFERENCES 18.1 FACT-M-1.1, "Extractionof Potassium Perfluorooctanesuflonateor Other Fluorochemical
compounds from Senim forAnalysisUsing HPLC-ElectrosprayfMass Spectrometry 18.2 ETS-9-24.0, "Operation and Maintenance of the Nlicromass Atmospheric Pressure
Ionization/MassSpectrometer QuattroIItn'plequadrupole Systems" 18.3 The validationTCportassociatedwith thismethod isFACT-M-1.1-V & 2.1-V-1,
19.0 AFFECTED DocuMENTS 19.1 FACT-M- 1.1,"Extractionof Potassium Perfluorooctanesulfonate from Liver forAnalysis
Using HPLC-Electrospray/Mass Spectrometry"
20.0 REV]SIONS
Revision Number.
I
Reason For Revision Section 6.1.2 Clarificatioonf HPI 100 system components. Section 11.1 Average of two curves,not standardvalues,areused for plottinglinearregression. Section 12.2.2.4Clarificatioonf solventramp. Section 17.1Changed from attachmentB toA.
Revision Date
05/04/'99
FACT-M-2.1 Analysisof LiverExtractUsing ES/NIS
3M E,-ivironmental Laboratory
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Report No. FACT TOX-030 laboratory Request Number-U2279
Laboratory Study
Study: Test Material: Matrix/FinaSlolvent: Method/Revision: AnalyticalEquipment System Number: InstrumentSoftwareNersion: Filename: R-Squared Value: Slope: Y Intercept: Date of Extraction/Analysr-. Date of Analysis/Analyst:
Group Dose--
Sample#
Concentration ug/mL
InitiaVlol. niL
Dilution Factor
FinalConc. ug/mL
Slope: Taken from linearregressionequation. Grc)up/Dose: Taken from thestudyfolder. S2mple#: Taken from thestudyfolder. Concentration (ug/mL): Taken from theMassLynx integratiosnummary. InitiaVlolume (mL): Taken from thestudyfolder. DilutionFactor: Taken from thestudyfolder. FinalConc. (ug/mL): Calculatedby dividingtheinitiavlolume ftom theconcentration
Attachment A: Data Sheet
FACT-M-2.0 Analysisof LiverExtractUsing ES,,NIS
3M Environmental Laboratory
Page 9 of 9 Page 152
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Report No. FACT TOX-030 laboratory Request Number-U2279
3M ENVIRONMENTAL
LABORATORY
METHOD
ExTRAcTioN OF PoTAssruim PERFLUOROOCTANESULFONATE
FLUOROCHE@MICAL
COMPOUNDS FROM SERUIM OR OTHER FLUID
USING HPLC-ELECTROSPRAY/NIASS
SPECTROMETRY
OR OTHER FOR A.@NALysis
Method Number: FACT-M-3.1
Adoption Date: 04/22/98
Author: Lisa Clemen, Glenn Langenburg
Revision Date: to Iat(ctS
Approved By:
Labor4dtoryManager
lvt@,--L @L=@ @7ro@UPLeader
:ix; @il -4 L4)Y-@K
Technical
Reviewer
Date
'? Date
C11.@3l@? Date
1.0 SCOPE AND APPLICATION 1.1 Scope: This method isfortheextractioonf potassiumperfluorooctanesulfonat(ePFOS)
or otherfluorochemicalcompounds from serum or otherfluid. 1.2 Applicable compounds: Fluorochemicalsurfactantosr otherfluorinatecdompounds.
1.3 Matrices: Rabbit,rat,bovine,and monkey serum, ratwhole blood,and ratmilk curd.
Word 6/95 3M Environmental
FACT-M-3.1 ExtractioonfPFOS ftom Serum and OtherFluids
Laboratory
Page I of 17 Page 153
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Report No. FACT TOX-030 laboratory Request Number-U2279
2.0SUMNIARY OF METHOD 2.1 This method describestheprocedureforextractinpgotassium perfluorooctanesulfonate
(PFOS) orotherfluorochemicalfstom serum,blood,or milk curdusingan ion pairing reagentand 5.0ml of ethylacetate.In thismethod, seven fluorochemicalswere extracted:PFOS, PFOSA, PFOSAA, ETFOSE-OH, POAA, PFOSEA, and FC-807 monoester (see3.0 Definitions)A.n ionpairingreagentisadded tothesample and the analyteionp@irispartitioneidntoethylacetate.Four ml of extractareremoved and put onto a nitrogenevaporatoruntildry.Each extractisreconstituteidn 1.0ml of methanol, then filteretdhrough a 3 cc plastiscyringeattachedto a 0.2pLm nylonfilteirntoglass autovials.
3.0 DEFINITIONS 3.1 PFOS: perfluorooctanesulfona(taenionof potassiumsalt)C,F,,SO,3.2 PFOSA: perfluorooctanseulfonylamideC,F,,SO,NH,
3.3 PFOSAA: perfluorooctanesulfonylamido (ethyl)acetatCe,F,.,SO,N(CH2CH,)CH,CO,-
3.4 ETFOSE-OH: 2(N-ethylperfluorooctasnuelfonamido)-ethylalcohol C,F,,SO2N(CH2CH,)CH,CH,OH
3.5 POAA: perfluorooctanoa(taenionof ai=onium saltC),F,,COO-
3.6 PFOSEA: perfluorooctanseulfonylethylamideC,F,,SO,N(CHCH,)H
3.7 FC-807 monoester C,F1,SO,N(CH2CH3)CH2CH20-PO,H)
3.8 Surrogatestandard:IH- IH-2H-2H perfluorooctanseulfonicacid
4.0 WARNINGS AND CAUTIONS
4.1 Health and safetywarnings 4.1.1 Use universalprecautionse,specialllyaboratorycoats,goggles,and gloveswhen handlinganimal tissuew,hich may containpathogens.
5.0 INTERFERENCES
5.1 There areno known interferenceastthistime.
6.0 EOUIPMENT 6.1 The followingequipment isusedwhileperformingthismethod. Equivalentequipment is
acceptable. 6.1.1 Vortex mixer,VV@R, Vortex Genie 2 6.1.2 CentrifugeM,istral1000 orIEC 6.1.3 Shaker,Eberbach or VWR 6.1.4 Nitrogenevaporator,Organomation 6.1.5 Balance ( 0.100 g)
FACT-M-3.1
Extractionof PFOS from Serum or Other Fluid
3M Environmental Laboratory
Page 2 of 17 Page 154
3m medical Department Study: T-6295.7
Report No. FACR TOX-030 laboratory Request Number-U2279
7.0 SUPPLIES AND MATERIALS 7.1 Gloves 7.2 Eppendorf or disposablepipettes 7.3 ElectronicpipettorE,ppendorf or equivalent 7.4 Graduated pipettes 7.5 Nalgene bottlesc,apable of holding250 mL and I L 7.6 Volumetric flasks,glass,typeA 7.7 Volumetric pipets,glass,typeA 7.8 I-CHEM vials,glass4,0 mL glass 7.9 Crimp cap autovials 7.10 Centrifugetubes,polypropylene,15 niL 7.11 Labels 7.12 Syringes,capable of measuring 5 @iLto 50 gL 7.13 Syringes,disposableplastic3, cc 7.14 Syringe filtersn,ylon,0.2 gm, 25 mm 7.15 Timer Note: Priorto using glassware and bottlesr,-ins3e times with methanol and 3 timeswith
Milli-Q' water. l@insesyringesa minimum of 9 timeswith methanol,3 rinsesfrom 3 separatevials.
8.0 REAGENTS AND STANDARDS 8.1 Type Ireagentgrade water,Milli-QT-mor equivalent;allwater used inthismethod should
be Milli-Q' water and may be providedby a Milli-TOQC plUSTIISystem
8.2 Sodium hydroxide (NaOH), J.TBaker or equivalent 8.3 Tetrabutylammonium hydrogen sulfate(TBA),Kodak or equivalent 8.4 Sodium carbonate (Na@C03), J.T.Baker or equivalent 8.5 Sodium bicarbonate(NaHC03), J.T.Baker or equivalent 8.6 Ethyl acetate,Omnisolv, glassdistilleodr HPLC grade 8.7 Methanol, Oninisolv,glassdistilleodr HPLC grade 8.8 Serum or blood,frozenfrom supplier 8.9 Control matrix or blank matrix forpurpose of standards,QC checks,blanks,etc. 8.10 Fluorochemical standards
8.10.1 PFOS (3M SpecialtyChemical Division),molecular weight= 538 8.10.2 PFOSA (3M SpecialtyChemical Division),molecularweight = 499
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FACT-M-3.1 ExtractioonfPFOS from Serum or OtherFluid
Laboratory
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8.11 8.12
8.10.3 PFOSAA (3M SpecialtyChemical Division),molecularweight= 585
8.10.4 ETFOSE-OH (3M SpecialtyChemical Division),molecularweight = 571
8.10.5 POAA (3M SpecialtyChemical Division),molecularweight= 431
8.10.6 PFOSEA (3M SpecialtyChemical Division)m,olecularweight= 527
8.10.7 FC-807 monoester (3M SpecialtyChemical Division).FC-807 isa mixture of triesterd,iestera,nd monoester fluorochemicalcomponents. The monoester molecular weight = 650
8.10.8 Surrogatestandard:4-H, perfluorooctanesulfonicacid(1-H,I-H, 2-H, 2-H C,F13SO,H) molecular weight = 428
8.10.9 Other fluorochemicals,as appropriate
Reagent preparation
8.11.1 10 N sodium hydroxide (NaOH): Weigh approximately200 g NAOH. Pour intoa 1000 mL beaker containing500 mL Milll_QTM water,mix untilallsolidsare dissolved.Storeina I L Nalgene bottle.
8.11.2 1 N sodium hydroxide (NaOH): Dilute 10 N NAOH 1:10. Measure 10 mL o f 10 N NAOH solutionintoa 100 niL volumetric flaskand diluteto volume using Milli_QTIwater. Storeina 125 mL Nalgene bottle.
8.11.3 0.5M tetrabutyalmmonium hydrogen sulfate(TBA): Weigh approximately 169 g of TBA intoa I L volumetriccontaining500 mL Milli_QTIwater.Adjust to pH 10 using approximately44 to 54 mL of 10 N NAOH and diluteto volume with Milli_QTIwater. While adding the lastmL of NAOH, add slowly because the pH
changes abnlptly.Storeina I L Nalgene bottle.
8.11.3.1 TBA requiresa check priorto each use to ensurepH = 10. Adjust as needed using I N NAOH solution.
8.11.4 0.25 M sodium carbonate/sodiumbicarbonatebuffer(Na2C03/NaHC03):
Weigh
approximately26.5 g of sodium carbonate(NaC03) and 21.0g of sodium
bicarbonate(,NaHC03) intoa I L volumetricflaskand bringtovolume with MilliQ' water. Storeina I L Nalgene bottle.
Standards preparation
8.12.1 PreparePFOS standardsforthestandardcurve.
8.12.2 Prepareotherfluorochemicalstandardsa,s appropriateM.ulticomponent fluorochemicalstandardsareacceptable(forexample, one working standard solutioncontaining1.00ppm PFOS, 1.02 ppm PFOSA, 0.997 ppm PFOSA.,k, and 1.10ppm EtFOSE-OH.)
8.12.3 Weigh approximately 100 mg of PFOS intoa 100 ml volumetn'cflaskand record the actualweight.
8.12.4 Bring to volume with methanol fora stockstandardof approximately 1000 ppm (pg/ml).
8.12.5 Dilutethe stocksolutionwith methanol fora working standardI solutionoF approximately 50 ppm.
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FACT-M-3.1 ExtractioonfPFOS from Serum orOtherFluid
Laboratory
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8.13
8.12.6 Dilutethe stock solutionwith methanol fora working standard2 solutionoc approx. 5.0 ppm.
8.12.7 Dilutethestocksolutionwith methanol fora working standard3 solutionof approx. 0.50 ppm.
Surrogate stock standard preparation
8.13.1 Weigh approximately50-60 mg of surtogatestandard1-H,I-H,2-H, 2-H, C,F,,SO,H intoa 50 ml volumetricflaskand recordthe actualweight.
8.13.2 Bring to volume with methanol fora surrogatestockof approximately 1000-1200 ppm.
8.13.3
Prepare a surrogateworking standard.Transferapproximately0.5 ml of surrogatestockto a 50 ml volumetricflaskand bringto volume with methanol fora working standardof 10-20ppm. Record the actualvolume transferred.
9.0 SAMPLE HANDLING
9.1 All samples are receivedfrozenand must be kept frozenuntilthe extractionisperfor-rned.
10.0 ()UALITY CONTROL
10.1 Matrix blanks and method blanks
10.1.1 Extract two 1.0 mL aliquotsof the appropriate matrix (serum or blood, with blood samples diluted1:1with Milli-Q""w'ater)followingthisprocedureand use as matrix blanks. See 11.1.4.
10.1.2 Extracttwo 1.0ml aliquotsof Milli-Q' water followingthisprocedureand use as method blanks.
10.2 Matrix spikes
10.2.1 Prepare and analyzematrixspikeand matrix spikeduplicatesamples to determine the accuracy of the extraction.
10.2.2 Prepare each spike using a sample chosen by theanalyst,usuallythe control matrix receivedwith each sample set.
10.2.3 Expected concentrationswillfallin the mid-range of the initiaclalibrationcurve. Additionalspikesmay be includedand may fallinthe low-rangeof the initial calibratiocnurve.
10.2.4 Prepare one matrix spikeand matrixspikeduplicateper 40 samples, with a minimum of 2 matrix spikesper batch.
10.3 Continuing calibration checks
10.3.1 Prepare and analyzecontinuingcalibrationcheck samples toensure the accuracy of the initiaclalibratiocnurve. Ifthe percentdifferencebetween the initiaclurve and the continuingcheck differby >30%, re-analyzesamples analyzed afterthe lastacceptablecheck.
10.3.2 Prepare one check per group of ten samples. For example, ifa sample set= 34, prepare and extractfourchecks.
3M Environmental
FACT-M-3.1 Extractionof PFOS from Serum or Other Fluid
Laboratory
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Report No. FACT TOX-030 laboratory Request Number-U2279
10.3.3 Prepare each continuingcalibratiocnheck ftom the same matrix used to prepare the initiaclurve.
10-3.4 The expected concentrationwillfallwithinthe mid-range of the initiaclalibration curve. Additionalspikesmay be includedthatfallin the low-range of the initial calibratiocnurve. This isnecessaryiftheanalystmust quantitateusingonly the low end of the calibratiocnurve (forexample, 5 ppb - 100 ppb, ratherthan 5 ppb - 1000 ppb).
11.0 CALIBRATION
AND STANDARDIZATION
11.1 Prepare matrix calibrationstandards
Note: Blood coagulatesin air;thereforem,inimize aircontactuntildilution.At this point,add TBA and bufferto each centrifugetube as instep 12.9,then add 1.0mL of the dilutedmatrixsample to each tube.
11.1.1 Transfer I n-lLof serum or I mL of blood (blood isdiluted 1:1 with Milli_QT,'vl water) to a 15 mL centrifugetube. The blood is similarin composition to milk curd and can be used inplace of milk curd forstandardcur-veswhen extracting thatmatrix.
11.1.2 Ifmost sample volumes are lessthan 1.0mL, extractstandardswith matrix volumes equal to thesample volumes. Do not extractbelow 0.50 mL of matrix. Record the sample volume on the extractionsheet.
11.1.3 While preparinga totalof twenty aliquotsin 15 ml centrifugetubes,mix or shake between aliquots.
11.1.4 Two I mL aliquotso,r otherappropriatevolume, serve as matrixblanks. Typicallyuse the standardconcentrationsand spikingamounts listedinTable 1, atthe end of thissection,to spike,in duplicate,two standardcurves,fora totalof eighteenstandardsand two matrix blanks.
11.1.5 Referto validationreportsFACT-M-3.1-V-1 and FACT-M-4.1-V-1, which list theworking rangesand theLinearCalibrationRange (LCR) forcalibration curves.
11.1.6 Use Attachment D as an aidin calculatingthe concentrationsof the working standards.See Section 13.0 tocalculateactualconcentrationsof PFOS in calibrationstandards.
11.2 To each standard,blank,or QC check,add appropriateamount of surrogateworking standardforthe concentrationto fallwithinthe calibratiocnurve range 5 ppb -1000 ppb.
11.3 Extract spiked matrix standards following 12.6-12.16 of thismethod. Use these standards to establisheach initiaclurve on themass spectrometer.
3M Environmenk--al
FACT-M-3.1
Extractionof PFOS from Serum or Other Fluid
Laboratory
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3m Medical Department St,-,dy:T-6295.7
Report No. FAC-- TOX-030 laboratory Request Number-U2279
TableI
Approximate spikingamounts forstandardsand spikes
using1.0ml ofmatrix
Working standard
@iL
Approx. finalconc.of
(approx.conc.)
analytein matrix
-
-
Blank
0.500 ppm 0.500 ppm 5.00 ppm 5.00 ppm 5.00 ppm 50.0 ppm 50.0 ppm 50.0 ppm
10
0.005 ppm
20
0.010 ppm
5
0.025 ppm
10
0.050 ppm
20
0.100 ppm
5
0.250 ppm
10
0.500 ppm
15
0.750 ppm
50.0 ppm
20
1.00 ppm
Table 2
Approximate spiking amounts for standards and spikes
using 0.5 mi of matrix
Working standard
@iL
Approx. finalconc.of
(approx.conc.)
analytein matrix
-
Blank
0.500 ppm 0.500 ppm 5.00 ppm 5.00 PPM 5.00 ppm 50.0 ppm 50.0 ppm
5
0.005 ppm
10
0.010 ppm
2.5
0.025 ppm
5
0.050 ppm
10
0.100 ppm
2.5
0.250 ppm
5
0.500 ppm
50.0 ppm 50.0 ppm
7.5
0.750 ppm
10
1.00ppm
12.0 PROCEDURF,
12.1 Obtain frozensamples and allow to thaw.
12.2 Vortex mix for 15 seconds,thentransfer1.0 mL or otherappropriatevolume to a 15 mL polypropylene centrifugetube. For blood samples,remove 0.5 mL and diluteto 1.0mL with Milli-Q' water.As soon afterdilutingas possiblep,ipetdilutedblood intoTBAbuffermixture shown in step12.9and mix well.
12.3 Retum samples to freezerafterextractionamount has been removed.
FACT-M-3.1 Extractioonf PFOS from Serum or OtherFluid
3M Environmental Laboratory
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12.4 Record the volume on the extractionworksheet. The finalmethanol volume equals the volume transferredfrom the sample.For example, if0.5 mL isremoved fora blood sample, the finalmethanol volume willequal0.5 mL.
12.5 Label the tube with the study number, sample UD, dateand analystinitialsS.ee attached worksheet fordocumenting theremaining steps.
12.6 Spike each matrix with the appropriateamount of standardas describedin 11.1 or Table I or 2 in thatsectionforthecalibratiocnurve standards.Also preparematrix spikesand continuing calibratiosntandards.
12.7 Spike allsamples, includingblanksand standards,ready forextractionwith surrogate standardas describedin 11.2.
12.8 Vor-texmix the standardcur-veswnples,matrix spikesamples, and continuingcalibration samples for 15 seconds.
12.9 To each sample, add I mL 0.5 M TBA and 2 mL of 0.25 M sodium carbonate/sodium bicarbonatebuffer.
12.10 Using a volumetricpipette,add 5 mL ethylacetate.
12.11 Cap each sample and put on theshaker for20 minutes.
12.12 Centrifugefor20 to25 minutes atapproximately3500 rpm, untillayersarewell separated.
12.13 Transfer4 mL of organiclayer,usinga 5 mL graduated glasspipettet,o a clean 15 mL centrifugetube.Label thisfreshtube with the same informationas In 12.5.
12.14 Put each sample on the analyticanlitrogenevaporatoruntildry,approximately 2 to 3 hours.
12.15 Add 1.0mL or otherappropriatevolume of methanol to each centrifugetube using a graduatedpipette.Methanol volume to add equalsthe initiavlolume of sample used for the extraction.
12.16 Vortex mix for30 seconds.
12.17 Attach a 0.2 @im nylon mesh filtetro a 3 cc syringeand transferthesample to this synnge. Filterintoa 1.5mL glassautovialor low-volume autovialwhen necessary.
12.18 Label the autovialwith the study number, animal number and gender,sample timepoint, matrix,finalsolvent,extractiondate,and analyst(sp)erforming the extraction.
12.19 Cap and storeextractsatapproximately4 *C untilanalysis.
12.20 Complete the extractionworkshect,attachedtothisdocument, and tapein the study notebook or includein studybinder,as appropriate.
FACT-M-3.1 Extractioonf PFOS from Serum orOther Fluid
3M Environmental Laboratory
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Report No. FACT TOX-030 laboratory RequeSt NUmber-U2279
13.0 DATA ANALYSIS AND CALCULATIONS
13.1
Calculations
13.1.1 Calculateactualconcentrationsof PFOS, or otherapplicablefluorochemical,in calibratiosntandardsusingthe followingequation:
mL of standardx concentrationof standard(ug /mL) mL of standard+ mL of surrogatestandard+ initiamlatrixvolume (mL)
FinalConcentration(gg/mL) of PFOS in matrix
14.0 METHOD PERFORMANCE
14.1 The method detectionlimit(MDL) isanalyteand matrixspecific.Refer toMDL report forspecificMDL and limitof quantitatio(nLOQ) values(seeAttachments B and C).
14.2 The following qualitycontrolsamples are extractedwith each batch of samples to ensure the qualityof the extractionand analysis.
14.2.1 Method blanks and matrixblanks
14.2.2 Matrix spikeand matrixspikeduplicatesamples to determine accuracy and precisionof the extraction
14.2.3 Continuing calibratiocnheck samples to determine the continued accuracy of the initiaclalibratiocnurve
15.0 POLLUTION PREVENTION AND WASTE MANAGEMENT
15.1
Sample waste isdisposed inbiohazard containers,flammable solventwaste isdisposed in high BTU containers,and used glasspipettewaste isdisposed in broken glasscontainers locatedin the laboratory.
16.0 RFcoRDs
16.1 Complete the extractionworksheet attachedto thismethod, and tape in thestudy notebook or includein study3-ringbinder,as appropriate.
17.0 ATTACHMENTS 17.1 Attachment A, Extractionworksheet 17.2 Attachment B, MDLILOQ values 17.3 Attachment C, LOQ Summary 17.4 Attachment D, Calibrationstandardconcentrationworksheet
18.0 P.EFERENCES 18.1 The validationreportsassociatedwith thismethod are FACT-NI-3.1 & 4.1-V-1.
3M Environmental
FACT-M-3.1 ExtractioonfPFOS from Serum or Other Fluid
Laboratory
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Report No. FACT TOX-030 laboratory Request Number-U2279
19.0 AFFECTFD DocuMENTS
19.1 FACT-M-4.1, "Analysisof Senim or Other Fluid ExtractsforFluorochemicalsusing HPLC-Electro sprayMass Spectrometry"
20.0 REvisIONS
Revision Number
I
Reason For Revision Validationof method to include7 fluorochemicalsa,n additionalmatrix, new API/MS(MS) systems,monkey senun crossvalidation, improvements to ion pairingextractionM,DL study,updatesin record keeping and storingpolicies,etc.
Revision Date
07/01/98
3M Environmental
FACT-M-3.1 ExtractioonfPFOS from Serum orOther Fluid
Laboratory
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Report No. FAC7 TOX-030 laboratory Request Number-U2279
Study
Sample Number
set ?'I* H,O Blank Blank
FC-Mix
approx.0.5 ppm actual ppm #W
-
FC-Mix approx.5 ppm actual ppm #W-
FC-;,@lix-
approx.50 ppm actual PPM #W
Date andInitialfsor
Std.or Comments
Study number where theori2inawlorksheetislocated,
Blank
Std
SerumExtr2ction Method
Vortex 15 sec.
amount
mL Date & lniti2is
Pit)ettMcatrix
Volume
mi
PipetteI ml of 0.5 M TBA, pH 10.
Std.
Pipette2 ml of 0.25 Na2CO3iO-25.M NaHC03 buffcr Std.
Pipette5 ml ofethyl acetate
TN-A-
Shake 20 min.
Centrifu.ge20-25 min.
Ccnffifuge speed:
Remove a 4 ml aliquot of or@ganiclayer
Put on Nitrogen Evaporator to dryness Evaporator
Temperature:
Add methanol
Volume
mi
TN-A-
Vortex 30 sec.
Filterusing a 3cc B-D syringcwith a 0.2pm SRI filteirntoa 1.5ml autosamr)levial
MS/MSD@'-
Cont. Checks: Spiked -
uL of a
ppm std (_
) fora finalconcentration of
ppm. MS/.-MSD used sample
Cont. Checks used same matrix as for std curve,
SurrogateStandard:Spiked _
uL of a _
ppm std(
-) to allsamples, standards,and blanks
Attachment A: Exrraction worksheet
FACT-M-3.1
Extraction of PFOS from Serum or Other Fluid
3M Environme-n-.al
Laboratory
Page 11 ofl'j Page 163
3m Medical IDepartmert Study: T-6295.7
Report No. FAC7 TOX-030 laboratory Request Number-U2279
MDLILOQ Compound
PFOS PFOSA PFOSAA ETFOSE-OH POAA PFOSEA Monoester
values forRabbit Serum:
MDL (ppb)
LOQ Linear CalibrationRange (LCR) (ppb) Approximate concentrationsto be used forpreparing the
Standard CalibrationCurve
1.38
4.39 5 ppb - 1000 ppb
2.23
7.09 10 ppb - 1000 ppb
2.84
9.04 10 ppb - 1000 ppb
3.90
12.4 15 ppb - 1000 ppb
4.31
13.7 15 ppb - 750 ppb
1.09
3.48 25 ppb - 1000 ppb
149
248 MDL and LOQ areestimateosnly.No validMDL was determinablefrom
MDL study.Any quantitatipoenrformedformonoesterwillbe an
estimatoenly.PleaserefertoFACT-M-3.1 & 4.1-V-I forspecifics.
MDLILOQ Compound
PFOS PFOSA PFOSAA ETFOSE-OH POAA PFOSEA Monoester
valuesforRat Serum:
IMDL
LOQ Linear CalibrationRange (LCR)
(p.pb) 1.27
i (ppb) Approximate concentrationsto be used forpreparing the
i 4.04
Standard CalibrationCurve 10 ppb - 1000 ppb
2.14
6.81 25 ppb - 1000 ppb
2.32
7.38 10 ppb - 1000 ppb
3.25
10.3 50 ppb - 1000 ppb
1.20
3.81 5 ppb - 1000 ppb
1.84 1 5.86 10 ppb - 1000 ppb
149
248 MDL and LOQ areestimateosnly.No validMDL was determinablefrom
MDL study.Any quantitatipoenrformedformonoesterwillbe an
I estimateonly.PleaserefertoFACT-NI-3.1 & 4.1-V-I forspecifics.
MDL/LOQ Compound
PFOS PFOSA PFOSAA ETFOSE-OH j POAA PFOSEA Monoester
valuesforBovine Serum:
MDL (ppb)
LOQ Linear CalibrationRange (LCR) (ppb) Approximate concentrationsto be used forpreparing the
Standard CalibrationCurve
2.11 5.04
6.70 16.0
25 ppb - 1000 ppb 25 ppb - 1000 ppb
2.34
7.45 260 ppb - 1000 ppb
11.3
35.8 1 50 ppb - 1000 ppb
4.64
14.8 15 ppb - 1000 ppb
3.71
11.8 15 ppb - 1000 ppb
149
MDL and LOQ areestimateosnly.No validMDL was determinablefrom
MDL study.Any quantitatipoenrformedformonoesterwillbe an
estimatoenly.PleaserefertoFACT-M-3.1 & 4.1-V-I forspecifics.
No dataisavailableforMDL or LOQ inMonkey Ser-um.Use validatedLinearCalibratioRnange instead. Pleasesee Attachment C (LOQ Summary) and @MDL study in FACT-M-3.1 & 4.1-V-1 forspecifics.
AttachmentA: Extractiownorksicet
FACT-M-3.1
ExtractioonfPFOS from Serum or OtherFluid
3M Environmental Laboratory
Page 12 of 17 Page 164
3m Medical Department Sl-udy: T-6295.7
Report No. FAC-@ T--)X-030 laboratory Request Number-U2279
NTDLILOQ ICompound
PFOS PFOSA PFOSAA ETFOSE-OH POAA PFOSEA Monoester
values for Nlonkey Serum:
MDL
LOQ
Linear CalibrationRange (LCR)
(ppb) .(ppb) Approximate concentrations to be used for preparing the
1.38 2.23 2.84 3.90 4.31 1.09 149
i 4.39 7.09 9.04 12.4 13.7 3.48 248
Standard
Calibration
Curve
MDL and LOQ areestimateosnly. No validMDL was deten=able from
MDL study.Any quantitatiopnerformed forPFOS willbe an estimate
only. PleaserefertoFACT-M-3.1 & 4.I-V-1 forspecifics.
MDL and LOQ areestimatesonly. No validMDL was detem-Linablferom
MDL study.Any quantitatiopnerformed forPFOSA willbe an estimate
only. Pleasereferto FACT-M-3. I & 4.1-V-I forspecifics.
N4DL and LOQ areestimatesonly. No validMDL was determinablefrom
MDL study.Any quantitatiopnerformed forPFOSAA willbe an estimate
only. PleaserefertoFACT-M-3.1 & 4.1-V-1forspecifics.
MDL and LOQ areestimatesonly. No validMDL was determinablefrom
MDL study.Any quantitatiopnerformed forETFOSE-OH willbe an
estimateonly, Pleasereferto FACT-M-3.1 & 4.1-V-1 forspecifics.
MDL and LOQ areestimatesonly. No validMDL was determinablefrom
N4DL study.Any quantitatiopnerformed forPOAA willbe an estit
only. Pleasereferto FACT-M-3.1 & 4.1-V-I forspecifics.
MDL and LOQ areestimatesonly. No validMDL was determinablefrom
MDL study.Any quantitatiopnerformed forPFOSEA-OH willbe an
estimateonly. Pleasereferto FACT-M-3.1 & 4.1-V-I forspecifics.
MDL and LOQ areestimatesonly. No validMDL was determinablefrom
MDL study.Any quantitatiopnerformedforELFOSE-OH willbe an
estimateonly. PleaserefertoFACT-M-3.1 & 4.1-V-I forspecifics.
MDL/LOQ Compound
PFOS PFOSA PFOSAA ETFOSE-OH
POAA PFOSEA Monoester
values for Rat Whole Blood:
MDL
LOQ
Linear CalibrationRange (LCR)
(ppb) (ppb) Approximate Concentrations to be used for preparing the
1.25
I 3.96
Standard Calibration Curve 5 ppb - 1000 ppb
1.77
5.65 10 --ppb- 1000 ppb
17.3
55.0 55 ppb - 1000 ppb
7.89
25.1
MDL and LOQ areestimatesonly. No validMDL was determinablefrom MDL study.Any quantitatiopnerformedforETFOSE-OH willbe an estimateonly. Pleasereferto FACT-M-3.1 & 4.1-V-I forspecifics.
4.73
15.1 15 ppb - 1000 ppb
24.2
77.1 80 ppb - 1000 ppb
58.0
185
MDL and LOQ areestimatesonly. No validMDL was determinablefrom
MDL study.Any quantitatiopnerformed formonoesterwillbe an
estimateonly. Pleasereferto FACT-M-3.1 & 4.1-V-1 forspecifics.
Pleasesee Attachment C (LOQ Summary) and MDL study inFACT-M-3.1 &- 4.1-V- I forspecifics.
Attachment A: Extractionworkshect
FACT-M-3.1
Extractionof PFOS from Serum or Other Fluid
3M Environmental Laboratory
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Report No. FACT TOX-030 laboratory Reques@-- Number-U2279
Ion Pain'ng Extractionof Fluorochemicals from Serum and Analysisby APIAI4S(MS)
Summary Table: LimitosfQuantitation
Compound
Matrix
MDL
Approximate linearrange2
LOQ
Low std
High std
PFOS
Rabbit
1.38ppb
4.39 ppb
5 ppb
1000 ppb
Bovine
2.11 ppb
6.70 ppb
25 ppb
1000 ppb
- Rat Monkey
1.27ppb nJd
4.04 ppb n/d
10 ppb 25 ppb
1000 ppb 1000 ppb
PFOSA
Rabbit Bovine
2.23ppb 5.04ppb
7.09 ppb 16.0 ppb
10 ppb 25 ppb
1000 ppb 1000 ppb
F-at
2.14 ppb
6.81 ppb
25 ppb
1000 ppb
Monkey
n/d
n/d
25 ppb
1000 ppb
PFOSAA
Rabbit Bovine
'kat Monkey
2.84 ppb 2.34 ppb 2.32 ppb
n/d
9.04 ppb 7.45 ppb 7.38 ppb
n/d
10 ppb 263 ppb 10 ppb 25 ppb
1000 ppb 1000 ppb 1000 ppb 1000 ppb
ETFOSE-OH
Rabbit
3.90 ppb
12.4 ppb
15 ppb
1000 ppb
Bovine
11.3 ppb
35.8 ppb
50 ppb
1000 ppb
POAA
Rat Monkey Rabbit
3.25 ppb n/d
4.31ppb
10.3 ppb
n/d
1
113.7ppb
50 ppb 10 ppb 15 ppb
1000 ppb I 1000 ppb
750 ppb
Bovine
4.64ppb
14.8 ppb
5 ppb
1000 ppb
Rat
1.20 ppb
3.81 ppb
5 ppb
1000 ppb
Monkev
ii/d
rL/d
5 ppb
1000 ppb
PFOSEA
Rabbit
1.03ppb
3.48ppb
25 ppb
1000 ppb
Bovine
3.71ppb
11.8ppb
5 ppb
1000 ppb
Rat
1.84ppb
5.86 ppb
10 ppb
1000 ppb
Monkey
n/d
n/d
5 ppb
1000 ppb
Monoester'
Rabbit
149 ppb
474.0 ppb
250 ppb
1000 ppb
Bovine
149 ppb
474.0 ppb
250 ppb
1000 ppb
Pa t
149 ppb
474.0 ppb
250 ppb
1000 ppb
Monkey
n/d
n/d
100 ppb
1000 ppb
I. Values formonoester areestimatesonly.
2. Higheststandard(approx.1500 ppb) was excludedfrom finalLCR and upper LOQ valuesdue topoor R & R
valuesand excessiveweightingof thecalibratiocnurve.
Compound: PFOS
Serum matrix
Prepared
R-ang of LCR from
range of
average
ave curve
standards
curve
(ppb)(ngi-L) (ppb)(ng/mL) (ppbXng/mL)
Range of LCR from
low ld
low td
curve
curve
(ppb)(ng/-L) (ppb)(nWmL)
Range of LCR from
high sld
high std
curve
curve
(ppb)(ng/-L) (ppb)(np)mL)
Rabbit
4.93- 1450 4.93 - 1450 49.3- 1000 49.3-97.6 4.93-97.6 97.6 - 1450 97.6 - 1000
Bovine
4.93 - 1450 4.93- 1450 97.6-1000 4.93-248 24.8 - 248 97.6 - 1450 97.6 - 1000
Rat Monkey
4.93- 1450 4.93 -976 24.8-976 4.93 - 1450 4.93- 1450 24
4.93-248 )3
9.76-248 97.6 - 1450
24.8-493 97.6 - 1450 1
248 - 1000
97.6 1000
Attachment C: LOQ Summary
FACT-,M-3.1 Extractionof PFOS from Serum or Other Fluid
3M Environmental Laboratory
Page 14 of 17
Page 166
3m Medical DeDartment study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
Compound: PFOSA
Serum matrix
Prepared rangeof standards
(ppb)(ng/mL)
Range of average curve
(ppbXng/mL)
Rabbit 5.00- 1470 5.00- 1470
LCR from ave curve
(ppbXng/TTiL)
9.89-1000
Range of low std curve
(ppb)(ng/mL)
LCR from low std curve
(ppb)(ng/mL)
Range of high std (ppcurve
b)(ng/mL)
LCR from high std curve
(ppb)(ngimL)
5.00-251
n/a
98.9- 1470 98.9- 1000
Bovine 5.00- 1470- 5.00- 1470 25.1-1000 5.00-98.9
nla
98.9- t470 98.9- 1000
Rat
5.00- 1470 5.00- 1470 50.0-1000 9.89-500 25.1-500 98.9- 1470 98.9-1000
5.00- 1470 5.00- 1470 98.9- 1000 25.1-500 25.1-500 98.9- 1470
n/a
Compound: PFOSAA
Serum
Prepared
matrix
rangeof
standards
(ppb)(ng/mL)
Rang of average curve
(ppb)(ng/mL)
LCR from ave curve
(ppb)(ng/mL)
Range of low std curve
(ppb)(ng/-L)
LCR from low std curve
(ppb)(ng/-L)
Range of high std curve
(ppb)(ng/-L)
LCR from high std curve
(ppb)(ng/-L)
Rabbit 5.20- 1540 5.20- 1540 104-1000 5.20-263 10.4-263 104- 1540 263- 1000
Bovine 5.20- 1540 5.20- 1540 263- 1000 10.4-521
n/a(1) 104- 1540 263- 1000
Rat
5.20- 1540 5.20- 1540 104-1000 5.20-263 10.4-263 104- 1540 263- 1000
Monkey 5.20- 1540 5.20- 1540 52.4-1000 5.20-263 26.3-263 104- 1540 263- 1000
Compound: Serum
matrix
ETFOSE-OH Prepared
range of
standards
(ppb)(ng/-L)
Range of
average
curve
(ppb)@ng/mL)
Rabbit
4.94- 1450 4.94- 1450
LCR from
ave curve
(ppb)(ng/mL)
Range of
low std curve (ppbXng/mL)
49.4- 1000
4.94-248
LCR from Range of LCR from
low std
high std
high std
Curve
curve
curve
(ppb)(ng/rnL) (ppb)(ng/-L) (ppb)(ng/-L)
9.78-248
97.8 1450
rVa
Bovine Rat Monkey
4.94- 1450 4.94- 1450 97.8-1000
4.94- 1450 4.94- 1450 494-1000
4.94- 1450 4.94-1450
97.8- 1000
4.94-248 4.94-248 4.94-248
4.94-248 n/a
9.78-248
97.8 1450 97.8 1450 97.8 1450
248 - 1000 97.8 1000 n/a
Attachment C: LOQ Summary
FACT-M-3.1 Extraction of PFOS from Serum or Other Fluid
3M E@-ivironmental Laboratory
Page 15 of 17
Page 167
3m Medical Departmert Study: T-6295.7
Report No. FAC-L TOX-030 laboratory Request Number-U2279
Compound: POAA
Serum
Prepared
mat3@x
rangeof standards
(ppbXng/mL)
Range of LCR from Rangeof LCR from Range of LCR from
average ave curve low std
low std
highstd
high std
curve
curve
curve
curve
curve
(ppb)(ng/-L) (ppb)(ng/rnL)(ppb)(ngirnL)(ppb)(ng/rnL)(ppb)(ng/mL) (ppb)(ng/mL)
Rabbit 5.01-1480 5.13- 1510 25.8- 1000 5.13-258
n/a
102- 1510
n/a
Bovine 5.01- 1480- 5.13- 1510 102-1000 5.13-258 5.13-258 102- 1510 258-1000
5.01- 1480 5.13- 1510 51.3- 1000 5.13- 102 5.13- 102 102- 1510 102- 1000
5.01- 1480 5.13- 1510 102-1000 5.13- 102 5.13-102 102- 1510 258- 1000
Compound: PFOSEA
Serum
Prepared Range of LCR from
matrix
rangeof
average ave curve
standards
curve
(ppb)(ng/-L) (ppb)(ng/mL) (ppbXng/rnL)
Rabbit 5.13- 1510 5.13- 1510 25.8-1000
Range of LCR from Range o I LCR from
low std
low std
high std
high std
curve
curve
curve
curve
(ppb)(ng/mL) (ppb)(ng/TnL) (ppb)(ng/-L) (ppb)(ng/-L)
5.13-258
ri/a
102 -1510
n/a
Bovine 5.13- 1510 5.13- 1510 102- 1000 5.13 -258 5.13-258 102 - 151o 258 loOO
Rat
5.13- 1510 5.13- 1510 51.3- 1000 5.13 - 102 5.13 -102 102 - 1510 102 1000
Monkey
5.13 - 1510 5.13 - 1510 102- 1000 5.13 - 102 5.13 - 102 102 1510 258 1000 1
Compound: Monoester
Serum matrix
Prepared rangeof standards
Range of average curve
LCR from ave curve
(ppb)(ng/-L) (ppb)(ng/-L) (ppbXng/-L)
Rabbit 4.94- 1450 9.78-978
n/a
Bovine 4.94- 1450 97.8- 1450
n/a
Rat
4.94- 1450 248- 1450 248-1000
FM-0-1@ly4-.94- 1450 49.4- 1450 97.8-1000
Ingeneral,thechromatographyforthemoncesterwas very poor (broadpeaks,highbaseline). Curves formonoester inrabbitand bovinewere unacceptableA.ny quantitatiopnerformedwith themonoesteris onlyan estimateand shouldnotbe used forreliablea,ccuratedatareporting.
AttachmentC: LOQ Summary
FACT-M-3.1 ExiTactioonf PFOS from Serum or OtherFluid
3M Environmental Laboratory
Pace 16 of 17 Page 168
3m Medical Department S::udy: T-6295.7
Report No. FAC7 TOX-030 laboratory Request Number-U2279
Ion PairStandard Curves - Fluids
Prep date(s): Analyte(s): Sample matrix:
Standard number: Equipment number: Finalsolventand TN: Blank fluid/identirier:
Method/revision:
Target analyte(s):
FC mix stdapprox. 0.500 ppm: FC mix stdapprox. 5.00ppm:
W398-64t W398-640
FC mix std approx. 50.0ppm:
W398-639
Surrogate stdapprox. 17.71ppm:
W398-605
Actual concentrationsof standardsinthe FC mix
PFOS PFOSA PFOSAA ETFOSE- POAA
OH
Std conc Std conc g/mL ug/mL
Std conc ug/TnL
Std conc Std conc ug/mL ug/mL
PFOSEA
Std conc ug/mL
Monoeste r
Std conc ug/mL
0.500 0.500 5.00 5.00 5.00 50.0 50. 50.0 50.0
0.507 1 0.532
0.507
0.532
5.07
5.32
5.07
5.32
5.07
5.32
50.1
53.2
50.1
53.2
50.1 1 53.2
50.1 1 53.2
0.501 0.501 5.01 5.01 5.01 50.1 50.1 50.1 50.1
0.509 0.509 1 5.09 5.09 5.09 50.9 50.9 50.9 --,50.9
0.521 0.521 5.21 5.21 5.2 52.1 52.1 52.1 52.1
0.501 0.501 5.01 5.01 5.01 50.1 50.1 50@l 50.1
Calculated concentrations of standards
PFOS Final
conc
PFOSA Finalconc
ng/mL
PFOSAA Finalconc
ng/mL
ETFOSE
Finalconc ng/mL
ng/mL
4.93
5.00
5.24
4.94
9.76
9.89
10.4
9.78
24.8
25.1
26.3
24.8
49.3
50.0
52.4
49.4
976
98.9
104
97,8
2@@
251
263
248
493
500
524
494
735-- -746
782
737
976
989
1038
978
in the sample matrix
POAA PFOSEA Monoester
Finalconc Finalconc Std conc
ng/mL
ng/mL
ng/mL
5.01
5.1
4.94
9.93
10.2
9.78
25.2
25.8
248
50.1
51.3
49.4
99.3
102
97.8
252
258
248
501
513
494
749
766
737
993
1017
978
All
Am't spikedniL
0.010 0.020 0. 0.610 0.020 0.005 0.010 0. 0.020
Surrogate Std conc ng/mL
2.64
Surrogate Finalconc
ng/mL 81.0
All
Final Volume
mL 1.015 1.025 1.010 1.015 1.025 1.010 1 1.015 1.020 I.C)25
All Am'tspiked
(mL)
0.005
Validated ranges - approximate concentrations
PFOS
PFOSA
-PFOSAA---- ETFOSE-OH
POAA
R2bbit 1 5-1000 ppb 10-1000 ppb 10-1000 ppb 10-1000 ppb 10-750ppb
Bovine
5-1000ppb 25-1000 ppb 263-1000ppb 5-1000 ppb 1 5-1000 ppb
R2t
10-100p0pb 25-1000 ppb 10-1000 ppb 50-500 ppb 1 5-1000ppb
Monkey
Estimatesonly. Use valuesfor Rabbit
PFOSEA
25-1000 ppb 5-1000ppb 5-1000ppb
AttaclunenDt: IonPairStandardCurves
FACT-M-3, i
Extractioonf PFOS from Serum or OtherFluid
3M E-@lv@-ronmental Laboratory
Page 17 of 17 Page 169
3m Medical Department Study: T-6295.7
Report No. FACT TO: 030 laborator
9,@
3M ENVIRONMENTAL
LABORATORY
METHOD
A.,NALysis OF POTASSIUM PERFLUOROOCTANESULFONATE
OR OTHER
FLUOROCHIE,NUCALS IN SERUM OR OTHER FLUID EXTRACTS USING
HPLC-ELECTROSPRAY/MASS
SPECTROMETRY
Method Number: FACT-M-4.1
Author: Lisa Clemen, Glenn Langenburg Approved By:
Adoption Date: 4/22/98 RevisionDate:
Laboratory Manager
1/tfl,l@., @Group Leader
A Lbp"@, TechnicalReviewer
Date
@/-1-7/@y Date
9)@gios Date
1.0 SCOPE AND APPLICATION
1.1Scope: This method isforthe analysisof extractsfrom serum or blood forfluorochemical surfactantsusing HPLC-electrospray/mass spectrometry.
1.2 Applicable Compounds: Fluorochemicalsurfactantosr otherfluorinatecdompounds, or other ionizablecompounds.
1.3Matrices: Rabbit,rat,bovine,or monkey se= and ratwhole blood or milk curd.
Word 6.0.1/95
FACT-M-4.1 Analysis of Serum or Fluid ExtractUsing ES/MS
3M Environmental
Laboratory
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Renort No. FACT TOX-030 laboratory Request Number-U2279
2.0 SUMMARY OF METHOD
2.1 This method describesthe analysisof fluorochemicalsurfactantesxtractedftom serum, whole blood,or milk curd using HPLC-clectrospray/massspectrometry,or similarsystem as appropriate.The analysisisperformed by monitoring a singleion characteristiocf a particularfluorochemical,such as thepotassium perfluorooctanesulfonat(ePFOS) anion, NI/Z= 499. Samples may alsobe analyzedusingan APUMS/MS system to furtherverify compound idefitification.
3.0 DEFINITIONS
3.1 Atmospheric Pressure Ionization(A-Pl):The Micromass platform systems allow for variousmethods of ionizationby utilizinvgarioussources,probes,and interfaces.These includebut are not limitedto:ElectrosprayIonization(ESI),Atmospheric Pressurechemical Ionization(APcI),7hermospray, etc.The ionizatiopnrocessin thesetechniquesoccursat atmospheric pressure(i.en.ot under a vacuum).
3.2Electrospray Ionization(ES, ESI): a method of ionizatiopnerformed atatmospheric pressure,whereby ionizationoccursthroughth@ productionof tinycharged dropletsin a strongelectricaflield.
3.3 Mass Spectrometry, Mass Spectrometer (MS), Tandem Mass Spectrometer (MSfiMS): The API platformsare equipped with quadrupole mass selectivedetectors.Ions are selectivelydiscriminatedby mass to chargeratio(ni/z)and subsequentlydetected.A single MS may be employed forion detectionor a series(MS/MS) formore specificfragmentation information.
3.4Conventional vs.Z-spray probe interface:The latestmodels of Micromass platform systems (post1998) utilizae "Z-spray"conformation.The sprayemittedfrom a probe is orthogonal tothe cone aperture.Inthe conventionalconformation itisaimed directlyatthe cone aperture,afterpassing through a tortuouspathway inthe counterelectrode.Thou-h the configurationisdifferentt,he methods of operation,cleaning,and maintenance arethe same. However, Z-spray components and conventionalcomponents arcnot compatiblewith one another,but only with similarsystems (i.eZ.-spray components are compatiblewith otherZspray systems,etc.)
3.5 Mass Lynx Software: System softwaredesigned forthespecificoperationof theseplatform systems. CurrentlyMassLynx has Windows 95 and WindowsNT 3.1 versions.All versions are similar.For more detailssee themanual specifictothe instrument(Micromass Platform IIor Quattro TIMassLynx or MassLynx NT USER'S GUIDE).
4.0 WARNINGS AND CAUTIONS 4.1 Health and Safety Warnings:
4.1.1 Use cautionwith the voltagecablesforthe probe. The probe employs a voltageof approximately 5000 Volts.
4.1.2 When handling samples or solventswear appropn'ateprotectivegloves,eyewear, and clothing.
Word 6.0.1/95
FACT-M-4.1 Analysisof Serum orFluidExtractUsing ESIMS
3M Environmental Laboratory
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4.2 Cautions: 4.2.1 Do not operatesolventpumps above capacityof 400 bar (5800 psi)back pressure. Ifthe back pressureexceeds 400 bar,the HP 1100 willinitiataeutomatic shutdown. 4.2.2 Do not nin solventpumps todryness.
5.0 INTERFERENCES 5.1 To minimize interferencewshen analyzingsamples forperfluorooctanoate(POAA),teflon
should not be used forsample storageor any partof instrumentationthatcomes incontact with the sample or extract.
6.0 EOUIPMENT 6.1 Equipment listedbelow may be modified in ordertooptimize thesystem.
6.1.1 Micromass ElectrosprayMass Spectrometer 6.1.2 HPIIOO low pulsesolventpumping system and autosampler
7.0 SUPPLIES AND MATERIALS 7.1 Supplies
7.1.1 High puritygrade nitrogengas regulatedto approximately 100 psi 7.1.2 HPLC analyticaclolunin,specifictsobe determined by the analyst 7.1.3 Capped autovialsor capped 15 ml centrifugetubes
8.0 REAGENTS AND STANDARDS 8.1 Reagents
8.1.1 Methanol, HPLC grade or equivalent 8.1.2 Milli-QTmwater,allwater used in thismethod should be Milli-QTmwater and may
be provided by a Milli-QTOC Plus system 8.1.3 Ammonium acetate,reagentgrade or equivalent 8.2 Standards 8.2.1 Typically one method blank, one matrix blank, and ten matrix standards are
prepared during the extractionprocedure. See FACT-M-3.1.
9.0 SAMPLE HANDLING 9.1 Fresh matrix standardsarepreparedwith each analysis.Extractedstandardsand samples
are storedin capped autovialsor capped 15 ml centrifugetubesuntilanalysis. 9.2 Ifanalysiswillbe delayed,extractedstandardsand samples can be refrigerateadt
approximately 4* C untilanalysiscan be performed.
FACT-M-4.1 Analysisof Serum orFluidExtractUsing ES,'NIS
3M Environmental Laboratory
Page 3 of 9 Page 172
3m Medical ]Department S-@udy: T-6295.7
Report No. FACT TOX-03C laboratory Request Numbe---U-2279
10.0 ()UALITYCONTROL 10.1 Method Blanks and Matrix Blanks
10.1.1 Analyze a method blankand a matrixblankpriorto each calibratiocnurve.
10.2 Matrix Spikes
10.2.1 Analyze a matrix spikeand matrixspikeduplicateper fortysamples. With a minimum of 2 spikesper batch.
10.2.2 Expected spike concentrationwsillfallinthe mid-range of the initiaclalibration curve. Additionalspikeconcentrationmsay fallin thelow-rangeof theinitial calibratiqncurve.
10.2.3 See Section 13 to calculatepercentrecovery.
10.3 Continuing Calibration Checks
10.3.1 Analyze a mid-range calibratiosntandardafterevery tenthsample. Ifa significant change ( 30%) in peak areaoccurs,relativeto the initiasltandardcurve,stopthe run.Only those samples analyzedbefore the lastacceptablecalibrationstandard willbe used. The remaining samples must be reanalyzed.
10.3.2 See Section 13 to calculatepercentdifference.
11.0 CALIBRATION AND STANDARD IZATION
11.1 Analyze the extractedmatrix standardspriorto and followingeach setof extracts.The mean of two standardvalues,ateach standardconcentrationw,illbe plottedby linear regression(r)forthe calibratiocnur-veusingMassLynx or othersuitablesoftware.
11.2 The r'value forthe data should be 0.980 or greater.Lower valuesmav be acceptableatthe discretionof the analystand documented approvalof the ProjectLead.
11.3 Ifthe curve does not meet requirements,perform routinemaintenance or reextracthe standardcurve (ifnecessary)and reanalyze.
11.4 For purposes of accur-acywhen quantitatinlgow levelsof analyte,itmay be necessary to use the low end of the calibratiocnurve ratherthan the fullrange of the standardcurve. Example: when attemptingto quantitateapproximately 10 ppb of analyte,generatea calibratiocnurve consistingof the standardsfrom 5 ppb to 100 ppb ratherthan the full range of thecurve (5 ppb to 1000 ppb). This willreduceinaccuracyattributetdo linear regressionweighting of high concentrationstandards.
12.0 PROCEDURES 12.1 Acquisition Setup
12.1.1 Click on startbutton in the Acquisition Control Panel. Set up a sample list.Assign a filena-meusing letter-MO-DAY-last digitof year-samplenumber, assigna method (NIS) foracquir-inga,nd type in sample descriptions.
FACT-M-4.1 AnalysisofSerum or FluidExtractUsing ES/NIS
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Report No. FACT TOX-030 laboratory Request Number-U2279
12.1.2 To create a method clickon scan button in the Acquisition controlpanel and selec'@ SIR (SingleIon Recording). Set IonizationMode as appropriateand mass to 499 or other appropriatemasses. A fullscan isusually collectedalong with the SIRS. Save acquisitionmethod. IfMS/MS instruments are employed, additionalproduct ion fragmentation informationmay be collected.See Micromass MassLynx GUIDE TO DATA ACQUISITION for additionalinformationand MPIM (Multiple Reaction Monitoring).
12.1.3 Typicafly the analyticalbatch run sequence begins with a set of extractedmatrix standards and ends with a set of extractedmatrix standards.
12.1.4 Samples are analyzed with a continuing calibrationcheck injectedafterevery tenth sample. Solvent blanks should be analyzed periodicallyto monitor possible analyte carryover and are not considered samples but may be included as such.
12.2 Using the Autosampler
12.2.1 Set up sample tray according to the sample listprepared in Section 12.1.1.
12.2.2 Set-up the HP II00/autosampler at the following conditionsor at conditions the analyst considers appropriateforoptimal response.Record actualconditions in the instrument logbook:
12.2.2.1 Sample size= 10 @iL injectionwith a sample wash
12.2.2.2 Inject/sample = 1 12.2.2.3 Cycle time = 15 minutes
12.2.2.4Solvent rwnp Time
0.00 min. 7.5 min. 11.0 min. 11.5 min.
MEOH
45% 90% 90% 45%
2.0 mM Ammonium acetate
55% 10% 10%
55 % 77:@]
Note: In thisinstrument configuration,the run must be set up on the electrospraysoftware with a "Waitinc, for inletstart"message before the "Start"button ispressed on the HP Workstation.
12.2.2.5Press the "Start"button.
12.3 Instrument Set-up 12.3.1 Refer to FACT-EP-3.0 for more details. 12.3.2 Check the solventlevelin reservoirsand refililfnecessary.
12.3.3 Check the stainlesssteelcapillaryat the end of the probe. Use an eyepiece to check the tip.The tipshould be flatwith no jagged edges. Ifthetipisfound to be unsatisfactory,disassemble the probe and replace the stainlesssteelcapillary.
3M Environmental
FACT-M-4.1 Analysisof Serum or FluidExtractUsing ESA@IS
Laboratory
Pace 5 of 9 Page 174
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Report No. FACT TOX--@30 laboratory Request Nurnber-U2279
12.3.4 Set HPLC pump to"On". Settheflowto 10 - 500 uL/min oras appropriate. Observe dropletscoming outofthetipoftheprobe. Allow toequilibratfeor
approximately 10 minutes.
12.3.5 Turn on thenitrogen.A finemistshouldbe expelledwith no nitrogenleaking around thetipof theprobe.
12.3.6 The instrumentusestheseparametersatthefollowingsettingsT.hese settingsmay changein ordertooptimizetheresponse:
12.3.6.1Drying gas250-400 liters/hour 12.3.6.2ESI nebulizinggas 10-15 liters/hour 12.3.6.3HPLC constantflow mode flow rate10 - 500 @iL/min 12.3.6.4Pressure<400 bar(Thisparameterisnotset,itisa guideto ensurethe
HPLC isoperatingcorrectly.)
12.3.7 Carefallyguidetheprobeintotheopening.Insertprobe untilitwillnot go any ftu-theCro.nnect thevoltagecablestotheprobe.
12.3.8 Record tuneparametersintheinstrumentlog.
12.3.9 Using thecross-flowcounterelectrodeintheES/MS sourceisreconunended for the analysisof biologicamlatrices.
12.3.10CIickon startbuttonintheAcquisitionControlPanel (thismay varyamong MassLynx versionss,ee appropriatMeassLynx USER'S GUDE). Pressthe start buttonat topof sample listE.nsure startand end sample number includesall samples to be analyzed.
13.0 DATA ANALYSIS AND CALCULATIONS 13.1 Calculations:
13.1.4 Calculatematrix spikepercentrecoveriesusingthe followingequation:
% Recovery
Observed Result- Background Result x 100 Expected Result
13.1.5 Calculatepercentdifferencuesingthefollowingequation:
% Difference= Exr)ectedConc.-CalculatedConc. x 100 Expected Conc.
13.1.6 Calculateactualconcentratioonf PFOS, orotherfluorochemicali,nmatn'x(@tg/ml):
(nizof PFOS calc.from std.Curve.x DilutionFactor@ x I jig (InitiVaollume ofmatrix(ml)+ ml ofSurrogateStandard) 1000 ncc,l
FinalVolume (mL)
14.0 NIETHOD PERFORMANCE
14.1 Method DetectionLimit(MDL) and Limitof Quantitatio(nLOQ) aremethod,analyte,and matnx specificP.leasesee FACT-M-3.1, Attachment A fora listinogfcur-renvtalidated MDL and LOQ values.
FACT-M-4.1 Analysisof Serum or FluidExtractUsing ES/NIS
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14.2 Method Blanksand MatrixBlanks
14.2.1Method blanksandmatrixblankswillbe analyzedwitheachsamplesetfor possiblecontaminationor carryover.Values are expected to fallbelow the lowest standardin the calibratiocnurve.
14.3 Matrix Spikes.
14.3.1 Matrix spikesare analyzedwith each sample setand thepercentrecoveriesare expected to fallwithin 30% of the spikedconcentration.
14.4 Continuing Calibration Checks
14.4.1 Continuing calibratiocnhecks areanalyzed ata minimum of afterevery 10 samples with eacb sample set.The percentrecoveriesare expected to fallwithin 30% of the spiked concentration.
14.5
Ifany criterilaistedin themethod performance sectionisn'tmet, maintenance may be performed on thesystem and samples reanalyzedor other actionsas determined by the analyst.All actionswillbe documented inthe instrumentrunlog,the maintenance log,or on the summary sheet with thesample results.
15.0 POLLUTION PREVFN'TION AND WASTE MANAGEMENT
15.1 Sample extractwaste and flanunablesolventisdisposed inhigh BTU containers,and glass pipettewaste isdisposed inbroken glasscontainerslocatedinthe laboratory.
16.0 REcoRDs 16.1 Store chromatogams in thestudyor projectfolder.Each chromatogram must have the
followinginfortnatioinncludedeitherintheheader or hand writtenon the chromatogram: study or projectnumber, acquisitiomnethod, integratiomnethod, sample name, extraction date,dilutionfactor(ifapplicable)a,nd analyst.
16.2 Plot calibratiocnurve by linearregressionand storeinthe study folder.
16.3 Printsample listfrom MassLynx and tape intotheinstrumentrunlog.
16.4 Printdata integratiosnummary from MassLynx and tape intothe instrumentrunlog.
16.5 Copy instrumentrunlog pages,includinginstrumentparametersand sample results,and storein appropriatestudyfolder.
16.6 Summarize data using suitablesoftwareand storein thestudy folder.
16.7 Back up electronicdata to appropriatemedium. Record in studynotebook the filename and locationof backup electronicdata.
17.0 TABLES, DIAGRAms, FLOWCHARTS, AND VALIDATION DATA 17.1 Attachment A: FACT-M-4.1 Data reportingspreadsheet 17.2 The validationr-lpora-stsociatedwith thismethod isFACT-INI-3.1 & 4.1-V-1.
FACT-M-4.1 AnalysisofSerum or FluidExtractUsing ES/NIS
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18.0 RIEFERENCF-S
18.1 FACT-EP-3.0, "Operation and Maintenance of the Micromass Atmospheric Pressure Ionization/MassSpectrometer Platform Systems"
19.0 AFFFCRED DOCUMENTS
19.1 FACT-M-3. 1,'Txtractionof Potassium Perfluorooctanesulfonatoer Other Fluorochemical Compounds from Serum or Fluid forAnalysisUsing HP L C-Electrospray/Mass Spectrometry'
20.0 RFVISIONS
Revision Number.
I
Reason For Revision Validation of method to include 7fluorochemicals addition of whole blood matrix, surrogate standard, new.4PIIMS(MS) systems, monkey sera cross validation,MDL study, updates in record keeping and storing policies, etc.
Revision Date
07/01/98
FACT-M-4.1 AnalysisofSerum orFluidExtractUsing ES AIS
3M Environmental Laboratory
Page 8 o[9 Page 177
3m Medical Department
St@udy: T-6295.7 Attachment A
Report No. laboratory Request
FACT TOX-030 Number-U2279
Laboratory Study
Study: TestMaterial: Matrix/FinaSlolvent: Method/Revision: AnalyticaElquipment System Number: InstrumentSoftwareNersion: Filename: R-Squared Value: Slope: Y Intercept: Dateof Extraction/Analyst: Dateof Analysis/Analyst:
Group Dose
Sample#
Concentration ug/mL
InitialVO).
niL
Dilution Factor
FinalConc. ug/mL
Slope: Taken from linearegressioenquation. Group/Dose: Taken fromthestudyfolder. Sample#: Taken from thestudyfolder. Concentr2tion(ug/mL): Taken from theMassLynx integratisounnunary. InitiaVlolume (mL): Taken fromthestudyfolder. DilutionFactor: Taken from thestudyfolder. FinalConc. (ug/mL): Calculatebdy dividintgheinitiavlolume from theconcentration
FACT-M-4.0 AnalysisofSerum orFluidExtractUsing ESAIS
3M Environmental Laboratory
Page 9 of 9 Page 178
3m Medical Department Study: T-6295.7 3M MedicalDepartment Study:T-6295.7
ATTACHMENT
D
DATA SUMMARY TABLES
Report No. FAC7 TOX-030 laboratory Request Number-U2279
ReportNo. FACT TOX-030 LaboratoryRequest Number-U2279
3M EnvironmentaLlaboratory 3M Environmental Laboratory
Page D-1 Page 179
3m Medical Department @-:::udy:T-6295.7 3M Medical Department Study:T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
ReportNo. FACT TOX-030 LaboratoryRequest Number-U2279
TableD-la.Sample Intervalasnd Types by IndividuaAlnimalfrom Study6329-223
ANPAAL ID
SERUM SAMPLES COLLECTED (CiTY-WEEK)
LIVERSAMPLES COLLECTED (DATLE)
REcavr-RySUBGROUP SERUM SAMPLES COLLEcrED (Cl7Y-WF-EK)
Group 1 (Conb%)I) 105508M 105517M
105519M
105520M
105526M
iO5527M 105529F
105530F
105531F 10SM5F
1 '05544F 105549F Group H (LowDo")
151 Samples
a Samples
72Samples
12---0,12.,4,6.8,12,16, 20.24,26,27i
2125/99
11--0,1,2,4,6,8,12.16, 20.24,26
2125/99
12-0,1,2,4,6.8,12,16, 20,24,26,2Tj
2/2-r@M
14--0,12,.4,6,8.12,16.Retoned 10ook)fw3107/00 18--27!2t8i,29.30,31,35,39,43.47,
20.24,26, 27,27i,2Tii
51,53,57,61,65,69,73,T7.79
14---o.1,2,4,61,2816' Returned10cojort3y107/00 18-27ii2i8,,29,30,313,5,39,43.47.
20,24,25, 27,2@i,i7ii
51,53,57,61,6,56.9.73.T7,79
12---01.,2,4,6,8,12,16, 20,24,26,27i
2125/99
14-0,1,2,4.6.81'2,16, Retumedtoook)ny3/D7/00-18-27il@1,28,29,30,31,35.39,43,47,
20,24. 25.27,27i.2Tii
51,53,57,61,65.69,73,77,79
12--o.1,2,4.6,8,12,16, 20,24,26,27i
212%9
12--C-.1,2.4.6,8,12.16. 20,24.26,27ii
2126/99
12--0,12,.4.6,8.12,16, 20,24,26.27ii
2125'99
12---0.21,4,5,8,12,16, 20.24.26.2T,
2125199
14-0,1,2,4,6,182,16, ReUned b oolony3107/00 18-27iii2,8,29.30,31,35.39,43,47,
20.24,26.27,27'i,2Tti
51,53,57,61,65.69,73.T7,79
99 Samples
8 Samples
-
105514M 105515M 105516M 105521M
iO5537F 10&%IF
1--0
B"@@assigned
12--0,1.2,4.6.8,12,15, 20.24,26,27i
12-0,1,2.4,6,8.12,16, 20.24,26,2Tii
12--0-,-1,2.4,6.8,12,16,
20,24,26,27ii 12-0,1,2.4.6,8.12,16.
20,24,26,27ii
2/26/% 2126/99 2/2M9 2/26199
1-0
BaseVAb
assvad
11--0.1.2,4,6,8,12,16, 20,24.26
12--0,12,,4,6,8,12.16, 20,24,26,2Tii
2125% 2126199
1--0
isswed
Returnedtocolony
Returnedtocolony Retumed tocolony
1-0
Returnedb colony
105547F 10555OF
12---0,12.,4,6,8,12,16,
20,24,26,27ii
12--0,12.,4,6,8.12,16,
1
20,24,26.27
2/26Sg 2t26M
.......
27 Day 183(2/23199) 27i Day 184(2125M) 2TiiDay 185 (2/26199) 27iiiDay 187(212&99) **7wo samples2/20/99 79 Sample on 2@2a/00 79i Sampleon 2/25/00 79iiSampleon 2/25/DO
Not*:SamplesforWeek 25 and Week 27 (RecoveryGroup)takenon same day(Day183,Z*23/99)
3M Environmental Laboratory 3M Environmeni--al Laboratory
Page D-2 Page 180
3m Medical IDepartment Szudy: T-6295.7 3M MedicalDeparbnent Study:T-6295.7
Rer)ort No. FACT TOX-030 laboratory Request Number-U2279
ReportNo. FACT TOX-030 LaboratoryRequest Number-U2279
TableD-ib.Sample Intervalasndtypes by IndividuaAlnimalfrom Study6329-223
ANUAL ID
SERUM SAMPLES COLLECTED (CITY-WEEK)
LIVER SAMPLES COLLECTED (DATE)
RECOVERY SUBGR(XJP SERUM SAMPLES COLLECTED (QTY-WEEK)
Group111 (MidDo")
132 Samples
12 Sampim
7 Sampl"
105505M 105510M 10551"M 105523M 105524M 105528M 105532F
105538F
105539F
105545F 105548F
105552F
14-0, 1,2,4,6,8, 12,16,
20.24,26,.27,271,27ii 12---0,12.4,6,8,12,16.
20,24,26,27ii 2--0.1,Z 4.6,8,12,16, 1 20,24,26,27ii 14-0.1,Z 4,6,8,12,16. 20,24,26,27,Z7-i2,7ii 12--0,12,,4,6,8.12.16,
20.24,26,27ii 12--0,1,2.4,6,8,12,16.
20,24,26,27i 12--0,1.2,4.6.8,12,16,
20,24,26,27i 12---C,1,Z 4,6,8,1126,,
20, 24, 26.27i 14-0.1. 2,4, 6.8,12,16,
20,24,26,27,2Ti,27ii
12-0,1, 2,4,6.8,12.16,
20,24,26.27i
12--0. 1.2,4,6. 8,12, 16,
20.24,26,27i
'4-0,1.2,4.6,8.12,16.
20,24, 2r.,2-7,27i,2Ti
3101/00Biopsy
2/26/99 2126W 3101100Biopsy 2/26/99 2/26M 2/251% 2125M 3/01/0B0iopsy
2/25199 2125M
3101/00Biopsy
18-27iii,28,29, 30, 31, 35, 39.43, 47,
51,53,57,61,65.69,73.77,79
18-27iii,28, 29,30, 31, 35, 39, 43,47,
51,53,57.616,5,69,73.77.79
18--27iii2,8. 29, 30,31, 35, 39, 43, 47,
51,53,57,61,65,69,73,T7,79
18-27ii2i8,,29,30,313,5,39,43,47.
51, 53,57, 61.65. 69, 73, 77, 79
Group [V (HighDo")
148 SwnpWs
105506M
11-0,1,2.4,6,8,12,16,
20.24,-
105507'M 12--02,01,2,2,44,,266.,82,71i2,16,
105509M 9-0,1.2,4.6,8.12,16,20
10551im
iDS512M
1". 1,2,4,6.8,12,16,
20, 24, 215,27, 27i.27ii
12--0.12,,4,6,8,12,16, 20,24,26,27i
105522M
14---0,1.2, 4. 6, 8.12.16,
1 20,24,26,27.2Ti.27ii
'4-0.1,2,4,6,8,12,16,
'05533F 20,24,26,27,2T.,2Ti
2--0. 1,2,4,6,8,12, 16,
'aSS34F
20,24,26,27.-
ioww
2--0,21,,4,6.8,12,16, 20.24.26,27i
10554OF
105542F
12---0,1.2, 4, 6, 8. 12,16,
20. 24, 26. 27ii
14-0.1,2.4.6,8,12.16,
20, 24,26. 27, 27i,27ii
105551F
12-0, 1,2,4, 6,8, 12,16,
20,24,26,27ii
14Samples
none
2125/99 none
9r22199 Biopsy, 2/21-@100
2r25M
9/22/99Biopsy,
2125= 9rZ2/9B9iopsy,
2/25100 2/26199
2/25/99
2/26/99
9/22199Biopsy,
2/25100
2r4W9
80 Samples
20-27iii,28,29, 30, 31,35, 39,43, 47, 51,53, 57, 61,65, 69,73, 77, 79, 79i,79ii
20--27iii2,8, 29,30, 31, 35, 39, 43, 47,
51.53,57,61,65,69.73,77.79.79i,79ii 20-27iii2,8,29,30.31.35,39.43,47, 51,53,57.61,65,69,73.77,79,79i.79ii
20-27iii,29.30.31,35.39,43,47,
51,53, 57,61, 65, 69.73, 77. 79, 79i,79ii
27 Day 183=3199) 27i Day 184 (2125/99) 27@ Day 185 (2126M) 27iiiDay 187 (2128199) '*Two samples2r2O/99 79 Sample on 2123/00 79i Sampleon 2/25/00 79iiSamp@e on 2125/00
Note:SarMiesforWeek 26 and Week 27 (ReooveryGroup)takenon same day (Day183,2i23i9g)
3M Environmental Laboratory 3M Environmental Laboratory
Page D-3 Page 181
3m Medical Department Study: T-6295.7 3M Medical Department Study:T-6295.7
Report No. FACF TOX-030 laboratory Request Number-@,72279
ReportNo. FACT TOX-030 LaboratoryRequest Number-U2279
TableD-2.Average PFOS ConcentratlonisnSerum by Dosage Group and Week fromStudyFACT Tox-030(BaselineD-ay 185)
Time Point AllPFOS values
LOQ@o@@
gWmL
Group IM
Qbnv&gfd
Group IF
Group 2M
d
Group 2F
Group 3M
Group 3F
Group 4M
Group 4F
Baseline
LOQ 0.025
Week 1
LOO 0.025
Week 2
LOO 0.025
Week 4
LOO 0,0152
Week 6
LOGO.0152
Week 8
LOO 0.0 152
Week 12
LOO 0.0152
Week 16
LOO 0,0152
Week 20
LOO 0.01-@2
Week 24
LOO 0.0 152
-AveragePFOS StdDeviaftn AveragePFOS StdDeviabm AveragePFOS StdDeviabm -AveragePFOS StdDeviadon AveragePFOS StdDeviabon AveragePFOS StdDeviabm AveragePFOS StdDeviatm AveragePFOS
Std DeviaUm
AveragePFOS
Std Deviabcn
-AveragePFOS Std Deviabm
<Loa NA <LOQ @LA <LOO NA <LOQ -I Anomaly NA <LOQ NA <LOQ -I Anomaly NA o.ow -1 Arwiaty 0.00811 0.0407
0.0110
0.0400
0.0120
0.0440 0.0101
-@:LOQ NA <LOG NA <LOQ NA <LOQ NA <LOQ NA 0.0226-2 Anomalies O.C)0189 0.0263-2Anomalies 0.00362 O@0432-2Aromalles
0.00851
0.0504
0.0127
0.0426-1 Anomaly 0.00784
<LOQ t'A
0.869 0.147 1.10 0.0835 1 3.20 0.577 3.61 0.430 4.73 0.432 6.69 0.578 11.2
2.44
12.3
1.40
14.5 3.06
<LOQ NA 0.947 0.110 1.10 0.0963 3.40 0.291 3.71 0.417 4.76 0.577 6.31 0.717 10.5
1.90
19.5 14.5
13.0 0.675
-@LC)Q NA 4.60 0.782
5.81 0.933 17.8 1.68 20.4 1.65 2Ei.0 3.30 35.2 5.39 56.2
5.a4
-63.7
6.71
65-9 6.88
<LOQ NA 3.71 0.455 5.39 O.gW 16.5 1.87 18.8 2-15 24.0 3,06 27.8 3.98 42.1
4.04
58.1.-.
7
60.4 7.24
-ELOQ NA 21.0 1.57 26.9 3.54 95.3 70.4 94.5 8.07 ID9 18.3 122 23.9 189
15.9
144
10.9
215 24.9
<LOQ NA 20.4 2.71 22.0 3.25 92.7 39.6 90.1 7.11 107 11.8 117 11.7 162
19.3
156
21.8
174 20.9
Week 26
Average PFOS
LOO 0.0152
SbdC)eviadw
Week 27
Average PFOS
LOO 0.024a
Sbd Deviatm
Day 183
Average PFOS
LOG 0.0 152 [Std Deviabm
Day 184
LOG 0.0152
Awa(M PFC)S Std Deviabm
Day 185
kveraw PFOS
LOO C@o 152
Std Deviabw
-CLCOZLessttante Lo&w Lnd of
0.0459
0.0143
0.0529 0.0145
--0.117-0.0764
0.0233-1 Anomaly NA
0.0432 0.00928
0.0506
15.8
13.2
82.6
66.8
173
171
0.0164
1.41 1.42 25.2
10.8
36.5
22.2
0.0416
15.9
11.1
68.1
58.5
194
160
0.0148
1 5.54
1.52
5.75
4.67
8.93
23.9
0.0533
85.0
81.7
249
230
0.0315
14.9
35.1
46.8
40.3
0.0352 0.00911
69.7
78.0
259
245
4.68
12.0
110
29.2
o.ow
3
294
321
0.0306
0.7
23.3
22.0
170
3M Environmental Laboratofy 3M Environmental Laboratory
Page D4 Page 182
3m Med4-cal Department Study: T-6295.7 3M MedicalDepartment Study:T-6295.7
Report No. FACT TOX-030 laboratory Pequest Number-U2279
ReportNo. FACT TOX-030 LaboratoryRequest Numt>er-U2279
TableD-3.Average PFOS ConcentrationsinSerum by Dosage Group and Week from Study FACT TOX-030 (RecoveryGroup)
Time Point
AllPFOS values
Group IM
GroupIF Group3M I Group3F
LOO (ligftl)
pg/mL
O.Omglkglday
0.15mgfkg/day
Day 187
Avemge PFOS 5,otnL) 0.03DO-1Anomaly 0.0457 1 79.1
39.5
LOO 0.0152
Std Deviabon
NA
0.0118 4.67
41.4
Week 28 LOO 0.0152
AveragePFOS fi@) StdDeviabon
0.0371 0.0124
0.0430 84.6
86.1
0.00821 1.51
3.59
Week 29 =0.0152
AveragePFOS (poVnL) StdDeviation
0.0665
0.0742 75.8
69.9
0.00362
0.000664 2.18
11.4
Week 30 LOOO.0152
AveragePFOS wo")L)
0.0313
0.0303 65.2
62.0
StdDeviation
0.000165
0.000485 4.60
10.6
Week 31 LOO 0.0152
AveragePFOS WcWnL) StdDeviation
0.0358 0.000567
0.0368 56.6
79.6
O.C)121 4.T7
43.8
Week 35
AveragePFOS ipgtyl)
0.049
0.0723 84.5
74.4
Loa O.co5m
Std Deviabon
0.00303
0.00352 12.0
9.53
Week 39
AveragePFOS (po"t.) 0.0391
0.0509 1 50.1
51.7
LOQ 0.00&96 Std DevLation
0.0106
0.000779 3.16
7.29
Week 43 LOO 000555
AveragePFOS StdDevtabw
0.0319 0.00"0
0.0368 0.0000923
45.7
58.1
1.12 1 0.249
Week 47 LOO 0.
Week 51 LOO O.DO555
AverigePFOS fmOnL) StdDeviation
Aver-agePFOS (po@nL) StdDeviation
0.0355 0.00221 0.0237 0.00333
0.0459 0.00323 0.0341 0.000403
48.3 1 42.6
3.69
6.70
37.9
35.1
2.62
13.2
Week 53
AveragePFOS (.otrc) 0.0331 1 0.0397 46.2
36.7
LOO 0.00555 StdDeviathn
0.0086
O.C)0311 3.30
6.24
Week 57 LOO O.oosm
AveragePFOS wo"*-) StdDeviation
0.0327 0.00526
0.0445 30.2
32.3
0.00385 2.36
1.34
Week 61 LOO 0.005M
AveragePFOS wotnl) StdDeviation
0.0351 0.00449
0.0448 31.6 0.00210 5.98
38.2 0.283
Week 65 LOG O@00565
Average PFOS 4*t@L) StdDeviatkr
0.0210
0.0360 32.9
37.6
0.00365 1 0.000= 1 0.0269 2.32
Week 69 LOG 0.005M
Average PFOS @wornl) Std De-Aation
0.0406 O@00313
0.04()0 26.4
.5
0.00301 2.59
3.46
Week 73 LOOO@00556
Wmk 77 LOQ 0.00&%
Average PFOS (Aovr-L) Std Deviabon AveraW PFOS StdDevtabm
0.0350 0.0115
0. 296 0.00535
0.0365 1 27.3
25.8
0.002&4 4.66
2.91
0.0305 22.5
23.0
0.00167 0.632
6.37
Week 79 LOG 0. I
AveragePFOS (vo",L) StdDeviation
0.0215 0.00296
0.0243 1 19.1
21.4
0.00355 1 0.805
2.01
Gmup 4M Group 4F 0.75rngtkgtday
267
258
42.0
15.2
249
236
21.7
18.3
223
194
66.9
19.0
143
162
38.0
7.87
161
185
46.1
21.9
181 i 171 19.5 1 io.i
146 1 161
16.1
11.1
78.8 16.8 124 25.9 94.7 38.4 1 BO.8 36.8
159 284 98.3 8.32 91.4 6.07 98.2 0.490
78.0 1-63
100 50.3
106 3.84 109 0.697
91.5
82.8
55.2
9.68
84.0
75.0
52.4
5.25
54.4
147
27.3
131
60.0
57.0
38.3
19.1
41.1
41.4
25.9
1.15
3M Environmental Laboratory 3M Envi-ronmen--al Laboratory
Page D-5 Page 183
3m Mel@ical Depart,-Pent- S@-udy: T-6295.7 3M MedicalDepartment Study:T-6295.7
Report No. FAC-- TOX-030 laboratory TZequest Numbe---U2279
ReportNo. FACT TOX-030 LaboratoryRequest Number-U2279
TableD-4a.PFOS Amounts ReportedInSerum by IndMdual Animal(Baseline-Week26)
PFOS
REPORTED
WEEK 0 I WEEK 1 I (ii )
y IEEK 2 WEEK 4 WEEK 6
WEEK 8 1 WEEK 12 WEEK 16
GroLrIp(C-bcQ
IOSSOBM IOS51TM
105519M 105520M
105526M
<LOQ .<Loo
<OQ -<LCO
-<LCO
<Loa
<Oa
<LOG <LOC
<LOG
<LOQ
4LOQ
<LOQ <Oa
<LOC)
<LOQ -<LOQ .<LC)Q -<LCQ
-CLOO
.<00 -.<Loa
<Oo
<Loa
<LCQ
<t-Oo <Loa
KLOO
<LOQ
<LOQ
0.0381 O@D430 @@-0.0423 <LOQ 0.0244
OM" -0,0408
0 03a2 O@0320
105527M
-<LOC)
<Loa
-<CG
-<LOQ
<OQ
0.03a5
006423
0.0615
105629F
-LOO
<LOQ
-<LCO
-<LOQ
&<00
0.0214
.<LOQ
0,0438
105&ICF 105531F
lossw
lossw
-LOO -<LOQ
.<LOQ
<LOG
<Loa <Loa
<Loa
-<OC)
.<Loo -<LOQ
<LOQ
-<LCQ
-<LOQ -LOQ
-<LOQ
<LOQ
<Oo <LCO
.CLOQ
<Oo
0.0244 0.0206 <LOQ <00
0.0243 0.0254
<LOQ 0.0238
-0.0515 0.0314 -Loa -LOQ
io&uw
<Loa
<LOQ
<Loa
<LOQ
-4-OQ
0.0240
000462
WEEK 20 WEEK 24
0.0348 0.0419 -0.0335 0.0300 0.0389 -00631 O@0617 0.(0@m5mm .0.0493 0.0253 .0.05M 0.0570
0,0"9 0.0486 O.D414 O.C)2B3 0.0397 -00613
..O,D498 -00497 0.0364 -LOO -0,0325 o.ow
WEEK 26
00496 -0.0539 00417 0.0254 0.0376 0.0669 o@()613 0.07ii 00431 00266 -0.04M 005%
Grow I (L106513M 105514M 105515M 10551&M lowim 105525AA 106537F
DO") <OQ <LOD .<()C)
<LOQ -<LC)Q -<LOO -LCO
0.793 .0.787 O.M2
109
1.10
-1.02 1.03 -1.19 -1,13
-1.19
-2.87 2.75 3.13 .4.03
-3.73
105541F 105543F
-LOO -LOO
-0929
1.16
-3.07
io5uw lO5U7F
-<LOQ -<LOG
O@931
-106
3.55
10555OF
.<Loa
O.a32
-0.980
#3.27
G-.Jp M (P&d Do-)
105505PA 105510M 10551&M 105623M 105524M 1056am 105&UF 105 Irw 105639F
<LOQ -LOO -LOQ -LOO -<LOQ -LOO -<Loa <LOC) <LOG
4.80 -4.19 5.48 3,54 425 5.52 -4.31 4.12 3,31
-6.07 4.82 .701 456 -624 6,15 -461 6.67 .465
.17.0 .17,2 -20.2 176 1-5.4 -19.2 16.8 18.7-.14@3 1
1o&%4w 105WF 105552F
.<oo <LCO <Oo
-3.69 3.72 3.12 1
528 -6@42 4.73
.18.7 -15.7 .14.9
GROM IV"0 00-)
iosm6m
1
1055UTM
105509M
im5lim
105512M
105522M
105533F
IDS&W
105536F
lossw
105542F
10555iE_
<Lco <LOG <00 <Loa -LOO -<LOQ -<LOQ <Oo -LOO -<Loa -<LOQ CLOO
21,3 -220 -18.8 .19.3 228 -21.6 -22.6 -18.1 -21.0 -16.8 2-4.0 -20.1
.29.9
.236
-25.1
-72.6
23.9
-54.8
22.6
"8.4
31.3
T7,4
28.8
.8Z2
249
.141
-26.0
.145
-23.5
.64.1
.19.5
-67.2
.-199-7,784 18.2 1 -60.2
indicatesa saffpe vwdhan exracbon voiume of<0 5 mL ShadW cells=rrcrtxrd
.3-67 .3.31 -3.26 .4.19
-4.28 3.66
.3.85 -3.27
21.0 Z2.5 -20.1 .18.6 .21.8 .18.5 .18.4 18.9 .18.4 ZZ7 -18.4_ le.1
-Gi.0 -8Z8 gZ3 917 .105
lC2 93-0 -M3 -82.8 90.8 -102 szo
4.61 4.17 5.05 510
5.2B 4.&5
6@20 648 6.55 -752
6.81 5.57
10.4 .9.47 10.1 -14.8
11.1 -123
12.5 10@7 11.9 14.1
11@5
4.98 3.94
-7,03 1 107 5.83 1 7.85
14.3 41.1
27.9 2Zl 25.1 24.5 31.6 24.6 27.6 24.3 26.5 24,5 22.3 19.1
40.1 1 -50,4
39@2
5zg
337
60.7
-35.3
5Z2
37.8
63.4
25.4
484
25.8
40.4
-32.8
373
278
46.3
32-2
43.1
23.2
470
24.8
38.7
---62,3 63.3 r,3,1 75,2 64,0 54.2 69.2 474 -78.2 45 .7 65.3 4Z7
125 86.1 103 92.3 118 131 110 1 121 102 105 116 87.3
116 106 123 99.4 167 -121 126 114 -918.0 -112 131 117
162
158
172
.138
197
152
179
126
216
143
155
145
1f>4 1 169
157
143
184
146
173
193
1
12E7
*1'532'
-14.7 .10.9 1 14@l -18.4
13,4 13.7
16@@@ 165 138 -169
-13,5 -148
.12.7 122
77, 65.2 58.8 597 696 -648 -63,1 486 -69.9 83.5 55.1 -61@7
198 188
207 247 .233 190 .200 -169
181 -150
130 .11.4
-129 -695 -72.1 -69@5 62 634 590 722 857 -645 556
-182
142 148 221 203 187 -155 177 165 -142
3M EnvironmentaLlaboratory 3M En-:-'-rcnmenl-.aLlaboratory
Page D-6 Page 184
3m Medical Department S::,ady:T-6295.7 3M MedicalDepartment Study:T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
ReportNo. FACT TOX-030 LaboratoryRequest Number-U2279
TableD-4b.PFOS Amounts ReportedInSerum by IndividuaAlnimal(Days 183-Day 185 and WGek 27)
PFOS
I DAY 183
REpoftTED
IU9"d4
DAY 184 69wc)
DAY 195 44@"ti
WEEK 27 (PwrnL)
GroupI(Ct.0
105508M
105517M 105519M 105520M 105525M 105527M 105529F 10553OF IOMIF 105535F IGS5411F 105UW
0.171 -0.0620
-
0.0758 -
@ <Loa 0.0233
a o.o4ie
@
0.0310
0.0257
-
0.0366 0.0498
-
0.0763 -
@ @ -
0.03M
GrouIp(LoDwos4)
io55l4M -
105515M - @
10551 sm
-
@
105521M
-
@
105537F
105541F
@
105547F
@
1055WF
@
Group 19(Mid Do")
losm5m
-@74@.4
66.4
70.3
los5lom
-
-
@
105518M
-
-
10SU3M
95.5
73.0
85.4
105U4M
-
-
@
iosuem
-
@
10 F
-
@
1056UF
-
a
-
IOSWGF
.107
W.5
101
la554V
-
105SUF
-
IOSMF
56.9
M.5
-678
Group IV (HighDo")
105506M
-
-
105507M
-
105509M
-
-
105511M
-218
181
309
105512M
-
105522M
202
336
-278
10553W
258
255
-441
105534F
-
-
105&W
-
iosuw
-
@
lasur 1 x 1
224
-201
105WIF I - I -
a
C Sanoe mimcbon daim forWeek Z7 data F,.Wplecobactedon Z?OM
irccatesa sanoe withan exbacw vokxm of<0.5 rrL
0.04M -
0.0695 -
O.OB35 0.0374 0.0318 0.0335
-
23.9 13.0 11,4 15.5 126 953 11.2
68-5 68.7 60.6 74.7 54,3 565
580
196* 184 -
202 11 1-
182 169 154 126
3M Envimnmental Laboratory
Page D-7
3M Environmental Laboratory
Page 185
3m Medical IDepartmert Szudy: T-6295.7 3M Medical Department Study:T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
Report No. FACT TOX-030 LaboratoryRequest Number-U2279
Table D-Sa.PFOS Amounts Reported InSenim by Recovery Group Animal (Day 187- Week 47)
PFO S REPORTED
I DAYig7 I 'AfEEK28 WEEK29 WEEK30
ULWMW
WoNrIL)
tughTIL) 4oftc)
WEEK31 64ord4
WEEK 35
WEEK 39 UOWL)
WEEK 43 WaktIL)
WEEK 47 WoknL)
Group I(CM&A
105520M I <.OQ
00284
-0.0890
-1055M 1055"F
00300 0.0373
.0@0459 -0@04M
0.06M .0,0738
105-154ww 0 C;-4717 -0@0372
0.0747
Group 11(M;dDws)
iosmsm
82-4
-85.7
773
IOSS23M
75@8
-83.5
.74-2
105639F
10.2
-88.7
T7,9
105562F
68.8
.83.6
61.9
Group IV (HighDoes)
105511M
237
-233
175
iosmm
297
264
270
105=F
269
249
207
IO&WF
248
223
180
Indicatesa sample withan extactcn vo@im of<0.5rnL
(3.0314 0.0312 0.0299 O.GMG
-88.4 61.9 -89.9 54.5
118 170 156 167
O.CW2 0.0354 0.0282 .0.0453
60.0 53.2 -111 -48.6
129 194 201 -170
0.0437 0,0480 0.0748 O.OM8
-93.0 76.1 .81.2 -67.7
167 195 164 178
0.0316 0.04M 0.0503 -0.0614
-62.4 -57.9 96.8 -0.5
.135 -158 -169 --.154
0.0287 0.03W O.OM O-M87
48.5 44,9 58.3 -M.0
68.9 90.7 179 139
0 0339 0,0370 O.Mi 0.04M
50.9 45.7 47.4 1 37.9
105 -142 104 92
Table D-5b.PFOS Amounts Reported InSerum by Recovery Group Animal (Week 51- Week 79)
PFOS
I WEEK 51
REPORTED I W,,r.)
Group I(Contal)
10@M=-() 1055" 105529F 10554OF
.0213 0.0261 O.M" 0.0338
Group II(INd Dos*)
1055iD5M
39.8
iOSS23M
36@O
105-1,,QF
44.5
1055W
-25.8
Group fV(HighD-)
10551im 105522M
-67.5 122
105533F
87.1
IOSWF
95.7
WEEK 53 WEEK 57
Wpl.1)
4*1,44
00269 0ON2 0-0375 0.0419
0.0289
0.0364 j 000.000424!4,7@8782@92O
0.0418
43.9
28.5
48.5
31.8
41,1
33.3
32.3
31.4
548
6a.5
107
89.5
986
103
979__
109
WEEK 61 COftt)
0,0319 0.0382 o00@04M 0.048
27.4 35.9 38.0 38.4
__64-7 138 108 log
WEEK 65 Wo,,L)
0.0184 0.0236 0.0364 0.0357
329_ 329 39.3 30.0
-52.5 .131 .89.7 -76.0
WEEK 69 WEEK 73
(,,%,nL) bo"t.) I
WEEK 77
WEEK 79
.0@0428
0,0383 O.D421 0.0379__
-0.0431 0,0269 0.0388 __0.0345
-0.0334 -0.0259 O@0317 -0.0294
0.0194 0.0236 0.0288 0.0218
24.6
240
.22-1
19.7
28,3
w,6
-23,0
185
36,9
279
-275
22,8
32.0
.23.7
-18.5
19.9
47.0
35.1
329
.121
.73.5
87.0
787
54.5
70,5
713
-240
.434
Indicateassaffnaswdh an etacbm vollrm of<0.5rnL
Table D-6.LOO Values Used InAnalyzes by Method and Usage Dates
METHOD
Sera
FACT-M-4.1 ETS-8-&O ETS4@-5.1
LJVW -FACT-M-2.0
FACT-M-2.1 ETS41-7.0
EFmcTivE DATE I
10/10/98 3tOl/99 4r26M
5/2&98 6103199 7/2Z%
LOQ
ngtml
4.39 15.2 5.55 roig 30.0 37.4 26.9
SAGE DATES
1/25M toZ22199 310&% tD4/17/99 5117M throughtm end ofshidy
1/25199to Sre2M 6tO3f99to 6/14199
7/29M tb rough the eridof study
3M Environmental Laboratory
Page D-8
3M Environmental
Laboratory
Page 186
3m Medical Der)art,7.e@7:S:@-..:dyT:-6295.7 3M MedicalDepartment Study-7.-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
ReportNo. FACT TOX-030 LaboratoryRequest Number-U2279
Table D-7. PFOS Concentrations In Uver by Dosage Group
DCSAGE GR(>tjp
COLLECNDN DATE
PFOS CALCULATM -1--A@PNFrOZS@
CONCENMTMN
(nwol
Group I(ControQ
105508M 105517M 105519M 105=M 105526M 1055Z7M 1055ZF 10553OF IDMIF 105535F 1055"F 105549F
2f25Q9 Z?-rv% 2r25199
2r25M :mdr*-. 2125t% 2/26/99 2r261% 2/25199 Not*@:,
Group 11(Lm Ome)
105514M
Z26/99
iD5515M
2r2&%
IM16M 105521M
2/26% 2/26M
105537F
2/25M
105UlF iC5547F
2/26M 2r26M
1055WF
2/26M
Grotip11 (Mid Do*&)
io5W5M
3101100Biopuy
105510M 105518M 105523M
Z26199 2r26f99 3/01/00 BIOPSY
105524M
2J261%
1055M
2126%
105532F
2r25/99
10553OF 105MF
2125M 3101/00Blop"
105545F 105548F 105552F
2/25199 2125% 3101/00Biopsy
Grcxjp IV (High Dose)
105506M ID55OTM
2125199
2 Anorrialies 143 -1 Anomaly
91
129
128 112 87 97
18237 22709 11417 16734 22818 24847 20102 20735
8252 42169 86173 10203 5W73 48203 8N21 49590 24728 66532 81376 1769C)
412474
2 Anomalies 0.143 0.091
0.129
0.128 0.112 0.087 0.097
18.2 22.7 11.4 16,7 22.8 24.8 20.1 20.7
8.25 42.2
86 10.2 58.7 48.2 80.4 49.6 24.7 66.5 81.4 17.7
412
lD5511M
w2z% Biop" Z25M
142465 23480
1 D5512M
2r2-riu%
378723
1 D5522M
gr22/99Biopsy zr25=
137561 70781
10=F
&r22/99Biopsy
1752a3
2t25100
42668
1055W
zr2&99
280575
io55W
2r25M
256669
10554OF
2/26M
267328
IOSS42F
%2Z99 Blop" 2r25W
421647 57895
105551F
2r26199
r
287223
<LOCT Less twn t@*Lower Lirriotf C)uanftton (26.9-37.4ng/g)
142 23.5 379 138 70.8 175 42.7 281 257 267 422 57.9 287
3M EnvimnmentalLaboratory
3M Environmental Laborat------y
Page D-9 Page 187
3m Medical Department Study: T-6295.7
3M MedicalDepartment Study:T-6295.7
ATTACHMENT
E
DATA SPREADSHEETS
Report No. FAC-- TOX-030 laboratory Request Number-U2279
Report No. FACT TOX-030 LaboratoryRequest Number-U2279
3M EnvironmentaLlaboratory 3M Environmental Laboratory
Page E-1 Page 188
3m Medical Depart-,nent Study: T-629A&TOX-030
Report No. FACT TOX-030
CovanceN6329-22l3aboratory Request
study ProducNtumbo(TestSubdarice): N(atruL Method(Revnion: AnmiyticEaqlu4mma Systm N=b@ Irmut@t Softwarwv@m: Fd@e: R-Squa-dValue
Slop. Y-kdacept@ Dwz ofExuvctmoWAnalylL
DateofAnslyan/Analyst DateofDataReduc6orL/Analyvt SALMPle D@sts
26 Week CapsuleToxicitSytudymth PFOS LnCynomclgwMonker
T-6295(PFOS) Monkey Sera FACT-M-3,1AtFACT-M-4.1 Soup020199 MmLy- 3 1 Sm Anachm-u Sm Atuch@u SeeAttichmmts SeeAtuLch@nts 07109/99RWW 02113/99MEE 02/16/9K9rH
BASEIINE N40NKEY SERA
Group
S@ple 0
Dme
MethodBik
M.tm Blk
RBS02099-H20BIk-I
PJ3Sa2O99.H20 Blk-2 RBS02099-SomBIk-I
PFOS Conc mg/=L 000
000
0.00
Couc"tmtiou ofPFOS
Z/.LLor% R., <LOQ
<LOQ
<LOQ
%4e.o PFOS ug/mL
<LOQ
RSD Std.D-. MS/MM RPD
NA
RBS02099-Som Blk-2
0.00
<LOQ
<LOQ
NA
QC - 250 ppb
&0=099-MS
299
121%
&0=099-MM
295
115%
119%
5%
Group I
1055MM+
1.28
<LDQ
Control
105517M+
1.32
<LOQ
0.0 nig/kiVday
105519M+
316
@LOQ
105520M,
1 46
<LOQ
105526m-
1,62
-LOQ
Group 2 L@W-DOOC O@03 Tn&Wday
105527M+ 105529f+ 105530F+ 105531F105535FI03544F I05549F
105513M+ 105514M 105515m,
1 48 2.28 l@13 l@73 146 1 60 5-42
2.63 1.59 0.340
<LOQ
].OQ
NA
<LOQ
<LOQ
<LOQ
<LOQ
<LOQ
<LOQ
@LOQ
NA
@LOQ <LOQ
<LOQ
105516M
265
<LOQ
105521M+
1 72
<LDQ
105525M.
1.90
<LOQ
<LC)Q
<LC)Q
105537F+
1 @33
105541F-
2@ 23
<LOQ
<LOQ
I05543F-
2.53
<LOQ
105546F+
2 50
<LOQ
rOS547F-
1 69
<LOQ
105550F+
1.50-
<LOQ
ILOQ
<LOQ
Gm@p 3
105505M
3.13
<LDQ
Mid-D@e
105510m+
1.04
<LOQ
0,15 mgwday
105518m+ 105523M+ 105524M+ 105523M+ 105532F+
l@51
<LoQ
0.930
<LOQ
1 92
<LOQ
2.69
<LOQ
<LOQ
<Loo
3@13
@LOQ
105539F
225
@LOQ
105539F I05545F+ 10554$F 105532F-
215
<LOQ
3 27
<LOQ
3 60
<LOQ
2.02
<LOQ
<I.OQ
<LOQ
Gmup 4
High-Dose
0 75 mgl*cicy
I05506M+ 105507M 105509M
2.19
<LOQ
2.79
<LOQ
2.06
<LOQ
10551IM
2,69
<LOQ
105512M+
2.64
<LOQ
105522M+ 105533F+
2.73
<LOQ
@LOQ
<LOQ
2.02
<LOQ
105534F+
2.54
'LOQ
I05536F+
2.95
<LOQ
105540F+
3@45
<LOQ
I05542F+
1.94
<LOQ
105551F
3.52
<LOQ
<LOQ
LOQ
L@t ofQu&nLitnum (LOQ): 4.39nwml
Date Entemd/By 02117199 LAC
Number-U2279
NA -@Joatpplicable
PFOS - Pcrfl@ooetw@lf@to
Date Veaw,& By 03123199 OMI, 06(07/00 PW
Dew purttyooffectad/nnfied09/12100nuidi0,9112/00LAC
+ S@ initvioall=eIm.tha0n.5m0I,conc=transohnosubledc@,dredtenutmGe4/28/I0.0A('
Exu-actioVnolume Ratio- htud Volurnw'Fmal%'ol=c
FACT-M-4 I Exmi 9@
3M Environmental
Laboratory
tox-030-sem223.1C
9/12/00
Page 189
3m Med@-cal Department Study: T-629i4C'iTOX-030
Report No. FA-.--TOX-030
Covance#6329-2l2a3boratory Request Nurr@cer-U2279
Study.
Product Nwnbet@Test Subst@e) Mat@ M@thod/R@@ ArAlricalEquipmcrd Synm N=b@ Lmu@@.1 Sft@.r./V-=. F.I.R-Squared Value
Stope@ Y.UILCmtpt: Dwe ofExvactborVAnalyst Date ofAnalysislAnalyst. Date of Data Reducuort/Amlyst
Sample Data WEEK I ?AONKEY SERA
Group
Dan
Sompl* 0
Method Blk
-
Ma= Blk
QC-250p-pb
Group I Cznlrol 0.0mga*dny
Gmup 2 Low-D@ 0 03 m4'cglday
Group 3 M@d-D@ 0 15 mgil*day
RBS02059-H20 Blk-1
RBS02059-H20
Blk.2
R.BS02059--c@ Blk-I
RBS02059-3@ Blk-2
i.MS02059-MS MXS02059-MSD
105508M
105517m+
105519@.i
105520.M
105526.M
105527.M
I05529F
105530F 105531F
105535F
105544F-
105549F
10551 SM+
105516@.1 105521%1
105537F 105541F+ 105547F 10555OF
105505M 105510M. 10531 B.M 105523\4 IC5524M 105528M 105532F105538F
26 Week CapsuleToxicityStudy withPFOS inCynomotgus Monkey,
T-6295 (PFOS) Moikey S.. FACT-M-3 I & FAC7-,ki-AI Md.l.. 041098 & A-ci,.06219?t lvl-Lr@ 3 1 See Attachment.
See Attachments See Attachments See Attachments
02/05/99SAH OZ/09/9,OZ/10199,02/12/99,0211-,,99HOI,DRB 02/10/99.02116/99.02/26199 1101,T)RB
PTOS Come. EVML 0.00 0.00 0,00 01)0 305
--304 0,00 000 0.00 0.00 0.00
0.00
000 o@oo 0.00 0.00 0.00 0.00 495 383 519 6",7 684 464 581 519
287 1109 342 221 319 413 161 257
Coacentmtion
Mean
of PFOS
PFOS
uy)ml or % Rtc
-LC>Q
ILOQ
ILOQ
<LDQ
<LOQ
@LCQ
123@'i
123%
123%
<LOQ
<LOQ
<LCQ
<LC>Q
ILOQ
ILOQ
@LOQ
<LC)Q
<I,OQ
.-[,C)Q
<LO(,)
<LOQ
C)793
o '6-
0832
1 C)9
0869
lic
c 929 0931
0832
0947
4 60
419
-5 48
3@%-l
1:5
5 5:
460
4 31 412
RSD Std.D*v. NISF.MSD RPD
NA NA_
NA_
NA 169 014, 11 6 0,110
170 0782
105539F
248
105545F@
184
105548F
232
105552F
195
3 31
3 69
3 '2
123
3 12
3 71
0 455
Grasp 4
I05506,'A
665
Z13
H*h-D@
10550'7M-
411
2"0
0'75 mglkg/dy
[05509m@
351
18 9
lossi Im-
492
19 3
105512.M
711
229
7 49
105522,M@
539
@l1 6
21 0
1 57
105533F-
564
22 6
105534F-
451
18 1
105536F-
393
21 ()
105540F-
419
i6R
105542F
749
24 0
13 3
10555IF-
377
20 1
204
2 71
Limitof QuantA&t@n (LOQ): 4 39 ng/niL
Data Entemd/By 02/10199.03/01;99 1,A-
Date Venfiodt By 03/23.199O?@4,L,
Date puritycm@udtveri6ed 09112/00ffutth0.9112/00 LAC
NA - Not appl=blc
- Serum srutwvolumelessdw 0 50 mi.,concentratiosnhsouldbe coruideretdcntatme 0
PFCS - Perfluorooct=@lf@ct
Fxtrwum Vol@c P@tio= Init@lVol@tfYmai Val@e
FACT-.%1-4 I Excel 97
3M En-,ri-ronmental Laboratory
tox-030-sem223.1C
9-:12iOO
Page 190
3m Medical
De-uartment
S--udy: T-624@kC-TTOX-030
ReDort No. FACT TOX-030
Covince#6329-22l3aboratory Request Number-U2279
Study
ProductN=ber(T@t Matrix
Sutmt@)
Method)Rcw.n. Aza"cal Eqwpmcnt Sywtem N=b@ Im@ent Soft@e/V@on F@enmc
'6 Week Cap%LdeTomcityStudy mth PFOS in(,%momolgw Monker T-6295 (PFOS) Monkcy 3ers FACT-M-3 I& FACT-M-4.1 M.d@tin. 041093 & A-ba D62498 M..Lym 3 1 See Artachm@tz
,t-SquaredValue Slope
See AttLc?unmu See Attachrnents
Y-',ntuc.pt Date of Extr=borvAnWyat
See AM&chments 02/09/99 JCP
Date of Anairm/Aradyst: Date ofd&ta Reductior@tAnalym:
02/15/99. 02122199 HOJ 02/19/99, 02125199 HOJ
Simple Data
WEEK
2 MONKEY GCGGF
SEP-A
Sample I
PFOS
Concentration
Mo..
RSD
D-
C..C.
ofPFOS
PFOS
Std.Do,.
ngl=L
vgt=L w % R"
mg/mL
MS/MSD RPD
.Mcg@d Blk
RS802D99-H20 Bik-I
0.00
<LOQ
RBS02099-H20 Bk-2
0,00
@LOQ
NA
Matu B&
RBS02099-S@ Bik-1
000
<LOQ
RB302099-Sm Bik-2
00()
<LOQ
NA
QC - 250 ppb
MK302099-MS
293
?AKS020WMSD
300
11ar/. 121%
12(r/.
2%
Group 1 Control 0 0 m&4*day
10550am 105517M 105519M. 10352DM-
A D9 3 07 4 53 7 oa
<LOQ <LOQ <LOQ <LOQ
105526M
2.02
<LOQ
105527M-
1.89
<LOQ
NA
105529F-
0.520
<LOQ
Group 2 L.--D.@ 0.03 mglkgiday
10553CF10553 1 F105535F 105344F105549F-
105514M105515M105516M, 105521M. 105537F-
1.0. 190 3.12 0380 0810 575 513 492 425 446
<LOQ <LOQ <LQQ <LCIQ <LIOQ
1 02 1 03 l@ 19 1 )3 1 19
<LOQ 1 10
NA
7 63 00835
105541 F
72'
ID5547F-
527
105350F+
550
1,16 1 06 0.980
879
1 10
0.0963
CMUP3
105505m-
227
Mid-Dome
105510M
301
0 11 mg'kwdy
105518M.
330
105523M
2RS
105524M-
195
105528M
394
105532F-
173
105539F
416
6.07 4 92 701 4 56 624 6 15 461 667
161
s al
0933
103339F-
32
4 65
G-.p 4 High-D@
105545F
329
1055ASF+
320
105552F
295
105506M-
"47
103507\4-
626
5,28 642 4,73
299 25+1
17@2
5 39
0930
0 15 mgkvdy
105509M
746
23.9
105511 m
706
22.6
105512M
976
31.3
13 1
105522M
8w
105533F
778
105534F-
650
28.8 24.9 26.0
269
3 54
105536F-
588
23.J
10554OF-
5A6
19.5
105542F-
377
19.9
14 8
10353 1F
568
13@2
.12 0
3@25
L@t of Quantitaton (LC)Q) 4.39 NWML
Date Entemd/By Date VcnficdfBy
02a2o99. 03102/99 LAC 031231" GML
Daiep@tyco@clecLsmnfied
09/17=ffui%k 09/112/00LAC
NA - Not appbcable PFCS - Perfluorooctanftulfwate
- S@ initia@lh@ lew Uw 0 50 mL. concentratons shotiidbe crmidered tenlbtiw D4/,,WOO LAC
Extm=on Voi=e Ratio- IjutW Volume/Fmal Volt=c
FAL7-M-.l I Excel 97
3M Env@---onmental
Laboratory
tox-030-wm223-IC
9iI2ioo
Page 191
3m Medical
Departmerit
Study:
T-629k4C@iTOX-030 Covince#6329-223
Report No. FACT TOX-030 laboratory Request Number-U2279
sk*
26Week CapsuleToxmty Studywith?FOS inCynmot" Monkeys
Pmduct Nwnber(restSub&Wwt) Matrix Method(R@aiL AzgyticalEquipmentSywtcm N=ber lmtn=mt Software/Vmlm Film-..
T-6295(?FOS) Monkey Sm ETS41-40 andETS-9-03 MadelineD41(?91A,m@ho 062499,& %4-Lym 3 1 and3 2 See Anuh@ts
Soup 020199
R-Sq=@d V.1Slope
Y-[ntacW. Date ofExtmcticr./ArmLyst. Date fAnsfy@WA@Wyt:
S@ Aft-h-u See AmtchmmU See AmLehnwnu
03102/99SAI-DRWW O-VD5M,OYOL'99.OV25/"
HOJIMEEI)RB
DateofData ReducteWAnWW:
@3/0&'99O.M6/99 KIWDRB
Sample Data
WEEK 4 MONKEY
SERA
Group Do**
PFC3 C@
CMM.NFDStl" ofrym
PF)OS
RSD gtdlD-.
IWN&L
*V'=L or % Rw
or/mL
MSIMSD RPD
med.d B&
R3SO3O79.H20 Bik-I
0,00
<LOQ
RBS03029.H70 Btk-2
0,00
<LCQ
<LC)Q
NA
Matrix Elk
ILBS03029-Sas Blk-I
000
@LQQ
RBW3M9.Sm 3&-2
0,00
<LOQ
<LOQ
NA
Matrix Blk
MKS03029LSen BLk-1
7.21
@LCQ
MKSO3Cr29-Sm Egk-2
7,17
<LOQ
MK503029-Sen B*-3
7,26
@LOQ
MKS03079@Sm Btk-A
632
<LOQ
ILOQ
NA
QC - 250ppb
MXS03029.MS-1
253
N,(KS03029.MSD-1
250
102%
101%
101-/.
1%
MKS03029-MS-2
142
99%
MXS03029-MSD-7
235
95%
3%
Group 1 Control 0 0 mga*day
105umm
543
105517M-
6.76
105519M-
791
10552om-
6 11
105526M
6-,3
<LOQ <LOQ <LOQ <LOQ
<LOQ
105527M,
198
@LCQ
<LOQ
NA
105529F-
663
<LOQ
10553CF-
611
<LOQ
10553 1F
9 19
<LOQ
105535F-
9 17
<LOQ
105544F
996
<LDQ
105549F-
8 74
<LOQ
ILOQ
NA
Group 2
105514M-
log
287
Lo..D@
105515M
1?2
75 2
O@03mgkwday
103516M
196
101
105537F-
186
313
181
403
320
0 57-
3.73
ICJ541F+
153
3.07
105547F
721
10555OF-
163
3.53
953
3,27
3,40
0291
1
Cr.* 3
105505M-
63 7
17.0
%d. D@
to55lom+
646
17.2
0 15 mg/)Wdoy
105518.M-
101
20+1
105523M
110
10552AM
96@3
105529.M-
957
1'6
15 4
9 47
192
179
168
105512F-
41,4
16,6
105539F
7
05539F-
11 5 9
@A3
:05545F103USF,
105557F+
46.7 Is 3 --559
7
:'-7
11 4
14.9
165
1
1 97
1
G@p 4
lit
L16
High-E)ose
:01 M
211
776
O@75n4/Wdy
1055cpgm.
273
5484
105511M +
24 2
48
105512M.
290
774
-38
IOSSIIM+
309
92.2
95,3
',04
105533 +
352
141
10353,4F-
3-63
145
105536F,
240
64,1
10554CF-
938
67.2
L-.t fQ@nWaom
105WF10555IF(LOQ): PFOS - 152 NWML
294
794
42 7
t5o
60,2
i
92 7
1
396
1
DateEntered/By OYOW", 03126t99LAC
DateVi6e& By 0312Y" GMI@
Datepwty co@te&vcrified- D9112MOmmh. 0911I= LAC
NA - Not appbcabk
- S@ initivaolhzme lessOw D@50mL. wntmtrat3onsshotddbe com@deredimtauve 04,29/00LAC
PFCS - PcrG@occtane&Wfamte
Extmcbm Voi=c R@tio- IRUW Volume(FmiaVoi=c
E'rS-8-50 Excel9-,
3M Environmental
Laboratory
lox-030-.m223-IC
9112/00
Page 192
3m Medical Department S'-udy: T-62-94C-YTOX.030
Report No. FAC7- TOX-030
Study: ProductNumber(TeitSubsu=):
Ma=: @.lethod(R@on A@t.ty@ Eq.p-ent Sytm N-b., Imtr=ent SoftwwefV@im FLIc@e: R-Squared Value: Slope Y-intmcept [).!eof ExtmcbotVAnLlyst Data of Ara?ynWAxA)yst. Date of Data ReductorVAnalyst:
Covance#6329-2l2a3boratory
26 Week C.psWe ToxicityShidy w2th PFOS inCynomoigm 1.@ionke@i
T-6295(PFOS) Monkey -'era ETS-94 0 and ETS-8-5,0 A@h. 062499 & Sup 020199 ki-Ly= 3 1 and3 See Anachmmts See Attachments See Anschmenti See Attachments
03ilO/99SAH 031l2f99.03121!99MEE.IDRB 03/1&199,03124/99LAC/DRB
Request Numher-U2279
Sample Data
WEEK 6 MONKEY
SERA
Group Dfte
Sample p
PFOS Come.
Concestraden ofPFOS
M... PFOS
RSD Std.Dtv.
ngf=L
ug/=L w % R"
ug/inL
MSIMSD RPD
Method Eflk
PBS03109-H20 EUk-1
000
<LOQ
RBS031096H20 8&-2
7 74
<LOQ
NA
MatrixBlk
RBS03109-Sm EUk-1
000
<LOQ
RBS03109-Sen Blk@2
4mig
<LOQ
MatrixBlk
MK503109-Sm Bik-1
2.56
<LOQ
MK303109-Sm EUk-2
2,55
<LOQ
MK303109-Scra Bik-3
1.93
<LOQ
MKS03109-Sen Slk-4
o@50()
<LOQ
N*A
QC -250 ppb
MXS03109-MS- 1
264
MKS03109LMSD-1
253
106%
101%
103%
4%
MKS03109-MS-2
243
MK303109-MSO-2
249
97%
1W/.
98*/.
Group I
lo550am-
000
<LCQ
Control
105517,%4@
000
<LOQ
0 0 mWkWday
105579m-
000
<LOQ
105520M
1 60
<LOQ
105526M 105527M-
0610 9@ 49
@LCQ
<LOQ
<[,OQ
NA
105529F+
1.56
<LOQ
103530F-
3,38
<LOQ
105531F
4..4
<LOQ
105535F-
000
<LC>Q
103544F-
0 DO
<LC)Q
105549F-
3@54
<LOQ
ILOQ
NA
C-.p 2
[05514M-
366
3 67
L--D-
105315M.
33.1
3,31
0 03 nWkWdy
105516M-
31@5
3.26
9
10552IM-
41 8
4,19
3 61
0 430
10553'?F-
42,7
4@28
103541F
45 7
3.66
10554?F-
3,6-4"-
365
ii 2
10355OF-
31.1
3.27
3 71
a 417
Gmap 3
105505M
87 4
21@o
M,d-Do-
105510m@
561
0 15 Wkg(day
105518M.
669
2..5 201
105523M-
61@9
18@6
105524M+
7-.7
105528M-
616
21 &
a @19
185
20 4
1 5@
105532F+
61 2
IS 4
105538F
94 5
189
105539F+
61 4
184
105545F
94 5
22,7
105549F+
61 3
194
11 4
105552F
670
16 1
is8
15
G@p 4
105506M-
18,
91@o
tiigh-D@
105507M-
165
97's
0.75 nWkiVday
105509M
230
92 3
10551im
234
93.7
105512m+
211
105
54
105522M+
201
102
9.1 5
80,
105533F
232
930
105334F-
166
833
105316F-
179
898
105540F
909
105542F-
203
la555lF
205
107
-90
82.0
90 1
711
LL=t of Quantitgum(LOQ). PFOS - 15.2rWmL
Date EntaedfBy 031l9t99,03124/9L9AC
Date V@fied/By O&il?f" SAH.05/19@00 PIO;P%V
Date pwry c@mted@mnfied 09flZ/00nm%k 09/IZM LAC
PFCS - Perfl@t@Wfomte
- Serum mbsj @l@ ten dw 0 50 mL, cmcentratiomshciddbe com:deredientat@ 04/28/00LAC
NA - Not apph=ble
ExtractioVnolume Ratio- liubalVoLume/Fmal %'ol=c
ETS-3-5 D Excel 97
3M Environmental
T ahcratory
lox-030-scm223-IC
9112/00
Page 193
3m Med@-cal Department
S@::udy: T-629F@kC-7TOX-030
Report No.
CovsnceO#6329-2l2a3boratory
Request
Study
26W@k CapsWe To@mty StAy 'nthPFOS m CYnomOigw -MOnkeYs
ProductNumbert7est Substance):
T-6295 (PFOS)
M.tr..
@Method(R@.on AnWyncil Eqwpmmt Syt@ Instr=mt Soft-@eV@on
@4@b@
Mmkcy sErS-8-40 md M 9-5 0 sup 02at99 Mu,Ly- 3.1-d 3.2
F,I,.-.:
S@-Afth.-u
R-Squ@d VaJue:
Sft Attachmmts
Slope*
See Aftct@enLs
Y-Ent@cept
See Artachmwts
Dateof ExtractiortAzWyst
03,03@99 RWW/ICP
Date ofAnaly%WAra&ISL
OV05t". 0,VO9/99,OV10,99,D-V2" DRB
Date of Data ReducwrVArQtyu:
03/0&'99.OY15199,03124M,03.r26MORB
Sam pie Data
%TEK 3 MONYM SMZA
Group
smpio 0
PFOS
M@
RSD
Don
C@
O(PFM
PF03
31.L0".
oV=L
ViaL w % Rse
aWmL
MSIMSD RPD
Method Bik Matnx Blk
RBS03039-K2O EQ. k
R.BS03039-H20 Blk-2
000
RBS03039-Sem Blk-1
00
ILBS03039-Sm BM-2
000
LoQ
@<LOQ
ILOQ
NA
@LOQ
@LOQ
ILOQ
NA
Mabrbe Blk
MKS03039-Sen Blk-@
323
LOQ
MXS03039-Sm B&-2
-210
<LOQ
QC.250 ppb
MXS03039-MS-l
174
69%
MXS03039-MSD@l
191
<LDQ
NA
72%
9-16
MKS03039-MS-2
205
82%
)4KS03039.MSD-2
lss
73%
10%
MKS03039.MS-3
111
MXS03039-MSD-3
203
Group 1
10550am
943
Control
105517M
768
72% 91%
<LOQ
LOQ
76%
11%
0 a mSA4(day
105519M
120
fO552OM
903
105526M
11.0
105527M
78.9
<LOQ
<LOQ
@LOQ
0<.03&5
@LOQ IA-mly
NA
105529F
16,0
00214
tOS53OF
193
00244
105531F
ISO
0.0206
105535F
14 5
<LOQ
1035."F
946
105549F
150
<LOQ 0.0240
0 @.26 -2 A@@&l@,
836 000199
Group 2
03514M
34 5
461
I-aw-Dose
:05513M
31 2
7
0 03 mgfwdy
103316M
"1
5.15
105521m
31 8
-5 10
105537F
46@ L
528
9 14
473
0 432
105541F
36.3
485
105547F
37.3
499
1
10555OF
344
394
4-6
011177
Group 3
105505M
122
279
Md-Dose
toi5lom
92 9
22.1
0.15mg/kviy
105518M
941
25@l
105523M
91 6
24.5
101524M
III
31.6
12 7
1
105528M
1
10"
24@6
26,0
3 30
105532F
961
276
105538F
106
24 3
105539F
926
265
105545F
122
24.5
10554F
69 4
'2 3
12
105552F
593
191
240
306
Group 4
05506M
a122
125
High-D@
;05507M
38
961
O@75mga*day
105509M
117
103
105511 m
198
92.3
105512M
115
[is
16 7
105522M
127
131
109
18 3
1
105533F
107
ilo
105534F
981
121
101 36F
100
102
1055,W
102
105
[05542F
113
116
11 1
105351 F
1
2
-873
1
107
11 0
L@t of QuRntitanonCLOQ): PFOS - 152 nwml
D@te Entmd,By OMS'99,03/24M. 03(26(99i-AC
Dste Venfi@,VBy OBIISM SAlt 051)1100 PJO, O5f23100& 05-124/0P0W
Date ptmryc@eoe&@fied 09/12,Wmmh, D9/l2jOOLAC
PFOS - PerflwrooctRnmuifo@le NA = Not apphcsble
Fxtncnon Volume Ratio- [=bidVolume/Fmal Volume
FACT TOX-030 Number-U2279
M-9.5 0 E@@i 97
3M Env@-rc)nme.-ita'-Llaboratory
tax-030-scm223-IC
9!12too
Page 194
3m med@-cal Department
Sz:udy: T-6291EA&TOX-030
Report Nc. FAC- TOX-030
Covance#6329-22l3aboratory Request Number-U2279
ShLdy:
Product NLunbMTest Matnx
Subgwxt):
Method/R@ion:
ArWybcal Equipment Systm N@b@
I-tr--t s.ft-./V.,.m FJ@c R-Sq@d Value:
Slope
26 Week CapsWe T=ctfy T-6291 (PFOS)
Monkey Sm ETS-8-4.0and M-9.5 0 Soup 020199
M-Ly- 3 2 S@ Attachrnmt, S" AtUchMMU See AttaclunmU
Study with PFOS
m Cy@molgLu
kionkrys
Y-Inl=cpt: Dote of Extriebori/ArWyst Date ofAngy&WAnalystDate of Data ReductolVAnalyst.
S" Amelunents
03/03M RWW/JCP
03/05/99,03/09/W.0-VI".0312.999 OPB
03/DM, DVI5/99,M".
ON7&'99 I)RB
Simple 1),ata
WEEK 12MONKEY SERA
G-" D.m
S@ple 0
PFOS Coo@ ogintl
conopmuldim of PFOS
vg/=L or% Rw
M@ PFOS ut/.L
RSD Std. D-.
RPD
Method Bik Mabrix Blk matrgx EQ QC -250 ppb
R.BS03039-H20 aik-1 R.BS03039-H20 EQ.',
RBS03039-SRBS03039-Sm MKS03039-Sen MKS03039-Scra
Ek- I ELk-2 RI-I B&-2
MKS03039-?AS-1 MKS03039.MSI)@l MKS03039-MS-2 MXS03039-MSr,2 MK503039-MS-3
0 DO 0 DO O.DO 0,00 323 2.10 174 191 203 195 111
<LOQ <LOQ <LOQ <LOQ
@LOQ
<LOO 69% 76% 92% 73% 72%
LOQ
NA
@I.DQ
NA
@LDQ
NA
-2@,.
9%
10%
MKS03039.MSD-3
203
81%
76%
11%
G-p 1 Conb@i 0 0 mg/Wday
G@p 2 Lo--Dom 0 03 mrwd.y
Cre" 3 Mid-D0 15 mVWday
G-P 4 High-E)OSC 0 75 mg(Wday
10550am 105517M to5si9m 105520M 105526M 105527M 105529F10533OF (05531 F 105535F 105544F 105549F 103514M 105515M 105516M
103505M 1055tom 1035ism 105523M103524M 10552am 105532F 105338F@055539F 0 545F 10554F 105552F 103-1@06M 103507M 05509M @0551 1 m 103512M 105522M05533F
309 269 329 12.7 21 3 30.1
114 16,4 19@o
943 181 233 41 8
443 414 451 579 34,8
36.9 488 143
135 133 Rs 0
]is
792
1
969 942
101 109 796 774
103 864
16
.13.9
149
R9 0
ID9
0,0381 0.0430 0 OA39 <LOQ D@D2" 00423 <LCQ 0,D243 O@0254 <LOQ 0.0238 0,0316
6,20 649 655
691 5,57 7.03 5,93 401 392 33.7 33.3 37.1 25 4 25: 32 279 322 232 248 116 106 123 99.4 167 121 126
0 0383. 1Anomaly
0 0263 -1 Anomaim 6.9 631
35
1
'.78
122
21 1 000811
010(33)362
963 0518
il4 0-17
1!3 3 39
i43 3 99
196
23 9
1
I L-,t ofq@tubm
(IA)Q):PFOS
PFOS - Patuoroocttnftulfanote
:05534F 105536F10554OF103542F 105351F 15,,'gi.L
Date p=ty
IDO
114
636
98.0
900
112
128
131
114
1
117
1
D.I.Enic,ed/By 01,09,99.03,124t",O-V26,9L9AC
DateVmfied/ By: OIVIM SAH,OY24= PW
.nded@vaiS@d 09/12100mnxk 09/12100LAC
Se@ mhal "I@ Im dun 0.50mi, cm@tmbom
ico 117
sholddbe comidmd t=tative04(7&00 LAC
\A - Notapp6c.ble
Extmctim Volume RAto - initw VohznejT@W Val=c
E7'S-9-50 Excel 97
3M Env4-ronmenL@-a 1 T aboratory
tox-030-$=223- IC
9/12100
Page 195
3m Medical Department
Study: T-629AC-TTOX.030
Report No. FAC7 i-OX-030
CovanccW6329-2l2a3boratory Request Number-U2279
Study: Prodwt Nmbci(Test Subel@e): main.: M.thod'P--: AnalyticaElqwpnient Syg= N=ber.
26 Wmk Capsule Tomcj?y Study mth T-6795 (PFOS) Moky S,ETS-9-4 0-d ET@-S. 5 0 Soup 020199
PFOS
in Cymmclgtu
Monkeys
lnswm=t Software/Vavm
Mu&Lynx 3 2
FLmme: R-Squared Value
Slopc Y-Invercept Nte ofExtracti@VAnafyst Date o(AnakyoWArAlyst, Date of Data lUductioWAna)yv,
Sample Data
See Anschrnents See AtLKh@ts See AV@hmmts See Amuhmuft
3/IV" SAHFRWW OYIYW,03/19/99 DRA(HOJ
03/16(W,03r24199 DR3
WEEK
16 MONKLFY
G rwap Dwe
SERA
SULF40 0
PFOS CML attaLL
concomuttkm acrym
ugfuLL or% Rw
M@ Pros og/nLL
RSD STILDWV.
Mcdmd Blk Mabu Blk M&hu Blk QC -250 ;Ypb
R.BS03129@H20 Bik-1
0.00
RBS031MH20BIk-2
000
RBS03129-Sm Bik-1
0.00
REM3129-Sm Bik-2
0.00
MXS03129-Sm B&-1
150
MKS03129-Sem Blk-2
76
MKS03129-MS-1
ag
MKS03129-MSD-1
:99
MKS031MMS-2
"
MKS03129-MSD-2
1I35
@LOQ <LOQ
<LOQ
<LOQ
<LOQ
@LCO
72% 76% 76% 9(Y%
@LOQ @OQ
ILOQ "4% 83%
NA NA NA -5% 16%
G@p 1 Corwol
105508M
21 @5
105517M -
204
0,0344 O.D409
0 0 mg(kwday
ID5519M-
21+1
0.0423
10557am 105526M 103527M
20 '
0+0332
199
(1.032()
394
0,0615
00407
27 1 00110
105529F
355
0.0438
10553OF-
251
00515
105531F
21.5
00314
105535F1035"F105549F
9.37
<LOQ
116
<LOQ
19
29.9
O@0462
0 0432 -2 Anomahn
0 OCS51
G@p 2
105514M
77.7
1
104
Low-Dm 0.03 mgkwday
105515M-
473
105516M
91 7
10552]M+
931
105537F
764
105541 F-
692
9.47 oll @4.R 11.1 12.3
21 9
11 2
1
2 44
105547F
668
10.7
91
10555OF
539
795
los
90
G-.p 3 Mid-Elmo 0 15 n-*IWday
105505m,
222
594
10551ONi
33.0
52.9
105519.',4
379
607
05523.%1
326
52 2
@ 05524,M 105529M 05532F @05538F 105339F
415,
1
634
36
2!2
404
2.9
37@3
3A7
1
463
10 4
562
5 84
05545F
323
'3.1
@05548F
323
470
959
105552F
241
38+7
1
421
404
Gr"p 4 H*@Dow 0 75mtwday
103506M 105307M 105509-M
@005555I:M2m 105522M 05533F
273
182
257 172
196
197
168
179
196
216
1
254
195
45
164
9 42
189
159
:05534F
1I%
137
105536F+
14
194
10554F
11
73
105541F
3
68
it 9
L@t ofq@maom
(LOQ): PFCS
10555[F 15 2 ngiml
1
1@9"'1
DatfEntm&llf.
127
I
162
OVOLV9.OY17199,03124(99 L.AC
I
193
Dole Vmfiedl By: WtL,99 SAH, 0511&00,05174/00PW
Date punty m@tedivenfiedi 09tt2/OOnunh.09/17,'0L0AC
PFOS - Pcrffuoroact@df@te
Semm @tW vidi@ Ins thm 0 50 mL, co@natom shotddbe c@id@ed imtnnw. 04/29100LAC
NA - Not sppii"blt
Extwtm Volme Ratio- InitiVaoltume;FinalVoi=e
ETS-9. 5 0 Fxc6 97
3M Environmental
Laboratory
tox-030-wm223-IC
9112/00
Page 196
3m Medical Department
S--udy: T-629iEACITOX-030
Report No. FAC'-7 TOX-030
Covsnce#6329-2l2a3 boratory Request Number-U2279
SDAY Prodwt Nuinber(Te3Stubstan") MotM,OtodfkAmilytiWEqup@t Systm N=b@ imt@t Soft@cfvmlm
Fdenarm: R-Sqwed V.1Slope. Y-int,-@pt DikbeofExtu-bort/Analyst: DateOfAAStYaWAnatyst:
DateofDaLs Rt&mtioiVAngM
26W"k CaouleTo)dc@StWywithPFOSm Cynoinolgiukionkeys T-6295 CPFOS)
kAonky Sm ETS-8.4,0@M E7S-9-5 0 Soup 020199 M-Lynx 3 1 Sm Anachments
S@ And=mts SftAftich@U See Attichmmt& 3115M ICP/SAH OYI&199.0312A/99D" OY17199,OYZY" DKB
Sample Data
V;EEK
20 MONKEY Grw* D@
Method Bik Mao= Blk
Mstnx Blk QC -250 ppb
SER.A
RI=3159-H20 8*-l RBW3159.H20 B&-2 iLBS03li9.SemBD(-] XBS031WSenSIk-2 MKS03159-Scn Sik-1 )AK.S03159,44nBlk.2
RWO3159.ms-l RM3MMSD-1
PFOS
C@
ng(ml 0.00 000 0.00 0,00
0.00 o.00
256 726
ofP703 igglaLwL% Rw
<LOQ <LOQ
<LOQ <LOQ
<LOQ <LOQ 103% 91%
PFOS ug/mL <LOQ <LOQ <LOQ
97-/.
RSD Sid. D@. MS/M3D RPD
NA
NA NA
13%
Cmtrot
Grmp 2 L@w-Dose 0.03 mwl*dy
Crww 3 Mid-D@ 0 15 mglwday
Crwp 4 Higt,D@ 0 75 mWI@Wday
L@tofQ@tUwn(LOQ)
RBS03159-MS-2 RBS03159.MSD-2
105-1.0am 105517M 105519m105520.M 105526.M
105527M105529F la533OF
105531F105535F 105544F105549F
103514M 05515.M
;05516.M 103521.k( 105337F 105541F 1055ATF 10555OF
105505M 105510M :0551sm
(05523M 105524M 105328M 105532F 105538F 105539F+
1055A5F 0554$F
105352F 105506M 10550-,M+ 105509M
10551im io55l2m 105522M 105533F 105534F
105336F105WF 105542F-
10555tf PFOS-152rWmL
219
U%
223
90%
30.4
0.0349
314.
0.06419
19.3
0.0336
23.2
00300
30.0
0.0369
31,5
1
516
0.0631 0.06[7
393
0.0579
29.3
0.0493
tg 4
0-0263
296
0,0505
391
0.0570
88,6
12@5
867
10,7
101
119
98.3
14,1
70@2
il'O
73 2
tt@5
966
t4.3
359
41 1
237
62.3
233
63.3
248
631
319
752
220
640
323
542
135
69 2
201
474
210
79.2
111
45.7
204
65@3
154
42@7
391
158
29,
139
315
152
352
126
309
143
302
1
145
393
169
303
143
214
146
"1
193
302
151
330
112
Dte EnteredfBy:03(OW". OYl7M9 LAC
DateVuific&BY: OIVIL'99SAH, 0511'7/0P0W
00400
00504 12.3 12,3 195
631
51 1
144
156
2%
29.9 00120
252
1
00127
11 4
1,40 14 6 179 744 145
105 6 71
25 4 14
762 109
14 0
1
218
PFOS - P@f=oocanesWfonam N A - Not wwyaed, mt appbelblt
D.tep@tycoff"ted@veri5ed0:9/12=nunkO9tl2=LAC Calculatemdthmi sam* 10555OF
S@=tWmhunelmd@0.50ML,@tmb@shoWdbecomWmdt-tswe
04r2M
L-AC
E.@.tim V@]@ Ratio- blib@VohimvTiW Volme
M-9.5 0 F@mi 97
3M Environmental
Laboratory
tox-03D-SCM223-IC
W 12/00
Page 197
3m Medical
E)epartment
Study:
T-6291FAC@TOX-030
Report No. FACT TOX-030
Covmnce#6329-22l3aboratory
Request Number-U22-/9
Study: PToductNmbcr(Ted Subsimm) Ma=: M.th.d(R@@i.i-: AnalytealEqutpnuouSyxu= N@ber
26Week CapsWe To)uctlyS"
T-6295 (PFOS) Monkey Sm M-9-4 0 -d ET@-8.50 Aeba 062499& Sop 020199
vathPFOS
m C)-romolg@
%lon@eYs
huuw@t Softwue/Vas=L Fdename:
V@Ly= 3 1 SeeA=KM=ts
R-Squared Value: Slope: Y-Intcroe;n: Dateof ExtwwWAnalyst: DateofAnitysWArak"t
Sm A=hrnwts SeeAtt.,@"u
S@. Aftachmmt, 3116,'9R9WWI-AK 03117/99M,OM,
0312Y"
DRBIMEE
Dot.ofdats ReducocriAr&4@t
O3W2l'99,=4?99.04/02/"DFLB
Sample Data
WEEK 24 MONXLRY SERA
Cr-P
sampit N
PFOS
c
om
Mmn
ITSD
C@
ofPFOS
PFOS
Std.D".
UVML
. w% Rm
@y)-L
MSMSD RPO
Medwd Blk
R.BS03169-H2O Blk-1
000
@LOQ
RBS03169.H7O Bik-2
000
<LOQ
@LCIQ
NA
Ma= Blk
ILBS03169-Sem Blk.I
ooo
<LOQ
P.BS03169-Sen 82.2
000
@LDQ
< LoQ
NA
QC -250 ppb
PBS03169-MS-1
219
ar/.
R.BS03169@MSD-1
736
95%
91! i
8%
R.BS03169,-MS-2
231
93%
PJM3169-MSD-2
96%
99-/.
ILBS03169-MS-3
224
90%
RSS03169-?ASD-3
220
89%
90-/.
2%
Grm* 1 conami 0 0 mWVday
1035mm
36.4
0.0"9
105517M
303
0,0496
105519M
258
D@0414
105570.1@(
194
0.0223
105526M
248
0.0397
105527M-
36.7
(1.0613
105529F
40.4
0.049%
10553OF-
242
0,0497
00440
177
1
00101
105531F
259
00364
105335F-
8.36
<LOQ
[055"F-
162
0,0325
A4
105549F
334
0.0446
0 0426 - IAn.@aly
ID0794
Grow 2
105314m-
14.7
L@-Dose
105515M-
1I1,4
0,9
0 03 m&Uday
1055t6M
132
:4.1
21 0
105521M,
141
IN@4
306
105537F
13'
@,4
1055AIF
133
:3'
105547F,
949
12.7
10555CF
109
122
5 18
13,0
0 675
G@p 3
105505M
251
7114
Mid-E@.se
105510M
196
652
O@15mgA,g/day
10551am
191
588
105523M
164
59@l
105324M
201
69.6
104
105529M,
155
64.8
659
688
105532F105539F 105539F105543F 10554OF 103552F+
:45
63@)
53
496
696
:,6"9
635
196
56 1
139
617
12 0
60 1
7 24
High-Do"
103506M
287
199
105507M
234
in
0 75mga*day
1055D9M
m
m
lo@51 1m
258
207
105512161
309
247
105522m+
233
233
F05533F
290
190
116
iis
2A9
105534F-
225
200
105536F,
207
169
Lvmt ofQumtutcn O.CQ@. PFOS
10554OF 10554,F 105551F@ 15@2ngirnl
219
151
240
191
1
131
150
174
Die Enined'By 03f24,99L&C
D@t@Vmfi@d)By 0811&1"SAM, O-V24,00PW
17 0
1
209
?FOS - Peduarooctwmulf@te
Datep=ry coffwe&venfie& 09112/WmrrLkD9/IVDOLAC - S@ mtialvol@ lessthm 0.50mL, @n@trato" shouldbe c@id@ed
W29100 LAC
%i-.Monburkd NA - Not app6-ble
ExtractonVol@e Rimo - lmtw Volume/FmalVol@c
ETS-9-5 0 Exat 97
3M Environmental
Laboratory
t.x.030-jm223-IC
9111,00
Page 198
3m Medical Department
S--udy: T-62StEAC'tTOX-030
Report No. FACT TOX-C30
Covance#6329-2l2a3boratory Request Number-U2279
shwr.
.1W6oekCapultToxiciSttyudyw7thPFOSinCynmoigusNionkeys
ProductNumba(Tnt Subsmrkce)
T-6295(PFCS)
Matrix
?.ionkeySem
Methad(R@.
ETS-8-A0 -d ETS-&S.O
AnaiytcaElquipmmt Sytm N@ber
Ameba 0-62498,Soup 020199
lmu@=t SoftwarvV@m:
'AsLy- 3.1
Fde@t
See AMWILmcnt3
R-Squared Vaiw:
Se. Anachm@ts
Slope
See Attachments
Y-lateTcept
See Attachments
Date orExlwtcWAraL]yst:
3,'16(99PWW/SAN
Date ofAn@OWAn*st:
03/17199.03r2l/99DRBIMEE
Date ofData ReduftordAna@v
03123/99,03122/99 ORB/MEE
Sam pieData
WEEK 26 MONKEY SERA
Group
S.Mpl. a
PF03
Comcmtmtion
M..n
RSD
D."
Conc.
of pros
Pros
Sta. Be-.
og/=L
uVmL or% Ret
mg/mL
M&MSD RPD
mee@d B& m.ou Blk
P.B303169.H2O Egk-1
000
P.BS03169-Ft2O Bik-2
0.DO
RBS03169-S@ Blk-1
0.00
<LOQ
<LOQ
ll.OQ
NA
<LOQ
RBS03169-S- Bik-2
000
<IDQ
NA
QC - 250 ppb
FLB303169-.MS- 1
210
85%
RBS03169.MSr)-i
232
94%
99%
10%
RBS03169IMS-,
229
RM3169.MSD-2
193
92%
7rA
95@'.
17%
RBS03169-MS-3
211
RBS03169-MSD-3
213
93%
86%
86%
1%
Group 1
1055ow
30.9
O@0496
Control 0 0 n*(Wday
105517M-
31.0
105519.M
27.1
0.0539 0.0417
105520M
16,8
0,0254
(05526M
26.7
0.0376
31.3
105327KI 105529F
Al.7
t
48.1
0.0669 0.0613
00459
00143
10353OF
597
0.0736
10353 1F
30 1
00431
105531 F
166
00266
105544F@
216
0.0433
12 5
105549F
34 7
0,0536
00506
0 016A
Group2
Lo@.D@
105514.k4
151
16,,
105515.M
143
16.3
0 03 rrtwkg/day
105516M
131
105521M-
)1,
13.8
9.91
16,9
15 8
1 41
105537F,
101
13.3
10554]F-
113
14,8
105547F
140
13.0
108
10555OF-
85 3
11.4
13
1 42
Gmup 3
105505M
253
9r2.9
Mid-Dose
1055]OM-
149
129
0 15 mwvday
1055]BM-
141
69.5
105523M-
176
72@ 1
105524M+
160
69 3
30 4
105529M
156
62.4
8,'6
::52
105537F
.109
63 4
105538F
150
59 0
105539F
'16
72.2
105545F
as 7
105548F-
145
64.5
163
105552F
142
55+6
668
1
108
Group 4
105506M
m
m
Hi$h-D@
105507M-
213
197
0 75 w4A*day
105509M
m
m
105511 A
248
142
101517.M
285
143
210
105522.M
299
221
173
36 5
105533F
340
203
105534F
308
IV
105536F-
155
135
10554OF
178
17'1
105542F
206
165
130
10555IF-
163
142
171
22@2
L@t ofQuantuwn (LOQ) PFOS 15.2nWmL
Date EnieredfBy. 03123t99 LAC
M %Amburld
On(.Vwfia& By 08/19,99SA)t 05f24iOOPW
Datepxmtyc@tc&verLf@d 09112=nwdt.09112= LjkC
PFOS - Perfluctoocw=Wfowe
Senun Lrutavloi=e lessdm 0.50mL, concentraocnsihowd be c@idered tentatiw 04,2&00 LAC
NA = 'Jotappbcable
Ex=acton Vohunc Ratio- ImtuaVohunt.'Fmal%'olme
ETS-9-5 0 E.@.1 97
3M Environmental
Laboratory
tox-030@@223-IC
9/12;00
Page 199
3m Medical
Departmer-'-
Sz:udy:
T-629f@-AC-YTOX-030
Report No.
Covince#6329-223 laboratory Request
FACT TOX-030 Number-TJ2279
Study
Pt.dwtN-bf(T.9 S-b@--)
met..:
A4.th@d/RA,Wyb.W
Syvm N@b@
R-SquLmd Valu.
SI.P.Y-t.t-.O: Dot :(Fxuwboo/AnskYrt
D.t: fAnaly"AA&Iyvt Dateof Deb PjhdnctoniAA&@YA
26Wwk Cap.W.T-ty Study-th Pros T-6295(PFt)S) %4..kySE,"3-9-I-4d M-8-5 I D.-y07G799
MwLynx 3 3 S. Aft-h.-t. SftAttackm@u S. AH.It-@.u St.AMehm@U 06101/DOSALIKJX 06/0&00.06JI4100,0611uwLANMMH 06la7)OO,WI5=.06Jl9fDLDA.VMMH
Cy.-ig-
kimky.
Sample Data
WEEK 27 MONKEY Groop Do"
,M.thodBlk M.= EQ QC . 250ppb G-p 1 Conftl 0a Vwdy
Grmp 2 l@-D@ 0 03 mWWd-Y
Gmep 3 .M.d-D@ 0 13 m&Wdsy
Gmup 4 H.Sh-D@ 0,75.&AqVday
Lmt ofq@izubm (LOQ)
PFOS- p@fl@w@Wfomte NA - Not Vpb"ble
SERA
se.pi.0
Pros
C.2c.
V.l
D6010-H@O Bik-5
000
I D601C).@MBIk-6
000
RBSM@o-sn :tk'5 0 Oc RBSM o-sm lk-6 000
105319m-ms-5
350
105519u-msrD)-5
353
103509M
53,1
103319%(
49.5
tos527M
$().1
1055)OF
73.1
105531F
431
105133F
366
[05544F
39,9
10551AM
172
105515M
187
loi5l6m
165
105 5 111'ki
273
105541F
181
10554-F
il7
10555OF
161,
105310M
316
1055]$M
116
105524M
2-,9
io55',BM
344
10533,F
,30
105533F
760
105545F
267
10554$F
300
105506m*
(05507M
4.24.
105312.%4
464
1055)AF
419
105536F
389
10554OF
377
10553IF
291
PFC)S 555ng@L
Dtt*Eaur-&By:
D.i.V-6.&13y
Dstepmtyco@tod(vmhed
ExtnctonVol@o
CamconLr.uos
M,sn
RSD
ofPros W.L .,% R..
PFOS
V.L
59& D-. M&(MSD RPD
@LOQ
@ LOQ
@LOQ
NA
<LOQ
@LOQ
@LOQ
NA
121%
122%
122%
1%
0,0461
0.1)430
27 4
0.0695
00529
00145
0.0633
0.0374
0.0318 0.0339
00416
35 5 1 ____0.0142
239
130
114
34 8
15,5
15 9
5 34
12.6
951
1
--11.2
1
2
68.5
68 7
60@6
8 44
747
681
5 ?5
54 3
56.5
30
7
658.1
59 1
4 67
196
114
461
202
194
993
192 169
164
14 9
126
160
23 9 ....
06/07100,0&]9tOLOAC
06/0&'0P0IW
09112JDOmmh.D9/12(DLOAC Ex",tm %,ol@cRato- lmtsival@&iFoW
Ra?3o Voh=c,TmalVol=t
Vol@c
Excel97
3M Erivironmental
Laboratory
1--030@-223-IC
9112too
Page 200
3m Medical
Departmert-- Study:
T-62-c@AC'YTOX-030
Report No. FACT TOX-030
Covance#6329-223 laboratory Request Number-U2279
S"
ProducNt=bcr(Tnt SubstAn") Msuix@ Method(R@m: AnilybcalEqLnpmcntSystm N=b@ irsu@mt SoftwucNmim:
Fdcnwne R-Scpwcd Value. SkV.Y-inum@PL DateofExawdon/Analyst DateofA..kynVAnalyst Date ofData Pxducncn/Analyst:
26 Week CapsWe Toxmry Study withPFOS inCynomo4w T-6295 (PFOS) Monkey Sera E7S4-4 0 -d ETS-9-50 Ameba 062498,Soup 020199,ALMadeline0410" %4@Lyrix 3.2 See Attachment&
%,(OnkeYs
Sm AMuhmcnts S" Attachments
SeaAuhmenu 04'D6/99RWW 04/07/99,0,VI2199.OA117/99,DS/14199,0511H7O1J9f9E)RJWEE/YIH 04109/99,0411YW,D4nO/99.05/17199,0-Vl&MHOJIDRa/KJfl
Sample DaU
DAY 193 MONKLRY Group
Do"
SERA
S..pi.0
Lmut
Method EiLk
R.BS04069-H20 Bai-i RBS04069-H20 B&-2
Mabix Bik
RBS04069-Scra H&-l
RBS04069-Sem B&-'
QC -250 ppb
MXS04069-MS-l MKS040691-MSD- 1
MKS04069-US-2
Group 1
MKS04OWMSD-2 105520M
Cmtrol
-105526M,
0.0 mgAtWday
105529F
105549F
Group 3
103505m+
%fid-D@
tO5323M
0.15mg/kWdy
105539F-
105152F
Group 4
105511M-
High-Dom
105572,\i
0.75 mg/Wdy
103533F
105542F
fQ-bubm (LOQ):PFOS 132 rWw.L
PFOS - Perfluoroocunaulfonate .4A - Notapplicable
Datep@ry
PF03
com..rwb"
A4@
RSD
Coo@
ofPros
PFOS
StL D4@.
agJ=L
V&NNL - % Rw
ugt=L
MSIMSD RPD
0.00
<LOQ
142
<LOQ
NA
NA
O.DO
<LOQ
12,1
<LCQ
NA
NA
254
102%
246
99%
101%
3%
267
lora
228
92%
locr/.
16%
129 297--
0171 00626
0 117
653 0 01!64
660
0.0756
59,2
21 3
00310
00533
00315
371
74.4
176
797
955
85 0
149
479
107
43.0
391
36.9
91.7
35 1
97.1
216
188
194
287
249
468
245
239
175
176
201
230
403
DoteEnLaed(By@ 19/99O.-VI". MOM LAC
DateV@Tihe&By =I 9t99SAH, beforOe&OVOC TY P,
c@tednoified: 09112100ffurdi0,9/12/00I.AC
- Serum cr@tlvaollumeIm dw 0.50mL, concmtntiom shouldbecomickiedteniatme04/28/00LAC
Extncton Volume Ratm - imtw VolmefFinalVolume
Ers-9-5 0 EXCel 97
3M Environmental
Laboratory
iox-030-wm223@IC
9111100
Page 201
3m Med@-cal Department
Study:
T-629@ACiTOX-030
Report No. FACT TOX-030
Covance#6329-223 laboratory Request Number-U2279
Study
ProductNumbct(TestSubstance) M.1m@ \4@Eh.d(R-@-: Analytc&ElqmPmmt SYstm N@b@ tnst@mt SoftwxrefV@on
-UcnmeR-Sq@d Val@: Slope Y-intacept: DateofExtnctiorJAnatyst Date fA..Iy,@eArAly.t Dateof DataRedu=oYVAA&tyst*
26Week Ca" ToxcrySh* withPFOS inCy-nmolVa Monkeys
T-6295(PFOS)
Monkey Sen E-@-3-4@OUW M-9.5 0 Ameba 062498.Soup010199.& MBdelme041098 M@Lym 3 2 SeeAnwh@-z See Aft&Chff-ts
S@ Attuh@ts SeeAttachmnu 04,061"RWW o4(07199,04/12/99,ovl7199,05/le",05I/]1O7I1/9D9RBIMELICII
o4to9t99,04115,99,0412W",05/17t99,051H1O9J(I9D9RB.IKJH
Sample Data
DAY134
MONKEY
Gnmp D@
SERA
smpl. 0
PFW Cwc ngtml
concumatwo serros
upf=L w % R"
Mma PF03 oW.L
RSD Sid.D-. MW.MSD RPD
M.dwd BA
PBS04D69-H20 BLk-I
O@OD
<LOQ
RBSOdM.H2O B&-2
142
<LOQ
NA
'4A
Mab-txBlk
P.BW4069-S. Ekk-1
000
@LN
-RBS04069-Scn Bik-2
12,?
<LOQ
NA
NA
QC -250 ppb
MKS04069-MS-1
254
102%
MKS04069-MSD-1
246
99%
3%
MKS04069-MS-2
267
108%
MKS44069.MSD-2
229
92%
16%
Gn.p 1 control O.DmgAWday
G@p 3 MLd-Dme 0 15mg/kg/dy
Iiigh-E)@e 0.75mo*day
105510M 105526M 105529F 105549F
105505M
10552.3M 105539F rO5552F105511m
105522M 105333F 103542F
12.3
<LCQ
232
0.0233
0.023.-3IAnmily
NA
436
0'0416
259
280
0.0297
0 0352
000911
621
664
6-,2
692
-730
69 7
469
sio
963
54
390
695
@20
192
ist
42 5
264
336
259
110
242
265
11,9
210
7.24
245
292
-=t ofquanotatiCoLnOQ) PFOS 152 neml
DateEntend/By 04119/99.05110M,09=99LAC DateVm&& By- Ogn4/99 SAH, befat 06/OgiD7OKR
Datepuritmymctedtvmfied: 09/12= mmh. 09112100LAC
PFOS - PmtuofooctinesWfonate
Sam 4ut&lvol=e lessOw 0.50mL, concentratosnhsowd be cons,&@edient=ve OV2&'DO LAC
N A - Not apphcablc
ExtractoVnoi=c Ratio- ijutwVoi=e/Fui4%'ol@c
ETS-9-5a F.X.,9l7
3M Env4.ronmental
Laboratory
lox-030-mm223,-lC
9;12-00
Page 202
3m Medical
Departrrent
Study:
T-6291FACYTOX-030
Report No. FAC-- TOX-030
Covancc#6329-22l3aboratory Request Number-U2279
Study: Prodmi N=bcr(ral
Substmw@.
Armiytic.EJquLpr@t System N=ba lmouawd Scft-./Venwn@ Fo@: R-Squmd Valm:
Slope: Y-intactpl: Date of Exu@-bordAnatywL Date o(Analy&WAnatyst Date of Data RaductLoWArAlyst
Sample Data DAY125 MONICEY SERA
r.,.w D-.
Smpieo
Mediod Blk Mau= BLk (2C -250 ppb
P BS04069-H20 nSO4069-RIO Rsso4o6g-scm
Blk-1 EM-7 alk-1
RBS04069-SCM R&-2 MKS04069'.MS-1
MXS04069-MSE)-l MXS04069-MS-2 MXS04069-MSD-2
Grmp 1 Corard O.OmgAqVday
105520#A 105526M (03529F 105-.'49F
Cc*" 3 Mid-Dose 0.15 mg4tday
105505M 105523M 105539F 105352F-
Grew 4 High-Dosc 0. 75 mglklvd-y
105511 m 105522M. 105533i7. 1035CF-
Lmt ofQu-nttation(LOQ): PFOS 15 2 ng/rnL
PFOS - P=t@oc-cunenUomu
Date p=6y
26 WftkC4psuleTomory Study %ith PFOS mc@momolgw Niankeys
T-6295 (PFCS) mm*cy sen M4.4 0 md ETS.9.3,0 Ameba 062M, Smp 020199, &.MadelLne 041098
M-Lym 3@2 See Anschmmts See AtMchnwnts
See Aft-hmmts See Attwtwnmts 04AD&99 RWW 04/07199,Ojjl2f99,04/17/".05/IAM,05117.99HOJ.'DRB:%IEE;Klli 04/0919g.uly".04,70/99,05117/99,0511&'99 HOJ,DRB.'@:]H
Pros
comessuradw
M@
RSD
C-
of PFOS
PFOS
Sid.D-.
mg/=L 000 14,19
egfml w % Rot
<LOQ
<LOQ
mg/mL N-A
MSIMSD RFD NA
000
<LOQ
1274
<LOQ
NA
NA
2N
246
1
102'A 99%
101%
1%
267
lOrA
229
92%
1DO%
16%
32.0
0.0366
215
37.3
0.0498
0,0432
000928
63.1
0.0763
561
23.6
0.0330
00546
00306
553
70.3
13-1
778
95,4
779
107
967
101
2?6
322
67.9
843
233
2116
309
7 49
15
m
294--
220
220
44
29
11
20:
371
1170-
Date Entaed'Br. 04/19/99.05/IG,99LAC
Date Vefifi@d/By@ OL125M SAH,befot.0610&,Oo TKR
wffecUA4mified: 09/12/00mmh. 09/12/00LAC
+ So= 6iitWvolume lessthan0,50mL, wncentritons ihowd be comidered tmubw
0412&/00 LAC
Ex.,l 9-,
3M Environmental
Laboratory
t--030--2nlC
9/1voc
Page 203
3m Medical Department
Study:
T-629aCTTOX-030
Report No. FAC-@ TOX-030
Covance#6329-22l3aboratory Request Numbe@--U2279
stwy: Pmduct Numb@r(Test Substance): Matrix: Method/Rcvision: AnalyticalEquipment System N@bcT InstrumenStoffare(Venion:
Filenarne; R-Squaied Value: Slope: Y-intercept:
Date of F-xtraction/Amlyst: Date of Analysis/Analyst: Date of Data Reduction/Analyst:
16 Week CapsuleToxicit)'Siudwyith PFOS inC%-namolgusMonkeys T-6295 (PFOS) Monkey Sm ETS-9-4.0and ETS-9-5.0 Amelia 062499.S..p 020199,& M.d@tin@ 04109A MassLy-nx 3.2 See Attachn=Ls See Attachments
See Att2ch@ts See Attachments
04.'0&,99RWW 04@07199,04@12.-199.U;17199,05.'14,99.05'17H.O9J9 DRn,.MEF-KIII
tiOJI)RB:K)li
Sample Data
DAY187 MONKEY
SERA
Group
Sampit 0
PFOS
Concentration
Mean
RSD
Dose
Cone-
ofPFOS
PFOS
Std. Dev.
ng/mL
up)ml or-% Rec-
uWmL
NISINISDRPD
Method Bik
RBSO,4069.H20 B Ik.1
0.0()
<LOQ
RBS04069-H20 Blk-2
14.2
<LOQ
NA
NA
Matrix Bik
RBS04069-Scia Bik@1
0.00
<LOQ
P,BS04D69-Scra Blk-2
12.7
ILOQ
',A
NA
QC -250 ppb
MKS04069-MS-1
254
10rI.
MKS04069-MSD-1
246
99%
3%
MKSD4069-MS-2
267
108%
MKS04069.MSD-2
223
92%
100-11.
16-,.
Group I
105520M
13.6
-LOQ
Control
105526M
21.1
0.0300
G@0300-I Anonuiv
NA
0,0mg(kwday
105529F
39.1
0.0373
25.9
105349F,
31.7
0.0541
0.0457
00119
Gmup 3
105305M
699
a2.4
5 91
.'Aid-Dusc
105523M
662
75.8
79,1
467
0.15 mglkg/day
105539F
63.7
10.2
105
105552F
499
68.9
39.5
41.4
Group 4
10551 lm
225
237
15.7
High-Dose
105522M
iss
297
2(17
42,0
0.75 mSAg/day
105533F
289
269
105542F
253
248
5.90
258
15.2
Limitofqu@titaiion(LOQ): PFOS 15.2ng/mL
Date Entered/By: 04;19i99,05/10199.05@20,9L9AC*
DateVcriricd/Bv:08;25.99SAH.Worc06,0900 TKR
Datepuritycomctc&ycrirted: 09;12100@h.09,'1200 LAC
PFOS - Perfluorooctanesulfonate
- Scmin initivaollume lessthan0.50 niL.concenrralinnsshoitlbdc consideredtentitic% 04 28:00 LA(
ETS-8-5 0 E.cci97
3M Env4-ronmental
Laboratory
TOX-03D-sem223-IC
01)13:2f)00
Page 204
3m Medical Department
Study:
T-6291FACITOX-030
Report No. FACT TOX-@130
Covancc#6329-22l3aboratory Request Number-U2279
study
Prod=tNumber(TeSsutbst@):
Matnx
McthodtRevwort
Analyncid Equtpm@
Syst@ N@b@
1-m@t
set...Vm@-
Fdtnamc
R-Squued V.Iuc: Slope
Y-Intacept:
Date of ExtacuaWAn&tyst
Date ofAnalysWAnalyst
Date of l)at.ReductioWAnalyst
26 Week CAPSUIE Tonary Study mth PFOS Ln Cymmolgw
T-6295(PPOS)
Monkey Sen
ErS-9-40 ad E7S.B.50
AmeLm 062498, Soup 020199. & MadeLLne 041099
M.@Ly-
32
SeeAnachmcnts
SeeAttachments
SeeAnachments
See AM&chm=Ls
o4tOL*99 RV/W
04111/99,04(17,W.05/14199 DR"EFIK;H
0411&".0&20/".OY17199
HOI/DRBIKJH
Mcmkeys
Sample Data WEEK 29 MONKEY
Gr-p
Dwe
Method8*
Matnx BLk
QC - 1,50ppb
SERA
3aspie 4
RBS04OMH20
PJLSO4M9-H2O RBS04099-sm
Blk.l
Bik-2 B&-l
RES04099-Se. Blk-2 MKS04089-&iS-1 MKS04U9-.%(SD-1 MKS04099-)AS-2 MXS040W.MSD-2
PFOS
CmVb&L 7.90
701 000 0690
260 267 249 264
C.Netwan"
(PFOS GV=L w % Rw
<LOQ
<LOQ <LOQ @LCQ 105,Y. lOrA 101% 106%
M@
PFOS ug/mL @LOQ
< I,OQ
106%
103%
RSD
SIL D@. MSIMSD RPD
NA
NA
-3%
6%
Gn" 1 Control 0,0 nMyVday
cc*" 3 kfid-Dm O@15 mgtkwday
Gn.q 4 High-[)o.c 0.75 aMAzp)day
Lmi ofqunbtabon (LOQ); PFOS
PFOS - PcrgwroocunesWf@te
105520M
19.4
0.0224
33 5
105526161-
26.4
0,0459
00371
0.0124
io5529F-
26.1
0.04M
11
1055OF-
20.0
00372
00430
0.191
105505M.
481
85@7
1-18
105523M-
511
835
846
151
105539F-
299
99.7
4 16
105552F-
355
936
96 1
3@39
103511 m-
536
105522V.
659
233
g@71
264
249
21 i
(05533F
366
249
7.76
105542F
423
223
236
IR,3_
15 2 naiml
Date Entemd/By
041191". 05/10/99 LAC
Date V-nfiedt By OIV2.V" SA.H, bef.. 0&0&;00 TKR
Date pmty
coffected4ymficd: 09'IVOD mnik 09tl2/00 LAC Scium @tial whune Ins Om 0 50 mL, concentratom
showd be comidefed tentauve OV2R/DO LAC
M-9-5 0 Excel 9'
3M Environmental
Laboratory
tox-030-sm22'-k-IC
9111*0
Page 205
3m Medical Department
Study: T-629fDA4Z@iTOX-030
Report No. FAC-- I-OX-030
Covance#6329-223 laboratory Request Number-U2279
Study
ProduvN=bcrfrnt Subst@)
Mtt=@ .M@thod/R@An.lylacEaql..p.@raSystm Number
tmtr@ Soft@cfVer@ FdcnAme: it-SquucdVW=:
Slope: Y.lntacqA: DateofExt=6orVAnal@st DateofAnalysis/AnL@/tt DateofdataRedwbcWAngyst
26 W"k CapsuleToxoty S" mth PFOS
T-6295(Pros) kionkeySen ETS-9-40 M ETS-9.50 Amelm 062498,Soup 020199.& MadcLintN M@Lym 3 2
S" AMichm=U SeeAtuchmenu SeeAttachm=ts SeeAttachments
0410&" RWW 04/11/99.04117/99.OY141D9R9B/MEEIKJH 04,16t99.04(2&199,05/17H/O9J9IDRAFKJH
inCNMOmOlg@ 1098
?,ionkeys
Sampk Data
WELRK 29 MONKLRY SERA
G-" Do" MettiodBlk Mau= B& QC -250 ppb
0.0mg/Wday Grm* 3 Mid-D@
0,15 g(Wday
FLBS04M-H20 Blk-I RJIS04089-HW M-2 RBS04089-Sen Bik-1 R13SO4019-Sen82-2
MXS04089-m&l MKSG4U9-USD-1 MKS04089.M&2
MKS04089-MSD-2 10552OM105526M
105329F105549F
105505M 105523)A105539F
105552F_
PF C@ nof
"7@I, 0,00 0,680 260 267 249 264 42.2 "7 38,7 681 656 417 613 432
A(PTOS -ChaLw % R-
<LOQ
-LI)Q <LOQ
@LOO
105% 109% 01%
@OeA 0.0690 0.0639 0.073 007487_
77-3 747 T79
619
PFOS uwml
RSI) SitD-. MSF.MSD RPD
@LOQ
NA
LOQ
NA
106','.
3%
103% 00665 00742 ?5 9 1 699
6%
5.45 O@00362 0994 0 OD0664
299 2 18 62
@14
Graw 4
io55lI.M
560
175
300
H4ti-Dou
105522.M
384
770
223
669
0.75m&4*day
105533F
641
207
9:3
105542F
549
Ito
194
10
Lmmiofq@tittwn (LOQ):PFOS - 15.n2giml
DartEnL@d/By 04/19199.OSIIO/9L9AC
DateVeiifiedBly- 09(2Y" SAK befm 0610&00TKR
Dateptmtyc@cte&@fied. 09112= mmk 09/12/DLOAC
PFOS - Pag=oocUr@dmile
+ St= "tW volumelessdm 0 50mL, concmtraf3omshowdbe consideretdentann,O.LrZ&% LAC
M-9-5 0
Excel97
1C
3M Environmental Laboratory
9;1.1.100
Page 206
3m Medical Department
S:::udy:T-6291FAC;iTOX-030
Report No. FAC'-7TrX-030
Covance#6329-223laboratory Request Number-U2279
Study. ProductN=ber(rest Substmcc).
m.tm: %4cthod(R@im: Anaiyt,W Eqwpmenl Sy.tm N=b@.
[mmunent Soft-afefV@m FkmmeR-Squazvd VaJw:
Slope. Y-1.1m.pt Dateor ExnutotvAn&W D.t. of AA&)yWAn@ty.t Date of Data RadmoorVAnskym:
26Week Capswe Tomoty T-6295 (PFOS)
Stidy %vith PFOS inCynmolgmMonkc)rs
Monkey sen
ETS-9-4 0 .d ETS-0-5 0
Ameha 062499.Soup 020199.& Madelme 041098
MmLynx 3 2
Sft Anadurmts See Anath@ts
Set Attechmmu
See Anach@nts
041" RWW
04111/99,041171",05/14,"r)Ra(MEE(KIH
OVI&M,04(20199,05/17/99 HOI/DRIVKIH
Sample Data
WEEK 30 MONKEY
SERA
Grewp D@ Method Rik
Mahu BIk QC -250 ppb
3ankpic 4
RBS04CMirO RBS04089-W@O
8&-1 Blk-2
RLBS04099-Sen EM-1
FLBS04099-Sem Blk-2 MKSO*099-MS-1 MK504099.%(SD-1 MKS04099-MS-2 MKSO4M9-MSD-2
P"
Cmc V*ML 790 7,01
0.00
O.Ug
260 267 249
264
c
of PFOS uwml w % R-
@LC)Q
<LOQ
<LOQ
<LOQ
to5% 109% jai%
106%
Mnn PFOS uW=L
ILOQ
<LOQ
106%
103v.
RSD Std.D-. m3m3D RPO
NA
NA 3%
6%
Gra* 1 Control
0 0 mg@kwday
10552W
20.4
0.0314
105526M
315
0.0312
00313
O@OW165
105529F
325
00299
1.60
iO5WF
291
00306
00303
O@000435
Gr" 3 Mid-Dom 0.15 mglkwday
Gr@p 4 High-Dose 0.75mg/W&y
105503m-
419
105523.M
54
105539F-
425
105552F
340
10551I?A
331
1055221%4 105533F
-
475
616
105547F
4*6"0
68.4 619 69.6 54.5 116 170 156 167
7.D6
652
4.60
1711
620
106
26.5
143
390
486
162
797
LmitofQumtitabon(LOQ) ?FOS-15,2ngimL
Date EntmdfBy Date Verified/By
04419/99,O-Vla(9L9AC OW2Y99 SAM, befon 06/0&100TKR
PFOS - PerfluorooctanesWfomte
Date punryconwed@vm6cd.
09/12=nunk D9/12JO0LAC
Set= ntal vohune lau than0 50 mL. wncentntiom showd be comidaed tentat)vc0.4"2&'00LAC
ETS-8-5 0 Exc 197
3M E@v@-ronmental
Laboratory
lox-O3O-sa223-IC
9112/00
Page 207
3m Medical
Department
Study: T -62 91E@Ci'TOX-030
Report No. FACT TOX-030
Covance#6329-223 laboratory Request Number-U2279
shutr
Pmdmt N=bcr(TcsSiubsb@e)
MatrEc:
M@th.dfR@
AnalytcalEquMmcnt Systan N@b@
lmtrmmt Sofmare/Vmton
26 W.k C&pgW, TO)d@stud@ythPFOSm CynmoiguMsonkeY,
T-6295 (PFOS) Monkey Sm ETS-9-4 0 -d ETS-9-5 0 Amcbx 062498,Soup 020199.& kiadclme04 1098 M@LyrLx 3.2
Fdcnam. R-Squared Value: Slope
Y-Iniacqn: DateofExticboiVAnWyst: Date ofAnky&WAnskyst: Date of Dots ReducWWAntlyst
See AtUchmenU See Anuhmmts
See Attachrnmts See Adhmmts OA/M@" RWW 0,VII,99,04117199.05/14" DRJVMEF,'KJH 04/t6M, "-20t", 05117/99 HOJIDRB(KIH
Sample Data
WEEK
31 MONKEY Group Don
SERA
S.Mpk 0
PFoO@0S3 C@ a mL
cswm 4(P703 w% R-
M@o PF3OS agimi,
RSO
SIL D@. M&MSD RPD
Method BI Me= Blk QC -250 ppb
Group 1 conbdl 0 0 mg*Wday Crvw 3 MW-Dow 0.15mg&Wday Creep 4 Hie-O@ 0 75 mg/Wday
PFOS - PerOuorooctmesLdfixute NA - Not Lppb@ble
ILBS0409%-H2O Blk-1 RBS04099-H20 Blk.2_
RBSOQMSM
Blk-I
3LES04M-Sen Blk-2
MXS040".Ms.t
MKS04M-MSD-1
MKSO4N9-MS-2 MKS040119-MSD-2
105520M
105526M IDJ529F 1055OF-
105505M 105523M 105539F-
105552F103511m
105522M 105533F 105542F@
Date p@ty
7@8"0g
<LOQ
701
ILOQ
NA
'0CF0_0 0690
<LOQ @LOQ
'06@'.
NA
260
105%
267
109-A
106@'.S
3@.
749
101%
2M o@26:4
106%
103%
6%
27.1
0.0362
1 59
36@7
-0 0354___
00359
0 00056?
24.3
0.0292
329
25 5
O.G433
00369
00121
591
60.0
843
398
53.2
566
4-'
sm
111
55 c
291
48.6
A3 9
399
"9
669
@94
161
46 1
591
201
399
170
1.5
Date Entmd/By 04/19199LAC
Date Veri6edtBy OW23M SAH, bcfm 06 0&00 TKR
coffectediwnfied: 09112100 =it, D9111100 LAC
S@ @tml vahlme Im d= 0 50 mL, concntranons should be conudaed
tmtztive OA/2&00 LAC
Fxtmcbon Vokume Rato - ImbiJ Vol@e!Fm&l %'oit@e
ETS-1-5 D
Excel 9,
3M Environmental
Laboratory
tox-0304ce23-IC
9JI2/00
Page 208
3m Medical Department
Study: T-62SAC-TTOX-030
Report No. FAC'-7TOX-030
Covance#6329-22l3aboratory Request NuTnber-U2279
S-dY,
ProductNumbcr(Test Substamce). .Me=*
.M.th.d/R@: A,alytc.E]qu*.nmi Sriem N-b@i
26Week Cap,,AtToxicitfytidy ithPFK)SinCynma*u
T-6295(PFOS)
Moky S@n ETS-8-4I and ETS-9-5.1
Ameba 062498
Monk-@-
Soft@tvv@tt F@ename R-Sq@td V" Slop@: Y-IMBFCOPL DateofExuscoon/Anafrt: DateofAnlysWAn&4@r DateofDataReductiorfAralyst
M=Lym 33 SeeAttachm=t3 See AnachmwtL See Anschinmts See Anactunents ORt25/99RWW Ogr28l991,0/05/W.06ilAM MEE(MMH D9/29/99l.GtD&199.0&15= MEEAA&MMH
Sample Data
WEEK 35 MOINXEY SERA
Gmep Don
Blk
.Me= Blk
QC - 250 ppb
G@p 1 cortrol 0,0ff*icwday
G@p 3 M@d-Dome 0 15 mpi*dmy
S..Pl.0
H20 Blk-1 H20 Blk-2 RabbitSem Blk-I -R@bbd S@ Bik-2 MKSM59,-MS-1 MK505289-.MSD-1 MK309259@MS-2 MK505289.MSD-2 10552OK4 105526M 105529F 105549F 105505M105523M 103539F105552F-
PFOS
Conmntmtion
co.c.
ttpiros
ng'ml
u"L or% Rec
0,00
<LOQ
000
<LOQ
0,DO
<LC)Q
000
<LOQ
227
91%
254
10'2%
256
103%
239
96%
273
0.0437
35 9
0.0490
74.7
0,0148
6100
0.0698
186
930
190
1
76 1
122
812
135-
677
Mean PFOS vg/=L
<LOQ @LCQ
97% 100-Y.
00459 00723
84 5 74 4
RSD Std.D". MSIMSD "D
NA
%A
11%
7% 660 000303 496 000352 14 1 120 i2g 9 53
Cr.up 4 0.75rVkWday
10551 I.M
417
105522.M
496
105533F
409
105542F
444
167
11.8
195
is!
19 5
164
5 94
178
171
101
Lmt ofQ@mbon (LOQ) PFOS 1 33 n6/mL
DateEntemd(By: 10105199,10107/99,D&IgiLDAOC
PFOS - Pcrfl@t@ulf@le
DateVerifieBdy/ betwe 06AM@00 TKR Da:ep=ty cmected@@%@fied 09112/0"0urK 09112/00LAC
Se@ @talwl=o leuth=0 50mL. concentratsohmowdbe @:deredtent@bw04t2&00LAC
NA - Not umtym@ notappbcable
Extmctm Votmc Ratio- IMtiSVlol@c.(FuW Volume
ETS-9-5 Excel9-
3M Env@-ronmental
Laboratory
to..030-.@m223-IC
911zloo
Page 209
3m Medical Department
Study:
T-62-ci;@kC;tTOX-030
Report No. FACT TOX-C3C
Covance#6329-22l3aboratory Request Number-U2279
StudyProductN@ber(T"t Substance)
26 Week CzptWe ToxicityStudy %ith PFOS o C5momokq@ Nionkeys T-6295 (PFIOS)
Mabu.Method(Re@wm Ana"cal Eqmpment System InstrumentSofcwwefVmim, F,Icnamc:
Monkey Scm ETS-9-4 I and ETS-8-5 I
Ame4a 062498 M=Lym 3 3 See AnwJumts
R-Squared Value
Slope Y-intercept. Date of ExtactiorVAnnJvm:
See Auach@b See Anachimnts See An@h@l@
Ogt25/99 RWW
D@t@ f Arky.WA@,.Iyv: Date of Debt ReduchorVAnalyst
09r2&199.lGtO5/990.6(WOO MEEfM?,4if 09f29/99.IGIM99, 06115/00MEE/IAS/Ni.Mil
Sample Data
WEEK 39 MONKEY
SERA
Gmep
3.0pit 0
D"e
?FOS come. ngt=L
Co@ntnij.n of Pros
agt=L.r % Roe
'Mean
PFOS ugiml
RSD Std.D". MSI.MSD RPD
Method BLk M.= BLk
H20 BBi-I H20 Bik-2 kabtntS@ B&- 1 R.bb,tS@ Rik-2
O.DO O.DO 0.DO 0,()0
<LOQ
<.OQ <LOQ <LOQ
Lc@Q
NA
NA
QC - 230 ppb
MKSOB=9-,MS-l
227
MKS05289-.MSD-1
254
91%
102%__
97%
11%
MKSOgngl-.MS-2
256
MKSO5n9.k4SD-2
239
103%
96%
100-1.
7%
G-.p 1 Control 0 0 mg/kWday
Gmap 3 M@d-D-@ 0,15 u*kgiday
10552cm
237
105526M
291
105529F
31 A
105549F-
.157
105505?4-
311
105523N(-
217
105339F-
142
103352F-
174
0.0316 0.0466 0.0503 0.0514 62.4 579 56,8 46.5
00391 00309 60 1 5) 7
271 00106
153 0000779
5.16 3 16 14 1 7 19
G"ap 4 H,gh-Dme 0 75 mpVkg/dy
105511M-
270
10551^.-A-
236
105333F-
338
10554'F-
210
135
110
158
1 16
16 1
169
696
154
1! 1
L=i of Q@titation(LOQ) PFOS - 5 55 ng@ml
Dole Entexed/By. 10/05/99.10/07/990.6;19;00 I,AC DateVerdied/By- b@fomO6/0&100 TKR
PFOS - P@flwrooctinmulf@it NA - N.t analyzd, notapph..bl@
Datepmrycmwediwrified: S@ mtW wl=e In& than0.30mL, concentrmuons3houldbe consid@edtenuaw. 04,129(00LAC
E,xtmcbm Volume Rato - ImbalVol@c,Fin@ @ olt=c
ETS-8-5 I Excel 97
3M Environmental
Laboratory
tox-030-sem223-IC
9/1 :@oo
Page 210
3m Medical Department
Study:
T-62-CACiTOX-030
Report No. FACT TOX-030
Covance#6329-22l3aboratory
Request Nurnber-U227-9
Study ProductNumbWTest Ma=. M@th.&'R.-,-. Analy@caJEqwpm=t
Substance). System \=ber
26 Week Capmde Tomarf Study @th ?FOS m Cynomoig@.Mor@ker T-6295(Pros)
MorikeySm ETS-&A I=d ETS-8-5 I Am." 062498
l@n=-t S.Itwwefvcnlm: Fdename R-Squared Value.
M=Lynx 3 3 See Attachments See Anachments
slop.. Y-tnimept:
See Attachrn=tm S.. Attch@t.
Date of ExtmcboWArA?yst:
OIV25/99 RWW
Date of Anakywo/Analyst Date of Data ReductoWAnityst:
SamplDeatiL WEEK 43MONKEY SERA
Gromp
Due
Sampb. 0
09/2&", ICY05/99.06(14/00MEE/MMH 09/29/99,IW6/99,06/15/00 MEE/IAS/MltH
Pros
Come. L
Con"atraUon orpros
wWmL or % Rtc
mean Pros agiml
RSD Std. Dev. MY.MSD RPD
Method Blk
H20 B&- 1
000
H20 Ba-2
000
@LOQ <LOQ
@LO()
NA
M.= Blk
Rabbit S@m Sk-I
000
RabbitBut Blk-2
D 00
<LOQ
<LO()
<LOQ
NA
QC - 250 ppb
MXSO$259@ms-I
227
MX3052MMSD.l
254
91%
107%
97%
11%
MXS09259@MS-2
256
MK305239-MSD-2
239
103% 96%
i00*/.
7%
Gr*up 1 Conami 0.0 mp-seday
105520M 105526).( 105529F 105549F
21,5 21.3 32.2 22.9
0.0287 00330 0.0369 0.0367
00319 00368
13.8 000440
0251 00000921
G-op 3 M,d- D@ 0,15 m&k*day 1 G@p 4
0 75 mglkg/dy
105505.M
162
fo5523.M
112
105539F
146
10555^@F-
-116
10351 IM
167
105 siz@m
226
105513F
447
10554-,F
347
46.5 44 9 59.3 58.0
66.9 90.7 179 139
45 7 58 1
198
1
159 1
2.44
I'll 0429
0249
21 4
16,9 178
28 4
1
L=t ofQ-ttat@on (LOQ) PFC)s - 5.55nWmL
Date EntadfBy
IQ/05/99, lDiO7/99,0019,'00 I.AC
Date Venfied'By befre 0610&00 TKR
Pros - Perfi@@wromte
Dam ptmty co"ectcd/wrified: D9/12/00mmil@ 09112,'00LAC 4 S@ =tal wi@s leu ti,@ 0,50 mL. concentratonsshouldbe comide@d tentatiw 041@.&tDOLAC
NA
antlyz@ riott;YpUcitble
Fxtract3onVolume Ratio - [niaw Volume!Final Volume
ETS-8-5 I Excel 97
3M Environmental
Laboratory
tox-030-wm223-IC
911zloo
Page 211
3m Medical
DepartTrer-z S::udy: T-62*kC-YTOX-0.30
Report No. FACT TOX-030
Covance#6329-22l3aboratory Request Numbe---U2279
S": ProductN@ber(Test Subs=") Matrix:
26WeekCapsuTl=eMty Stud@yth PFC)mSC',Iomol'".Ionke5@ T-6295(PFOS) Monkey Sm
M@th,,&'R--, AnalybcalEqwp@t
System N@ber
Imu@cni SoftwwcdrV@m: Fdename:
R-squared Vahle:
Slop. Y-Int"ccpt D@i. ofExwcbWArA@yn. Date ofAna@y"AAa)yv:
Dote ofDel& Reduchon/Anslyst
ETS-8-4 I and ETS-8.5 I AM." 062498 M-Lym 3@3 See Anachments See Anwhmente See Anachmmts See Anach@t. O&r23M RWW 0912&W, 10/05/990,6/14/00 MEEFMMH D9[29/99.10/W", 06/15/00 MEEIIASIM@,111
SiLmple Data
WEEK
47 NdONKEY
Group 0-t
Method Bik
MatrixBlk
QC - 250 ppb
SEPA
Sampi* 0
H20 EU- 1 H20 Bk-2 R&bbd Sm Blk-1 Rabbri3ers Blk-2 MKS=59.MSl MK3052MLAISD-1 .MX-U=59-L(S-2 MK305n9.LtSD-2
Pros
Come. ughal 000 0()D 000 000 227 254 236 239
C.0c.atmu.0 of Pros
ughal.r -AR,c
<LOQ
<LOQ <.OQ <LC)Q 91% 102% --163% 945%
%1.2. Pros uWmL
<LOQ
ILOQ
97%
100-@6
RSD Std.D.,. MS/MSD RPD
',A
N
!I%
7%
Group 1
Control 0,0m&iwdy
105520M
25,4
105526M
27.7
io5s29F
36@O
105549F
32.6
0.0339 00370 0.0431 0.0436
00355 00459
623 0.00221
704 000323
Group J MW-D@ 0 15 n*,kwday
105505M
152
105523M
114
105539F
lis
10555'F
114
50,9
7 65
45 7
483
3,69
47 4
15 7
379
426
670
L..t
4 H*-D@ O@-5, n*(Wday
fQ@tut@ (LOQ)
PFCS
10551 I.M 105522k4:00,1,1,F33
-F - 5 55ngml
263
105
212
142
124
312
104
277
92
1 983 1
Data Entaod/By 1WO5199,10107/99.0&19;00 L-AC
Date VerifiedB/y before06109100TKFZ
21 0 759 8 4",
32
PFOS - PerCuorooctn@uLfonate N A - Not awyzed, not apph@ble
Oweptmtyco@tedtwnf"*
OW121DOnutiko9llZ,'0L0AC
S@mbaJ@h@l@thmG5OmLcmcm@tio@shoWdbecomideredicntatiw.
Exractim Volume Ratio LnitaVJol=@'Foal Voh=e
04,r2glOLOAC
ETS-9-5 I Excel9?
3M Environmental
Laboratory
tox-030-mm223-IC
91 t21,00
Page 212
3m Medical Department
Study:
T-629AC-YTOX-030
Report No. FACT TOX-C30
Covance#6329-22l3aboratory Request Numbei--U2279
Study
ProductN@ber(Tat Substance)
Mabu,
M.Lhod(R-.@ Analytcal EquWm=t
System N@ber
imr@t softwwwven@m
F@e@c
R-Sq@ed Value
slope
Y-Intercept:
Date of ExwacbofVAnWyxt:
Date ofAna"WAnslyst
Dole of Dam RoductiorVAjudrt
26 Week CapWe TomcityStudymth PFCS T-6295 (PFOS) Monkey Seri ETS-9-4 I and ETS-9-5 I Ameba 062498 \4usLynx 3 3 See Attachrnmu See AMwhrmnti See An-.hm.nt, See Attachments
09@25/99 RWIW 09,-291", 10/05199,06114)00 MEEFM'AH O9t29199, 10/06,99.0&15100 MEE/lASiMMH
C@norneigus MonkeYs
SampleDsts WEEK 51 MONKEY
Group Dan
SERA
3S.Ple 0
PFOS Conc. nV=L
Concontmtlon OFFFOS
oVmLor%Rec
Mean PFOS G"L
tRSD d. D"@ MS/MSD RFD
K4.d.d Bik
H20 Blk-1 H20 Bik-2
0.00 000
<LCQ @LCQ
@LOQ
NA
Maou BIk
Rabbt Sm Bik-1 Rxbba Sets Blk-2
0.00 0.00
<LOQ
<LOQ
@LOO
NA
QC - 250 ppb
Group 1 Control o@o mwlwday
Group 3 Mtd-Dm. 0 15 m&Agidy Group 4 HISK-D@ 0 75 rWkg/day
MXSM259.m&l MK305289'-MSD-1
MK308259-MS-2 MK305299LMSD-2
105520M 105526M 105529F 105549F 105505M 105523M 105539F 105552F1055 1IM105522M 105533F 105542F
227 254 256 239
13.3 195 343 29.6 119 109 111 52 135 365 261 297
91% 102% 103% 96%
0.0213 o@0261 0.0344 0.0339_
398 360 44.5 758 675 122 97.1 95.7
97% 1001/. 00237 0 03A I 37 9 35 1 94 7 91 4
11%
7% 0 140
00333 1.18 O@000403 6.92 '.62 37 6 13@2 406 38,4 665 607
@w o(Q@
(LOQ): PFCS - 5.33nlyml
Date EntaedfBy: Date V.nfied/ By.
tO/05M, 10107/99.06119,'00LA befom 06109100 TKR
PFOS - Perfluorooctanerdf@le NA - Not araly=d, notapph=ble
Date p=Ty co"ecc&wnhed:
09/12100 mmh. D9/1 Z;00 LAC
Semm irubalwhune lessthin 0 50 mL- cencenrmtiom should be comidered tentabn
Fxtmction Volume Rj6o - liubalVohimelPmal Volume
D4/28100 LAC
F-T@-8.5 I Excel 97
3M Environmental
Laboratory
lox-030-semn3- IC
w 12100
Page 213
3m Medical
I)epartment
Study:
T-629t@kC-TTOX-030
Report No. FACT TOX-030
Cov2nce#6329-22l3aboratory Request Number-U2279
study productNumbetiCTfttSubst@) Ma=: Metho&R@on, Analytcal Equipment Symtcm Number
lmwament So*wwciVcntm
26 Week Capsule To)aoty Study mth T-6295 (PFOS) Morkey Sm ETS-8.4 I -it ETS-8-5 I
PFOS
in L@nomolgw
S..PO20199
M=Lynx
33
-Monkey$
Fder=c
R-Sq@.d Value
Slope:
Y-intemept:
Date of ExuscttoWAna)yst
Date or ArmkyoWArWym@
Date or Data ReductbovAnai@@
SampDiaeta
WEEK53MOriKEYSERA
Group
Sompi. 0
D-
.Method Bik Mabu Blk
QC - 250 ppb Gmep I Control
0.0 ffwwday
H20 131k-5 H20 B[k-5
RAbbit Sera Bik-5
RAbbit Sera Blk-5
I
I
MKSI 1039-MS-6
i
MK311039-kiSD-6
MKSI 1039-MS-5
1
MKSI 1039-MSD-5
i
105520,M
i
105526M
105529F
1055,99F
See Am=@inents See Aftchmenu See Attachments See Artachmmts I IIDY" SAL itioCI99, liiiII99, illl&199 L-@s 11,VL99, llil2/99,llt2V" MMKQAS
PFOS
C.M.
I
ng/mL
0,113,0
2.20 2.50 295 29 4 374 380
33.6 49.9 46.83 52
Comcomtmtlon efpyos
oVaL or % Re.
<LOQ <LCQ
<LOQ <LCQ 00237 00236
2% 11114%
00-0.16.9 00375 00419
M.." PFOS uLVmL
"W
ILOQ
00236
113%
00331 00397
RSD Std. M,. MSI.MSD RPD
N-A
NA 0 192 00000451
21/. 26.1 00086 0782 00311
G@p
3
Mid-D@
0. 15 mg4cg/day
105505M 105523M 105539F 105552F-
2-i 103 91
439
41,1 32 3
46 2 36 7
73 3105 17 0 6 24
G-up 4 H%h-Dow 0,75 mg/kWday
lossi im 1055221,1-
103533F 105542F
137 267 246 244
54.8 ol
98 6 97 9
9R 2
45 5 368 0499 -0490
Limit arq@tnaoon
(LDQ) PFOS - 5 55 nWmL
Date Ente@d/By Date Venfiedi By
I I/]SM. 11174199 LAC before 06/08/00 TKR
PFOS - Pcr(t@w..Wfmatc NA - Nm @ppb"ble
Date puntycor@te&wntied.
09/121OOffuTdi,09/lZ/001,%C
Although labitd n MSIMSD-6. th@ -r@ not *@d =d %U be umd
bl..k. LAC IIIISM
Se@ irutiawll=e Was than 0.50 mL, concertntons ihotjd be consid@ed tenmw@ 04@@.&OO LAC
Cxm=on
Voltane RAtm - lmt)alVolmwYinal %'ol-.c
ETS-8.5 I Exccl97
3M Environmental
Laboratory
lox-030-scm223-IC
Page 214
3m Medical Department
Study:
T-629]EACTTOX-030
Report No. F-z@C--
Covance#6329-22l3aboratory Request NuTioer-U2279
Study ProducNt@ber(TestSubstance) kia=: Method/Re%uion Analytc2ElciiupmeSnyttem N=ber
F'de@e: R-SquaredVejue: slope
26WeekCapoWeTmmty Study@th PFOS. C)@o@.1" li--k-r
T-6295(PFOS) monkeysra ETS-9-4I and ETS-9-51 soupozOI99 M-Ly- 33 Se,Anaclun=ts SeeAnach@nts SeeAmwhmnt3
Y-Inter@pt DateofExtmetaWAxa@fst DateorAnaly@Anatnt: DateofDataReductioWArtalyst.
SeeAftwhm-ts IliG3/9S9AL tliC4t99.11/11I1t9l9t.&19L9AS IItO&'991,1;12199,11/221M9M9H/IAS
SampleData
WEEK 57 MONKEY Cmup Dee*
Method BLk .Ma= Blk
QC -250ppb Gmup 1 Control
O@OnWkWday GroupJ MA-Dose
0 15mo*day
SERA S..Pla.
H20 M-5 H20 BM-5 RabtntS@ EUk-5 Rabbit-%enBLk-5 MKSI lC3g'-.M3-6 M"11039-MSD-6 MKSI IC39@MS-5 MK311039-MSD-5 105520.M 105526M 105529F 105549F 105505M 105523.M 105539F 10555!F
PFOS C"cI.L ngim 0830 1 07 2.20 2.50 29.5 29 A 374 380
36.1 45 4 59.9 52.1 71 1 79 4 8'3a,1
Concawtmtion ofpfos
I upOuLw % Roe <LOQ <LOQ @LOQ <LOO 00237 O@0236 112% 114%
0.0299 0.0364 O.D472 0,0419 29,5 31.9 33.3 31 4
RSD Std.N@. MIS/,MSD RPD
<LDO
NA
I,OQ
NA
0 192
00236 00000453
113%
2%
16
0 0327
0005126
963
00445
000385
7'3836
13
32 3
11 34
G@p 4 High-Dme 0 75 mgtkgiday
10351iM
2'_6"6
1055',ZM-
105333F
2'
105341--
2781
66.5
'08
99 5
-180
!6@
03
3 53
@09
106
3 S4
Lmt of Quantitaton(LOQ): PFOS 5 55n&@.L
DateEntemdri3y 11115/991,lt24/99LAC DateVeri5o&By before06108/00i-KR
PFIOS= PerO"@=c$W(Omte NA - Not pph..bi,
Datepmry comcteda@fied D9/12/0n0uyik09ilZ'(L)AOC *- Althou&lhabeleudMSWSD-6, thc@werenotsplkeadnd@,lLc usedn bt"l LAC 11115199 + Be@ irutvmolh@e lessthm0.50mL,concmtrano@shoulbdeconsiderteedntauw 0,4179/0L0AC
ExtractiVoonlme RAI%O-lnrrjVwol=c@FmalVol=e
ETS-8-5I Excel9-,
3M Environmental
Laboratory
tox-030-wmn3-IC
Page 215
3m Medical Department
Study:
T-629ACYTOX-030
Report No. FACT TOX-030
Covance#6329-22l3aboratory Request Number-U2279
Sh@dyProductNumber(Tftt Substance) Mat@.: Method(R-o. ArWytcal Eqiupment System N=bcr IrubwneritSoftwwcfVemon Fdename: R-Squar.d Val@: Slope, Y-Lntercept Date of ExMzCWWAruLlyst, Date of AnalywA@Ax%alrti Date ofData ReductioWAna"t
26 W"k Capztde Tomaty Study @th PFCS T-6295 (PFOS) ).IonkeySe@ ETS-9-4@ I and ETS-9-3 I souPO20199 @M.sL),nx 3,3 See Attachments See Anctwn-t, See Attachtnmt3 S" Attact.@.nt, 11103/99 SAL ll/04199. 1ltiim, Iitiv" LAS 11/0". 1I/lZ'99,111'22199MMHGAS
m (')no@lg@
Monken
Sample Data
WEEK
61 MONKEY Group D@
Method Blk
Ma= Blk
SERA
QC - 250 ppb
Cmup 1 control 0.0 n%Wkglday
Group 3 Mid-D-. 0 15 ff%i*day
Cr.op 4 H.gh-Dme 0.75 rn&W&y
Lumt ofQusnt=on (LOQ) PFOS
PFOS NA - Not appb@bic
SAMP4. 0
)420 Etlk-5 H20 BM-5 RabbitSm Blk-5 Rabbit S@ Blk.5 MKS[ 1039-MS-d MKSI 1039-MSD-6 MKS] 1039-MS-5 MKSI 1039-MSD-5 105520M. 105526.'A
105529F 105549F io5505M 10557,3M 105539F105552F 05511 M @05522.,i 05533F :0554,F 3 35 NWML
Date p@ry
PFOS Conc. W@L
Conceptraden
i Mtan PFOS
I
R.c
ug/=L
RSD Std.. MS(MSD RPD
0830 107 2.20 2.50 29.5 29 4 374 380
eLOQ <-Oq cLOQ <LOQ 0,0237 0.0236 112% 114%
<LOQ LC)Q
00236 113%
--
NA
NA 0.192 -00000453
2%
39.9 47.7 54.0 57 7
0.0319 0.0382 0.0433 O.D46
00351 00448
12.3 0,00449
4,69 O.DD210
684
27 4
189
995
35,9
31 6
598
94
390
0.742
95 :
38.4
39 2
0.293
162
64.7
50,2
339 1
271
136
1()0
50.3
08
0640
1
273
1
11 09
-1
109
0697
Date Entemd'By: 11/15/99,11124t99 LAC
Date Verified/By: before 0610&100 TKR
coffcctedfvenfied 09/12100 nvnh. 09/12;DO 1,%C
Aid@ugh labetedu MWMSD.6, that wac not ipikedand wiU be used= biwl'u LACII/15199
Se@ mtial @i=c l@ d= 0.50 mL. concen@bms showd be consideredtmtstw G4/28100 LAC
E.xbwoon Vol@e Ratio- ImtW VolumvFinal Voi=c
E7S-8-3 I acal 97
3M Environmental
Laboratory
wx-030-w@223-IC
9/IZIDO
Page 216
3m Medical Department
Study:
T -6 2 9 @A-& TOX-030
Report No. FAC'-" TOX-030
Covance#6329-223 laboratory Request Number-U2279
stay,
ProducNtmber(TtriSubmmcr) %(at=
M,thod(R@ All@l_'ty@.1 Eqp.-t Sy.- -4--,
sftw..V-@
26 Wk C.p.W. T-.ity Stdy -th PFOS . Cy-@il-
T-6295(Pros)
M-ky S..
Mg-4.1 -d M-8-5 I Rby 100699
M-Lr@ 3 3
M@.ky.
S. Anwlm"
S- Aft.W-t.
S- An.,h@t.
Y-tm-.Pt
S" Aftch-b
Ehft :f FAVUU../A.4y@
DetofAulyvWAAWy-t
Date ofd%ts RdacwwAAalyv
Sample Data
04124= SAL'=
04125=,M7W.Un&W.0510M
LA-'@IAXIH:AD%'
04,'27/W,05101=.05101100.DSM4/00 W
WEEK
65 MONKEY
Group
D-
SERA
smpi. 0
Method aLk Mau= ft
0424Q-H2D Blk.3
I
04240-H20 Blk.4
RBSU74()-S- Bik-3
RBS042&&S- Blk-A
PT()S
C-c. VML
0300 0.390 0930 273
C.--Wsti"
(pros sf.Lw % Rec
:LOQ
LOO @LOQ
@LOQ
Pros
.@O.L
LOQ
LOQ
RSD
St&D-. MS/MSD RPO
NA
IIA
mKso4240-sem Bik-3
864
16.9
MKS04140,-Sm Bik-A
110
0.00951
000144
QC -250 ppb
MKS04240-Sm-?AS-3
310
1m
WKS04240-S--LtSD-3
236
MX304240-Sm-MS4
306
JAXS04240-Saa&MSD-4
326
92% 119% 127%
107% 1
27%
123%
6%
Group I C..tml D@O MVWday
I(lis2o)A
12,7
M 526.'A
14@l
*5529F
31.5
W5549F
24,7
D.0194 0.0236 0.0364 OM03 57
00210 D 0360
174 OLOO365
143 -OOM522
G@p 3
?4d-D0.15 mSAWdy
C@.p 4 HiBb-D-
0.75 mgrxwd.y
05505M
05523M
101119F M5 0151.2IM: @al 5 %1 05533F-
1I091,
1
344
393
261
1
360
1 3 -i 6o
254
52 5
597
131
1 915
4654
!9 7
0.0920 OLD269 6.18 2@32
60.3
55 2
11,7
I2
60
92 9
968
LLma o(Q@t3ta@
(LOQ) PFCS
5.35orml
Data pmty
Dt. Eb@.A/By@ DataV-F.& By:
05/01=. 05109/00 I.AC'CSH D&WW TYR 09112:= w..k 09112,'DLDAC
PFUS - Perfluaroactm"Wf@t.
s@ imta vol@
thm 0 50 mL, conc@tntom houJdb* @dnvd tmtab@,
NA - Not ppli-bl@
V.I-. R@ - ltd Vol-.T,,.lVt-@
0417&'00 LNC
M-8-5 Excel 97
3M Environmental
Laboratory
t-.030-.m223-IC
9,1ii0o
Page 217
3m Medical Department
Study: T -6 2 9 @A& TOX-030
Report No. FACT TOX-030
CovmcOfi329-223 laboratory ReciuestNumber-U2279
Study:
Prodmi V=btr(Tm Subewce)
mum M@th.d/R-"alyucalrqw,.m
SyUm
N@b@
lnmwnerd Saft@WN,'@ FJ@:
R.Sqmed VWu# Slope: Y-1@.P. D@ of Exu@rdAradyw D," offA@@ly.WA." t@." D"
Sample Data
WEEK 69 MONKEY
SERA
Cr..p D-
I..Pk x
%imhod Bli M@L- BLk
QC - 250 ppb
Gr.up I C."Lrw 0.0~.y
Gm'p 3 N6d.D@ O@ 15 MWkgld-Y c-p 4 High.rkm. 0 75 g/kgldy
0424G.H2o Blk.3 0420-H20 Blk-4 RB3*4240-Sm Blk.3 JLBSOC34&Sm Blk-4 MSU240-Sm Eft-3 ,WS04240.SmBtk4 W--44240-S-US-3 W304240-S-MSD.3 MK304240.3-US4 mx3N240.3-MSD4
10552DM4 105526M losszw 105549F IOS505M 1055zm 105539F 105552F lossilm 105522M. 105533F lG5-U2F
L,= ofQ.==.n (LOQ):PTOS - 5,55-&-L
PFOS -
DK. pvy
26W..k Cpl@k T..my Stdy uh PFOS . Cy....Ig-
T-6295 (PFOS)
Mo@ky S@m STS." I-d E'rS-&5I R.by 100699
M--Ly.. 3 3
S. Adwhmrrb
Sn AaWhmgMs
Sn AUWhmco
S. AV-h04@24MO SAL4" 04/2YW. 04,77,00Wn=.
OSMVW IA&%M'ADV
k%a@k,y,
pros conc.
aV=L
C@.i-u.. fPros
%ftL . % R"
Pros fIL
0.300 0.3" 0,930 2,75 16
@LOQ @LOQ @LOQ @LOQ 000750
-LOQ <LOQ
11.0
000954
000152
310
172%
ZU
m
107%
306
119%
326
117-A
123%-
22.2
0.0432
26 3
oom
00406
3Z5
O@0421
24,4
0,0379
00400
361
24.6
371
213
264
459
369
406
320
34 S
311
4170
21_
$40
411
73@7
S25
711
?5 0
DK, E.Un&By: OSMVOO,OYOWW LAR-CSII Do. Vmfl.& By- O&M2= TXR
OWI 2= m,@jt DWI ZVC LAC
mgW voh@ Un thm 0 50 mL. cmcmm.@.
RSD Sid.D-. M&IMSD RPD
NA
169 0,001"
2'?*/.
G*A 7.71 000313 752 000301 goo 2,19 100 346 624 52 4 700 525
h@Wd b. c ...i&,,dtcmauw
04,2&00 I.AC
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Euti 97
3M Environmental
Laboratory
lox-030-aa23-IC
9. 1
Page 218
3m Medical
Departmerit
sz:udy: T - 62 9 @A& TOX-030
cov"ce#6329-223
Report No. FAC7 TOX-030 laboratory Request Number-U2279
3tiWy
26 Wftk Cprik Taxic@ Sludywth PFOS m Cy@mc4gm Moarfs
Produa N-umber(TINSubKmcl):
T-4203(PFOS)
Mwm
IA.thodAt@nAAW.,.dcEWqUtp@ Syu @@b@
]@@
monlgy Sm ETS.".: -d ET3-8-5 1 Rutry 100699 M..Lym 3 3
Fd@:
S. Azt.h..u
R-Squamd vwu:
S. ANWA@
Slope: Y.Lm-":
St.Av-h@ S. AM.CH-
D.u :(Ea@.t-VAA-tYDes fAR*MWMmiyg
04124@00SALXRK 04/2M. 04M/00. 04t2g=. C".VOO IAS.%t\ffADV
D- fD"
OAMM. OS.-LO.M.090M QSMLM LAS
S@ple Doin
WEEK 73 MONKEY SERA
Pros
C@estrath
RSD
D.@
C-.
I PTO
.1d.
,f/,L
g,:Lporro%SR
uV@L
MS/MSD RPD
\ikb.d 131k
OG4*-H2o aik-3
0.300
@LOQ
042WH20 9&.4
O@3"
@LOQ
NA
Mmm Blk QC -2M ppb
RB3O-C24O.3mBA-3 RRSOC240.SMBlk-4 W=4244@.S=Blk-3
WLW42WS-Bik4 mxsD424s@s-US-3 .MKM4200-S@MSD-3 MXSU240-3-MS-4 NOCS04V&S@MSD4
0.930 215 86-4 11.0 ])a 236 306 326
@LOQ LC)Q 000750 0 omu IZZ% "% 1is% 17)-A
LOO 000852
-12.3%
MA 169 0 001"
6%
C-up 1
Control 0.0 &4Wdy
M320M.
22.2
0.0431
323
'"326M
17@6
0.0269
o035O
0.oils
)05329F
22@6
0.0386
- 76
ms549F
U.7
0,0345
0.0365
000284
G ..p 3 @,W.D0.15.9&wd"
G-.p 4
*5505M
163
M3523M+
ist
W5539F
160
105532F-
131
*4"jllM
403
74,0
17.1
306
213
4"
279
113
23+7
259
2+91
35 1
so 2
Hi&h-Dm
20@322?A-
374
--733
U4
173
0.75 ,gItWdy
:35533F
326
54 5
191
!055c-r.
=7
240
1.7
131
L.w fQ@
(LOQ)PFOS 5 35
Do. Fjgm&By OSM3MO.OS"= LAC CSII
D.u V.,ido&By Ofi'O2tOTOKR
Dw. p.,Uy
0*12MG m.@k "112100LAC
PFOS - PttlMwrooMW=Wrmgc
- S- in" "h@ k. th.0.5m0L.
h..Idb@ I.-d-d
.4A - @iOtUPPILCtb[C
F@ummm Vol=* Rmmo - INXW Vol=&FmW %'oM=,e
D4,2&100LAC
ETS-8-S.1
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Laboratory
lox.4306mra=3-IC
9-1Z=
Page 219
3m Medical Department
Study:
T-629$Ac7rTOX.030
Report No. FAC--R TOX-030
Co,ance#6329-223 laboratory
Request Number-U2279
sn-tr Prod= 4-bg,(T.*S.b.M@)
ma@-
VALh.&%-, A..ryL@*EqLvm@ Sy- - N-b[@mu.matsft-vv-:,
26W-.Ic,qwk T-way &-4 .9h PFC)-S C),...ig.A-kr 7-6293(PFOS) %4-k.y3ETS44 I d ETS-2-5I Ruby 1006" NU.LY- 3.3
Fdo@,
S..A=Wn@ms
R-Sq.wW VW-:
SetAtLKtunents
St." Y-1@cpt
D@ :fF=.u.WADdyN
S..Aawl..,"
S. Adh@ 04r4l4M SALXJK
Diu fAnat)iWAra": D- fD-RW@An.":
04aS'DO OU77MO. OV7M OVOIW IXS'@M"ADN' 04/77= 'OSiOlM.OVOIIOG.OS06M IAS
Sample Dots
WIEEK 77 MONKEY SERA
creep Dose
pros
C-@ ."L
ofprw W.L - % R@
...
Pro$ C-L
RSD Std.D.,.
%43,?ASD RFD
U.th.dBlk Mom Blk
0300
04240-H2OBik4
0390
RSSM240-SM EU-3
0930
RBSU240,S-BIkA
275
<LOQ
@LOQ
@LOQ
<LOQ
ILOQ
NA
QC -2SO ppb
MK-gU240-SeMB&-l MKS04240-SeMB&4--MKSN24O.B-M3-3 MK304240.3-MSD-3 MKS04240.5@MSA PAKS04240-s@MSD4
8.64 -11-0
310 236 306 326
0.00750 00095 122% 92% 119-A 127%
1 000952
16.9 000144
21 6%
cmup I
CordrW 0 0 mWkVday
toss2om.
12.7
o,033.4
Ito
10552CA-
11.9
000259
002%
0 DOSIS
1055VF
21,9
0.031,
546
lG5S49Y.
Is 2
0.0294
a 030i
000167
C@op 3 Mi&D@ 0 15.&Udxy
Cmup 4 H.gb@D@ 0 75 &&Vdy
10550SN4-
12D
105523M,
101
105539F-
101
10555IF-
70,3
10551im
424
105522M
Sli
105533F
463
lO5S42F-
ZLI
210
2.3,0
1
D 632
17.3
277
125
230
6.37
319
63 8
170
32 3
336
-4'3a45
570
191
L-a .1 O..nWA@ (LOQ)!PFOS PFOS - Pafluwooctan"Wfmmie
5 55 -&'-L
Da. E.Urd)By OYOUN. OYD9= LAC@CSII
Dde V-&df By 06M2MO TXR
DKt pmty comnedN@Agd: OlwI2MO ffvn?L09/1',IDLOAC
+ S@ LNAW vobm im thm 0 50mL, concntm.@,
houldbec.mdcfed lmmve
.4A- Not apphcabk
E@- Vi- R@@ - T-@-VIh-.1f..lN .1-,
04!23M LAC
ETS-4.5 I
M Ex,d 91
3 Environmental
Laboratory
9;1-%
Page 220
3m Medical Department
S--udy: T-629$AC7rTOX-030
ReDort No. FACT TOX-030
Covanc@06329-223 laboratory Reques'@ Number-U2279
sludy
PmductNumba(Testsubowce)
MMU.
M.Lh@d'R-
A@.IYUW Eq-Pm-W Sy@
l@
S.R-.V-
N-b@
u wk cpw. 'foam Uidj @thPFOS
T-6295 (PFOS) 14.m.y SETS-2-4,1 wLd ETS-3-5,I R.Ply 1006" Nt..Ly- 3.3
FU@: R.Squw" Vaiw
31-" Y-in@-Pt D@ :rEnruoWA@.iyK Dal FARWYIWAMIYK: D@ OrDes R-40,b.VA.":
Sampk Data WEEK 79 MONY@EY SEI;LA
a-" D-
S..Pi..
S.. AD-hm.-I So ARKNrAw S44Anl@ S. Abtn@ 04,74= SAII= 0412YW.04fZ7MO.OVMMOVQYW 04/77=. 01101=. OVOIM OS@04M
IASNO."ADV IAS
Pros C... .V L
C.Ma.mu.. f PFDB
t/.L .,% R.,
M... PFOS
RSD Sid.DM&'MSD RPD
L6.LhodIft W..= Elk
0424&H2O Bik-3 04240-H2OBlk4 ItB304240-S.. Blk@3 Rasoduo-s- Eak@ MX3"240.SmM-3 FAK304240.3- Blk4
0300 a 3" 0930 2.75 8.64 110
-LOQ @LOQ <LOQ -LOQ OLOO750 0009S4
<7.(Y@ 000152
NA
NA 169 D 001"
QC - 250 ppb
?4K3042@W3@MS-3
310
-MX30424(@.-S@M=-3
2m
im
m
10-/.
27./.
MXS"24&S@MS-4
304
MXSCM24&3-MSr)4
326
119%
127%
1ZP,4
6%
r-P 1 C.@dfd 0.0 WU4"
W5320M
id 1
0-0194
133
IOM26M
17.9
O.D236
00,115
0002%
05329F
221
o.out
146
105@49F
13.6
0.(1211
0 D243
0,00355
0.15 g&wdy
ivssosm M523M M55'JgF IC3552F
152
ll).7
4.22
III
it's
!9 i
0905
142
221
940
133
19,9
'1 4
2voi
G@p 4
iossii-im
293
22's
63 1
High-D@
105522. 1M-
321
394
41 1
159
0.75mtwd"
105@23-IF
262
2.79
105542-IF
253
:0@
414
1.15
Lmm ofQ%==aam (LOQ) PFOS 5 55 gftL
DS& E@*My
05103M.O"IOD LACCSH
I),"vfflfitB&y. O6m2m TKR
Do,p.,Nyc@.dh-Mf.d
09/12'OO-mkOg/12,DOE.Al'
PFOS NA - Not WpUcabLe
S@ E@-
in@ @t@ lm Om 0.50mL conc.@@.V.1- R&U. - U." V.I-.F.W V-i-
h.Wd b. c.-dmd (mw@
04rlt,00 LAC
acel 9@
3M Environmental
Laboratory
w..030.=.M-IC
Page 221
3m Medical
IDeT)artment Study:
T-6295.7
Report No.
FACT-TOX-030 laboratory Covance# 6329-223
Request
FACT TOX-030 Number-U2279
Study. PniductNumber(Test Substame): Mauu: Mc&iod?Revision: Analyucal Equipment SysLcm Numi@ ]muu@nt Soft.aie/Venwn Date fEx:racti.VAmly.t: Date of Analysis/ArLal)st. O.I.,,fData Reducu,4VAmly,i
Sample Data
26WcckCapsuic ToxicityStudywith PFOS inCymi@-IgusM,,nkc%,
T-6295 (PFOS)
Monkey I-i%-w
f-ticn=c
See Allachrr)cnl@
FACT-M-1.0 & FACT-M-2.0. 2. 1.FT@-8.1 R..@quwcd Value. See Artach=nls
Ameba 062493. Madclim (M ID". r).,@yO
S- Atta@h=ni@
MassLynx @.2 & 3,3
Y-Imm@@pt
.4;mALt2ch@n"
0918,99. O&tl 1199.05123/00 SAH/SRP/St-.*FJ%Al.
05119199,05/22M. 06/09M. ON14/99. 07/29/99.
O@f25/00 KjHiHOJIMEFJiAWIA.3
05/20&9. 05/25/99,O&ID/99. W22199, 09.104199.10/12199.50,'26M KJHFHOI NEFJMMHIIAS
MONKEY LIVER
Group Dwe
Week 27
Sample 0
Method Blk
Method Bik McthM Blk
Mwm Blk
Matrix Blk Matrix Blk Matnx But
QC - 230 pph 05119/99
QC - 250 pph 0& 11/99
RBLDS]89-H20 Blk.3
RBLO5189-H2
RBLD6ll9.H20 BLk- I1
RBL.061 M..-0523G.H20 Blk-5
05230@H20 Blk-6
RBLDS189-LIT
RBLOSI89-L@T RBLD6119-L@-r Blk-II
RBLO6119o
RBLD5230-L@-r BLk-5
RBLO523&L%T MKLDS230-Lvr
Blk-6 Blk-.56
M"5230-Lvr
105508m-ms
105508M.MSD
105517M.MS 105517M.MSD
QC - 250 ppb OSf23/00 GroupI Control
0.0 mg/kglday
Group 2 L@--Dow 0.03 mgkS/day
cxt- 5123/00
MKLDS230-MS.5 MKLO5230-MSD-5 105509M 6)11199 105517M 6/11199
105-148M -..- I1 105517M 51i@"
105519M 105527M
5 9199 51
1 &199
105530F
10553]F
105535F 105544F
1(15514M
IW575M
105516M
lvs2im 105537F
105541F
105547F
105547F 10555OF
Gmup 3 Mid-D,nc 0 15 mglkgtda)
105510M 1055]SM [05524M 105529M 105532F 105539F
105545F
1055"F
C@.p 4 Higl@D.0.75 mS*4/day
105507M 105512M 105.S34F
IQ553,6F
IC554OF
105551F
L@.1 -f Q@utal@
(LOQ): PR-OS - 30 0 ngig
NA - N,x ")zc4 notappl@hi. PPOS - Perflw@=@ulfinate
PFOS Cok- c@.
offo(a 0.00 0.454
0.1)0 NA
concewuudm
W.01=..
<LOQ
<LOQ <LOQ
NA
Mmn PFX)S
<I.OQ
RSD Std.N,. M.VMSD RFD
NA
NA
o@
<LDQ
1.64
<LCQ
<1.(X@
NA
,0.4003 o@oo
<LOQ <LOQ <LOQ
<I,OQ
NA
NA
1.2.@
0.391 15.2
NA
<LOQ
<LOQ <LOQ
<LC)Q
NA
@[.OQ
NA
9,7 492 305 3()0 305
<LOQ 174%
iim 101% 103%
<LDQ
NA
1421,
1021,
332
111%
292
98%-
1()4"
13,@
564
O@564
143
0.143
477
0,477
119
0,119
R
91
O.D91
22.2
129
0.129
0.121
C)0269
128
0.129
112
0.112
87
0.097
169
97
0.097
0.106
00179
19237
182
22709
227
11417 167.14 228 IR
11.4 16.7 22.8
270
17 A
4
24947
248
623 20102 '2'0'735
283 20.1 20.7
9 73
22.1
2.11
42169
42.2
96173
86
59673
59@7
48201
49@2
59.8
195
80421 49590
80.4 49.6
66-532
66.5
214
81376
91.4
69.5
149
4,12474
412
@ 8721
379
280575
291
25(@669
257
267329
267
287223
287
6.01
396
219
S,O()
273
136
Date EaLcraYBy: 05/25199. O6/lOi99. 06122/99. 10@12N9 I.AC Date Verified/By: 0&02tM PJW. OW5/00 TKR
[)arePunry coffwtcdvcrirv.&"/12)00 mmh. 091121001,AC'
Smpic dcu@mdm
ouW= aW wm not u)cludedinany calculaix,m
Sample used forMS/MSD appun tobe spikedaccnuntingfm I,iwmo,%ffies. gaznpic105507 &
,S=pic [Of,507M willbe used forthe MS/MSD and 105518NI c,@c. Verified,
R=S=plt=xu@iodaWngwiLhMS/MSD.
This@alue@@m,iu"- inin@@icutat@,m,
S=p@c dctemirmd an )utliearnd wu not imludcd inw@ calculai%,nsW.@ mcxtractcj
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3M EnV4 ronmental
Laboratory
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9/12100 I." I'm
Page 222
3m Medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
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3m Medical Department Study: T-6295.7
Report No. FAC'-7TOX-030 laboratory Request Number-U2279
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3m Medical Department Study: T-6295.7
3M MedicaDlepartmenSttudyT:-6295.7
ATTACHMENT F EXAMPLE CALCULATIONS
Report No. FACT TOX-030 laboratory Request Number-U2279
ReportNo.FACT TOX-030 LaboratoRreyquestNumber-U2279
Formula Used for Sera Analyses in Study FACT TOX-030
AR (ng/mL) x DF x SC x FV (mL) )< 1.0jig = pg/mL x PC = Reported Cone (Mg/mL) EV(-m L) 1000 ng
Calculation Used for Group 3, Week 1, Animal ID 105505M
287 ng/mL
x 10 x 0.9275 x
I mL ML
x 1.0 gg 1000 ng
5.32 @ig/mL x 0.864 4.60 pg/mL
AR- Analyticalresultfrom MassLynx summary DF- Dilutionfactor SC-PFOS saltcorrectionconstant(0.9275) FV-Final extractvolurne(1.0mL unlessotherwisenoted) EV-Volume of sera extracted PC-PFOS puritycorrectionfactor(86.4%)
Formula Used for LiverAnalyses inStudy FACT TOX-030
AR (ng/g)x a curve(1)x SC x DF x 1.0pg = pgigx PC = [PFOS] sample(Aglg)
-ds-a-mp-Te-
1000 ng
a curve isassumed tobe: I g liver 5 mL H20
Calculation Used for Group 3, Week 27, Animal ID 105510M
524 ng/g x I g/ 5 mL x 0.9275 x 100 x 1.0gg = 48.8 gg/g x 0.864 = 42.2 pg/g
0.9963 g/ 5mL
1000 ng
AR- Analyticalresultfrom MassLynx sununary a cur-ve-Density of the liverstandardcurve,assumed to be Ig Iiver/5 ml water a sample-Density of the liversample (1 g sample/5 mL H,O) SC-PFOS saltcorrectionconstant(0.9275) DF- Dilutionfactor PC-PFOS puritycorrectionfactor(86.4%)
3M EnvironmentalLaboratory 3M Environmental Laboratory
Page F-1 Page 225
3m Medical Department Study: T-6295.7
3M Medical Department Study-T-6295.7
ATTACHMENT
G
INTERIM CERTIFICATE
OF ANALYSES
Report No. FACT TOX-030 laboratory Request Number-U2279
Report No. FACT TOX-030 LaboratoryRequest Number-U2279
3M EnvironmentaLlaboratory 3M Environmental Laboratory
Page G-1 Page 226
3m Medical ]Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Reques@'- Number-U2279
PuriW
INTEPJM CERTIFICATE OF ANALYSIS
Revision1(917100)
Centre AnalyticalLaboratoriesCOA Reference 023-018A
3M Product: PFOS, Lot 217
Reference #: SD-018
Test Name
Purity: 86.9% Specifications
Result 86.9%
Appearance Identification
NMR Metals (ICP/MS)
I. Calcium 2. Magnesium 3. Sodium 4. PotasSiUM2 5. Nickel 6. Iron 7. Manganese Total% Impurity(NMR) Total% Impurity (LC/MS) Total % Impurity (GC/MS) Related Compounds POAA Residual Solvents(TGA) Purityby DSC InorganicAnions (IC) 1. Chloride 2. Fluoride 3. Bromide 4. Nitrate S. Nitrite 6. Phosphate 7. Sulfate4 OrganicAcids' (IC) 1. TFA 2. PFPA 3. HFBA 4. NFPA Elemental Analysis': I . Carbon 2. Hydrogen 3. Nitrogen 4. Sulfur 5. Fluorine
VA-dteCrystallinePowder
I . TheoreticalValue = 17.8% 2. neoretical Value = 0% 3. IleoreticalValue = 0% 4. TheoreticalValue = 5.95% 5. lbeoreticalValue = 60%
Conforms
Positive
1. 0.005 wtjwt-% 2. 0.001 wt./wt.% 3. 1.439 wt./wt.% 4. 6.849 wt./wt.% 5. <0.001 wt./wt.% 6. 0.005 wt./wt.% 7. <0.001 wtjwt.%
1.93 wt./wt.% 8.41 wt./wt.%
None Detected
0.33 wt./wt.% None Detected Not ApplicableT-
I. <0.015 wt./wt.% 2. 0.59 wt./wt.% 3. <0.040 wt./wt.% 4. <0.009 wt./wt.% 5. <0.006 wt./wt.% 6. <0.007 wt./wt.% 7. 8.76 wt./wt.%
1. <0.1 wt./wt.% 2. <0.1 wt./wt.% 3. 0.10 wt./wt.% 4. 0.28 wt./wt.%
1 . 12.48 wt./wt.% 2. 0.244 wt./wt.% 3. 1.74 wt./wt.% 4. 8.84 wt./wt.% 5. 54.1 wt./wt.%
COA023-018A
3M Env4j-ronmental
Laboratory
ExactCopy of Orig;,nal
LAL
In!Llai
Date
Page I of3
Page
227
3m Medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
INTEHM CER TIFICATE OF ANALYSIS
Centre AnalyticalLaboratoriesCOA Reference#: 023-OISA
Date of Last Analysis: 08/3 1/00
Expiration Date: 08131/01
Storage Conditions: Frozen:5-IO'C
Re-assessment Date: 08/31/01
'Purity= 100%.- (sum of metal impurities,1.45% +LC/MS impurities,8.41%+Inorganic Fluoride,0.59%+NNM impurities,1.93%+organic acid impurities,0.38%+POAA, 0.33%)
Total impurity from alltests= 13.09% Purity = 100% - 13.09% = 86.9%
2Potassiwn isexpected in thissaltform and is thereforenot considered an impurity.
3Purityby DSC isgenerallynot applicableto materialsof low purity.No endotherm was observed for thissample.
4S ulfur in the sample appears to be'converted to S04 and hence detectedusing the inorganic anion method conditions.The anion resultagreeswell with the sulfur determination in the elemental analysis,lending confidence to thisinterpretation.Based on the results,the S04 isnof considered an impurity.
'TFA BIBA NFPA PFPA
Trifluoroaceticacid Heptafluorobutyricacid Nonofluoropcntanoic acid Pentafluoropropanoic acid
6'Meoreticalvalue calculationsbased on the empirical formula, C8F17SO3-K+ (MW=538)
This work was conducted under EPA Good Laboratory PracticeStandards (40 CFR 160).
COA023-018A 3M Environmental Laboratory
Pagc 2 of 3 Page 228
3m Medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
INTE)UM CERTIFICATE OF ANAL YSIS
CentreAnalyticalLaboratorieCsOA Reference#: 023-018A
LC/N4S PurityProfile:
Impurity C4 C5 C6 C7
Total
wtjwt.% 1.22 1.33 4.72 1.14 8.41
Note: The C4 and C6 values were calculatedusing the C4 and C6 standard calibration curves,respectively.The C5 valuewas calculatedusing the average response factors from the C4 and C6 standardcurves. Likewise,the C7 value was calculatedusing the average response factorsfrom theC6 and C8 standardcurves.
Prepared By: Reviewed By:
David S. Bell ScientistC,entre AnalyticalLaboratories
Date
John Flaherty
Date
LaboratoryManager, Centre AnalyticalLaboratories
COA023-018A 3M Environmental Laboratory
Page 3 of 3 Page 229
3m Medical Department S--udy: T-6295.7
Report No. FAC-@ TOX-030 laboratory Request NuT,-@Der-U2279
INTE"M CER TIFICATE OF ANAL YSIS
Revision1(917100)
Centre AnalyticalLaboratoriesCOA Reference 3M Product: PFOS, Lot 171
023-018B
Reference #: SD-009
Purity: 86.4%
Test Name
Specifications
Purity'
Result
86.4%
Appearance Identification
NMR Metals (ICP/MS)
I . Calcium 2. Magnesium 3. Sodium 4. Potassium' 5. Nickel 6. Iron 7. Manganese Total% Impurity(NMR) Total % Impurity (LC/MS) Total % Impurity (GCIMS)
Related Compounds -
POAA
Residual Solvents (TGA)
Purity by DSC
Inorganic Anions 1 . Chloride 2. Fluoride 3. Bromide
(IC)
4. Nitrate
5. Nitrite
6. Phosphate 7. Sulfate 4 Organic Acids 5 (IC)
1. TFA
2. PFPA 3. HFBA
4. NFPA
Elemental Analysis':
I . Carbon
2. Hydrogen
3. Nitrogen
4. Sulfur
5. Fluorine
WliiteCrystalliPnoewder
I.
Theoretical Value = 17.8%
2.
Theoretical Value = 0%
3.
Theoretical Value = 0%
4.
Tbeorctical Value = 5.95%
S.
Theoretical Value = 60%
Conforms
Positive
I. 0.017 wt./wt.% 2. 0,007 wt./wt.% 3. 1.355 wtjwt.% 4. 6.552 wt./wt.% 5. 0.003 wt./wt.% 6. 0.004 wt./wt.% 7. <0.001 wt./wt.%
1.00 wt./wt.% 10.60 wt./Wt.%
None Detected
0.30 wtjwt.%
None Detected Not Applicable'
I. <0.015 wt./wt.% 2. 0.27 wt./wt.% 3. <0.040 wt./wt.% 4. <0.009 wt./wt.% 5. <0.006 wt./wt.% 6. <0.007 wt./wt.% 7. 8.82 wt./wt.%
1. <0. I wt./wt.% 2. <0. I wt./wt.% 3. <0. I wt./wt.%
4. <0.25 wt./wt.%
1 . 12.08 wt./wt.% 2. 0.794 wt./wt.% 3. 1.61 wt./wt.% 4. 10.1 wt./wt.% 5. 50.4 wt./wt.%
COA023-018B
3M Env@-ronmental
Laboratory
E)= COPY of Odginal
[AL
1 .1
InE;i-
L)ato
Pagel of3 Page 230
3m Medical Department Study: T-6295.7
Report No. FACT TOX-030 laboratory Request Number-U2279
INTERIMCERTIFICATEOF ANALYSIS
Centre AnalyticalLaboratoriesCOA Reference 023-018B
Date ofLast Analysis:08/31/00
ExpirationDate: 08/31/01
StorageConditions:Frozen:S-10'C
Re-assessmentDate: 08/31/01
'Purity= 100% -(sum ofmetalimpurities1,.39% +LC/MS impurities, 10.60%+InorganicFluoride,0.27%+NMR impurities1,.00%+ POAA, 0.30%)
Totalimpurityfrom alltests= 13.56% Purity= 100% - 13.56% = 86.4%
2Potassiumisexpectedin thissaltform and isthereforenotconsideredan impurity.
3purityby DSC isgenerallynotapplicabletomaterialsoflow purity.No endotherm was observed forthissample.
4Sulfurin thesample appearstobe convettedto S04 and hence detectedusingthe inorganicanionmethod conditions.The anionresultagreeswellwith thesulfur determinationintheelementalanalysisl,endingconfidencetothisinterpreta5onB.ased on theresultst,heS04 isnotconsideredan impurity.
'TFA HFBA NFPA PFPA
Trifluoroacetaicid Heptafluorobutyriaccid Nonofluoropentanoicacid Pentafluoropropanoiaccid
6Theoreticalvaluecalculationbsased on theempiricalformula,CsFl7SO3-K+ (MW=538)
This work was conductedunder EPA Good LaboratoryPracticeStandards(40 CFR 160).
COA023-01813 3M Environmental Laboratory
Page 2 of 3 Page 231
3m Medical Department Study: T-6295.7
Report No. FAC'-7 TOX-030
laboratory Request Number-U2279
INTERIM CER TIFICATE OF ANAL YSIS
CentreAnalyticaLlaboratorieCsOA Reference#: 023-018B
LC/MS PurityProfile:
Impurity C4 C5 C6 C7
Total
wt./wt.% 1.03 1.56 6.38 1.63 10.60
Note: The C4 and C6 valueswere calculatedusingtheC4 and C6 standardcalibration curves,respectivelyT.he C5 valuewas calculateudsingtheaverageresponsefactors from theC4 and C6 standardcurves.Likewise,theC7 valuewas calculatedusingthe averageresponsefactorsfrom the-C6and C8 standardcurves.
PreparedBy:
David S.Bell
Date
ScientistC,cntreAnalyticalLaboratories
Reviewed By:
John Flaherty
Date
LaboratoryManager, CentreAnalyticalLaboratories
COA023-018B 3M Environmental Laboratory
Page 3 of 3 Page 23,2,,
3m Medical Department Study: T-6295.7
3M Medical Department Study-T-6295.7
ATTACHMENT H
REPORT SIGNATURE
PAGE
Report No. FACT TOX-030
laboratory Request Number-U2279
Report No. FACT TOX-030 LaboratoryRequest Number-U2279
;71
AndrewM. Seacat1,5tl-Stt:@ri,dDyirector
Date
John L.BOenhoff,Ph.D.,Sponsor Representative
Date
Dale L.Bacon, LaboratoryManager
Date
3M EnvironmentalLaboratory 3M Environmental Laboratory
Page H-1 Page 233