Document QXVz5NR8yO7XaBYjgKwYkK6z7
ANALYTICAL ILABORAToRy REPORT
ON THE
Determinationofthe Presence and Concentration
of Perfluorooctanesulfonat(ePFOS)
(CAS Number: 2759-39-3)
inthe Serum of Sprague-Dawley@' Rats Exposed to Potassium Perfluorooctanesulfonatveia Gavage
LaboratoryReport No. U2779 Requester ProjectNo. 3M Tox 6295.13
Study Dates Study Initiati1o0n:June 1999 Sample AnalysisInitiati2o2n:June 1999 Sample AnalysisCompletion:28 June 1999 Study Completion:At signing
Perfluoroodariesuffonate CAS Number-2759-39-3
3M EnvirorunentaLlaboratory ReportNo. FACT Tox-loa
LaboratoryRequest Number (U:@N)-U2779
TABLE OF CONTENTS
Study Personneland Contributo.r.s...................................................1 ....................... StatementofCompliance...........................................................2........................ GLP Study.......................................................................3....................... QualityAssuranceStatement........................................................3.......................
Introducbon......................................................................4....................... Purpose...................................................................................4................................... TestSystem .....................................................................4....................... Sample Collectfoannd Ana"is .....................................................5........................
Sample Receipt..................................................................5........................
Materialasnd Methods .............................................................6........................ Chemical Characterizati.o.n.......................................................6........................ Method Summaries ...............................................................7....................... ProtocolDeviatfon.s..............................................................8........................
DataSummary, Analysesa,nd Resub ................................................8........................ Summary of QualityControlAnalyses Results............................................8.......................... Summary of Sample Results...........................................................8..........................
StatistiMceatlhods................................................................9........................ DataQualityObjectvesand DataIntegrf.t.y...........................................9........................
StatementofConclusion............................................................9.......................
References......................................................................1.0.......................
Attachments....................................................................1.0........................
Page i
Peffluomodanesuftnate CAS Number-2759-39-3
STUDY PERSONNEL AND CONTRIBUTORS
AnalyticalChemistry Laboratories: SerumAnalyses AdvancedBioAna"calServiceIsn,c. 15 CatherwoodRoad IthacaN,Y 14850 KristeJn.Hansen,Ph.D.,StudyDirector John R. PerkinsP,h.D.,AssistanStcien6fiDcirector
In-lifeTesting Laboratory Argus Research LaboratoryI,nc. 905 Sheehy Drive,BuildinAg Horsham,PA 19044
Raymond G. York,Ph.D.DABT, StudyDirector
Sponsor 3M ToxicologyServices-MedicalDepartment 3M Center,Buildin2g20-2E-02 St Paul,MN 55144-1000 MarvinT.Case,D.V.M.,Ph.D.,SponsorRepresentative
3M Enviror,,,-ieLnatbaolratory ReportNo. FACT Tox-I08
LaboratoryRequest Number (LRN)-U2779
Page 1 of 10
Perfluomoctanesutfbnate CAS Number-2759-39-3
3M EnvironmentalLaboratory ReportNo.FACT Tox-108
LaboratorFy*uest Number (LRN)-UZR9
STATEMENT OF COMPLIANCE
Study Title:
AnalyticaLlaboratoryReporton the Determinationofthe Presence and Concentrationof Perfluomoctanesulfonat(ePFOS) intheSerum of Sprague-DawleyoRats Exposed to Potassium PerfluomoctanesuffonatveiaGavage
Study ldentificaboNnumber
FACT Tox-I08
This studywas conducted incompliancewithFood and Drug AdministratioGnood LaboratoryPractice(GLP) RegulationsforNonclinicaLlaboratoryStudies[DataRequirement(s):21 CFR ( Part58)],withtheexceptionsin the builetedlisbtelow.Inadditiont,he presentstudyhas been auditedretrospectiveblyyan independentquality assurance unit.Auditproceduresand findingsforauditsperformed atthe3M EnvironmentalLaboratoryand at participaticnogntractlaborato@esare housed withdocumentation perfinentothisstudy inarchivesatthe3M laboratoryand vwllbe retainedfora periodnottoexceed tenyears.The analyticaplorbon completed atthe 3M EnvironmentalLab was performed inaccordancewith3M EnvironmentalTechnology and SafetyServices Standard OperafingProcedures.
ExceptionstoGLP compliance:
Two separatestudydirectorwsere assignedto thein-Ifpfhease and theanalyficaplhase ofthisstudy
The ABS finalreportdoes nothave a Statementof Compliance
The QAU statementintheABS finalreportindicatecsompliancewithEPA 40 CFR Part792, ratherthan FDA 21 CFR Pan 58
Dose confirmatonanalyseswere notconducted accordingtothe GLP regulationsa;nalyticamlethod was not fullyvalidated
Not allraw datawere vefifiebdy thegroup leaderor designee
StudyDirector
ao Date
&.@@
tr4lil-
SponsorRepresentative
Dag
Page 2 of10
Perfluomoctanesutfonate CAS Number-2759-39-3
3M Envimnmentai Laboratory ReportNo. FACT Tox-108
LaboratoryRequest Number (U:ZNYU2779
GLP STUDY QUALiTy AssuRANCE
STATEMENT
Study Tifle:
AnalyticalLaboratoryReport on the Determinationofthe Presence and Concentrationof Perfluorooctanesulfonat(ePFOS) inthe Serum ofSprague-Dawleyo Rats Exposed to Potassium PerfluorooctanesulfonatveiaGavage
Study IdentificaboNnumber
FACT Tox-1 08
This studyhas been inspectedby the 3M EnvironmentalLaboratoryQualityAssurance Unit(QAU) as indicatedin the followingtable.The findingswere reportedtothe study directorand management.
12-30-99
01-06-00 DraftFinalReport
01-11-00
01-07-00
6'QA Representative
Date
Page 3 of 10
Perfluorooctanesulfonate CAS Number-2759-39-3
3M EnvironmentalLaboratory Report No. FACT Tox-108
LaboratoryRequest Number (LRN)-U2779
INTRODUCTION
0
11
C8Fl7-6
-0
-
11 0
Perfluorooctanesuff(oPnFaOtSe)
CAS Number:2759-39-3
Chemical Formula: C8Fl7SO3-
MolecularWeight: 499
Purpose
The purpose ofthe study istodetermine the presence and concentrationofPFOS (C8Fl7SO3-) inratserum samples collecteddudng the study of Fl offspringof FO generationfemale ratsexposed to potassium perfluorooctanesuIfonate viagavage. .
Data qualityobjectivesforthisanalyticasltudy (outlinedinthe 3M EnvironmentalTechnology and SafetyServices protocolforFACT Tox-1 08) were met.
Test System
Inthe present study,two groups offemale ratswere used as the testsystem. Group IconsistedofcontrolFO female ratsthatwere administeredonly Tween 80 (vehicle)G.roup 11FO female ratswere administered1.6 mg of potassium perfluorooctanesulfonatpeer kg ofbody weight/day in0.5% Tween 80 (testarticleT)h.e dose corresponds to a concentrationof0.32 mg/mL. Table 1 outlinesthe FO generationfemale ratpopulation demographics forstudy T-6295.13. Group 11FO female ratswere treatedwiththe testarticl4e2 days pnor to cohabitationa,nd through day 14 (pharmacokineticsubgroup) or day 21 postpartum (lactatioannd delivery). Fl male and female ratpups were not directlaydministeredthe testarticleb,utwere exposed to the chemical through matemai gestabon (inuteraexposure) and duringlac;tabonF.l pups were identifieads being from Group I or 11C.ross fosteringwas randomized; halfofthe pups from each group were cross fosteredwith Group Ior 11 females creatingfourFl animal subgroups (A-D).The identificatiaonnd cross-fostehngprocedure isdocumented inthe in-lifsetudy report(FinalReport 418-014 forstudy T-6295.13 page 11-10)V.adous physicaland biological parameters were monitored intestanimals.
Table 1. FO Generation Rat Population Demographics for Study T-6295.13
InitiaQluantity Acclimated Control(Group 1) Exposed orTreated (Group 11) Pharmacokinetic Sample Subgroup
86 virginfemale rats 42 female rats 36 female rats 10 female rats
78 virginfemale rats 42 mated female rats
36 mated female rats 10 mated females (8 control2, treatedrats)
25 mated femalearartaltss 25 mated female rats
None
Page 4 of 10
Perfluorooctanesulfonate CAS Number-2759-39-3
3M EnvimrrentalLaboratory ReportNo. FACT Tox-108
LaboratoryRequest NLwnber(LRNYU2779
The testsystem species and strainselectedwas theCD:CDOBR VAF/PluO (Sprague-Dawley)ratreceivedfrom Charles RiverLaboratoriesI,na,permanentlyidentifieudsing a MoneP sell@piercienagrtag.FO generationrats were identifiewditheartags.Fl generationratswere identifiaesd partof eitherGroup Ior 11lifterbsu,twere not individualtlaygged,and allparameterswere evaluatedintermsofthe lifte(rdam and littenrumbers are in Attachment E, Table 4).FO virgifnemale ratswere at least60 days of age and weighed approximately200-225 g when received(Weightdataare includedinArgus Research Laboratodes,lnr-f,inarleportforstudyT-6295.13on filaetthe 3M archives)M.ale ratsofthesame source and straiwnere used onlyas breedersand were not administeredthetestarticloer consideredpartofthetestsystem.
Smimple Collection and Anahmis
FO and Fl animals assignedtothecontrolpoolwere culledon day 1 postpartum.On day 14 postpartum,samples were collectedfrom theFO mated female rcftand Fl pups assignedto thephartnacokinefiscubgroup.On day 22 postpartum,samples were collectefdrom theremaininganimals inthetestsystem.Allcollectedsamples were immediatelyfrozenon dryiceand maintainedfrozen(-70*Cor below)untislhippedtothe3M Environmental Laboratodes.
Inthe analyticasltudyreportedhere,sera samples collectedfromthe populationofexposed animals (generation FO) and theiorftpring(generatioFnl) were analyzedforthepresenceof PFOS.
Sera samples were extractedby a liquid-liqeuxitdractiopnrocedureusingan ionpairingagentand ethylacetate. The extractswere quantitativealnyalyzedusingturboionsprayliquicdhromatography/mass spectrometry (LC/MS) inselectedionmonftodng (SIM)mode, and PFOS levelswere evaluatedagainstextractedstandards. Analyticadletailsare includedinthisreportf;urthedretailsare availablienthestudybindermaintainedby the 3M FluodneAnalyticaClhemistryTeam (FACT);thebinderislocatedinthe3M archives.
Analyses assessing thepresence and concentrarfionfPFOS inthe seraofSprague-Dawley ratswere conducted incompliance withGood LaboratoryPracticeRegulations(21CFR 58).Validatedmethods and standardoper-afing procedureswere followedduringthepreparationand analysisofthesamples associatedwiththisstudy.
SAMPLERECEIPT
Samples were receivedfrom Argus Research Laboratodessporadicallyd,uringand atthe end ofthein-lipfhease ofstudy,from November 1998,throughFebruary,1999. Samples receivedwere packaged indryice.Specimens were registeredwiththe3M EnvironmentalLaboratoryand transferretdo a freezerforstorage.
Samples ofbody tissuesand fluidostherthan ratserum were collectedand receivedfrom Argus Research Laboratories(Protocol418-014,Study T-6295.13),butwere notpartofthescope ofanalysisintheprotocol determinedby thestudydirector.
Specimens sentto Advanced BioAnalybcalServices,Inc.(,ABS) foranalysiswere receivedand trackedaccording tothe Sample TrackingSystem StandardOperatingProcedure.Specimens senttoABS willbe returnedto the3M EnvironmentalLaboratoryupon completionofanalysisand submissionofthesubcontractlaboratory(fsi)nal reportS-pecimens willbe maintainedinthe3M EnvironmentalLaboratoryspecimen archives.Sample receipt, identificatisotno,rage,and chainofcustody protocolsand data arelocatedinthestudybinderforthisreport(FACT Tox-108);the binderislocatedinthe3M archives.
Page 5 of10
Perfluorooctanesutfonate CAS Number-2759-39-3
3M Enviioi-.i,,@-L,a,broarlatory Report No. FACT Tox-1 08
LaboratoryRequest Number (LRN)-U2779
MATERIALS AND METHODS
Chemical Characterization
Table2 presentsinformatiornegardingcharacterizatoifotnhetestc,ontrola,nd referencseubstancesused inthe in-Iffpehase ofthisstudy.
Table2.Characterizatioannd Treatmentofthe TestSubstance,Control,and Reference MaterialsinStudy FACT Tox-108
TestSubstance Source Preparation Maximum StorageT-ime StorageConditions Chemical Lot Number PhysicalDescriptioannd IdentitAynalyses Puhty Stability
ControlMaterial Source Preparation Maximum StorageTime
Storage Condidons Chemical Lot Number PhysicalDescdpton and IdentitAynalyses Pudty
Stability
PotassiumPerfluorooctanesulfonate 3M SpecialtCyhemicals Daiiy-Records maintained intheraw data ExpiratioMnay 2000 Room temperature 217 FC-95,Whitepowder
99.28% 48-hrdataofpreparedformulationosn filweiththesponsor DeionizedWater J.T.Baker,PhillipsbuNrJg Suspensionswere prepareddaily Unknown
Room temperature Tweens80--M03HO5, L06662, AND M29477 0.5% Tweenz) 80 inReverse Osmosis DeionizedWater
There are no known contaminants inthe dietthatwould interferweith thisstudy. 48-hrdata of prepared formulationson filewiththe sponsor
Page 6 of 10
Perfluorooctanesuttonate CAS Number-2759-39-3
3M EnvironmentalLaboratory Report No. FACT Tox-1 08
LaboratoryRequest Number (LRN)-U2779
Table 2. Characterizationand Treatment of the Test Substance, Control,and Reference Materialsin Study FACT Tox-108 (continued)
AnalyticalReference Material PFOS (Perfluorooctanesulfonate)
Source
3M SpecialtyChemicals
Preparabon
Analybcalprocedureinthe ABS finalreport(AttachmentF)
Maximum Storage Time
Unused referencematedalwillbe retainedforuse by the 3M EnvironmentalLaboratoryand willbe discardedwhen thequalitoyf preparationo longeraffordsevaluation
Storage Conditons
Room temperature
Chemical Lot Number
171
PhysicalDescdptionand IdentitAynalyses
Light-colorepdowder
Pudty
99.49%
Stability
Undetermined
Dose analyseswere performedon testsubstancesamplestakenatvadous timesduringthe in-lipfhease ofthe study:dataare locatedinthe studybinderforthisreport(FACT Tcx-108) and arepresentedinAttachmentD.
Reserve samples ofcontrolmatedalsfromthe3M EnvironmentalLaboratoryanalyseswillbe storedatthe3M EnvironmentalLaboratoryfora periodnottoexceed 10 yearsfollowintghe effectivdeateofthefinatlestruleo,r untitlhe qualitoyfthepreparationno longeraffordsevaluationa,s willany reservesamples oftestsubstance retumed fromthe in-lipfhease ofthestudy.Reserve samplesofcontromlatedalfromABS willbe storedatthe subcontractlaboratodesinsuch a manner thatthecontromlate@alswillbe preservedforuse inensuingstudies.
Method Summaries
Followingisa bdefdesc@ptionofthemethods used du@ng thisanalyticasltudyby ABS. Detailedeschptionsof thesemethods are presentedinAttachmentC.
ABS Preparatoryand AnalyticaMlethod:Method Validatiofnorthe QuantitationfPerfluorooctanesulfonate (PFOS) inRat Serum by Tuto IonSprayLC/MS.
Analyticasltandardstocksolutions,tandardspikingsolutionsi,ntemalstandardstocksolutionsi,ntemal standardworkingsolutionsc,ontrolblanks,qualitcyontrolstocksolutionsq,ualitcyontrolsamples,and study samples are preparedindilutiownisthappropdatevolumes ofmethanolorpudfiedwaterinpreparatiofnor extractioTne.trabutyalmmonium hydrogensulfat(e1mL of0.5molarsolutioni)sadded toallqualitcyontrol and studysamples,alongwith2mL of0.25molarsodium carbonate/0.25molarsodium bicarbonateW,ater (500pL)isadded tothe controbllank,and 5OOpL oftheintemalstandardworkingsolutioinsadded toallother tubes.FivemL ofethylacetateisthenadded toeach tube,and thetubesare placedon a reciprocaslhakerat medium speed for20 minutes.The tubesarethencentdfugeda,nd theorganiclayeristransferretdoa clean polypropylenteube.The organiclayerisevaporatedtodrynessina TurboVapTm atabout20*C under nftgen. The dded extractasrethenreconstitutweidthacetonitdiaend water,and 200pL oftheextracits transferretdoan autosamplertubeforanalysis.
Page 7 of10
Perfluomoctonesuffbnate CAS Number-2759-39-3
3M EnvimnrrientaLlaboratory ReportNo. FACT Tox-108
LaboratoryRequest Number (LRN)-U2779
Equipment used atASS:
LC/MS/MS System:
Autosampler Waters 717plus Mass spectrometerPE SCIEX API 365 withTurbolonSprayT"interface Analyticaclolumn:KeystoneBetasHT"Cie, 2.lx5Omm (5pm) Mobilephase components:
Component A-1 0:90medmol:2 mM ammonium acetate Component B--W:10 methanol:2mM ammonium acetate Injecbonvolume: 3-5pL Column temperature:Ambient Curtaingas: UHP nitrogen Nebulizergas: UHP nitrogen Ionsprayvoltage:-3000V DedusteOng potential-:35V Negativeionsmonitored: m/z--499.0forPFOS [M-KT m/z=427.0 forteb-a-H-PFOS[M-H]Totalrun time:8.0minutes
Protocol Deviations
There were no deviationfsromtheoriginaplrotocol.
DATA SUMMARY, ANALYSES, AND RESULTS
Summary of Quality Control Analyses Resufts (ABS) The inter-assapyrecisio(nrelatisvteandarddeviatiort-RSDd)atafromdailyqualitcyontroslamples rangedfrom 1.57-4.01%forPFOS, and theinter-assayccuracy(relatievreror-RE)rangedfrom -7.32-10.%1. Bothare acceptableranges.
The inter-assapyrecisio(nRSD) ofstandardsrangedfrom1.11-5.83%forPFOS. The inter-assay accuracy(RE) fromstandardsrangedfrom-5.86-11.0%.Allareacceptableranges.
Coefficientosfdeterminabonwere ->0.9954.
RefertotheABS finarleport(AttachmentF,Tabie2)forprecisioannd accuracydataon theanalysesof qualitcyontroplartalvolume(one-to-tednilubons).
Summary of Sample Results (ASS) FollovAngisinfbrrnabornegardingsampleanalysesinthepresentstudy:
The samples inanalyticarlunnumbers 1 and 3 were reassayedbecause themeasured concentrations exceeded thecalibratiroanngeand upper limiotfquantitabo(nULO) (refetroTable6 inattachmentF). Smallervolumeswere reextractefdromthesamples and reana@zed.Reassayed samples resulteidn measured concentrationwsithinthecalibratiroannge,and thedatawere reported(refetroTable6 in attachmentF).
Odginaldataorcopiesthereofareavailablaetthe3M EnvironmentalLaboratory.
Page 8 of10
Perfluorooctanesutfonate CAS Nuffiber-2759-39-3
3M Envimnmental Laboratory ReportNo. FACT Tox-I08
LaboratoryRequest Number (LRN)-U2779
STATISTICAL METHODS
At ABS,datafrompeakareaswereintegrabtyetdhePE SCIEXprograMmacQuanTIA,versio1.n4, on a
Macintosh computer. Folloviinpgeak area integrationM,acQuan resultsdata were converted totextfilesm,oved to the ABS fileserver,and analyzed withthe Watson7m software package (version5.3.1.01 from PSS, Inc.,Wayne, PA). The Watson analysisapplieda weighted (1/y)quadraticregressiontothe data,and calculationwsere performed on unmunded numbers; however, standard and qualitycontroldata were rounded tothree significant figurespriorto reportingthe data.
DATA QUALITY OBJECTIVES AND DATA INTEGRITY
No circumstances existedduringthe present study thatwould have affectedthequalityor integritoyfthe data.The followingdata qualityobjecfives(DQOS) were followedduringthe study:
Linearity-The coefficienotfdetermination(e)of the standardcurve was equal toor greaterthan 0.98 Limitsof Quantitabon(LOQ)-Equal to the lowestacceptablestandardinthe calibratiocnurve
0 Duplicateacceptable precision- <30% Spike acceptable recoveries- 70% to 130% Use ofconfirmatorymethods-no confirmatorymethods were used Derrkonstrabonof specificity-specificwiatsy demonstrated by chromatographic retentiontime,mass spectral
[N&KI product ioncharacterization
Assuming thatspike recovery studiesform a suitableindicatioonfendogenous analyterecovery,data are quantitativteo:t30%. The validitoyfthisassumption has not been verifiedby othertechniques.Inserum analyses,the limiotfdetection(LOD) forPFOS isapproximately1.75ng/mL and the limiotfquanttabon (LOQ) is 0.05pg/mL PFOS.
STATEMENT OF CONCLUSION
Statement of Conclusion:
Under the conditionsofthe present studies,PFOS was observed inthe sera of FO female ratsexposed during the in4ifephase ofthe study.AdditionallyP,FOS was observed insera tissuestaken from Fl generationpups from female ratsexposed to the testsubstance,and inFl generationpups exposed tothe testsubstance vialactation, but not exposed intgefo.
Page 9 of10
Perfluomoctanesuffonate CAS Number-2759-39-3
REFERENCES
None.
3M EnvironmentaLlaboratory ReportNo.FACT Tox-108
LaboratoryRequestNumber (LRN)-U2779
ATTACHMENTS AttachmentA: Sample Receiptand Chain of Custody Docurrientabon
Attachment8: Protocol Attachment C: Extractioannd AnalyticaMlethods Attachment D: Dose ConfimiationAnalyses Attachment E: Data Summary and Tables Attachment F: AnalyticaRleports from ContribOng Laboratories Attachment G: Report SignaturePage
Page 10 of10
Perfluorooctariesuffbnate CAS Number-2759-39-3
3M EnvironmentalLaboratory Report No. FACT Tox-108
LaboratoryRequest Number (LRN)-U2779
ATTACHMENT A SAMPLE RECEIPT AND CHAIN OF CUSTODY
DOCUMENTATION
Sample receiptand chain ofcustody informationisdocumented inthe binderforthisreport(FACT Tox-108);@'le binderislocatedinthe 3M archives.
Perftwmoctanesulfonate CAS Nuniber-2759-39-3
ATTACHMENT B PROTOCOL
3M EnvironmentalLaboratory ReportNo. FACT Tox-I08
ratdrRyequestNumber (LRN)-U2779
3M Environmental Technol*Lv and Services
PO Box 33331 St.Paul.MN 55133-3331 6127786442
Protocol #FACT-TOX-108
Study Title
Oral (Gavage) Cross-FosteringStudy ofPFOS inRats
PROTOCOL
Author Lisa Clemen
Date: June 8, 1999
Perfortning Laboratory 3M EnvirorunentalTechnology & SafetyServices
3M EnvirorunentaLlaboratory 935 Bush Avenue
St.Paul,MN 55106
Laboratory Project ldentirication FACT-TOX-108 U2779
3M Environmental Laboratory
Page 1 of 10
Protoco#lFACT-TOX-108
StudyIdentification Oral(Gavage)Cross-FosterinSgtudyofPFOS InRats
TestMaterial Sponsor Sponsor Representadve
Study Director
Perfluoroocstualnfeonaiccidpotassiusmalt (T-6295)
3M ToxicologyService-sMedicalDepartment 3M Center,Building220-2E-02 St.Paul,MN 55144-1000
Marvin T.Case,D.V.M., Ph.D. 3M ToxicologyServices Telephone:651-733-5180 Facsimile:651-733-1773
KristenJ.Hansen,Ph.D. 3M EnvironmentalTechnology and SafetyServices Building2-3E-09 651-778-6018
Study Location(s) In vivo Testing Facility
AnalyticalTestingLaboratory
Argus Research LaboratoriesI,nc. 905 Sheehy Drive,BuildingA Horsham, PA 19044
3M EnvironmentalLaboratory Building2-3E-09 935 Bush Avenue St.Paul,MN 55106
3M Environmental Laboratory
Page 2 of 10
Sub-ContracLtaboratory
Proposed Study Timetable Study InitiatioDnate Study Completion Date
Protoco#lFAC T-TOX-108
AdvanceBdioanalytiScearlviceIsn,c. 15 Cathetwood Road IthacaN,Y 14850
BattellMeemorial Institute 505 King Avenue Colwnbus, Ohio 43201-2693
June 08,1999 June 08,2000
1. STUDY
Oral (gavage)cross-fosterisntgudyof potassiumperfluorooctanseulfonicacid(PFOS) inrats.
Z PURPOSE
Thisanalyticasltudyisdesignedtodeterminelevelsof potassiumperfluorooctanesulfonate (PFOS) inspecimensofliverand senun ofrats.The in-lifpeortionofthisstudywas conducted atArgus ResearchLaboratoriess,tudy#418-014.Allserum sampleswillbe extracteadnd analyzedatAdvanced BioanalyticaSlervicesI,nc.and allliversamplesextracteadnd analyzedat BattellMeemorial InstituteA.dditionalanalysesmay be performedatthe3M Environmental Laboratoryas methods aredevelopedand validated.Ifadditionaalnalysesareperformedan amendment tothisprotocolwillbe written.
3. REGULATORY COMPLIANCE This studywillbe conductedinaccordancewiththeUnitedStatesFood and Drug AdministrationG,ood LaboratoryPracticeSstandards,FinalRule 21 CFR 58,withtheexception thatanalysisof thetestmaterialmixtureforconcentrations,olubilithyo,mogeneity,and stability willnotbe conducted,and istheresponsibiliotfytheSponsor.
4. QuAuTyAssuR.4NcE The 3M EnvirorunentaLlaboratoryQualityAssuranceUnitwillreviewtheprotocoland audit studyconduct,data,and finalreporttodeterminecompliancewithGood LaboratoryPractice Standardsand with 3M EnvirorunentaLlaboratoryStandardOperatingProcedures. The QA Unit atthesub-contracltaboratorwyillaudittheirstudyconduct,data,and resultrseport priortosubmittingtothe3M EnvironmentalLaboratory.
3M Environmental Laboratory
Page 3 of 10
Protocci#FACT-TOX-108
5. TESTMATERIAL 5.1 RefertoArgus ResearchLaboratoryprotocolforstudy#418-014.
6. CONTROL MATRICES 6.1 ldentiricationRat liverand serum and/orrabbitliverand senun,traceabilintuymbers willbe recorded in theraw data and included in thefinalreport
6.2 Source Argus Research and/or Sigma Chemical 6.3 Physical Description Rat liverand serum and/orrabbitliverand senan 6.4 Purity and Stability Not applicable 6.5 Storage Conditions Frozen at -20 *C 10 *C or -50 *C 10 *C 6.6 Reserve Matrix A portionof the controlmatrix willbe retainedin the 3M archives
foras long as the qualityof the preparationaffordsevaluation,but not longer than ten years followingthe effectivedateof the finaltestrule(ifapplicable).
6.7 Disposition Matrices willbe retainedat the 3M Environmental Laboratory per GLP regulation.Certainmatrices(feces,urine,and blood) may be disposed afterQAU verification.
6.8 Safety Precautions Refer toMSDS forchemicalsused. Wear appropriate laboratoryattirea,nd follow adequate precautionsforhandling biologicalmaterialsand preparing samples foranalysis.
7. REFERENCE MATERIAL 7.1 ldentirication Potassium perfluorooctanesulfonate(PFOS), lot#s 171, 215, or 217 (equivalentlots)
7.2 Source 3M SpecialtyChemicals 7.3 Physical Description White powder 7.4 Purity and Stability Purityof PFOS is99% or greater.Stabilithyas not been
determined. 7.5 Storage Conditions Room temperature 7.6 Reserve Material A reservesample from each batch of PFOS used in thisstudy will
be retainedas long as thequalityof thepreparationaffordsevaluation,but not longer than ten yearsfollowingtheeffectivedateof the finaltestrule(ifapplicable).
7.7 Disposition Unused referencematerialwillbe retainedforuse by the3M EnvirorunentalLaboratory and willbe discardedwhen the qualityof preparationno longer affordsevaluation.
3M EnvironmentalLaboratory
Page 4 of 10
Protoco#lFACT-7'OX-108
7.8 SafetyPrecautionsRefertoMSDS forchemica'lussedW.earappropriate laboratoryattirea,nd followadequateprecautionfsorhandlingbiologicamlaterialsand preparingsamples foranalysis.
TESTSYSTEM Female mts were used asthetestsystemand were maintainedand dosed as describedinArgus Researchprotocol#418-014. Group I controlanimalsdidnotreceivethetestsubstancewhile thegroup 2 treatedanimalsreceivedthetestsubstanceata concentratioonf 1.6mg/kgtday for6 weeks. RefertoArgus Researchprotocol#418-014 fortabularpresentatioonf data.Dosing of thefemale animalsingroup 2 was continuedduringmating,gestationa,nd lactationC.rossfosterinogf thepups bom tothecontroldams were randomized,halfof thepups were placedon controldams whiletheotherhalfwere placedon thePFOS dosed dams. Likewise,thesame was done with thegroup 2 pups. Each of thesepups willbe marked to identifwyhethertheyarefrom controlor PFOS dosed dams.
9. SPECIMEN AND SAMPLE RECEIPT
The 3M EnvironmentalLaboratorywillreceivehomogeneity samplesand specimensof the followingbody tissuesand fluidsfrom theindicatepdointsinthestudy.Allspecimenswillbe packed on dry iceforshipping.
Body tissue/fluid
Collected
Serum - Dam and Pup animals
Urine and feces- Dam animals
Liver- Dam and Pup animals
Milk SecretingGlands - Dam animals Milk - Dam animals
At lactatiodnay 14 and terminatioonfthestudy Afterterminatioonf thestudy
At lactatiodnay 14 and tenmnationof thestudy At lactatiodnay 14 and terminatioonfthestudy At lactatiodnay 14
Expected # of specimens
60 Dam and 34 Pup 48 Urine and 48 Feces 60 Dain and 34 Pup 58
10
Totalnumber of expectedspecimens:352 Totalnumber of testanimals:36 Totalnumber ofcontrolanimals:42
Specimens sentto3M EnvirorunentaLlaboratoriewsillbe receivedand trackedaccordingto applicableStandardOperatingProcedures.
3M Environmental Laboratory
Page 5oflO
Protoco#lFAC T-TOX-108
10.PREPARATORY METHODS
10.1 FACT-M- I-1,Extractionof PotassiumPerfluorooctanesulfonaotreOtherAnionic FluorochemicalSurfactanftrom LiverforAnalysisUsing HPLC-Electrospray/Mass Spectrometry
10.2 ETS-8-4.1,Extractionof PotassiumPerfluorooctanesulfonaotreOther FluorochemicalCompounds from Serum or OtherFluidforAnalysisUsing BPLCElectrospray/MasSspectrometry
10.3 Ifpreparatorymethods otherthanthoselistedabove areused,an amendment to this protocolwillbe written.Any deviationfsrom thesemethods willbe documented and includedwith thestudydata.
10.4 Ifanalysesaresub-contractetdootherlaboratorieasn,amendment willbe writtento includetheirmethods and copiesof eachmethod willbe attachedtothisprotocol.
II.ANALY77CAL METHODS
11.1 FACT-M-2. 1,AnalysisofFluorochemicalisnLiverExtractsUsing HPLCElectrospray/MasSspectrometry
11.2 ETS-8-5.1,AnalysisofPotassiumPerfluorooctanesulfonaotreOtherFluorochemicals inSerum or OtherFluidExtractsUsing HPLC-Electrospray/MassSpectrometry
11.3 Ifanalyticamlethods otherthanthoselisteadbove areused,an amendment tothis protocolwillbe written.Any deviationfsrom thesemethods willbe documented and includedwith thestudydata.
11.4 Ifanalysesaresub-contractetdootherlaboratorieasn,amendment willbe writtento includetheirmethods and copiesof eachmethod willbe attachedtothisprotocol.
12.DATA QUALITY OBJEC77VES
The number of spikes/duplicatuesse,of surrogatesa,nd informationon otherdataquality indicatorasreincludedintheanalyticamlethods. In additiont,hefollowingcriteriwaillbe met:
12.1 Linearity r'@:0.98
12.2 Limits of detection / quantitatfon
12.2.1 Method DetectionLimit(MDL) forPFOS
a) Serum: 1.75ppb
12.Z2
b) Liver:15ppb
LimitofQuantitatio(nLOQ) - Equaltothelowestacceptablsetandardin thecalibratiocnurve
3M Environmental Laboratory
Page 6 of 10
Protoco#lFAC7-TOX-108
IZ3 Duplicateacceptablperecision< 30% forthemethod
IZ4 Spikeacceptablerecoveries70% -130%
lZ5 Use ofconrirmatormyethods Indeterminsaatmeplewsilblere-analyzuesdinga confirmatorymethod. Ifa confirmatorymethod isused,an amendment to this protocolwillbe wiitten.
12.6 Demonstration of speciricityChromatographicretentiotnime,mass spectral daughterioncharacterization.
13. SuB-CoNTRAcTED
ANALYSIS
13.1 Allanalysesasdetailedin thisprotocolwillbe performedat3M Environmental LaboratoriesB,uilding2-3E-09,935 Bush Avenue, St.Paul,h4N 55106,atAdvanced BioanalyticaSlervicesI,nc.,15 Catherwood Road, Ithaca,NY 14850,or atBattelle Memorial Institut5e0,5 King Avenue, Columbus, Ohio 43201-2693.
13.2 An amendment tothisprotocolwillbe writtenifanalysesareperformedat laboratorieostherthan3M EnvirorunentaLlaboratoriesA,dvanced Bioanalytical Services,Inc.,orBattellMeemorial Institute.
14. STATIS77CAL ANALYSIS
Averages and standarddeviationwsillbe calculatedT.he statisticmaelthods thatwillbe used are describedbelow:
14.1 Data transformations and analysis Data willbe reportedas theconcentration (weight/weighotrweight/volo)fPFOS ormetabolitpeertissueorfluid.
14.2 Statisticalanalysis Statistiucssedmay includeregressioannalysisof concentrationosvertime,and standarddeviationcsalculatefdortheconcentrations withineach dosegroup. Ifnecessary,simplestatistictaelstss,uchas Student'st test, may be appliedtoevaluatestatisticdailfference.
15.REPORT A reportcontainingalltheresultosf thestudywillbe preparedby the3M Environmental Laboratory.Ifanalysesare sub-contractetdootherlaboratorieesa,ch laboratorywillpreparea reportand submitittothe3M EnvironmentalLaboratoryforinclusioinnthe3M Environmental Laboratoryreport.Each reportwillincludeb,utnotbe limitedto,thefollowingw,hen applicable:
15.1 Name and addressofthefacilitpyerformingthestudy
15.2 Datesupon which thestudywas initiateadnd completed
15.3 A statementofcomplianceby theStudy Directoraddressinagny exceptiontsoGood LaboratoryPracticeStandards
3.M Environmental Laboratory
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Protoco#lFACT-TOX-108
15.4 Objectivaensdproceduraessstateidntheapprovepdrotocoiln,cludianngychanges intheoriginaplrotocol
15.5 The testsubstanceidentificatiboynname, chemicalabstractnsumber orcode number, strengthp,uritya,nd compositionor otherappropriatceharacteristiicfsp,rovidedby theSponsor
15.6 Stabilitaynd thesolubilitoyfthetestsubstancesunder theconditionsof administratioinf,providedby theSponsor
15.7 A descriptioonfthemethods used toconductthetest(s)
15.8 A descriptioonf thetestsystem
15.9 A descriptioonf any circumstancesthatmay have affectedthequalityor theintegrity of thedata
15.10 The name oftheStudy Directorand thenames of otherscientistpsr,ofessionalsa,nd supervisorypersonnelinvolvedinthestudy
15.11 A descriptioonf thetransformationsc,alculationosr,operationsperformedon the data,a summary and analysisof theanalyticaclhemistrydata,and a statementof the conclusionsdrawn from theanalyses
15.12 Statisticmaelthods used toevaluatethedata,ifapplicable
15.13 The signedand datedreportsof eachof theindividuaslcientisotrs otherprofessionals involvedinthestudy,ifapplicable
15.14 The locationwhere raw dataand thefinalreportaretobe stored
15.15 A statementpreparedby theQualityAssuranceUnitlistintghedatesthatstudy inspectionsand auditswere made, and thedatesof any findingsreportedtotheStudy Directorand Management
Ifitisnecessarytomake correctionosr additiontso a reportafterithas been accepted,the changeswillbe made in theform of an amendment issuedby theStudy DirectorT.he amendment willclearlyidentiftyhepartof thereportthatisbeingamended, thereasonsforthe amendment, and willbe signedby theStudy Director.
16.LocATioN oFRAwDATA,
RECORDS, AND FINAL REPORT
Originaldata,or copiesthereofw,illbe availablaetthe3M EnvirorunentaLlaboratoryto facilitaatueditsof thestudyduringitsprogressand beforeacceptanceofthefinalreport.When the finalreportiscompleted,alloriginaplaper data,includingthoseitemslistebdelow,willbe retainedinthearchivesof 3M EnvironmentalLaboratoryforatleasta periodof timeas specified by regulationa,nd as establishebdy 3M EnvironmentalLaboratoryStandardOperating Procedures.
3M Environmental Laboratory
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Protoco#lFACT-TOX-108
16.1 Thefollowirnagwdataandrecordwsilbleretainiendthestudyfoldeirnthe study/projecatrchivesaccordingto 3M EnvironmentalLaboratoryStandardOperating Procedures: 16.1.1 Approved protocoland amendments 16.1.2 Study correspondence 16.1.3 Shippingrecords 16.1.4 Raw data 16.1.5 Approved finalreport(originaslignedcopy) 16.1.6 Electroniccopiesof data '
16.2 The followingsupportingrecordswillbe retainedseparatelfyrom thestudyfolderin thearchivesaccordingto3M EnvironmentalLaboratoryStandardOperating Procedures: 16.2.1 Trainingrecords 16.Z2 Calibratiornecords 16.Z3 Instr=ent maintenance logs 16.Z4 StandardOperatingProcedures,Equipment Procedures,and Methods
17.SpEcimEN RETEN77ON Specimens willbe maintainedinthe3M EnvironmentalLaboratoryspecimenarchivesfora periodof time as specifiebdy regulatioonras longas thequalityof thepreparatioanffords evaluationb,ut notlongerthantenyearsfollowingtheeffectivdeateofthefinatlestrule(if applicable)a,nd as establishebdy 3M EnvironmentalLaboratoryStandardOperatingProcedures.
18.PROTocoL AMENDMENTS AND DEVIA77ONS Planned changesto theprotocolwillbe intheform ofwrittenamendments signedby theStudy Directorand theSponsor'sRepresentativeA.mendments willbe consideredaspartof the protocoland willbe attachedto thefinalprotocolA.llchangestotheprotocolwillbe indicated inthefinalreportA.ny otherchangeswillbe intheform of writtendeviationss,ignedby the Study Directorand filedwiththeraw data.
3M Environmental Laboratory
Page 9oflO
lg.ArrAcHmENTs
19.1AffachmentA Preparatoarnydanalytimceatlhods
20.SiGNATuREs
Protoco#lFAC T-TOX-108
MarvinT.Case,D.V.M.P,h.D.S,ponsoRrepresentative
Date
i@-ristenH'aJn.sen,Ph.D.,3M EnvironmentalLaboratoryStudyDirector Date
3M EnvironmentaLlaboratory
Page 10 of10
StudyTide Oral(GavageC)ross-FosterSitnugdyofPFOS inRats
PROTOCOL AMENDMENT NO. I
Amendment Date: August 12,1999
Performing Laboratory 3M EnviromnentaTlechnology& SafetyServices
3M EnviromnenW Laboratory 935 Bush Avenue St.Paul,MN 55106
Laboratory Project ldentfrication ET&SS FACT-TOX108 LIRN U2779
3M EnvironmentaLlaboratoty
ProtocoFlACT-TOX108 AmendmentNo.I
Thisamendment modifiesthefollowinpgortio'n(osf)theprotocol:
1. PROTOCOL READS: Section2.0statetshatallliversampleswillbe extracteadnd analyzedat BattelleMemorial Institute.
AMEND TO READ: All liversamples willbe extractedand analyzed atthe3M Environmental Laboratory.
REASON.- Due to time constraintst,heliverextractionand analysiswillbe performed atthe 3M Environmental Laboratory.
2. PROTOCOL READS: Section 10.0 and 11.0 listthefollowingmethods to use forextraction and analysis:
FACT-M- 1.1 "Extracfionof Potassium Perfluorooctanesulfonatoer Other Anionic Fluorochemical Surfactantfrom Liver forAnalysisUsing BPLC-Electrospmy/Mass Spectrometry" FACT-M-2.1 "Analysis of Fluorochemicals in Liver ExtractsUsing HPLC-Electrospray/Mass Spectrometry" AMEND TO READ: The extractionand analyticalmethods to followatthe3M Environmental Laboratory are: ETS-8-6.0 "Extracfionof Potassium Perfluorooctanesulfonatoer Other Fluorochemical Compounds from Liver forAnalysis Using BPLC-Electrospray/Mass Spectrometry" ETS-8-7.0 "Analysis of Potassium Perfluorooctanesulfonatoer Other Fluorochemical Compounds in Liver ExtractsUsing BPLC-Electrospray/Mass Spectrometry"
REASON: The extractionand analyticalmethods FACT-M- 1.1 and FACT-M-2. 1.,respectively, were updated on 07/22/99 to ETS-8-6.0 and ETS-8-7.0. These methods were updated to replace the extractionsolventethylacetatewith a differentextracfionsolventMTBE (methyl tertbutyl ether),POAA and Monoester were removed from the standardmix, and M556 was added to the standardmix. The analyticalmethod was updated to includelinearregressionwith 1/xweighting and a few minor changes in theEPLC 1100 instrumentparameters.
3M EnvironmentalLaboratory
ProtocoFlACT-TOX108 AmendmentNo.I
3. PROTOCOLREADS:Sectio1n0.4and11.4stattehaitfanalysaersesub-contratcotoetdher laboratorieasn amendment willbe writtentoincludetheirmethods.
AMEND TO READ: The extractioannd analyticamlethods to followatAdvanced Bioanalytical Serviceswillbe attachedto theprotocol. REASON: The analyticamlethods atthesub-contracltaboratorwyere notincludedintheoriginal protocol.
4. PROTOCOL READS: Section12.2.1b) listtshelivermethod detectiolnimitas 15 ppb.
AMEND TO READ: The livermethod detectiolnimitis8.50ppb (ng/g).
REASON: The validatiosnupportingmethods ETS-8-6.0and ETS-8-7.0includesa lowermethod detectionlimitforPFOS.
Amendment Approval
ar@vm Case,D.V.M., Ph.D.,SponsorRepresentative
Date
L
KrisJ.Hansen, Ph.D.,S'tudy Director
Date
3M EnvironmentaLlaboratory
StudyTide Oral(GavageC)ross-FosteSrtiundgoyfPFOSinRats
PROTOCOL AMENDMENT NO. 2
Amendment Date: September30,1999
Pertbrming Laboratory 3M EnvirorunentTaelchnology& SafetyServices
3M EnvironmentalLaboratory 935 Bush Avenue
St.Paul,MN 55106
Laboratory Project ldendflcadon ET&SS FACT-TOX108 LIRN U2779
3M EnvironmentLaalboratory
ProtocolFACT-TOX108 AmendmentNo.2
Thisamendmentmodifietshefollowinpgortion(osf)theprotocol:
1. PROTOCOL READS.' Section2.0statesthatallliversampleswillbe extracteadnd analyzedatthe3M Environmental Laboratory.
AMEND TO READ: No liversamples willbe extractedand analyzed.
REASON: Liver resultsareno longerrequired.
2. PROTOCOL READS: Section 16 statesthat the originaldata, or copies thereof,will be availableat the 3M Environmental Laboratory to facilitataeuditsof the study during itsprogressand before acceptance of the finalreport.When the finalreportiscompleted, alloriginalpaper data, including:approved protocol and amendments, study correspondence,shipping records,raw data,approved finalreport,electroniccopiesof data,trainingrecords,calibratiornecords, instrument maintenance logs and standard operatingprocedures,equipment procedures,and methods willbe retainedin the archivesof the 3M Environmental Laboratory.
AMEND TO READ: Section 16 statesthatthe originaldata,or copiesthereof,willbe availableat the3M Environmental Laboratory to facilitataeuditsof the study during itsprogressand before acceptance of the finalreport.When the finalreportiscompleted, alloriginalpaper data, including:approved protocoland amendments, study correspondence,shipping records,raw data,approved finalreport,and electroniccopiesof datawillbe retainedin the archivesof the 3M Environmental Laboratory. All correspondingtrainingrecords,calibratiornecords, instrument maintenance logs,standard operatingprocedures,equipment proc6dures,and methods willbe retainedin the archivesof the facilitpyerforming each analysis.
REASON. Clarificatioonf the dispositionof archived recordsifanalysesareperformed ata sub-contract laboratory.
3M EnvironmentalLaboratory
ProtocoFlACT-TOX108 Amendment No.2
3. PROTOCOL READS.' Sectio1n7statetshastpecimenwsilblemaintainiendthe3M EnvironmentLalboratory specimen archives.
AMEND TO READ: Specimens willbe maintainedinthe3M EnviroranentaLlaboratoryspecimen archives.All specimens sentto sub-contracltaboratoriewsillbe returnedtothe3M Environmental Laboratoryupon completionof analysisand submissionof thesub-contract'labomtory(s) finalreport.The specimenswillbe returnedwiththefollowingdocumentation:thesigned originaclhain of custodyand recordsof storageconditionswhileatthesub-contracftacility.
REASON:
Clarificationf thedispositioonf specimensand documentationforanalysesperformedby a sub-contracltaboratory.
Amendment Approval
Marvin Case,D.V.M., Ph.D.,Sponsor Representative
Date'
KristenJ.Hansen, Ph.D.,StudyDirector
/0 Date
3M Environmental Laboratoty
Pedkwooctariesuffonate CAS Nuniber-2759-39-3
ATTACHMENT C EXTRACTION AND ANALYTICAL METHODS
3M EnvironmentalLaboratory Report No. FACT Tox-108
LaboratoryRequest Number (LRN)@U2779
Proprietaraynd Confidental
AOVANCEO m SIOANALYTICAL
SERVICES, INC.
r
METHOD VALIDATION REPORT
TITLE:
METHOD VALIDATION FOR QUANTITATION OF
PERFLUOROOCTANESULFONATE RAT SERUM BY TURBO ION
THE
SPRAY
(PFOS) IN LC/MS
DATE:
26 August 1999
REPORT:
99VDJA01.Ml.DOC
AUTHORS:
PREPARED FOR:
NUMBER OF PAGES:
David J.Anderson, M.S.
Amie J.Prince,B.S.
Holly D. Ross, M.S.
3M Environmental Technology and Safety Services
St.Paul,MN 55133-3331
50
15 Catherwood Road s Ithaca,New York 14850 s (607) 266-0665 a Fax (607)266-0749
AUTHORS:
FOR: DATE: TITLE:
DavidJ.Anderson,M.S. Amie J.Prince,B.S. HollyD. Ross,M.S.
3M EnvironmentalTechnologyand SafetyServices
26 August1999
METHOD VALIDATION FOR THE QUANTITATION
OF,PERFLUOROOCTANESULFONATE
(PFOS) IN
RAT SERUM BY TURBO ION SPRAY LC/MS
ABSTRACT
A sensitivsep,ecifiacc,curataen,dreproducibalnealyticmaelthodwas developebdy Advanced BioAnalyticalServices,Inc.,Ithaca,New York toquantitate perfluorooctanesulfona(tPeFOS) inratserum samples. Serum samples (50 pL) were extractedby a liquid-liquiedxtractionprocedureto isolatetheanalytefrom rat serum. Sample extractswere reduced todryness,reconstituteda,nd analyzed by turbo ionsprayliquidchromatography/mass spectrometry(LC/MS) inthenegativeion mode. The assaydemonstrateda lower limitof quantitatio(nLLQ) of 0.05 jig/mL. using50-jiLsample aliquots.The calibratiocnurveswere fitfrom 0.05 gg/mL to 20 gg/mL forPFOS by a weighted (I/Y')quadraticequation.The coefficientosf determinationofthe calibratiocnurves ranged from 0.9962 to0.9965.
Precision*andaccuracyqualitycontrol(QC) samples were preparedatconcentrations of 0.2,6,and 18 jig/mL PFOS. Qualitycontrol(QC) samples were preparedata concentratioonf 100 gg/mL PFOS forpartiavlolume analysis.The intra-and interassayprecision(RSD) resultscalculatedfrom allQC samples ranged from 1.92% to 4.87% forPFOS. The intraa-nd inter-assaayccuracies(RE) calculatedfrom QC samples ranged from -3.58% to 5.58% forPFOS. The mean extractionrecoveries were from 87.6% to 100% forPFOS and 89.9% forthe internasltandard(IS).
PFOS was measured as stableinratserum forup to24 hours atambient temperature. PFOS was measured asstableinratserum at-20 *C, currentlyforup to 33 days,and
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afterthreefreeze/thawcycles.Reliableresultwsere obtainedforsample extracts reinjecte2d7 hoursafterinitiarleconstitution.
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QAUSTATEMENT
PeriodincspectionftshemethodvalidatifoonrthequantitatoifoPnFOS inrat serum were conductedby theQualityAssuranceUnitof Advanced BioAnalytical Services(ABS) forcompliancewithEPA GLP regulation(s40CFR Part792).
The studywas inspectedon thefollowingdates: 13,21 May 1999; 7,8, 14,15 June 1999; 1,2 July 1999;3,4 August 1999.
Resultsof theinspectionwsere reportedto ABS Management on: 13,21 May 1999;7, 8,14,15 June 1999; 1,2 July 1999;3,4 August 1999.
Resultsof theinspectionwsere reportedto theStudy Directoron 5 August 1999.
Based on theinspectionsand thedatareviewed,thisreportisa complete and accuraterepresentatioonf thedata.
KhthleenCorm'ack,B.S. QualityAuditor
Lie? Date
MMM
AOVANCEO SIOANALYTICAL SERVICES, INC.
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99VDJAOI.Mi.DOC
TITLE:
ReportNumber: Reportedby:
SIGNATURE PAGE
METHOD VALIDATION FOR THE QUANTITATION OF
PERFLUOROOCTANESULFONATE
(PFOS) IN RAT
SERUM BY TURBO ION SPRAY LC/MS
99VD 0 Ml.DO
David J.AndeVon, M.S. Research Scientist
Z@, kh Lf.57- q
Date
Reviewed by:
4-4 KkthleenCor-mack,B.S.
AssociateAuditor
ALtn qg Date -J
Authorizedfor C4,
Releaseby:
John R.!PerkinsP,h.D.
Date
AssistanStcientifiDcirector
AOVANCED BIOANALYTICAL
SERVICES. INC.
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TABLE OF CONTENTS
ABSTRACT ...............................................................2................... QAU STATEMENT .........................................................4................... SIGNATURE PAGE ........................................................5.................... TABLE OF CONTENTS .....................................................6................... LIST OF TABLES ..........................................................8................... LIST OF FIGURES .........................................................9................... 1. INTRODUCTION ......................................................1.0....................
2. EXPERIMENTAL .....................................................1.0...................
2.I.CHEMICALS AND MATERIALS ..........................................1.0.................... 2.2.LC/MS INSTRUMENTATION ............................................1.0................... 2.3.SAMPLE PREPARATION AND EXTRACTION PROCEDURE .....................11................. 2.4.RAT SERUM VALIDATION DATA ........................................i.I.................... 2.5.ASSAY EVALUATION .................................................1.2...................
2.5.1.Intra-and Inter-AssayAccuracy ....................................1.2.................... 2.5.2.Intra-and Inter-AssayPrecision....................................1.2.................... 2.5.3.PartiaVlolume Analysis...........................................12.................... 2.5.4.Lower LimitofQuantitatio(nLLQ) .................................1.3.................... 2.5.5.Selectivit.y.....................................................1.3.................... 2.5.6.CarryoverEvaluation.............................................1.3.................... 2.6.STABILITY OF PFOS IN QUALITY CONTROL SAMPLES ......................13.................. 2.6.1.Ambient-TemperatureStabilitoyf PFOS inRat Serum ..................13.............. 2.6.2.FreezerStabilitoyf PFOS inRat Serum at-20 *C .....................1.4.................. 2.6.3.Freeze/ThawStabilitiyn Rat Serum .................................1.4.................... 2.7.REPRODUCIBILITY OF RErNiECTING EXTRACTED SAMPLES ..................14.............. 2.8.EXTRACTION RECOVERY ..............................................1.4.................... 3. RESULTS AND DISCUSSION ...........................................1.5....................
3.1.ASSAY EVALUATION RESULTS .........................................1.6.................... 3.1.1.Intra-and Inter-AssayAccuracy ....................................1.6....................
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3.1-2I.ntra-ndInter-AssParyecisi.o.n......................................... 16
3.1.3L.ineari.t.y........................................................ 16
3.1-4P.artiVaollumeAnalysi.s............................................... 16
3.1-5L.owerLimitofQuantitat(iLoLnQ) ..........................1.7.............
3.1-6S.electiv.i.t.y...................................................... 17
3.1-7C.arryoveErvaluati.o.n.....................................1.7...............
3.2S.TABILITYOF PF,OSINQUALITY CONTROL SAMPLES ....................1.7.................
3.2.1.Ambient TemperatureStabilitoyfPFOS inRat Serum ................1.7...............
3.2.2F.reezeSrtabiloiftPyFOS inRatSerumat-20*C.................1.8.............
3.2.3.Freeze/ThawStabilitoyfPFOS inRat Serum ........................1.8................
3.3.REPRODUCIBILITY OF RErNiEcTiNG ExTRAcTED SAMPLES ................1.8...............
3.4.ExTRAcTiON RECOVERY .................................................1.8...................
4. CONCLUSIONS
...........................................................1.9...................
5. DATA RETRIEVAL ........................................................1.9...................
6. REFERENCES .............................................................1.9...................
7. TABLES ..................................................................2.0...................
8. FIGURES .................................................................3.1...................
9. APPENDIX A: QUANTITATION
OF PERFLUOROOCTANESULFONATE
(PFOS) IN RAT SERUM BY TURBO ION SPRAY LC/MS ...................3.7..............
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LIST OF TABLES
Table1: Intra-AssayAccuracy and Precisionof thePFOS Assay inRat Serum for QC Samples ........................................................................... 20
Table2: Inter-AssayAccuracy and Precisionof thePFOS Assay in Rat Serum for QC Samples from Three ValidationRuns ..............................2.1....................
Table 3: Accuracy and Precisionof thePFOS Assay inRat Serum forCalibration Standardsfrom Three ValidationRuns ................................2.2....................
Table 4: CalibratioCnurve ParametersforPFOS inRat Serum ....................2.3................ Table 5: PartiaVlolume Analysisof PFOS inRat Serum .........................2.4.................... Table 6: Lower LimitofQuantitatioonfPFOS inRat Serum ......................2.5.................. Table 7: Ambient-TemperatureStabilitoyf PFOS inRat Serum After24 Hours......2.6.... Table 8: FreezerStabilitoyfPFOS inRat Serum at-20 *C .......................2.7.................... Table 9: Stabilitoyf PFOS inRat Serum AfterThree Freeze/Thaw Cycles..........2.8........
Table 10:ReproducibilitoyfReinjectinEgxtractedSamples ContainingPFOS after 27 Hours inReconstitutioSnolution..................................2.9.....................
Table 11:ExtractionRecovery of PFOS from Rat Serum ..........................3.0.....................
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LIST OF FIGURES
Figur1e:Full-ScSainnglMeS MassSpectruomfPFOS ............................................. 31
Figure2: Full-ScanSingleMS Mass Spectrum of Tetra-H-PFOS ................................... 32
Figure3: Mass Chromatograms of PFOS and itsInternaSltandardinControlBlank Rat Serum Extract..................................................................... 33
Figure4: Mass Chromatograms of PFOS in a Rat Serum ExtractSample Containing InternaSltandardOnly (ZeroSample).................................3.4..................
Figure5: Mass Chromatograms of CalibratioSntandardI inRat Serum Extract ContainingPFOS (0.05pLg/mL)and theInternaSltandard................3.5.............
Figure6: Mass Chromatogrmns of CalibratioSntandard10 inRat Serum Extract ContainingPFOS (20 Ag/mL) and theInternaSltandard..................3.6..............
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1. INTRODUCTION
Thepurposoefthirseporitstodescritbheemethodvalidatifonrthequantitative determinatioonf perfluorooctanesulfon(aPtFeOS) inratserum samplesafter modificatioonfa previousmethod (1).The objectiveosfthemethod validatiownere tovalidatea simpleextractiopnrocedure,determinethelower limitof quantitation forroutineanalysisd,eterminetheextractiornecoveriesof theanalyteand internal standard(IS),determinetheanalytestabilitiynratserum atambienttemperature, long-termfreezerstorage,and overthreefreeze/thawcycles,and toprovidespecific, accuratea,nd reproduciblqeuantitativreesultbsy turboionsprayliquid chromatography/massspectrometry(LC/MS).
2. EXPERIMENTAL
2.1. CHEMICALS AND MATERIALS Perfluorooctanesulfon(aPtFeOS, Lot# 171)was obtainedfrom 3M, Inc. The internal standard(IS)forPFOS was IH,IH,2H,2H-perfluorooctanseulfonicacid(Tetra-HPFOS). The internasltandard(Lot#59909) was obtainedfrom 3M, Inc.A detailed lisotf chemicalsand materialissfound inAppendix A.
Stockand working solutionwshich were used topreparethecalibratiocnurvesfor theanalyteswere preparedas describedinAppendix A. Stock solutionussed inthe preparatioonf qualitycontrol(QC) sampleswere preparedseparatelfyrom those used inpreparatioonf thecalibratiocnurves.
Preparationof allsolutionussed duringextractioannd analysisaredescribedin Appendix A.
2.2. LC/MS INSTRUMENTATION The liquidchromatography/massspectrometrysystem consistedof two LC- IOAD pumps (Shimadzu,Columbia,MD 21046),a SCL- IOA pump controlle(rShimadzu,
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Columbia,MD 21046), a WISP 717plus autosmnpler(Waters AssociatesM,illipore Corporation,Milford,MA 01757),a BetasilC,,(2 x 50 mm, 5 gm) column (KeystoneScientificI,nc.,BellefonteP,A 16823),and a PE SCIEX API 365 mass spectrometer(PE SCIEX, Concord,Ontario).A detailedlisotf theinstrumentation and instrumentconditionsisfound inAppendix A.
2.3. SAMPLE PREPARATION
AND EXTRACTION
PROCEDURE
For each analyticarlun (tray)d,uplicate50-gL aliquotsof thecalibratiocnurve swnpleswere preparedas describedinAppendix A. The nominal (theoretical) concentrationosf PFOS inthecalibratiocnurveswere 0.05,0.1,0.25,0.5,1,2,4,8, 16,and 20 gg/mL.
Rat serum qualitycontrolsamples were preparedin advance of thevalidationstudy atnominal (theoreticaclo)ncentrationosf0.2,6,and 18 gg/mL forQC I,QC2, and QC3, respectivelya,s detaileidnAppendix A. A dilutionQC (QC4, 100 gg/mL) was preparedata concentrationexceedingthe upper limitof the calibratiocnurve range (20 gg/mL), and was assayedusinga 10-folddilutionforpartiavlolume analysis.
Calibrationstandardsand QC samples were extractedby the proceduredetailedin Appendix A.
2.4. RAT SERUM VALIDATION DATA
The datawere collectedusingselectedion monitoring(SIM) turboionsprayLC/MS inthe negativeion mode. Peak areaswere integratedby the PE SCIEX program MacQuan, version1.4,residingon a Macintosh computer. Following peak area integrationt,heresultstablesfrom MacQuan were saved as textfilesand uploadedto theAdvanced BioAnalyticalServices(ABS) fileserverwhere a weighted(1/y') quadraticregressionwas performed using the softwarepackage Watson v 5.3.1.01 (PSS,Inc.,Wayne, PA 19087).All datawere rounded to no lessthan three significanftiguresby ABS priortoreportinginTables I through11. The datafor the ratserum validationarestoredin ABS Notebook 2304.
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Allcalculationwsere based on thepeak arearatioof theanalytetotheinternal standard.Concentrationsof eachanalyteinqualitycontrolsampleswere determined by inversepredictiofnrom thecalibratiocnurve.
2.5. ASSAY EVALUATION
2.5.1. Intra-and Inter-AssayAccuracy The intraa-nd inter-assaayccuracyof themethod was assessedby determiningthe relativeerrorobservedintheanalysisof qualitycontrolsamples. The mean concentratiofnoreach qualitycontrolevelwas dividedby thetheoretical concentrationO.ne was subtractedfrom theresultc,onvertedtopercentand expressedasRE. QC I throughQC3 were assayedinreplicateosf five.Inaddition, theRE was reportedforstandardsatalllevelsover threeruns.
2.5.2. Intra-and Inter-AssayPrecision The intraa-nd inter-assapyrecisionofthemethod was assessedby determiningthe RelativeStandardDeviation(RSD) observedforqualitycontrolsample data.The mean concentratioannd RSD were calculatefdorthefirsrtun and overthreerunsfor intra-assaaynd inter-assapyrecisionr,espectivelyQ.C I throughQC3 were assayed inreplicateosf five.In additiont,heRSD was reportedforstandardsatalllevels overthreeruns.
2.5.3. PartialVolume Analysis The effectof dilutionon the analysisof PFOS inratserum was determinedby partial volume analysis.QC4 (100 jig/mL)was preparedcontainingPFOS atapproximately fivetimestheupperlimitofquantitatio(nULQ). FivereplicateosfQC4 were dilutedten-foldand analyzed.The RSD and RE were reported.
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2.5-4. Lower Limit of Quantitation(LLQ) Rat serum controlsamples from six separateindividualswere spiked with PFOS ata concentratioonf 0.05 @Lg/mL.The LLQ was determinedby obtainingthebackcalculatecdoncentrationfsrom thesecontrolsamples. The overallmean, RSD, and RE were alsocalculated.
2.5.5. Selectivity The selectiviotfytheassaywas determinedby LC/MS. To monitorforinterference from thebiologicamlatrix,ratserum samplescontainingneithertheanalytenorthe internasltandard(controlblank)were assayedwithallexperiments.
2.5.6. Carryover Evaluation The carryoverofanalytefrom one injectiotrofthenextwas assessedby analyzinga controlblankinjecteidmmediatelyaftera highcalibratiosntandard(STDIO, 20 Ag/mL).
2.6. STABILITY OF PFOS INQUALITY CONTROL SAMPLES QC I throughQC3 were usedtodeterminethestabilitoyf theanalyteduringsample storage,extractiona,nd analysis.
2.6.1. Ambient-Temperature StabilitoyfPFOS inRat Serum The stabiliotfyPFOS was evaluatedby storingQC samples ateach concentration levelatambienttemperature(ca.25 *C) fornominaltimepointsof 0,2.5,6,and 24 hoursafterthawing.All QCs were assayedinreplicateosf five.
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2.6.2. FreezeSrtabiliotfyPFOS inRatSerumat-20*C ThefreezsetrabiloiftPyFOS wasevaluatbeydstorinQgC sampleasteach concentratiolnevelat-20 *C for7, 13,and 33 days.Additionalfreezerstability timepointswillbe reportedinan addendum to thisreport.AllQCs were assayedin replicateosf four.
2.6.3. Freeze/Thaw Stabilitiyn Rat Serum The stabilitoyf PFOS was evaluatedafterthreefreeze/thawcycles.The mean concentrationosf theQC samplesafterthreefreeze/thawcycles(i.e.a,tleast2 hours frozenstorageatthenominaltemperatureof-20 *C followedby thawingatambient temperaturefor30 minutes)were compared to themean concentrationosf freshly thawed QC samples.AllQCs were assayedin replicateosf five.
2.7. REPRODUCIBILITY OF REINJECTING EXTRACTED SAMPLES
The reproducibiliotfyreinjectinrgeconstitutesderum extractwsas investigatebdy reinjectinagsetof previously-assayesdtandardsand QC sampleswhich had been storedafterinjectioantapproximately25 *C for27 hours.The RE of theQC sampleswas used to assessprocessedsample stabilitiyn thereconstitutiosnolution. AllQCs were assayedinreplicateosf five.
2.8. EXTRACTION REcovF.Ry
The extractiornecoveryof PFOS from ratserum was determinedby comparingthe peak arearatio(PAR) ofsamples(0.25,4,and 16 gg/mL) spikedafterextraction (post-extracwti)ththePAR ofsamplesspikedbeforeextractio(npre-extractT)h.e internasltandardwas spikedpost-extractiofnorallsamples.The recoveryofthe internasltandard(4 gg/mL) was assessedfollowinga similarapproachusingPFOS as thereferenceT.he extractiornecovery(% Recovery)was determinedby dividing thepre-extracPtAR by thepost-extracPtAR and expressingtheresultas a percentage.Fivereplicatewsere used ateach concentratiolnevel.
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3. RESULTS AND DISCUSSION A quantitatiavnealyticparloceduruesingturboionsprayLC/MS inthenegativieon mode was developed to meet thehigh sensitivitsyp,ecificitayn,d reproducibility requirementsforthe determinationof PFOS inratserum. The full-scasningleMS mass spectrumof PFOS showed an abundant (M-K]' ionatm/z = 499 (Figure1). The full-scasningleMS mass spectrum of Tetra-H-PFOS showed an abundant [M-H]- ionatm/z = 427 (Figure2).
The followingselectedionmonitoring(SIM) was used toquantifytheanalytesinrat serum:
PFOS Tetra-H-PFOS (IS)
m/z = 499.0 m/z = 427.0
The peak labelingof fall-scadnatadoes not accuratelyrepresentthe performanceof theinstrumentinSIM mode. The SIM ionswere derivedfrom separateexperiments usingnarrow-rangescanning,which more accuratelydepictstheoperationof the instrumentinthe SIM mode. The mass chromatograms of a representativceontrol blank ratserum extractareshown in'Figure 3. Mass chromatograms f@om a representativceontrolratserum extractcontainingonly theinternalstandard(zero sample),are shown inFigure4.
Figures5 and 6 aremass chromatograms ofrepresentativextractsfrom calibration standardsI and 10,respectively.
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3.1. ASSAY EVALUATION
RESULTS
3.1.1. Intra-and Inter-AssayAccuracy
The intra-assaayccuracy(RE) datafrom QC samplesrangedftom -2.35to5.58% for PFOS (Table1).The inter-assaayccuracyrangedfrom -3.58to4.95% forPFOS (Table2).These dataindicataecceptableintra-and inter-assaayccuracyforthe determinatioonf PFOS inratsenim.
3.1.2. Intra-and Inter-AssayPrecision
The intra-assapyrecisiondata(RSD) ranged ftom 1.99to 3.28% forPFOS atallQC concentratiolnevels(Table1).The inter-assapyrecisionresultsfrom QC samples rangedfrom 1.92to4.87% forPFOS (Table2).The RSD rangedfrom 0.613to 4.38% forcalibratiosntandardsatalllevels(Table3).These dataindicataecceptable intra-anidnter-assapyrecisionforthedeterminationof PFOS inratserum.
3.1.3. Linearity
The calibratiocnurveswere fitby a weighted(1/y2)quadraticregression. Coefficientosfdeterminatio(nr2 )were 2:0.9962forPFOS inratserum. The calibratiocnurvestatistiacrseshown inTable 4.
3.1.4. PartialVolume Analysis
The resultsof partiavlolume analysisof QC4 isshown inTable 5. The precision (RSD) ofQC4 samplesdilutedIin10 was 2.71%. The accuracywas 5.89%. These dataindicataecceptableaccuracyand precisionforpartiavlolume analysisforthe determinatioonfPFOS inratserum.
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3.1-5. Lower Limit of Quantitation(LLQ) Table 6 shows the lower limitof quantitation(LLQ) data.The serum LLQ experimentdemonstratedthat0.05pg/mL isan acceptableLLQ forPFOS. The precisio(nRSD) was 4.95% forPFOS. The RE was 4.57%.
3.1.6. Selectivity The assaywas specififcorPFOS. No chromatographicinterferencewsere observed inany of thecontrolserum samplesanalyzed(Figure3). The controlblanksand zerosamplesdidshow some evidenceof smallchromatographicpeaks atthe retentiotnimesof theanalyte.These peaks were not quantifiablaes theywere below thelowerlimitofquantitati(oLnLQ).
3.1.7. Carryover Evaluation CarryoverofPFOS and theIS was evaluatedby injectioonfan extracterdatserum controlblankfollowingan injectioonf an extractehdigh standard(STD 10).The responseforthesmallchromatographicpeak attheretentiotnime forPFOS was comparabletotheresponseof a ratserum controlblank injectebdeforethehigh standardT.hus,carryoverisnegligiblfeorPFOS. There was no evidenceof carryoverfortheinternasltandard.
3.2. STABILITY OF PFOS IN QUALITY CONTROL SAMPLES
3.2.1. Ambient Temperature Stabilityof PFOS in Rat Serum The resultosf theambient stabilitoyf PFOS inQC samplesareshown inTable 7. The mean predictedconcentrationdseviatedfrom 4.45 to 10.5% from the0-hour valuesforallQC levelsand timepoints.Based on thesedata,PFOS was stableinrat serum forup to24 hoursatambienttemperature.
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3.2.2. Freezer Stabilityof PFOS in Rat Serum at-20 *C The resultosf thelong-termstabilitoyfPFOS inQC samples storedat-20 OC are presentedinTable 8. The PFOS concentrationdseviatedfrom 0-hourvaluesfrom -2.76to 12.3% forallQC levelsstoredup to33 days.
Resultsof freezerstorageaftertwo,four,and eightmonths willbe reportedas an addendum to thisreport.
3.2.3. Freeze/Thaw Stabilityof PFOS in Rat Serum The resultsof thefreeze/thawstabilitoyf PFOS in QC samples afterthree freeze/thawcyclesisshown inTable 9. PFOS was stableafterthreefreeze/thaw cycleswithdeviationsrangingfrom -1.38% to 10.1% from the0-cyclesamplesfor allQC level(sTable9).
3.3. REPRODUCIBILITY OF REINJECTING EXTRACTED SAMPLES The resultsofreinjectinrgeconstitutesdamplescontainingPFOS afterstoragefor27 hoursatapproximately25 *C inreconstitutisoonlutionareshown inTable 10. Reinjectinpgrocessedsamplesafter27 hours inreconstitutisoonlutionwas appropriatweithRE valuesrangingfrom -6.33to 4.59% at27 hoursforallQC levels.
3.4. EXTRACTION REcovERY The mean recoveriesof PFOS and Tetra-H-PFOS areshown in Table 11. The mean recoveriesrangedfrom 87.6to 100% forPFOS The mean recoveryforTetra-HPFOS was 89.9%.
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4. CONCLUSIONS
TheturbioonsprayLC/MS assapyrocedurfeorthedeterminatoifoPnFOS inrat serum has proven tobe sensitives,pecifica,ccuratea,nd reproducibleI.tshigh sensitiviatlylowsreliablaend reproduciblqeuantitatioonf PFOS down toa levelof 0.05 gg/mL inratseruxnbased on 50-gL samples.
5. DATA RETRIEVAL The datafortheratserum validatioanrestoredinA13S Notebook 2304 and inthe ABS Archives.
6. REFERENCES 1. Advanced BioAnalyticaSlervicesI,nc.Report98AGKPO2.MMM. AnalyticaRleportfortheDeterminationof Perfluorooctanoataend PerfluorooctanesulfoniantHeuman Serum by LC/MS. GraceK. Poon, Ph.D.,David Hardwick,B.S.,and Ellen'PaceM,.A.T.,6 February1998.
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7. TABLES
Table 1:
Intra-Assay Accuracy and Precisionof the PFOS Assay in Rat Serum forQC Samples
TheoreticalConc.-
PFOS Concentration(gg/ML)
QCI
QC2
QC3
0.2
6
18
Run 9
0.210
6.52
17.9
0.202
6.31
18.0
0.206
6.17
16.7
0.205
6.32
18.0
0.194
6.35
17.3
Mean RSD RE
0.204
6.34
17.6
2.93
1.99
3.28
1.77
5.58
-2.35
RSD = (SD/Mean) x 100 RE [(Mean/TheoreticalI)]-x 100
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Table 2:
Inter-AssayAccuracy and Precisionof the PFOS Assay in Rat Serum forQC Samples from Three ValidationRuns
TheoreticalConc. Run 9
PFOS
QCI
0.2 0.210 0.202 0.206 0.205 0.194
Concentration(gg/mL)
QC2
QC3
6
18
6.52
17.9
6.31
18.0
6.17
16.7
6.32
18.0
6.35
17.3
Run 10
0.187
6.44
16.9
0.186
6.44
17.3
0.182
6.32
17.5
0.189
6.19
18.0
0.182
6.31
17.4
Run 11
0.194
6.17
18.2
0.197
6.13
17.1
0.184
6.41
17.6
0.192
6.15
17.7
0.184
6.24
17.0
Mean
0.193
6.30
17.5
RSD
4.87
1.92
2.66
RE
-3.58
4.95
-2.73
RSD = (SD/Mean) x 100 RE= [(Mean/TheoreticalI)]-x 100
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Table3:
AccuracyandPrecisiofnthePFOS AssayinRatSerumfor CalibratiSotnandardfsromThreeValidatiRounns
PFOSCalibratSitoanndaCrodncentrat(igogn/mL)
TheoreticalSTDI@ STD2 STD3 STD4 STD5 STD6 STD7 STD8 STD9 sT-DIO
Conc. 0.05 0.1 0.25 O.S
1
2
4
8
16 20
Run 9 0.0483 0.0972 0.251 0.480 0.942 2.10 0.0530 0.101 0.252 0.483 0.938 2.13
Run 10 0.0491 0.0951 0.239 0.469 0.954 2.16 0.0542 0.101 0.251 1 0.479 0.942 2.11
Run 11 0.0510 0.0960 0.251 0.469 0.945 2.21 0.0510 0.0995 0.252 0.477 0.948 2.13
4.48 7.61 15.8 20.0
4.5.5 7.70 16.2 19.9
4.58 8.05
19.6
4.43 7.87 155-97 20.0
4.40 7.64 15.8 20.3
4.53 7.78 15.6 20.0
Mean 0.0511 0.0983 0.249 0.476 0.945.- 2.14 4.50 7.78 15.8 20.0 RSD (%) 4.38 2.65 2.07 1.15 0.613 1.90 1.62 2.13 1.22 1.08 RE (%) 2.20 1 -1.67 1 -0.207 1 -4.78 1 -5.53 1 7.05 f 12.4 1 -2-80 1 -1.00 -0.0764
RSD = (SD/Mean)x 100 RE= [(Mean/TheoreticaIl])x-100
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Table 4:
CalibrationCurve Parameters forPFOS inRat Serum
Run
Quadratic
Coefficient Intercept Coefficienotf
Coefficien(tA)" Linear(B)
(C) Determinatio(nr')
9
-0.0010769
0.13730
0.00042009
0.9965
10
-0.0010516
0.14535
0.0014910
0.9962
11
-0.0012359
0.15173
0.00088515
0.9964
@ll
I
Mean
0.14479
0.00093206
MoM-um=-M=w 0.9964
I
a:y Ax' +Bx + C, weighted I/Yl
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Table 5: PartialVolume AnalysisofPFOS inRat Serum
PFOS Conc.(gg/mL)
QC4
TheoreticaClonc.
100
Run 9
(I in10dilution) 111
105
105
104
104
Mean
106
RSD
2.71
RE (%)
5.89
D = (SD/Mean) x 100
RE [(Mean/TheoreticaIl])x- 100
. ........................
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Table 6: Lower Limit ofQuantitationofPFOS inRat Serum
Run 11
PFOS
'McoreticaCloncentrationConc.Found (gg/mL)
0.0548
LLQ
0.0489
(0.05gg/mL)
0.0499
0.0554
0.0527
0.0520
Mean
0.0523
RSD (%)
4.95
RE
4.57
RSD (SD/Mean)x 100
RE [(Mean/Theoretical)x-11]00
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p
Table 7:
Ambient-Temperature Hours
Stability of PFOS in Rat Serum After 24
Run I I
PFOS (gg/mL)
0--NM-m@
QC (TheoreticaClonc.)
QC 1 (0.2gg/mL)
Mean RSD (%) %DEV from 0 Hour
0 Hour 0.194 0.197 0.184 0.192 0.1840.190 3.03 NA
2.5 Hour 0.187 0.181 0.184 0.180 0.178 0.182 1.91 -4.20
6 Hour 0.177 0.179 0.180 0.183 0.189 0.182 2.52 -4.45
24 Hour 0.190 0.187 0.191 0.182 0.190 0.188 2.01 -1.16
6.17
6.17
6.36
6.55
QC 2 (6gg/mL)
6.13
6.30
6.38
6.53
6.41
6.26
6.35
6.85
6.15
6.28
6.22
6.66
6.24
6.24
6.11
6.81
Mean RSD (%) %DEV from 0 Hour
6.22
6.25
6.28
6.68
1.82
0.797
1.86
2.16
NA
0.525
1.05
7.42
QC 3 (18gg/mL)
18.2
18.0
18.1
19.1
17.1
18.0
18.0
19.4
17.6
17.7
17.6
19.2
17.7
17.9
18.2
19.4
17.0
18.0
18.0
19.7
Mean RSD (%) O/oDEV from 0 Hour
17.5
17.9
18.0
19.4
2.84
0.719
1.26
1.19
NA
2.33
2.39
10.5
NA: Not Applicable RSD = (SD/Mean) x 100 %DEV from 0 Hour [(X Hour Conc. - 0 Hour Conc.)/OHour Conc.]x 100
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Table 8:
Freezer Stabilityof PFOS in Rat Serum at -20 OC
QC
PFOS g/mL)
Nominal Concentration
0 Hour (Run 2)*
7 Days 6)*
13 Days (Run 3)**
QC 1 (0.2ug/mL)
0.213 0.209 0.208 0.208 0.207
0.225 0.222 0.218 0.219
0.211 0.210 0.217 0.214
Mean RSD (%) %DEV from 0 Hour
0.209 1.24 NA
0.221 1.32 5.72
0.213 1.55 1.84
6.02
6.22
5.97
QC 2
5.71
6.15
5.84
(6ug/mL)
6.00
6.39
6.07
6.06
6.27
5.99
5.69
Mean RSD (%) %DEV from 0 Hour
5.89 3.08 NA
6.26 1.62 6.19
5.97 1.58 1.20
QC 3 (18ug/mL)
Mean RSD (%) %DEV from 0 Hour
20.2 18.6 18.9 18.2 18.9 18.9 3.96 NA
19.1 19.5 19.8 19.3
19.4 1.37 2.52
18.8 18.2 18.8 17.9
18.4 2.42 -2.76
NA: Not Applicable RSD = (SD/Mean) x 100 %DEV from 0 Hour = [(Conc.- 0 Hour Conc.)/OHour Conc.] x 100
*From ProtocolFACT-TOX- I10 **From ProtocolFACT-TOX-1 11
33 Days (Run 16)
0.245 0.234 0.228 0.232
0.235 3.17 12.3 6.45 6.13 6.58 6.37
6.38 2.97 8.28 18.6 18.8 18.7 18.7
18.7 0.395 -1.30
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Table 9: StabilitoyfPFOS inRat Serum AfterThree Freeze/Thaw Cycles
Run 10 QC (TheoreticaClonc.)
QC 1 (0.2gg/mL)
Mean RSD (%) %DEV from 0 Cycle
PFOS (gg/mL)
0 Cycle
3 Cycles
0.187
0.177
0.186
0.177
0.182
0.185
0.189
0.185
0.182
0.189
0.185
0.182
1.70
3.12
NA
-1.38
6.44
QC 2
6.44
(6jig/mL)
6.32
6.19
6.31
Mean
6.34
RSD (%)
1.66
%DEV from 0 Cycle
NA
6.59 6.61 6.44 6.39 6.40 6.49 1.63 2.35
16.9
19.2
QC 3
17.3
19.1
(18gg/mL)
17.5
19.2
18.0
19.6
17.4
18.7
Mean
17.4
19.2
RSD (%)
2.31
1.80
%DEV from 0 Cycle
NA
10.1
NA: Not Applicable RSD = (SD/Mean) x 100 %DEV from 0 Cycle= [(3Cycle-0 Cycle)/OCycle]x 100
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Table 10:
ReproducibilitoyfReinjectingExtractedSamples Containing PFOS after27 Hours inReconstitutioSnolution
QC 1; (0.2gg/mL)
Mean RSD (%) RE
QC 2 (6gg/mL)
Mean RSD RE
QC 3 (18gg/mL)
Mean RSD RE (%) NA: NotApplicable RSD = (SD/Mean)x 100 RE = [(MearvneoreticaIl]x)-100
PFOS t=o Hours (R n 10)
0.187 0.186 0.182 0.189 0.182 0.185 1.70 -7.50
6.44 6.44 6.32 6.19 6.31 6.34 1.66 5.62
16.9 17.3 17.5 18.0 17.4 17.4 2.31 -3.29
W'mL)
t--27Hours (Run 12)
0.187 0.182 0.188 0.188 0.190 0.187 1.61 -6.33
6.39 6.02 6.19 6.55 6.22 6.28 3.23 4.59
17.3 18.2 18.1 17.3 17.6 17.7 2.40 -1.73
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Table 11: Extraction Recovery of PFOS from Rat Serum
TheoreticalConc. Pre-Extraction
Post-Extraction
inserum (gg/mL) PFOS Spike 1
(0.25pg/mL) Run 14
Mean PFOS Spike 2 (4gg/mL) Run 14
Mean PFOS Spike 3 (16gg/mL) Run 14
Mean Tetra-H-PFOS
Spike IS (4;lg/mL)
Run 13
Mean
Response (AreaRatio)Response (AreaRatio)
0.03160 0.02850 0.02930 0.02790 0.03050
0.02880 0.03010 0.02950 0.02930 0.02960
0.02956
0.02946
0.4597 0.4751 0.4776 0.4724 0.4772
0.5270 0.5304 0.5335 0.5298 0.5392
0.4724
0.5320
1.649
1.874
1.679
1.857
1.719 1.535 1.612
1.869 1.887 1.864
1.639
1.870
0.4068
0.4460
0.3884 0.4043 0.3921 0.4078
0.4423 0.4445 0.4512 0.4412
0.3999
0.4450
O/oRecovery*
110 94.7 99.3 95.2 103 100
87.2 89.6 89.5 89.2 88.5 88.8
88.0 90.4 92.0 81.4 86.5 87.6
91.2 87.8 91.0 86.9 92.4
*(IndividuaRlesponse forPre-Ext./IndividuRaelsponse forPost-Ext.x) 100
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8. FIGURES Figure 1: Full-ScanSingleMS Mass Spectrum ofPFOS
Spectrumfrom PROS Q I 98 91 84 77 70 63 56 49 42 35 28 21 14 -
7. 349 360
3.19e7 cps 499 [M-Kl-
399 449
L
420
480
540
ff,/Z
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Figure2: Full-ScanSingleMS Mass Spectrum ofTetra-H-PFOS
Spectrum from Tetm-H-PFOS Q]
96 90 84 78 72 66 60 54 48 42 36 30 24 18 12 6
350
407
L 400 nl/z
1.94e7 cps
427
[M-H]-
450
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Figure3:
Mass Chromatograms ofPFOS and itsInternalStandard in ControlBlank Rat Serum Extract
rrvz 427.0
I.O7c3cps
90 . so 70 60 so 40 30 20 10 -
ni/z 499.0
2
3
Time, min
4 3.54e2 cps
90 so 70 60 50 40 . 30 20 -
10 1
2
3
4
Time, min
Allquantitationresultsand figureswere prepared from non-smoothed data.
AnaMe
PFOS Tetra-H-PFOS (IS)
Ion ni/z= 499.0 mlz = 427.0
RetentionTime 3.1 2.9
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Figure 4:
Mass Chromatograms ofPFOS ina Rat Serum ExtractSample ContainingInternalStandard Only (ZeroSample)
mlz 427.0
2.34e5 cps
9080 70 60 50 40 30 20 10
ffi/z 499.0
90 80 70 60 50 40 30 20 10 -
2 Time, min
4 3.78e2 cps
1
2
3
Time, min
Allquantitationresultsand flgureswere prepared from non-smoothed d2t2.
Anal= PFOS
Tetra-H-PFOS (IS)
lm mlz = 499.0
m/z - 427.0
RetentionTime 3.1 2.9
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Figure5:
Mass Chromatograms ofCalibrationStandard I inRat Serum ExtractContainingPFOS (0.05gg/mL) and theInternal Standard
ni/z 427.0
3.82e5 cps
90 80 70 60 so 4030 20 10
rn/z 499.0
2
3
Time. min
4 2.1lc3 cps
z
90
80
70
60
so
40
30
20
10
1
2
3
4
Time,min
Allquantitationresultsand flgureswere prepared from non-smoothed data.
AnaL= PFOS Tetra-H-PFOS (IS)
im rn/z= 499.0 m/z = 427.0
RetentionTime 3.1 2.9
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Figure6:
Mass Chromatograms ofCalibrationStandard 10 inRat Serum ExtractContainingPFOS (20gg/mL) and theInternalStandard
m/z 427.0
3.52e5 cps
9080 70 60 50 40 30 20 10
1
m/z 499.0
90 80 70 60 50 40 30 20 10
2
3
Time, min
4 5.l4e5cps
1
2
3
4
Time, min
Allquantitationresultsand flgureswere prepared from non-smoothed data.
AnalZe PFOS Tetm-H-PFOS (IS)
L9jl m/z = 499.0
ni/z= 427.0
RetentionTime 3.1 2.9
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9. APPENDIX A: QUANTITATION PERFLUOROOCTANESULFONATE TURBO ION SPRAY LC/MS
OF (PFOS) IN RAT SERUM BY
AUTHORS:
David J. Anderson, M.S. Amie J.Prince,B.S. HollyD. Ross,M.S.
TABLE OF CONTENTS
A.1.0 A.2.0 A.3.0 A.4.0 A.5.0 A.6.0 A.7.0 A.8.0 A.9.0 A.10.0 A. 11.0
Chemical Structure(s.)...............................................3.8.................... Specimen(s)........................................................3.8.................... Assay Principle.....................................................3.8..................... Compounds ........................................................3.8..................... Chemicals .........................................................3.8..................... Materialsand Equipment .............................................3.9..................... Preparationof Solutions..............................................4.2.................... Preparationof QualityControlSamples .................................4.5..................... Liquid-liquiEdxtractioPnrocedure.....................................4.6..................... InstrumentConditions...............................................4.7..................... Calculations........................................................4.9....................
MMM
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A.1.0CHEMICAL STRUCTURE(S)
0
11 CgF,7-S-0-K+
11 0
C6FI3-C H2
0
11 C-S-OH
H2 11
0
PotassiumPerfluorooctanesulfonate MW = 538
1H, IH, 2H, 2H-PerfluorooctanSeulfonicAcid MW = 428, InternaSltandard
A.2.0 SPECIMEN(S) This assayuses 50-@LLaliquotsofratserum. Rat serum samples arestoredat-20*C.
A.3.0 ASSAY PRINCIPLE PFOS and itsinternalstandardT,etra-H-PFOS, areextractedfrom ratserum samples (50 gL) usinga liquid-liqueixdtractiopnrocedure.The organiclayerisevaporated todrynessand thenreconstitutedA.n aliquotisthenanalyzedby turboionspray liquidchromatography/massspectrometry(LC/MS) inthenegativeionmode.
A.4.0 COMPOUNDS PFOS: Lot# 171,99.976% purity3,M, Inc.,Minneapolis,NfN. Tetra-H-PFOS: Lot# 59909,90% purity,3M, Inc.,Minneapolis,N4N.
A.5.0 CHEMICALS Allchemicalsmay be substitutewdiththatof an equivalentmanufacturerand grade ofchemical.
MMM
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Acetonitrile Ammonium Acetate EthylAcetate Methanol Rhodapex mass calibration solution
Sodium Bicarbonate Sodium Carbonate,Annhydrous Tetrabutylammonium Hydrogen Sulfate Water
Rat Serum Rat Serum
Cat# 0154, Burdick& Jackson, Muskegon, MI 49442
Cat# 24,019-2,Aldrich,Milwaukee,Wi 53201
Cat# 100-4,Burdick& Jackson, Muskegon, MI 49442
Cat# 230-4,Burdick& Jackson, Muskegon, MI 49442
A mixtureof 0.11 mM trifluoroacetaiccid (J.T.Baker,PhillipsburNgJ, 08865),0.52 mM Rhodapex CO-436, I mM ABEX EPI10 and I mM ABEX EP- 120 (allthree suppliedby Rhone-Poulenc,Inc., Cranbury,NJ 08512) in 1:1 methanol:water.
Cat# 3509-01,J.T.Baker,PhillipsburgN,J 08865
Cat# 3604-01,J.T.Baker,PhillipsburgN,J 08865
HPLC Grade,Cat# J360-07,J.T.Baker, PhillipsburNgJ, 08865
High Purity(NANOpure), Bamstead Model D7331 UltrapureWater System, Dubuque, IA 52001
Lampire BiologicaLlaboratories, PipervillPeA, 18947
HarlanBioproductsforScience,Inc., IndianapolisI,N 46229
A.6.0 MATERIALS AND EQUIPMENT
Mass Spectrometer
PE SCIEX API 365 atmosphericpressureionization tandem triplqeuadrupolemass spectrometerequipped withTurbolonSprayTMinterfaceP,E SCIEX, Concord, OntarioL4K 4V8
Data system
API StandardSoftware,MacQuan v 1.4,LC2Tune v 1.3,MacDAD v 1.3,Bundlerv 1.3,Multiviewv 1.3,
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HPLC Pump
and Sample Controlv 1.3,on a Power Macintosh,PE SCIEX, Concord,OntarioL4K 4V8
Shimadzu LC- IOAD pump, Shimadzu Co.,Columbia, MD 21046
LC Pump Controll,-.r Shimadzu SCL- IOA, Shimadzu Co.,Columbia, MD 21046
Autosampler
Waters717plus,Waters AssociatesM,illipore CorporationM,ilford,MA 01757
HPLC Column
BetasilCl,,5 gm particlseize,2.1x 50 mm, Cat
#852055-701,Keystone ScientifiIcn,c.,BellefonteP,A 16823
Harvardsyringe pump II
HarvardApparatusInc.,South Natick,MA 01760
Multi-tubveortexer
Balance pH Meter Mechanicalshaker NANOpure-LTV waterpurification system
Cat# 58816-115,VV*RR ScientificW,est Chester,PA 19380
Model FX-300, AND Ltd.,Tokyo, Japan Model 340,Coming Inc.,Coming, NY 14830 Cat# 6000,Eberbach Corp.,Ann Arbor,MI 48106 Bamstead,Dubuque, IA 52001
Microbalance
Model MT-5, Mettler-ToledIonc.,Hightstown,NJ 08520
Micro weigh boats
Weigh boats
SorvallRT-6000D refrigerated centrifuge
Cat# 0219-0041,Perkin-ElmerCorp.,Norwalk, CT 06859
Cat# 12577-025,VVRR ScientificW,est Chester,PA 19380
Cat# 83071,DuPont Co.,Wilmington,DE 19898
Beckman GS6KR Refrigerated centrifuge
Beckman, PaloAlto,CA 94304
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Turbovap LV Evaporator Pipettes
Pipettetips
Polypropylenetubes
Screw-capped Polypropylenevials Screw-capped Polypropylenevials PlugTite MultipurposeCaps Pyrex volumetric flask SolventFiltration Apparatus
Nylon Titan Membrane Filters PEEK tubing
LiquidNitrogen
GastightGlass Syringes
Cat#43750,Zymark InstrumentsH,opkinton,MA 01748
Cat# P-5000,P-1000,P-200,P-100,RaininInstrument Co., Wobum,MA01888
RT-20, RT-200, C-5000, CP-25, CP-50, CP-250, RaininInstrumentCo.,Woburn, MA 01888
13 mm x 100 mm, Cat# 15070-574,VWR Scientific, West Chester,PA 19380
16.5x 57 mm, Cat# 60.542,SarstedtI,nc.,Newton, SC 28658
16.5x 101 mm, Cat# 60.541,SarstedtI,nc.,Newton, SC 28658
Cat# 78-127-0019-100,Elkay Products,Inc., Worcester,MA 0 1607
Cat# 28014P-10,28014P-25, 28014P-100,28014P1000,Kimble/Kontes,Vineland,NJ 08360
Cat# 953781-0000,953751-0000,953753-0000, 953826-0000,953827-0000, Kimble/Kontes,Vineland, NJ 08360
0.45@Lm ScientifiRcesources Inc.,Cat# 74547-NN, Eatontown,NJ 07724
0.005"i.d.x 1/16"o.d.,Cat# 1535,Upchurch Scientific Inc.O,ak Harbor,WA 98277
Suppliedin-housefrom bulk tank,BOC Gasses, Buffalo,NY 14210-2005
Cat# 1750,Hamilton Company, Reno, NV 895 10
Othergenerallaboratoryglasswareand supplieswere used.
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A.7.0PREPARATION OF SOLUTIONS NANOpurewater(18megaohm-cm.o)requivalesnhtoulbdeusedwherevewrateirs calledfor.Mix allsolutionwsell.
A-7,1 PreparationofAnalyticalStandard Stock Solutions AnalyticalStandard Stock Solution,PFOS (I mg/mL): Weigh approximatel5y mg of PFOS (aftecrorrectiofnorpurity)on a microbalanceand transfeirttoa polypropylenevial.Dilutewiththeappropriatveolume ofmethanoltoyielda I mg/mL solutionP.reparea freshsolutioneverythreemonths. Storethesolutioant 4 *C and bringtoambient temperaturebeforeuse.
Standard Spiking Solutions PrepareStandardWorking SolutionsA throughJ in 5-mL class"A" volumetric flasksaccordingtothefollowingdilutiosncheme. Dilutetothe5-mL mark with watertoyieldthefinalconcentrationP.reparefreshsolutionseverythreemonths. Storethesolutionast4 'C and bringto ambienttemperaturebeforeuse.
Standard Working
A B c D E F G H 1
Volume Spiked SolutionUsed
(gL)
1000
Stock
800
Stock
400
Stock
200
Stock
100
Stock
250
200 gg/mL (A)
125
200 gg/mL (A)
62.5
200 gg/mL (A)
500
10 gg/mL (F)
250
10 gg/mL (F)
PFOS Final Conc. .(@tg/mL) 200 160 80 40 20 10 5 2.5 1.0 0.5
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A.7.2 PreparatioonfInternaSltandardStockSolutions InternaSltandardStockSolutionT,etra-H-PFOS(Img/mL): Weigh approximately5 mg of Tetra-H-PFOS on a microbalanceand transferitto a polypropylenevial.Dilutewith an appropriatevolume of methanol toyielda I mg/mL solutionP.reparea freshsolutionevery threemonths. StoretheSo
lutionat 4 *C and bringto ambient temperaturebeforeuse.
A.7.3 Preparation ofInternalStandard Working Solution InternalStandard Working Solution (4 jig/mL Tetra-H-PFOS): Add 400 iLLof InternaSltandardStock Solutionto a I00-mL class"A" volumetricflask.Diluteto themark with water togivea 4 gg/mL Tetra-H-PFOS solution.Storethe solutionat 4 *C and bringto ambient temperaturebeforeuse. Preparefreshsolutionas needed.
A.7.4 Preparation of Standard Curve and Control Blank Preparefreshcalibratiosntandardsforeach analyticalrun by combining 360 p.Lof ratcontrolserum and 40 gL ofthe analyticasltandardworking solution(seetable below) inlabeled1.7-mL microtubes.Preparecontrolblanksand zero samplesby combining 360 gL of ratcontrolserum with 40 pLLof water. Vortex each for60 seconds.
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AnalyticaSltandardDilutioTnable:
@Stan,1dnd=arrdd
10 9 8 7 6 5 4 3 2 1
Volume SSppiVikoke'edu:dm((@pL)
40 40 40 40 40 40 40 40 40 40
Solutiotno use A B c D E F G H 1 1
gL control serum 360 360 360 360 360 360 360 360 360 360
MalConc. (jig/mL)
20n@oLn)c* 16 8 4 2 1 0.5 0.25 0.1 0.05
A.7.5 Preparation of Other Solutions 0.25 M Sodium Carbonate/0.25 M Sodium Bicarbonate: Weigh 26.5 g of sodium carbonateand 21 g of sodium bicarbonateand dissolvein approximately900 mL of HPLC-grade water. Transferthesolutionto a 1000-mL volumetricflaskand dilute tothemark with HPLC-grade water. Mix thesolutionthoroughly.Storeatambient temperature.Preparea freshsolutionevery threemonths.
I M Ammonium Acetate: Add 7.7 g of ammonium acetateto a 100-mL volumetric flask,dissolveinNANOpure water,and stiruntilcompletelydissolved.Dilutetothe mark with NANOpure water. Storeatambient temperature.Preparea freshsolution every threemonths.
2 mM Ammonium Acetate: Combine 2 mL of IM ammonium acetateand 900 mL NANOpure water ina I000-mL volumetricflask;stiruntilcompletelymixed. Dilute tothe mark with NANOpure water.Store atambient temperature.Prepare a fresh solutionevery threemonths.
am=
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10 M SodiumHydroxide:Add 40gofsodiumhydroxidteoa 100-mLvolumetric flaskd,issolveinNANOpure water,and stiruntilcompletelydissolved.Dilutetothe mark withNANOpure water.Storeatambienttemperature.Preparea freshsolution everythreemonths.
1 M Sodium Hydroxide: Add 10 mL of 10 M sodium hydroxidetoa 100-mL volumetricflask.Dilutetothemark with NANOpure water;stiruntilcompletely mixed. Storeatambienttemperature.Preparea freshsolutioneverythreemonths.
0.5M Tetrabutylammonium Hydrogen Sulfate,pH 10: Weigh 16.98g of tetrabutylammoniumhydrogen sulfateand dissolvein40 mL of NANOpure water. AdjustedthepH to 10.0with 10 M and I M sodium hydroxide.Transferthesolution to a I00-mL volumetricflaskand dilutetothemark withNANOpure water.
10:90Methanol:2 mM Ammonium Acetate(Mobile Phase EluentA): Add 100 mL of methanol and 900 mL of 2 mM ammonium acetateto a 1000-mL Pyrex bottle. Mix thesolutionthoroughlyand filtetrhesolutiotnhrougha 0.45gM filtewritha vacuum flaskS.toreatambienttemperature.Preparea freshsolutioneverythree months.
90:10 Methanol:2 mM Ammonium Acetate (Mobile Phase Eluent B): Add 900 mL of methanoland 100 mL of 2 mM ammonium acetatetoa I000-mL Pyrex bottle. Mix thesolutionthoroughlyand filtetrhesolutionthrougha 0.45PLM filtewritha vacuum flask.Storeatambienttemperature.Preparea freshsolutioneverythree months.
A.S.0 PREPARATION OF QUALITY CONTROL SAMPLES
A.8.1 Preparation of QualityControl Stock Solutions QC Stock Solution,PFOS (I mg/mL): Weigh approximately5 mg of PFOS (after correctiofnorpurityo)n a microbalanceand transfeirttopolypropylenevial.Dilute
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withtheappropriatveolume ofniethanoltoyielda I mg/mL solution.Storethe solutionat4 OC and bringtoambienttemperaturebeforeuse. Preparea fresh solutionevery threemonths.
A-8.2 Preparation of Serum QC Samples QC4 (DilutionQC, 100 gg/mL PFOS): Add 1000;iL QC Stock Solutiontoa 10mL class"A" volumetricflasktoyielda 100-lig/mLsolutionD.ilutetothemark withcontrolserum,cap and mix.Aliquotsof approximately0.2mL areplacedin polypropylenevialsand storedfrozenat-20 *C.
QC3 (18gg/mL PFOS): Add 450 gL QC StockSolutiontoa 25-mL class"A" volumetricflasktoyielda 18-gg/mL solution.Dilutetothemark withcontrol serum,cap and mix.Aliquotsof approximately0.5mL areplacedinpolypropylene vialsand storedfrozenat-20 'C.
QC2 (6jig/mLPFOS): Add 150 liLof QC StockSolutiontoa 25-mL class"A" volumetricflasktoyielda 6-gg/mL solution.Dilutetothemark withcontrolserum, cap and mix.Aliquotsof approximately0.5mL areplacedinpolypropylenevials and storedfrozenat-20 *C.
QCI (0.2@Lg/mL PFOS): Add I11.1 pL ofQC3 toa I0-mL class"A" volumetric flasktoyielda 0.2-gg/mL solutionD.ilutetothemark withcontrolserum,cap and mix.Aliquotsof approximately0.5mL areplacedinpolypropylenevialsand stored frozenat-20 *C.
A.9.0 LIQUID-LIQUID EXTRACTION PROCEDURE 1. Preparefreshcalibratiosntandardsforeach run accordingtoSectionA.7.4. 2. Thaw QC samples. 3. PrepareQC4 samples(diluteIdin 10)intwo steps:
a)Add 180 liLofcontrolserum and 20 gL ofQC4 into1.7-mL microtubesand
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vortex.
b)Aliquot50 liLofdilutedQC4 intolabeled16 x 100 mm Polypropylenetubes. 4. Aliquot50 liLof each controlblank,zerosample,calibratiosntandarda,nd
qualitycontrolsamples 1-3intolabeled16 x 100 mm polypropylenetubes. Standardsand blanksare-.analyzeidnduplicate.AllQC samplesareanalyzedin replicateosf five. 5. Add ImL of 0.5M tetrabutylammoniumhydrogen sulfatep,H 10 to eachtube. 6. Add 2 mL of0.25 M sodium carbonate/0-2M5 sodium bicarbonatetoeach tube. 7. Add 500 liLof theInternaSltandardWorking Solutionto eachtube(except controlblank,add 500 gL water). 8. Add 5 mL ethylacetatetoeachtube. 9. Shake thetubeson a reciprocaslhakeratmedium speed for20 minutes. 10.Centrifugethetubesat3000 rpm for20 minutesat20 *C. 11.Freezetheaqueous phase inan acetone/dryicebath and keep thetubesinthe bathan additiona5l minutes. 12.Transfertheethylacetatelayertoa fresh,labeled13 x 100 mm polypropylene tube.
13.Evaporatetheethylacetatelayertodrynessina TurboVapTm atapproximately 20 *C undernitrogen.
14.Reconstituttehedriedextractsintwo steps: Add 500 ;iLacetonitrialned vortexfor60 seconds. Then add 500 pL waterand vortexfor60 seconds.
15.Transfer200 gL of theextractoa labeledpolypropyleneautosamplervial.
A.10.0INSTRUMENT CONDITIONS
HPLC Conditions: Eluent(gradient)
Mobile PhaseA: 10:90methanol:2mM ammonium acetate(v/v) Mobile Phase B: 90:10 methanol:2mM ammonium acetate(v/v)
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EluentGradientConditions:
Time (min) 0 1.0 5 5.5 8
Flow Rate Autosampler AutosamplerTemperature InjectioVnolume HPLC Colunm
HPLC Column Temperature TypicalInitiaClolumn Pressure AutosamplerRun Time
%B 45 100 100 45% Stop
300 gL/min. Waters 717plus Ambient 3 to5 gL Keystone BetasilC,,,5 gm particlseize2,.1 mm x 50 mm Ambient 90 bar 8.0minutes
Anal3l
RepresentativReetentionTime (minutes)
PFOS
3.1
Tetra-H-PFOS(IS)
2.9
Mass S.pectrometerConditions:
CurtainGas NebulizerGas TurboIonSprayTm Temperature TurbolonSprayTmAuxiliaryGas
UHP Nitrogen UHP Nitrogen 400 *C LJHP Nitrogenat8 L/min
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IonsMonitored:
Analyte PFOS Tetra-H-PFOS (IS)
IonizatioMnode Ion Spray Voltage DeclusteringPotential MS AcquisitioTnime Pause Time
Ion Monitored m/z = 499.0 m/z = 427.0
NegativeIon -3000 V -35 V 5 minutes 2 ms
Dwell Time
500 ms 500 ms
Calibrattehemass axisof theinstrumentby infusionof Rhodapex mass calibration solutio(nSectionA.5.0)ata flowrateof 10 liL/min.Optimizethesensitiviotfythe instrumentusingan infusionof a 10 jig/mL solutionof theanalyteat 10 AL/min into a flowof 190 pL/min ofmobilephase usingthegradientconditionatwhich the analyteelutesfrom theLC column (100% eluentB). Mass spectrapleak widths shouldbe approximately0.6arnuathalf-height.
One setof calibratiosntandardswas injectedatthebeginningand one setof calibratiosntandardswas injecteadttheend of eachanalyticarlun (tray).
A.11.0 CALCULATIONS
Calculatedconcentrationasrebasedon peak arearatioosf PFOS toTetra-H-PFOS. The peak areafortheanalyteionisdividedby thepeak areaforthecorresponding internalstandardion.
Data generatedfrom samplesinthisstudywere acquiredand integrateudsing PE SCIEX softwareapplicationSsample Control(v.1.3)and MacQuan (v.1.4).The validatiodnatawere formattedintheABS laboratoriynformationmanagement system (Watson,v.5.31..01).Alldatawere rounded tono lessthanthreesignificant figuresby ABS priortoreporting.
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AcceptanceCr teriaforSampleAnalysis CalibratisotnandardTsh:e coefficieonftdetertninat(iro)nmustbe @:0.98A.tleast three-fourthosf theindividualcalibratiosntandardreplicatewsillhave deviations within 15% from theirnominal concentrations.
LLQ acceptancecriteriaA:t leastone replicataetthe LLQ must exhibita deviation within20% from itsnominal concentrationI.fthiscriterioinsnotmet, both replicateasrerejectedand thestandardsatthe nexthigher levelare subjectedtothe same test.
Qualitycontrolsamples:At leasttwo-thirdsof theindividualQC sample replicates willhave deviationswithin 15% from theirnominal concentrationsw,ithatleast one replicateateach QC concentrationmeeting thiscriterion.
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Perfluorooctariesutfonate CAS Number-2750@30-3
ATTACHMENT D DOSE CONFIRMATION
ANALYSES
3M EnvironmentalLaboratory Report No. FACR Tox-108
LaboratoryRequest Number (LRN)-U2779
Propnetaryand Confidential
lox-iuo
Argus 418-014
Study: ProductNumber(Test Substance): Matrix: Method/Revision: AnalyticalEquipment System Number: InstrumentSoflwareNersion: Date ofExtraction/Analyst: Date ofAnalysis/Analyst: Date ofData Reduction/Analyst:
Argus 418-014, Oral (Gavage) Cross-FosterinSgtudy of PFOS
PFOS (T-6295.9)
Twccn Dosing Vehicle
See listori
ETS-8-4.1& ETS-8-5.1 Madeline04lO98 MassLynx 3.2 9/13/99[AS
See Attachm See Attachm See Allachm
9/15/99[AS 9/16/99IAS
Sample Data
Tween Dosing Confirmation
Group Dose
Sample N
QC
B-418-014-B,11/1/98(302ppbMS)
B-418-014-B,1/27/99(302ppbMS)
Group I Control 0.0mgikg/day
B-418-014-A(11/01/98) Diluted1/1
B-418-014-A(1/27/99) Diluted1/1
Group 2 1.6mg/kg/day 0.32mg/ml
B-418-014-B(11/01/98) Diluted1/808
B-418-014-B(1/27/99) Diluted1/808
LimitofQuantitatioLnimit(LOQ) = PFOS = 30 nglg
Method DetectionLimit(MDL): PFOS = 15 ng/g
PFOS = Pcrfluorooctanesulfonate
ExpectedConc. PFOS ng/mi 201 201 0
0
320000
320000
PFOS Cone. ng/mi 199 141
0
0
252516
276069
PFOS % Recovery Accuracy
99% 70% <LOD
<LOD
79%
86%
NR = Sample notreceivednor reported. NA = Not Applicable
Date Entercd/Analyst: DateVeriflcd/Analyst:
9/27/99GML
ETS-8-4.1 Excel97 VersionSR2
AttachmentD FACT Tox-108doseconfirm.xis
Perfluorooctanesutfonate CAS Nuniber-2759-39-3
ATTACHMENT E DATA SUMMARY TABLES
3M EnvimnrrientaLlaboratory ReportNo. FACT Tox-I08
LaboratoryRequest Number (LRN)-U2779
Proprietaraynd Confidential
Perfluorooctanesuffonate CAS Number-2750-30-3
3M EnvironmentalLaboratory ReportNo. FACT Tox-108
LaboratoryRequest Number (LRN)-U2779
Table 1.Concentrations of PFOS in Rat Serum Samples from Study FACT Tox-I08
<LLQ: Less thanthe Lower LimitofQuantitabon(0.05pg/mL)
118899l00011@p
R
p118901 p
18903
18903P
18904
18906
18907
18907P
18908
18909
18910
18910P
18911
18911 P
18912
18913
18913P
18915
18915P
18917
18917P
18918
18918P
18919
18920
18922
18922P
18923
18923P
18924
18924P
18926
18926P
18927
18927P
0.0507 <0LL3LL2QQ3R[@Ol0<.(0O323]<(00.5015)
4.80 35.7 <LLQ[0.04621<(0.05) <LLQ[0.03291<(0.05) 1.35 33.5 2.41 1.06 <LLQ[0.0316]<(0.05) <LLQ[0.03821<(0.05) 0.0798 0.123 <LLQ[0.0376]<(0.05) <LLQ[0.0341]<(0.05) <LLQ[0.0398]<(0.05) <LLQ[0.0221]<(0.05) <LLQ[0.0242]<(0.05) <LLQ[0.0355]<(0.05) <LLQ[0.02211<(0.05) <LLQ[0.0323]<(0.05) <LLQ[0.0247]<(0.05) <LLQ[0.03401<(0.05) 1.96 <LLQ[0.04121<(0.05) <LLQ[0.0367]<(0.05) <LLQ[0.0291]<(0.05) <LLQ[0.0331]<(0.05) 2.72 30.7 <LLQ[0.0323]<(0.05) <LLQ[0.02291<(0.05) <LLQ[0.03051<(0.05) <LLQ[0.0318]<(0.05)
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Table 1.Concentrationsof PFOS inRat Serum Samples from Study FACT Tox-108 (continued)
<LLQ: Less than the Lower LimitofQuantdabon (0.05pg/mL)
lwmi.
18929 18931 18931 P 18932 18934 18934P 18935 18935P 18936 18936P 18937 18938 18939 18939P 18940 18940P 18941 18942 18943 18943P 18946 18947 18948 18950 18951 18951 P 18952 18952P 18953 18953P 18956 18956P 18957 18957P 18958 18958P
2.40 <LLQ[0.0382]<(0.05) <LLQ[0.0196]<(0.05) <LLQ[0.03991<(0.05)
1.25 34.1 <LLQ[0.0316]<(0.05) <LLQ[0.0206]<(0.05) <LLQ[0.0302]<(0.05) <LLQ[0.02301<(0.05) 1.80 <LLQ[0.0359]<(0.05) <LLQ[0.0311)<(0.05) <LLQ[0.03081<(0.05) <LLQ[0.0330]<(0.05) <LLQ[0.02311<(0.05) 5.34 1.12 65.1 82.2 157 86.9 96.1 66.4 72.4 59.2 90.8 48.3 67.0 53.8 97.5 89.3 69.1 93.2 68.3 56.2
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3M EnvircT@-,antaLlaboratory ReportNo. FACT Tox-108
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Table 1.Concentrations of PFOS in Rat Serum Samples from Study FACT Tox-108 (continued) <LLQ. Less thanthe Lower Limd ofQuantitabon(0.05pg/mL)
18959 18960 18960P 18961 18961 P 18963 18964 18964P 18965 18967 18968 18969 18970 18970P 18971 18972 18972P 18973 18973P 18974 18976 18977
59.2 78.0 93.6 69.1 47.6 83.6 85.6 92.9 75.9 74.2 80.9 78.6 99.3 96.9 218 66.9 58.2 81.9 79.5 172 77.9 124
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Table 2. Repeat Analysis of Rat Serum Samples from Study FACT Tox-1 08
<ULQ: Greaterthan theUpper Umft ofQuantitatio(n20.Opg/mL)
I
18903P 18907P
0
Day 14 >ULQ-28.5284>(20)
3
0
Day 14 >ULQ-30.8172>(20)
3
1
35.7
5
35.7
1
1
33.5
5
33.5
1
18924P
0
Day 14 >ULO-27.5496>(20)
3
1
30.7
5
30.7
1
18934P
0
Day 14 >ULQ-36.8737>(20)
3
1
34.1
5
34.1
1
18971
1
Day 14 >ULQ-219.5172>(200)
1
2
218
3
218
2
L
Reasons for Reassay:
1) Run 3 concentration exceeded calibrationrange 2)Run 1 concentratioenxceeded calibratiornange
Reasons forReported Conc:
1)Run 5 concentrabonwithincalibratiornange 2) Run 3 concentratiownithincalibratiornange
Table 3. Pharmacokinetic Subgroup--Concentrations of PFOS Samples from Study FACT Tox-108
<LLO: Less thanthe Lower LimitofQuantftatio(n0.05pg/mL)
in Dam
and LitterSerum
10 -
1
18910
<LLQ[0.03161<(0.05) 1891 OP
1
18911
0.0798
18911 P
1
18913
<LLO[O.0341]<(0.05) 18913P
1
18915
<LLQ[0.0221]<(0.05) 18915P
1
18926
<LLQ[0.0323]<(0.05) 18926P
1
18927
<LLQ[0.0305]<(0.05) 18927P
1
18939
<LLQ[0.031 1]<(0.05)
18939P
1
18940
<LLQ[0.0330]<(0.05) 1894op
11
1895@=
97.5
11
18971
1
218
18956P 18971 P
NA-Sample notassayed. Insufficiesnatmple volume foranalysis.
<LLQ[0.03821<(0.05) 0.123
<LLQ[0.03981<(0.05) <LLQ[0.0242]<(0.05) <LLQ[0.0229]<(0.05) <LLQ[0.0318]<(0.05) <LLQ[0.0308]<(0.05) <LLQ[0.02311<(0.05)
89.3 NA
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Table 4.PFOS Concentrations in Dam and Cross-Fostered LifterSerum Samples by Dosage Group
<LLQ: Less thanthe Lower LimitofQuantitabon(0.05pg/mL)
Sample notreceived
1 1
liurA-@Fl 'i@
1
18903 18907 18908 18909 18918 18920 18924 18929 18934 18936 18937 18941 18942
18901 18904 18906 18912 18917 18919 18922 18923 18931 18932 18935 18938
1
18943
1
18947
1
18948
If
18957
I1
18960
I1
18964
I1
18967
18968
18969 18970
11
18973
11
-1-8974
18946
18950
18951
18952
18953
18958
11
18959
11
18961
11
18963
I1
18965
11
18972
11
18976
18977
4.80 1.35 2.41 1.06 <LLQ[0.0323]<(0.05) 1.96 2.72 2.40 1.25 <LLQ[0.0302]<(0.05) 1.80 5.34 1.12
0.0507 <LLQ[0.04621<(0.05) <LLO[O.03291<(0.05) <LLQ[0.03761<(0.05) <LLO[O.03551<(0.05) <LLO[O.03401<(0.05) <LLQ[0.0412]<(0.05) <LLQ[0.0291]<(0.05) <LLQ[0.03821<(0.05) <LLQ[0.03991<(0.05) <LLQ[0.03161<(0.05) <LLO(O.03591<(O@05)
65.1 86.9 96@ 1 69.1 78.0 85@6 74.2 80-9 78.6 99.3 81.9 172
157 66.4 72.4 90.8 67.0 68.3 59.2 69.1 83.6 75.9 66.9 77.9 124
.11ni
A
18976P
A
18963P
A
18953P
A
18961 P
A
18946P
A
18952P
A
18972P
A
18950P
A
18959P
A
18977P
A
18958P
A
18951 P
A
18965P
B
B
B
B
B
B
B
B
B
B
B
8
1
18931 P 18932P 18938P 18935P 18922P 18923P 18917P
18-9-19P18901 P 189NP 18912P 18906P
c
18968P
c
-18973P
c
18970P
c
18969P
c
18974P
c
18967P
c
18964P
c
18943P
C
18957P
c
18948P
C
18947P
c
18960P
D
18918P
D
18929P
D
18941 P
D
18920P
D
18908P
D
18937P
D
18934P
D
18909P
D
18907P
D
18942P
D
18924P
D
18903P
D
18936P
53.8 47.6 48.3 58.2 -
56.2 59.2
<LLQ(0.01961<(0.05)
<LLQ[0.02061<(0.05) <LLQ[0.03671<(0.05) <LLQ(0.03311<(0.05) <LLQ[0.0221]<(0-05)
<LLQ(0.03231<(0.05)
79.5 96.9 -
92.9 82.2 93.2
93.6
<LLQ(0.0247]<(0.05) 34.1 33.5 30.7
35.7 <LLQ[0.02301<(0.05)
Propnetaryand Confidential
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3M EnvironmentalLaboratory ReportNo. FACT Tox-108
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ATTACHMENT ANALYTICAL
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Title:
QuantitativeDeterminationof Perfluorooctanesulfonate (PFOS) inRat Serum from Study #FACT-TOX-108 Using Turbo Ion Spray LC/MS
Date:
27 August 1999
Authors:
David J.Anderson, M.S. Amie J.Prince,B.S. Holly D. Ross,M.S.
Prepared For:
3M EnvironmentalTechnology and Safety Services St.Paul,MN 55133-3331
ABS Report No.:
99ADJAOI.MI.DOC
Study Protocol:
FACT-TOX-108
Number ofPages:
16
Summary and Conclusions
The concentrationofperfluorooctanesulfona(tPeFOS) was determinedinratserum samples collectedduringthe study #FACT-TOX- 108 usinga sensitives,pecifica,ccurate, and reproducibleanalyticamlethod developed by Advanced BioAnalyticalServices,Inc., Ithaca,NY.
Rat serum samples (50 gL) were extractedby a liquid-liquiedxtractiopnrocedureto isolatePFOS and the internasltandard,1H,IH,2H,2H-perfluorooctanesulfonicacid (Tetra-H-PFOS).Followingevaporationand reconstitutiosna,mple extractswere analyzedby turboion sprayliquidchromatography/mass spectrometry(LC/MS) inthe negativeion mode.
All samples were successfullaynalyzed withinfourruns.The lower limitof quantitation was 0.05 gg/mL forPFOS. The precisionofthisassay(RSD) as deter-minefdrom the analysisof qualitycontrolsamples forPFOS was:54.01%. The precisionof thisassay (RSD), asdeterminedfrom thecalibratiosntandardsforPFOS was:55.83%. The relative error(RE) of the assay,as determined from the analysisof thequalitycontrolsamples ranged from -7.32to 10.1%. The RE of the assay,as determinedfrom the analysisof calibratiosntandardsranged from -5.86to 11.0%.
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SIGNATURE PAGE
QuantitativDeetenninationofPerfluorooctanesulfon(aPtFeOS) in Rat Serum from Study #FACT-TOX-108 Using Turbo Ion Spray LC/MS
ABS ReportNo.: 99
mi c
Reportedby:
MI C David J.Andafson,M.S. Research Scientist
*ZiAt4us-T
Date
Reviewed by:
Authorizedfor Releaseby:
;tzkdo,P.A-4,-mact-
en Cormack, B.S. AssociateAuditor
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99ADJAOI.Mi.DOC
QAUSTATEMENT
Periodincspectioofntshebioanalytipcoarltioonfstudy#FACT-TOX-108were conductedby theQualityAssuranceUnit of Advanced BioAnalyticalServices(AJ3S)for compliancewithEPA GLP regulation(s40 CFR Part792).
The studywas inspectedon thefollowingdates: 22 June 1999; 1,2,7,July1999; 12 August 1999. Resultsof theinspectiownere reportedto ABS Management and PrqjectTeam Leader on: 22 June 1999; 1,2,7,July1999; 12 August 1999. Resultsof theinspectionwsere reportedtotheStudy Directoron 12 August 1999.
Based on theinspectionasnd thedatareviewed,thisreportisa complete and accurate representatioonf thedata.
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99ADJAOI.Ml.DOC
TABLE OF CONTENTS
SIGNATURE PAGE ........................................................2.................. QAU STATEMENT .........................................................3................. TABLE OF CONTENTS .....................................................4................. LIST OF TABLES ...........................................................5................. I. INTRODUCTION ......................................................6.................
1.1.Study Descriptionand Objective.........................................6................. 2. N4ETHODS ............................................................6.................
2.1.AnalyticaPlrocedure(s.)...............................................6................. 2.2.Assay Site...........................................................7................. 2.3.Data Processing.......................................................7................. 3. RESULTS .............................................................7................. 3.1.Assay Performance ....................................................7................ 3.2.AnalyticaRlesultsforStudy #FACT-TOX-108 ............................8................. 4. SUMMARY AND CONCLUSIONS .......................................8................. 5. DATA RETRIEVAL ....................................................8................. 6. REFERENCES .........................................................8................ 7. TABLES ..............................................................9................
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99ADJAOI.Ml.DOC
LIST OF TABLES
Tablel: Summary ofSample and Assay InformationforProtocolFACT-TOX-108 ....9.. Table 2: Inter-AssayPrecisionand Accuracy forPFOS QualityControlSamples inRat
Serum forStudy#FACT-TOX-108 ...................................1.0................. Table3: Inter-AssayPrecisionand Accuracy forPFOS CalibratioSntandardsin Rat
Serum forStudy#FACT-TOX- 108 ...................................I.I................. Table 4: CalibratioCnurve StatistifcosrtheDeterminationof PFOS inRat Serum for
Study #FACT-TOX- 108 ............................................1.2................. Table 5: ConcentrationosfPFOS inRat Serum Samples from Study #FACT-TOX-108
............. ....................................................1.3 ................. Table 6: RepeatAnalysisofRat Senun Samples from Study #FACT-TOX-108 .......16...
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99ADJAOI.Mi.DOC
1. INTRODUCTION
1.1. StudyDescriptiaonndObjective
Theobjectiovfethistudwyastodeterminteheconcentratioofns perfluoroo'ctanesulfo(nPaFtOeS) inratserum samplescollecteduringthestudy#FACTTOX-108, "Oral(Gavage)Cross-FosterinSgtudy of PFOS inRats."Rat serum samples were analyzedusinga liquid-liqueixdtractioannd turboionsprayliquid chromatography/massspectrometr(yLC/MS) assay.
2. METHODS
2.1. AnalyticalProcedure(s)
PFOS concentrationwsere determinedin ratserum accordingtothevalidateLdC/MS method (1).Serum samples(50gL) were extractebdy a liquid-liqueixdtraction procedureusingethylacetatetoisolatPeFOS and theinternasltandard(IS), IH,lH,2H,2H-perfluorooctasnuelfonicacid(Tetra-H-PFOS)from ratserum.Following evaporationtodrynessand subsequentreconstitutiosna,mple extractswere separatedby reversed-phascehromatographyon a 2.1x 50 nun (5 @im)BetasilTmC,,column (KeystoneScientifiIcn,c.B,ellefonteP,A) with an initiamlobilephaseof55% EluentA (10:90methanol:2mM ammonium acetatea)nd 45% EluentB (90:10methanol:2mM ammonium acetate)P.FOS concentrationwsere determinedby turboionsprayliquid chromatography/massspectrometry(LC/MS) inselecteidonmonitoring(SIM) mode. The negativeionsmonitoredwere:
m/z = 499.0forPFOS [M-Klm/z = 427.0forTetra-H-PFOS [M-H]-
Study sampleconcentrationwsere determinedfrom a weighted(I/Y')q,uadratic regressioonf peak arearatios(peakareaof PFOS/peak areaof Tetra-H-PFOS)versus nominal concentratioonftencalibratiosntandards.The nominalconcentrationosf the calibratiosntandardswere 0.05,0.1,0.25,0.5,1,2,4,8, 16,and 20 gg/mL PFOS.
The lowerlimitofquantitati(oLnLQ) forthisassaywas determinedtobe 0.054g/mL PFOS. Qualitycontrol(QC) serum samplesatthreedifferenctoncentration(s0.2,6,and 18 ;ig/mLPFOS) were analyzedwith each assaybatchinreplicateosf four.DilutionQC samples(QC4, 100 jig/mL)were preparedateach dilutiotnhatwas used duringa particulaarssayand were analyzedwith each assaybatchinreplicateosf fourasneeded.
The acceptancecriterifaorcalibratiosntandardsstipulatetdhattheback-calculated concent' rationosf atleasthree-fourthosf theindividuaclalibratiosntandardreplicates must not deviatemore than 15% from theirnominal concentratio(nexceptattheLLQ). At leastone duplicateattheLLQ must exhibita deviationwithin20% of thenominal
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99ADIAOI.MI.DOC
concentration.The coefficieonftdetermination(r')must be @tO.98.The acceptance criterifaollowedareinaccordancewithABS StandardOperatingProcedures.
The acceptancecriterifaorthequalitycontrolsamplesstipulatetdhatatleastwo-thirds of theindividuaQlC sample replicatemsust notdeviatemore than 15% from their nominal concentrationsA.t leastone replicataeteach QC concentratiomnust exhibita deviationwithinl 5%.
A summary of thesample and assayinformationforstudy#FACT-TOX- 108 isgivenin Table 1.
2.2. Assay Site
Allsampleswere analyzedatAdvanced BioAnalyticalServices,Inc.,IthacaN,Y.
2.3. Data Processing
The datawere collecteudsingturboion sprayLC/MS selectedionmonitoring(SIM) in thenegativeionmode. Peak areaswere integratebdy thePE SCIEX program MacQuan, version1.4,residingon a Macintoshcomputer. Followingpeak areaintegratiotnh,e resulttsablesfrom MacQuan were saved as textfileasnd uploadedtotheABS fileserver where a weighted(1/Y'')quadraticregressiownas performedusingthesoftwarepackage Watson (v 5.3.1.01PSS, Inc.,Wayne, PA 19087).Calculationwsere performedon unroundednumbers.Allcalibratiosntandardand QC resultwsere rounded tono lessthan threesignificanftiguresbeforereporting.
3. RESULTS
3.1. Assay Performance
The performanceof theassayforPFOS as determinedfrom theanalysisofdailyquality controlsamplesisdocumented inTable 2. The inter-assapyrecision(RSD) ofquality controlsamplesrangedfrom 1.57to 4.01% forPFOS. There was no marked inaccuracy intheresultfsrom thesequalitycontrolsamples;therelativeerror(R.E)rangedfrom -7.32to 10.1%.
The performanceofdailycalibratiocnurvesisdocumented inTable 3. The inter-assay precision(RSD) of thestandardsranged from 1.11 to 5.83% forPFOS. There was no marked inaccuracyintheresultsfrom thesestandardst;herelativeerror(RE) ranged between -5.86to 11.0%.
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99ADJAOI.Mi-DOC
The slope,y-intercepatn,d coefficienotf determination(r')foreach analyticarlun are presentedinTable 4. The r'valuesranged from 0.9954 to0.9982 forPFOS inmt serum.
AllABS personnelassignedto analyzesamples forthisprojectwere requiredto successfulleyxtractqualitycontrol(QC) samplesand calibratiosntandards.Resultsof theextractiownere reviewedby a trainedanalystagainstthepre-definedacceptance criterifaorthisassay. Resultsaremaintainedinthestudyrecordsof ABS.
3.2. AnalyticalResultsforStudy #FACT-TOX-108
PFOS concentrationisnratserum from Study #FACT-TOX- 108 arepresentedinTableS. Alldatawere rounded tono lessthanthreesignificanftiguresbeforereportinginTableS. Study samplesrequirinrgepeatanalysisforStudy #FACT-TOX- 108 arepresentedin Table 6.
4. SUMMARY AND CONCLUSIONS
The concentratioonf PFOS was determinedinratserum samplescollecteduringthe study#FACT-TOX- 108.
PFOS was isolatefdrom serum by a liquid-liqueixdtractiopnrocedureand determinedby LC/MS.
The qualityofthedeterminationwsas satisfactotrhyroughout.The LLQ was 0.05gg/mL PFOS. The precisionoftheassay,asdeterminedfrom theanalysisof qualitycontrol samples was -<4.01% forPFOS.
5. DATA RETRIEVAL
The calculatecdoncentratiodnatafrom theanalysisof ratserum samplesforStudy #FACT-TOX-108 aremaintainedon fileinthearchivesof theAdvanced BioAnalytical ServicesI,nc.I,thaca,NY inABS Notebook 2319.
6. REFERENCES
1. Advanced BioAnalyticaSlervicesValidationReport99VDJAOI.MI.DOC. Method ValidatiofnortheQuantitatioonfPerfluorooctanesulfon(aPtFeOS) in Rat Serum by Turbo Ion Spray LC/MS. David J.Anderson,M.S. Amie J.Prince, B.S.,and HollyD. Ross,M.S. 26 August 1999.
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99ADJAOI.Ml.DOC
7. TABLES
Table1:
Summary ofSampleand AssayInformatiofnorProtocoFlACT-TOX108
Species/Matrix:
Rat/Serum
SampleCollectiaonndStoragIenformation:
Anticoagulant/Stabilizer: ReportedSample CollectionDates:
Dates Received atA13S: StorageTemperature atABS:
None 7 January 1999 to 29 January 1999 16 June 1999 -20 OC
Assay Information: Assay Period:
22 June 1999 to 28 June 1999
Analyte:
Potassium perfluorooctanesulfonate (PFOS)
AnalyticalStandard:
PFOS
Lot No:
171
Source:
3M
InternaSltandard:
Lot No: Source:
IH, IH,2H,2Hperfluorooctanseulfonicacid (Tetra-H-PFOS) 59909 3M
CalibratioRnange: RegressionMethod: WeightingFactor: Lower LimitofQuantitation: Upper LimitofQuantitation:
quadratic
1/y2
0.05gg/mL 20 pg/mL
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Table2:
Inter-AssParyecisiaondAccuracyforPFOS QualitCyontrol SamplesinRatSerum forStudy#FACT-TOX-108
Run No.
QCI
0.2
PFOS Concentrat(igogn/mL)
QC2
QC3
QC4
QC4
6
18
100
100
(Iin10Dilution()Iin20 Dilution)
1
0.187
6.19
17.5
110
NA
0.192'
6.22
17.3
109
NA
0.191
6.22
17.5
110
NA
0.182
6.14
17.3
108
NA
2
0.191
6.13
16.9
NA
NA
0.191
5.91
16.8
NA
NA
0.190
6.20
16.5
NA
NA
0.192
6.19
16.7
NA
NA
3
0.172
6.02
17.0
114
107
0.174
6.22
16.7
ill
106
0.175
5.94
17.0
110
100
0.177
6.08
17.1
109
103
5
0.184
6.37
17.3
109
NA
0.187
6.36
17.5
113
NA
0.197
6.39
17.5
ill
NA
0.183
6.33
17.1
109
NA
Mean
0.185
6.18
17.1
110
104
RSD (%)
4.01
2.33
1.92
1.57
2.92
RE
-7.32
3.04
-5.00
10.1
3.97
RSD = (SD/Mean) x 100% RE = [(Mean-Nominal)/Nominalx]100%
NA: Not Applicable.
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99ADJAOI.Mi.DOC
cnW)> m C)0
< < z >z
C,3>n
mm zn
Table3:
Inter-AssaPyrecisioannd AccuracyforPFOS CalibratioSntandardsinRat Serum forStu NFACT-TOX-108
Run No. 1
STDI 0.05 0.0479 0.0490
STD2 0.1
0.105 0.112
STD3 0.25 0.240 0.258
2
0.0508 0.102 0.245
0.0503 0.0985 0.240
3
0.0474 0.105 0.237
0.0513 0.109 0.245
5
0.0498 0.0936 0.231
0.0553 0.0982 0.244
Mean
0.0502 0.103 0.242
RSD (%) 4.90
5.83
3.20
RE
0.450
2.82
-3.04
RSD = (SD/Mean) x 100% RE = [(Mean-Nominal)/Nominal]x 100%
PFOS Concentratio(nigimL)
STD4
STD5
STD6
STD7
0.5
1
2
4
0.488 0.891
2.03
4.24
0.509 0.935
2.12
4.51
0.488 0.973
2.07
4.37
0.483 0.970
2.05
4.41
0.476 0.944
2.12
4.52
0.479 0.934
2.07
4.54
0.483
0.952
2.19
4.45
0.507 0.933
2.21
4.47
0.489 0.941
2.11
4.44
2.54
2.71
3.09
2.23
-2.21
-5.86
5.34
11.0
STD8
s
8
7.64
1
8.03
1
7.97
1
7.93
1
7.91
1
7.84
1
7.79
1
7.89
1
7.88
1
1.52
1
-1.55
Page II of 16
I
Table 4:
CalibrationCurve StatisticfsortheDeterminationofPFOS inRat Serum forStudy #FACT-TOX-109
Run No. Quadratic
Linear
Coefficie(nAt) Coefficie(nBt)
1
-0.0007277
0.1225
2
-0.0005896
0.1392
3
-0.0006758
0.1401
5
-0.0004928
0.1345
Mean
-0.0006215--@- 0.1341
y = Ax' + Bx + C, weightedI/y'
Intercept (C)
0.001121 0.0009484 0.001454 0.001190
0.001178
Coefficienotf Determina(tri2)on
0.9959 0.9982 0.9959 0.9954
0.9964
,.mom
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Page 12 of 16
99ADJAOI.Ml.DOC
Table5:
ConcentrationfPsFOS inRatSerumSamplesfromStudy#FACTTOX-108
Rat PFOS Concentration
Number*
(gg/ML)
18901
0.0507
18901P <LLQ[0.0323]<(0.05)
18903
4.80
18903P
35.7
18904 <LLQ[0.0462]<(0.05)
18906 <LLQ[0.0329]<(0.05)
18907
1.35
18907P
33.5
18908
2.41
18909
1.06
18910 <LLQ[0.0316]<(0.05)
1891 OP <LLQ[0.0382]<(0.05)
18911
0.0798
1891 1P
0.123
18912 <LLQ[0.0376]<(0.05)
18913 <LLQ[0.0341]<(0.05)
18913P <LLQ[0.0398]<(0.05)
18915 <LLQ[0.0221]<(0.05)
18915P <LLQ[0.0242]<(0.05)
18917 <LLQ[0.0355]<(0.05)
18917P <LLQ[0.0221]<(0.05)
18918 <LLQ[0.0323]<(0.05)
18918P <LLQ[0.0247]<(0.05)
18919 <LLQ[0.0340]<(0.05)
18920
1.96
18922 <LLQ[0.0412]<(0.05)
18922P <LLQ[0.03671<(0.05)
18923 <LLQ[0.0291]<(0.05)
18923P <LLQ[0.0331]<(0.05)
18924
2.72
18924P
30.7
18926 <LLQ[0.0323]<(0.05)
18926P <LLQ[0.0229]<(0.05)
18927 <LLQ[0.0305]<(0.05)
18927P <LLQ[0.0318]<(0.05)
18929
2.40
*Rat Number with a "P" indicateas
pup sample.
<LLQ: LessthantheLower Limitof
Quantitatio(n0.05gg/mL)
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Page 13 of 16
99ADIAOI.Mi.DOC
Table5:
(ContinueCdo)ncentratioonfsPFOS inRatSerumSamplesfrom Study#FACT-TOX-108
Rat PFOS Concentration
Number*
(gg/ML)
18931
<LLQ[0.0382]<(0.05)
1893 1P
<LLQ[0.0196]<(0.05)
18932
<LLQ[0.0399]<(0.05)
18934
1.25
18934P
34.1
18935
<LLQ[0.0316]<(0.05)
18935P
<LLQ[0.0206]<(0.05)
18936
<LLQ[0.0302]<(0.05)
18936P
<LLQ[0.0230]<(0.05)
18937
1.80
18938
<LLQ[0.0359]<(0.05)
18939
<LLQ[0.031 1]<(0.05)
18939P
<LLQ[0.0308]<(0.05)
18940
<LLQ[0.0330]<(0.05)
18940P
<LLQ[0.0231]<(0.05)
18941
5.34
18942
1.12
18943
65.1
18943P
82.2
18946
157
18947
86.9
18948
96.1
18950
66.4
18951
72.4
18951P
59.2
18952
90.8
18952P
48.3
18953
67.0
18953P
53.8
18956
97.5
18956P
89.3
18957
69.1
18957P
93.2
18958
68.3
18958P
56.2
*Rat Number with a "P" indicateas
pup sample.
<LLQ: Less thantheLower Limitof
Quantitatio(n0.05@Lg/mL)
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Page 14 of16
99ADJAOI.Ml.DOC
Table 5:
(Continued)ConcentrationsofPFOS inRat Serum Samples from Study #FACT-TOX-108
Rat
PFOS Concentration
Number*
(;Ig/ML)
18959
59.2
18960
78.0
18960P
93.6
18961
69.1
18961P
47.6
18963
83.6
18964
85.6
18964P
92.9
18965
75.9
18967
74.2
18968
80.9
18969
78.6
18970
99.3
18970P
96.9
18971
218
18972
66.9
18972P
58.2
18973
81.9
18973P
79.5
18974
172
18976
77.9
18977
124
*RatNumber witha "P" indicateas
pup sample.
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Page 15 of 16
99ADJAOI.Mi.DOC
m 1>
mbo 11)>< <Z>
Cm))>znm !n 0
zn
Table 6:
Repeat Analysisof Rat Serum Samples from Study #FACT-TOX-108
Rat Treatment Time Number*
Original Conc. ug/ml
Original Curve Number
18903P 18907P 18924P 18934P 18971
0 Day 14 >ULQ-28.5284>(20)
3
0
Day 14 >ULQ-30.8172>(20)
3
0
Day 14 >ULQ-27.5496>(20)
3
0
Day 14 >ULQ-36.8737>(20)
3
1
Day 14 >ULQ-219.5172>(200)
1
>ULQ: Greaterthanthe Upper Limitof Quantitation. *Rat Number with a "P" indicatesa pup sample.
Reason for
Reassay
1 1 1 1 2
Reassay Conc. ug/mi
35.7 33.5 30.7 34.1 218
Reassay Curve Number
5 5 5 5 3
REASONS FOR REASSAY: 1).Run 3 concentratioenxceeded calibratiornange. 2).Run I concentrationexceeded calibratiornange. REASONS FOR REPORTED CONC: 1).Run 5 concentratiownithincalibratiornange. 2).Run 3 concentratiownithincalibratiornange.
Reported Conc. ug/mi
35.7 33.5 30.7 34.1 218
Page 16 of 16
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ADDENDUM
TO THE BIOANALYTICAL
REPORT
Title:
Addendum - QuantitativeDeterminationof PerfluorooctanesuIfonate(PFOS) in Rat Serum from Study #FACT-TOX-108 Using Turbo Ion Spray LC/MS
Date:
13 October 1999
Addendum Report: 99ADJAOI.MI.ADD.DOC
OriginalReport: 99ADJA01.MI.DOC
Authors:
David J. Anderson, M.S. Amie J.Prince,B.S. Holly D. Ross, M.S.
Prepared For:
3M Environmental Technology and SafetyServices St.Paul, MN 55133-3331
Number of
Pages:
3
15 Catherwood Road a Ithaca,New York 14850 a (607) 266-0665 o Fax (607) 266-0749
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Title:
SIGNATURE PAGE
Addendum - QuantitativeDeterminationof Perfluorooctanesulfona(tPeFOS) inRat Serum from Study #FACT-TOX- 108 Using Turbo Ion Spray LC/MS
ABS Report No.: 99AD I.Mi. DOC
Reported by:
3
David J.Andddso-n,M.!@.
Date
Research Scientist
Reviewed by:
.*eathllee"nCSo@ ack,B AssociateAuditor
Authorizedfor Release by:
John RIPerkins,Ph.D. AssistahtScientifiDcirector
Accepted by:
I /,@ KrisHanson,Ph.D.
3M Study Director
Date
Date
4 Date
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Page 2 of 3
99ADJAOI.Ml.ADD.DOC
ADDENDUM SUMMARY
ADDENDUM Additionof Study Directorsignatureon the SignaturePage. The signaturepage of thisaddendum indicateascceptanceof the originalreport.
REASON FOR ADDENDUM OriginalGLP reportrequiresthe signatureof the Study Director.
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Page 3 of 3
99ADJAOI.Mi.ADD.DOC
Perfluomoctariesuffonate CAS Number-2759-39-3
ATTACHMENT G REPORT SIGNATURE PAGE
3M EnvironmentalLaboratory ReportNo. FACT Tox-108
LaboratoryRequest Number (LRN)-U2779
KrifteJ-.n'HansenP,h.D.S,tudyDirector
Date
MarvinT Case,D.V.M.,Ph.D.,Sponsor Representabve
gate
DaleL.Bacon,LaboratorMyanager
Date
Propnetaryand Confidenbal
StudyTitle AnalyticLaalboratoRreyporotntheDeterminatoifotnhePresencaendConcentratoifon
Perfluorooctanesulfona(tPeFOS) intheSerum of Sprague-Dawley"Rats Exposed toPotassiumPerfluorooctanesulfonavtieaGavage
REPORT AMENDMENT NO. I
Amendment Date: 19 April2000
Petforming Laboratory 3M EnvironmentalTechnology & SafetyServices
3M EnvironmentalLaboratory 935 Bush Avenue St.Paul,NlN 55106
Laboratory Project Identification ET&SS LRN-U2779
ET&SS FACT Tox-108
3M EnvironmentaLlaboratofy
FACT Tox-108 ReportAmendment No.1
Thisamendment modifiesthefollowinpgortion(so)fthefinalreport:
1. FINAL REPORT. Make thefollowiandgdititoonthefinarleporttext.
ADD:
Aftetrhefinarleporwtasissue(dsigneadndarchiveidt)w,asdiscovertehdathepurity valuesstatedfortheanalyticarleferencematerialand testsubstancewere inaccurateT.hese valueswere based onlyon NMR analysesS.ubsequentchemicalcharacterizatiiosnoccurring to determinetheactualpurityofthesessubstances(PFOS Lot 171 and 217).The finalreport willbe amended to detaitlheanalyticarlesultussingthepurityvaluesfrom thecertificatoefs analysiswhen theyareissuedforPFOS Lot 171 and 217.
REASON:
To describethechangesthatwillbe made to thefinalreportwhen thecertificaotfeanalysis isissuedforPFOS Lot 171 and 217.
2. FI)VAL REPORT. Make thefollowingadditiontotheexceptionslisitntheStatementof Compliance section.
AMEND To READ:
The purityand stabilitoyf thetestsubstanceand analyticarleferencematerialare unknown and was notdeterminedpriortotheinitiatiofnthisstudy.
REASON:
The Statementof Compliance sectionwas incomplete.
3. FINAL REPORT. The purityof thetestsubstanceis99.28% (Lot217),and analyticarleferencematerialis 99.49% (Lot171)aslisteidnTable2.
AMEND TO READ:
The purityofthetestsubstanceand analyticarleferencmeaterialisteidnTable2 is unknown.
REASON:
The purityvaluesstatedforthetestsubstanceand analyticarleferencemateriallisteidnTable 2 areincorrect.
3M EnvironmentaLlaboratory
FACT Tox-108 ReportAmendment No.I
Amendment Approval
T-Ca,4,
M@@in T.Case,D. V.M, Ph.D.,SponsorRepresentative
Date
Kristen J Hansen, Ph.D., Study Director
Date
3M EnvironmentalLaboratory