Document byqKLkJB3rkd1bybpbENRJGnO
lAbOMtDry ComposiRteport AnalyticaRleportsofData for FluorochemicalAnalysisinHuman Sera
LIEMS No. 1623
TestingLaboratory 3M EnvironmentaTlechnology& SafetyServices
3M EnvironmentalLaboratory FluorineAnalyticaClhemistryTeam (FACT)
2-3E-09 935 Bush Avenue, St.PauL MN 55106
Laboratory Cont"t KrisHansen,Ph.D.
Bldg.2-3E-09 P.O.Box 3331 St.Paul,MN 55133-3331 Phone: (651)778-6018 FAX: (651)778-6176
Requesters LarryZobel,JeffMandel,Gemy Olsen
3M MedicalDepartment Bldg.220
St.Paul,MN
page I
3MDnIMONMENTAL LABORA7'ORY
.....................
no compositereportmciudestentechnicarleporttshatwere issuedtothe3M MedicalDepmunat btween March 2,1998and April24,1998.Each mpm do=ncits theresultosfanalysiosfhuman 9= mniples collectefdromvarious==. Inmost am, eachtechnicarleporitncludemsformatlonaboutthedateof ddiveryofthedatatotherequesterI.aterpretatiomftheresultisstheresponsibiliotfythe3M Medical
Departrnerd-
Althoughrigorousqualitcyontrolmeasuresand 3M EnvironmentalLaboratoryStandardOpwating
Proceduresand methodswere followedwhen possiblet,heaoqmmttonoftlusdatawas notn==* coum-tedaccordingtoapplicablGeood LaboratoryPracticesD.ata was collectetdomad m=mbate needsto helpd@ar@ thepotentiaflorfunmn healthconcernsi;twas notalwayspossiblteofollowlaboratory proceduresthatwere inplaceatthefim. Data was wdnic@ mvL-@@ by 3M Ew&oumemW Lab technical st4 butwas notrewev@vdby theQualityAssuranceUmt inpl= at3Ni
Appendix A includetsheanalyticanlzdwds thatwere followedinthecollectioonfthedatam44xfftindgxw
technicarleports.
ETS-8-4.1ExtractioonfPotassiumPcrflwroocLmesWfonateorodia FluorocbemicalQmmgpdg
Serum forArahsis UsingHPLC-Elecftospray/h4ass
withthefollowingmeptlon: ethylacetate
was added totheaqueousexuw insteaotfiMME.
ETS-&5.1 AnalysisofPotassiumPeffluorow==Mnate orotherFluorochemicaClormxxmds inSenun
ExtractsUsingIHPLC&LeqMEMA4ass
. Data kduded inthePhaseI[andPhase M reports
was collecteudsingESHE, whiledataforsubsequentphaseswere collecteudsingESMSIZ. Detailcsanbe
foundineachWJmical reporti,ncludedinAppendicesB ftmgh K
ChromalogaphicdataforeachUdinicalreporitsmdived atthe3M En*mnenW Lab.
KrisHan-wA Ph.D.,P&icipalAnalyticaklxestiptor
Date
Appendix A: AnalyticaMlethods
Appendix B: Phase2 Appendix C: Phase3
Appendix D: Phase4 Appendix E:Phase 5
Appendix F: Phase6 Appendix G: Phase7 Appendix H: Phase8 Appendix 1:Phase 9,partI Appendix J:Phase 9,part2 AppendixK: Summary ofPOAA Imb
forPhases2-9
Page 2
3M ENviRoNwNTAL
LABORATORY
METHOD
ExTRAcTiON OF POTASSIUM PERFLUOROOCTANESULFONATE
FLUOROCHEMICAL
COMPOUNDS FROM SERUM FOR ANALYSIS
ELECTROSPRAY/MASS
SPECTROMETRY
OR OTHER USING HFLC-
Method Number: ETS-84.1
Adoption Date: 03/01/99
Author: Lisa Clemen, Glenn Langenburg
Revision Date:
Approved By:
LaboratoryManager
Date
Group Leader
Date
TechnicalReviewer
Date
1.0 SCOPE Am APPLicATioN
1.1 Scope: This method isforthe extractioonf potassiumperfluorooctanesulfona(tPeFOS) or otherfluorochemicaclompounds from serum.
1.2 Applicable compounds: Fluorochemicalsurfactantosr otherfluorinatecdompounds.
1.3 Matrices: Rabbit,rat,bovine,monkey, and human serum or otherfluidsas designatedin thevalidationreport.
Word 6/95
ETS-9-4.1 Extractionof PFOS from Senun
Page I of 14
2.0 SUMMARY OF METHOD
2.1 This method describetsheprocedureforextractinpgotassiumperfluorooctanesulfonate (PFOS) or otherfluorochen@caslurfactantfsrom serun-o4r otherfluidsu,singan ion pairingreagentand methyl-tert-buteytlher(MtBE). Inthismethod,sevenfluorochemicals were extractedP:FOS, PFOSA, PFOSAA, ETFOSE-OI-L PFOSEA, M556, and surrogate standard(see3.0 Definitions)A.n ionpairingreagentisadded to thesample and the analyteionpairispartitioneidntoMTBE. The MTBE extractisremoved and put onto a nitrogenevaporatoruntildry.Each extractisreconstitutiend1.0mL of methanol,then filteretdhrougha 3 cc plastiscyringeattachedto a 0.2limnylonfilteirntoglassautovials.
2.2 These sample extractasreanalyzedfollowingmethod ETS-8-5.1 or otherappropriate method.
3.0 DEnNrrioNs 3.1 PFOS: perfluorooctanesulfona(taenionofpotassiumsaltC)sFl7S% 3.2 PFOSA: perfluorooctanseulfonylamidCegFl,7SO2NH2
3.3 PFO SAA: perfluorooctanseulfonylamido(ethyl)acetaCtieF 17SO2N(CH2CH3)CH2CO2
3.4 ETFOSE-OH: 2(N-ethylperfluorooctasnuelfonaniido)-etahlyclohol
CSF17SO2N(CH2CH3)CH2CH20H
3.5 PFOSEA: perfluorooctanseulfonyelthylamideC8Fl7SO2N(CH2CH3)H
.3.6 M556: Cl@F17SO2N(H)(CH2COOH)
3.7 Surrogatestandard:IH- IH-2H-2H perfluorooctanseulfoniaccid
4.0 WARNINGS AND CAUTIONS
4.1 Healthand safetywarnings 4.1.1 Use universaplrecautionse,specialllyaboratorcyoats,goggles,and gloveswhen handlinganimaltissuew,hich may containpathogens.
5.0 INTERFTRENCFs
5.1 There areno interferenckensown atthistime.
6.0EouipmzNT
6.1 The followingequipmentisusedwhileperformingthismethod. Equivalentequipmentis acceptable. 6.1.1 Vortexmixer,VWII, VortexGenie2 6.1.2 CentrifugeM,stral 1000orEEC 6.1.3 Shaker,EberbachorVWR 6.1.4 NitrogenevaporatorO,rganomation
ETS-8-4.1 ExtractionofPFOS kom Senun
Page 2 of 14
6.1.5 Balance(0.100g)
7.0 SUPPLIES AND MATERJALS
7.1 Gloves
7.2 Eppendorf or disposablepipettes 7.3 Nalgene bottles,capableof holding250 mL and I L 7.4 Volumetric flasks,glass,type A 7.5 I-CHEM vials,glass,40 niL glass 7.6 Centrifugetubes,polypropylene,15 mL 7.7 Labels 7.8 Oxford Dispenser -,-3.0to 10.0 mL 7.9 Syringes,capable of measuring 5 pL to 50 pL 7.10 Graduated pipettes 7.11 Syringes,disposableplastic3, cc 7.12 Syringefiltersn,ylon,0.2 gm, 25 mm 7.13 Timer 7.14 Crimp cap autovialsand caps 7.15 Crimpers Note: Priorto using glasswareand bottlesr,inse3 times with methanol and 3 times with
NM-QTMwater. Rinse syringesa minimum of 9 times with methanol,3 rinsesfrom 3
separate vials.
8.0 REAGENTS AM STANDARDS 8.1 Type I re!y4ntgrade water,NM-QTM or equivalent;allwater used inthismethod should
be Mflli-Q water and may be providedby a MM-Q TOC Pluim system 8.2 Sodium hydroxide (NAOM, J.T Baker or equivalent 8.3 Tetrabutylammorium hydrogen sulfate(TBA),Kodak or equivalent 8.4 Sodium carbonate(Na2C03), J.T.Baker or equivalent 8.5 Sodium bicarbonate(NaHC03), J.T.Baker or equivalent 8,6 Methyl-T-Butyl Ether,Omnisolv, glassdistilleodr BPLC grade
8.7 Methanol, Omnisolv, glassdistilleodr EPLC grade 8.8 Serum or blood,frozenfrom supplier 8.9 Fluorochemical standards
8.9.1 PFOS (3M SpecialtyChemical Division),molecularweight = 538 8.9.2 PFOSA (3M SpecialtyChemical Division),molecularweight = 499 8.9.3 PFOSAA (3M SpecialtyChemical Division),molecularweight = 585
ETS-8-4.1 ExtmctioonfPFOS fromSenun
Page3 of14
8.9.4 ETFOSE-OH (3M SpecialtCyhemicalDivision)m,olecularweight= 570
8.9.5 PFOSEA (3M SpecialtCyhemicalDivision)m,olecularweight= 527
8.9.6 M556 (3M SpecialtCyhemicalDivision)m,olecularweight= 557
9.9.7 Surrogatestandard4:-H, perfluorooctanseulfoniaccid(I-K I-I-L2-K 2-H CsFl3SO3H) molecularweight= 428
8.9.8 Other fluorochemicalsa,s appropriate
8.10 Reagent preparation
NOTE: When preparinglargervolumes thanlisteidnreagent,standardo,r surrogate preparationa,djustaccordingly.
8.10.1 10 N sodium hydroxide(NaOIi):Weigh approximately200 g NAOH. Pour intoa 1000 mL beakercontainin5g00 mL NM-i:fm water,mix untilallsolidsare dissolved.Storeina IL Nalgenebottle.
8.10.2 1 N sodium hydroxide(NaOH):. Dilute10 N NAOH 1:10. Measure 10 mL of 10 N NAOH solutioinntoa 100 mL volumetricflaskand dilutteo volume usingMUiQTm water. Storeina 125 mL Nalgene bottle.
.8.10.30.5M tetrabutylammoniuhmydrogen sulfat(eTBA):Weigh approximately169 g ofTBA intoa I L volumetriccontainin5g00 mL MI-Q" water.AdjusttopH 10 usmg approximately44 to 54 mL of 10 N NAOH (WhileaddingthelastmL of NAOK add slowlybecausethepH changesabruptly)D.ilutetovolume withNMwater. Storeina I L Nalgenebottle.
8.10.3.1TBA requiresa check priorto eachuseto ensurepH =.10. Adjustas neededusing I N NAOH solution.
8.10.4 0.25 M sodium carbonate/sodiumbicarbonatebuffer(Na2C03/NaHC03):
Weigh
approximately26.5g of sodium carbonate(Na2C03) and 21..O-ogf sodium
bicarbonate(NaHC03) intoa I L volumetricflaskand bring'to-volumweithNEE-@.
QTm water. Storeina 1 L Nalgene bottle.
8.11 Standards preparation'
8.11.1 PreparePFOS standardsforthestandardcurve.
8.11.2Prepareotherfluorochemicasltandardsa,sappropriateM.ulticomponent fluorochemicasltandardsareacceptable(forexample,one working standard solutioncontaining1.00ppm PFOS, 1.02ppm PFOSA, 0.987ppm PFOSAA, and 1.10 ppm EtFOSE-OH.)
8.11.3Weigh appro)dmately100 mg of PFO S intoa 100 mL volumetricflaskand record the actualweight.
8.11.4Bring to volume withmethanolfora stockstandardof approximately1000 ppm
(@L9/ML).
8.11.5 Dilutethe stocksolutionwithmethanol fora working standardI solutionof approximately50 ppm.
8.11.6 Diluteworking standardIwithmethanolfora workingstandard2 solutionof approx.5.0 ppm.
ETS-84.1 ExtractioonfPFOS from Senun
Page 4 of14
8.11.7DiluteworkingstandardI withmethanolfora workingstandard3 solutionof approx.0.50ppm.
8.12 Surrogate stockstandard preparation
8.12.1 Weigh approximatel5y0-60 mg ofsurrogatestandardI-K I-K 2-K 2-K CgFl3SO3H intoa 50 mL volumetrifclaskand recordtheactualweight.
8.12.2 Bringto volume withmethanolfora surrogatestockof approximately1000-1200 PPM.
8.12.3Preparea surrogateworking standard.TransferapproximatelyI mL of surrogate stockto a 10 mL volumetricflaskand bringto volume withmethanolfora Working standardof 100 ppm. Record theactualvolume transferred.
9.0 SAWLF, HANDL]ING 9.1 AU samplesarereceivedfrozenand must be kept frozenuntilthe extractioinsperformed.
9.2 Allow samplesto thaw to room temperaturepriorto extraction.
10.0 OuALrry CoNTRoL
10.1 SolventBlanks,Method blanks and matrix blanks 10.1.1An aliquotof 1.0mL methanolisused as a solventblank.
10.1.2Extracttwo 1.0mL aliquotosfl@ffi-Ql"waterfollowingthisprocedureand use as method blanks.
10.1.3 Extracttwo 1.0mL aliquotosftheserum followingthisprocedureand use a's matrixblanks.See 11.1.4.
10.2 Matrixspikes 10.2.1 Prepareand analyzematrixspikeand matrixspikeduplicatesamplesto determine theaccuracyof theextraction. 10.2.2 Prepareeach spikeusinga sample chosenby theanalystu,suallythecontrolmatrix receivedwitheach sample set. 10.2.3 Expected concentrationwsillfalilnthemid-rangeoftheinitiaclalibratiocnurve. Additionalspikesmay be includedand may fallinthelow-rangeoftheinitial calibratiocnurve.
10.2.4 Prepareone matrixspikeand matrixspikedupecateper 40 samples,with a minimum of2 matrixspikesperbatch.
10.3 Continuingcalibratiocnhecks 10.3.1Preparecontinuingcalibratiocnheck samplesto ensuretheaccuracyoftheinitial calibratiocnurve.
10.3.2 Prepare,ata minimum, one continuingcheck pergroup of IO'samples.For example,ifa sampleset= 34,fourchecksarepreparedand extracted.
10.3.3 Prepareeach continuingcalibratiocnheck from thesame matrixused to prepare theiniticaulrve.
ETS-8-4.1 ExtractioonfPFOS from Sennn
Page 5 of14
10.3.4 The expectedconcentrationwsillfallwithinthemid-rangeof theinitiaclalibration curve.Additionalspikesmay be includedthatfallinthelow-rangeof theinitial calibratiocnurve.Thisisnecessaryiftheanalystmust quantitatuesingonly the low end ofthecalibraticounrve(forexample,5 ppb - 100 ppb,ratherthan 5 ppb - 1000 ppb).
11.0 CALIBRATION AND STANDARDIZATION
11.1 Preparematrixcalibratiosntandards
11.1.1TransfeIrmL ofserumtoa 15 mL centrifutguebe.
11.1.2 Ifmost samplevolumes arelessthan 1.0mL, extractstandardswith matrix volumes equalto thesamplevolumes. Do not extractlessthan0.50mL of matrix. Record each sample volume on theextractionsheet.
11.1.3 While prepa#nga totaloftwenty aliquotisn15 mL centrifugteubes,mix or shake between aliq@uots.
11.1.4 Two I mL aliquotso,r otherappropriatveolume,serveas matrixblanks.Typically use thestandardconcentrationasnd spikingamounts listedinTable 1,attheend of thissectiont,o spike,induplicatet,wo standardcurves,fora totalof eighteen standardst,wo matrixblanks,and two method blanks.
11.1.5Referto validatiorneportETS-8-4.0 & ETS-8-5.0-V-1,which listtsheworking rangesand theLinearCalibratioRnange (LCR) forcalibratiocnurves.
11.1.6Use AttachmentD as an aidincalculatintgheconcentrationosf theworldng standards.See Section13.0to calculataectualconcentrationosfPFOS'in calibratiosntandards.
11.2 To each standardb,lank,or continuingcheck,add appropriataemount of surrogate working standardfortheconcentratiotno falwlithinthecalibration.cuir-avnege 5 ppb 1000 ppb.
11.3 Extractspikedmatrixstandardsfollowing12.6-12.16ofthismethod. Use thesestandards to establisehach initia6l@@e on the mass spectrometer.
ETS-8-4.1 Extractionof PFOS from Senun
Page 6 of 14
Table 1
Approximate spikingamounts forstandardsand spikes
Usi g 1.0ML of matrix
Working standard (approxc.onc.)
ILL
Approx.finaclonc.of
analyteinmatrix
-
-
Blank
0.500 ppm
10
0.005 ppm
0.500 ppm
20
0.010 ppm
5.00 ppm
5
0.025 ppm
5.00 ppm
10
0.050 ppm
5.00ppm
20
0.100 ppm
50.0pprn
5
0.250ppm
50.0ppm
10
0.500ppm
50.0ppm
15
0.750 ppm
50.0ppm
20
1.00ppm
12.0 PROCEDURE
12.1 Obtainfrozensamplesand allowto thaw atroom temperatureor in a lukewarm waterbath.
12.2 Vortexmix for15 seconds,thentransfe1r.0mL or otherappropriatveolume to a 15 niL polypropylenecentrifugteube.
12.3 Return unused samplesto freezerafterextractioanmounts have been removed. 12.4 Record theinitiavlolume on theextractiownorksheet.
12.5 Label thetubewith thestudynumber,sampleBD, dateand analystinitialsS.e.e attached worksheet fordocumentingthe remainingsteps.
12.6 Spikeallsamples,includinbglanksand standardsr,eadyforextractiownith surrogate standardas describedin11.2.
12.7 Spike each matrixwiththeappropriateamount of standardas describedin11.1,or Table 1 inthatsectionf,orthecalibratiocnurvestandards.Also preparematrixspikesand continuingcalibratiosntandards.
12.8 Vortex mix thestandardcurvesamples,matrixspikesamples,and continuingcalibration samplesfor 15 seconds.
12.9 Check to ensurethe0.5 M TBA reagentisatpH 10. Ifnot,adjustaccordingly.
12.10 To each sample,add I mL 0.5M TBA and 2 mL of 0.25M sodium carbonatelsodium bicarbonatebuffer.
12.11 Using an Oxford Dispenser,add 5 mL methyl-tert-buteytlher. 12.12 Cap each sample and put on theshakerata settingof 300 rpm, for20 minutes. 12.13 Centrifugefor20 to25 minutesata settinogf3500 rpm, or untilayersarewellseparated.
ETS-8-4.1 ExtractioonfPFOS from Serum
Page 7 of 14
12.14Labelafres1h5mL centriftuugbeewiththesameinformataisoinn12.5. 12.15Remove4.0mL oftheorganilcayetrothicslea1n5mL centriftuugbee. 12.16 Put each sampleon theanalyticanlitrogenevaporatoruntildry,approximatelyI to 2
hours. 12.17 Add 1.0mL of methanolto eachcentrifugteubeusinga graduatedpipette. 12.18 Vortex mix for30 seconds. 12.19 Attach a 0.2 gm nylonmesh filtetro a 3 cc syringeand transfetrhesample to thissyringe.
Filterintoa 1.5mL glassautoviaolr low-volume autoviawlhen necessary. 12.20 Label theautovialwith thestudynumber,animalnumber and gender,sampletimepoint,
matrix,finalsolvente,xtractiodnate,and analyst(sp)erformingtheextraction. 12.21 Cap and storeextractastroom temperatureor atapproximatel4y 'C untilanalysis. 12.22 Complete theextra@@onworksheet,attachedtothisdocument,and tapeinthestudy
notebook or includeinstudybinder,asappropriate.
13.0 DATA ANALYSIS ANID CALCULATIONS
13.1 'Calculations 13.1.1 CalculateactualconcentrationosfPFOS, or otherapplicablfeluorocherinicianl, calibratiosntandardsusingthefollowingequation: mL of standardx concentratioonf standard(gg LLIQ mL of standard+ mL of surtogatestandard+ initimaaltrixvolume (mL)
FinalConcentratio(n4mL) ofPFOS inmatrix
14.0 MIETHOD PFMORMANCE 14.1 The method detectiolnimit(MDL) isanalyteand matrixspeciflcR.efertoMDL report
forspecifiNcML and ffiniotfquantitati(oLnOQ) values(seeAttachments B and C). 14.2 The followingqualitycontrolsamplesareextractewditheachbatch of samplesto evaluate
thequalityoftheextractioannd analysis. 14.2.1Method blanksand matrixblanks. 14.2.2Matrix spikeand matrixspikeduplicatseamplesto determineaccuracyand
precisioonf theextraction. 14.2.3 Continuingcalibratiocnheck samplesto determinethecontinuedaccuracyofthe
initiaclalibratiocnurve. 14.3 Referto section14 of ETS-8-5.1formethod performancecriteria.
15.0 POLLUTION PREVENTION AND WASTE MANAGEMZNT
15.1 Sample waste isdisposedinbiohazardcontainersf,lammablesolventwaste isdisposedin highBTU containersa,nd used glasspipettewaste isdisposedinbroken glasscontainers locatedinthelaboratory.
ETS-8-4.1 ExtractioofnPFOS fromSenun
Page8 of14
16.0RFcoRDs
16.1 Complete theextractiownorksheetattachedto thismethod,and tapeinthe study
notebook or includeinthe 3-ringstudybinder,as appropriate.
17.0 ATTAcHmzNTs 17.1 Attachment A, Extractionworksheet 17.2 Attachment B, L@MLJLOQ valuesand summary 17.3 Attachment C, Calibrationstandardconcentrationworksheet
18.0 REFIZRENCES
18.1 The validationrepoit associatedwith thismethod isETS-8-4.0 & S.O-V-l.
18.2
FACT-M-3. 1,"Analysis of Senun or Other Fluid Extractsfor Fluorochemicals using IHPLC-ElectrosprayMass Spectrometry"
19.0 AFncrED DocummNTs
19.1 ETS-8-5. 1, "Analysisof Serum or Other FluidExtractsforFluorochemicalsusingBPLCElectrosprayMass Spectrometry"
20.0 RFvisioNs
Revision Number
I
Reason For Revision Section 12.21 Changed to includesample storage atroom temperature. Section 12.13 Added the shaker speed. Section 12.17 Finalvolume is1.0mL; not adjustedforinitiavlolumes less than 1.0mL.
Revision Date
04/02/99
ETS-8-4.1 ExtractionofPFOS from Senun
Page 9 of 14
3M ENvmoNwNTAL
LABORATORY
METHOD
ANALYSIS
OF POTASSIUM PERFLUOROOCTANESULFONATE
OR OTHER
IFLUOROCHEAUCALS IN SERUM ExTRAcTs USING
HPLC-ELECTROSPRAY/MASS
SPECTROMEETRY
Method Number: ETS-8-5.1
Author: LisaClemen,RobertWynne Approved By:
Adoption Date: 03/01/99 RevisionDate:
LaboratoryManager
Date
Group Leader
Date
TechnicalReviewer
Date
l.b SCOPE AND APPLICATION 1.1Scope: Thismethod describesthe analysisof serum extractsforfluorochemicalsurfactants
usingBPLC-electrospray/massspectrometry.
1.2Applicable Compounds: Fluorochemicalsurfactantosr otherIluorinatecdompounds, or otherionizablecompounds.
1.3 Matrices: Rabbit,rat,bovine,monkey, and human serum,or otherfluidsas designatedinthe validatiorneport.
Word 6/95
ETS-8-5.1 AnalysisofSenun ExtractUsing ES/A4S
Page Iof9
2.0 SUMMARY OF METHOD
2.1 Thismethod describetsheanalysisof fluorochemicaslurfactantesxtractedfrom serum or otherfluidsu,singBPLC-electrospray/massspectrometryo,r similasrystemas appropriate. The analysiissperformedby monitoringa singleioncharacteristoifca particular fluorochemicals,uchas theperfluorooctanesulfona(tPeFOS) anion,nVz--499. Additionallys,amplesmay be analyzedusinga tandem mass spectrometerto furtherverify theidentitoyf a compound by detectingdaughterionsoftheparention.
3.0 DEFUGTIONS 3.1 Atmospheric PressureIonization(API):The Mcromass QuattroI[t[riplqeuadrupole
systemsallowforvariousmethods of ionizatiobny utilizivnagrioussources,probes,and interfacesT.heseincludebut arenot limitedto:ElectrospraIyonizatio(nESI),Atmospheric PressurechemicalIonizatio(nAPcl),Thermospray,etc.The ionizatiopnrocessinthese techniquesoccursatatmosphericpressure(i.e.n,otunder a vacuum).
3.2 ElectrosprayIonization(ES, ESI): a method ofionizatiopnerformedatatmospheric pressurew,hereby ionsinsolutionaretransferretdothegasphase viatinychargeddroplets. These chargeddropletsareproduced by theapplicatioonfa strongelectricaflield.
3.3 Mass Spectrometry, Mass Spectromete r (MS), Tandem Mass Spectrometer (MS/MS): The API QuattroH triplequadrupolesystemsare equippedwith quadrupole mass selectivdeetectors.Ionsareselectiveldyiscriminatebdy mass to chargeratio(nVz)and subsequentldyetected.A singleMS may be employed foriondetectionor a serie(sMS/MS) formore specififcragmentatioinnformation.
3.4 Conventional vs.Z-spray probe interface:The latesmtodels ofMcromass Quattro R triplqeuadrupolesystems(post1998)utilizae"Z-spray"conformation.T.he sprayemitted from a probe isorthogonalto thecone aperture.Intheconventionaclonfor'mationitisaimed directlaytthecone aperturea,fterpassingthrougha tortuouspathway inthecounter electrode.Though theconfiguratioinsdifferenth,emethods ofoperation,cleaninga,nd maintenancearethesame. However, Z-spraycomponents and conventionalcomponents are notcompatiblewithone another,butonlywithsimilasrystems(i.e.Z,-spraycomponents are compatiblewithsome otherZ-spraysystems,etc.)
3.5 Mass Lynx Software: System softwaredesignedforthespecifiocperationofthese QuattroIItriplqeuadrupolesystems.CurrentlyMassLynx hasWindows 95 and WindowsNT 4.0versions.AllversionsaresimilarF.or more detailsseethemanual specifitco the instnunen(tMcromass QuattroIItriplqeuadrupoleMassLynx orMassLynx NT User's Guide).
4.0 WARNINGS AND CAUTIONS
4.1 Healthand SafetyWarnings:
4.1.1 Use cautiowniththevoltagecablesfortheprobe.When engaged,theprobe employs a voltageof approximately5000 Volts.
ETS-8-5.1 Analysisof SeniinExtractUsingES/MS
Page 2 of 9
4.1.2 When handlingsamplesor solventswear appropriatperotectivgeloves,eyewear, and clothing.
4.2 Cautions: 4.2.1 Do not operatesolventpumps above capacityof 400 bar (5800 psi)back pressure. iftheback pressureexceeds400 bar,theBPI 100 willinitiataeutomaticshutdown.
4.2.2 Do not runsolventpumps todryness.
5.0 INTERFERENCES
5.1, To minimizeinterferencwehsen analyzinsgamplest,eflonshouldnotbe usedforsample storageor any partof instrumentatiotnhatcomes incontactwiththesampleor extract.
6.0 EOLTIPMENT 6.1 Equipment listebdelow may be modifiedinorderto optimizethesystem.Document any
modificationisntheraw data as method deviations. 6.1.1 NEcromass QuattroH triplqeuadrupoleMass Spectrometerequippedwith an
electrospraiyonizatiosnource 6.1.2 BPI 100 low pulsesolventpumping system,solventdegasser,column compartment,
and autosainpler
7.0 SUPPLrEs AND MATERIALS 7.1 Supplies
7.1.1 High puritygradenitrogengas regulatetdo approximately100 psi(House air system)
7.1.2 BPLC analyticaclolumn, specifictso be determinedby the an@dy@tand documented intheraw data.
7.1.3 Capped autovialosr capped 15 mL centrifugteubes
8.0 REAGIENTS AND STAMARDS 8.1 Reagents
8.1.1 Methanol,BPLC gradeorequivalent
8.1.2 NM-Q"z" water,allwater used inthismethod shouldbe N&M-Qlm water or equivalenta,nd may be provided by a MM-Q TOC Plus system or othervendor
8.1.3 Anunonium acetate,reagentgrade or equivalent
8.2 Standards
8.2.1 Typicalltywo methodblankst,wo matrixblanksa,nd eighteemnatrixstandardasre
prepared duringthe extractionprocedure. See ETS-8-4.1.
9.0 SAMIPLE HANDLING
ETS-8-5.1 AnalysisofSerum ExtractUsing ES/MS
Page 3 of 9
9.1 Fresh matrixstandardsarepreparedwith each analysisE.xtractedstandardsand samples arestoredincapped autovialosr capped IS mL centrifugteubesuntilanalysis.
9.2 Ifanalysiwsillbe delayed,extractedstandardsand samplescan be refrigerateadt approximately4' C, oratroom temperatureu,ntilanalysicsan be performed.
10.0 OUALrry CONTROL
10.1 Solvent Blanks, Method Blanks and Matrix Blanks 10.1.1 Solventblanks,method blanksand matrixblanksareprepared and analyzedw.ith each batchto determinecontaminationor carryover.
10.1.2 Analyzea method blankand a matrixblankpriorto each calibratiocnurve.
10.2 Matrix Spikes 10.2.1Matrixspikes'arpereparedand analyzedto determinethematrixeffecton the recoveryefficiency.
10.2.2 Matrixspikeduplicateasrepreparedand analyzedto measure theprecisionand the recoveryforeach analyte.
10.2.3 Analyzea matrixspikeand matrixspikeduplicatpeerfortysamples,with a minimum of2 spikesperbatch.
10.2.4 Matrixspikeand matrixspikeduplicatceoncentrationwsillfallinthemid-rangeof theiniticaallibraticounrve.Additionalspikeconcentrationmsay falilnthelowrangeof theinitiaclalibratiocnurve.
10.3 Continuing CalibrationVerifications
10.3.1 Continuing calibratiovnerificatioanrse analyzedto verifythe continuedaccuracy of the calibratiocnurve.
10.3.2Analyzea mid-rangecalibratiosntandardaftereverytenthsample,witha minimum of one perbatch.
11.0 CALIBRATION AND STANDMWMATION
11.1 Analyzetheextractemdatrixstandardspriorto and followingeach setof extracts.The averageoftwo standardcurveswillbe plottedby linearegressio(ny= my + b),weighted I/x,not forcedthroughzero,usingMass]Lynxor othersuitablseoftware.
11.2 Ifthecurvedoes notmeet requirementsp,erformroutinemaintenanceor reextracthe standardcurve (ifnecessary)and reanalyze.
11.3 For purposesof accuracywhen quantitatinlgow levelsofanalyte,itmay be necessaryto usethelow end of thecalibratiocnurveratherthanthefiffrlange ofthe standardcurve. Example: when attemptingto quantitataepproximately10 ppb of analyteg,eneratea calibratiocnurveconsistinogf thestandardsfrom 5 ppb to 100 ppb ratherthanthefall rangeof thecurve(5ppb to 1000 ppb). Thiswillreduceinaccuracyattributetdo linear regressiowneightingof highconcentratiosntandards.
ETS-8-5.1 Analysisof Senun ExtractUsing ES/MS
Page 4 of 9
12.0PRocEDuREs
12.1AcquisitiSoentup
12.1.1Clickon starbtuttonintheAcquisitioCnontrolPanel.Setup a sample Est.Assign a filenameusingMO-DAY-last digitofyear-samplenumber,assigna method (MS) foracquiringa,nd typeinsunple descriptions.
12.1.2 To createa method clickon scanbuttonin theAcquisitiocnontrolpaneland select SIR (SingleIon Recording)orNIRM. Se'tIonizatioMnode as appropriat'eandmass to 499 or otherappropriatmeasses.A fullscanisusuallycollecteadlongvvitthhe SIRS. Save acquisitiomnethod. IfMS[MS instrumentasreemployed,additional productionfragmentatioinnformatiomnay be collectedS.ee Mcromass MassLynx GUI]DE TO DATA ACQLJISITION foradditionailnformatioannd MRM (Multiple ReactionMoiitoring).
12.1.3 Typicallytheanalyticablatchrun sequencebeginswith a setof extractedmatrix standardsand ends with a setof extractedmatrixstandards.
12.1.4 Samples areanalyzedwith a continuingcalibratiocnheck injectedaftereverytenth sample. Solventblanksshouldbe analyzedperiodicaltloy monitorpossibleanalyte
carryoverand arenotconsideredsamplesbutmay be includedas such.
12.2 Using theAutosampler
12.2.1 Setup sampletrayaccordingtothesample fisptreparedinSection12.1.1.
12.2.2 Set-uptheBPI I00/autosampleratthefollowingconditionsor atconditionsthe analystconsidersappropriateforoptimalresponse.Record actualconditionsinthe instrumentlogbook:
12.2.2.1 Sample size= 10 gL injection
12.2.2.2Inject/sainp=le1 12.2.2.3 Cycletime= 13.5minutes
12.2.2.4Solventramp =
Time
0.00 min.
8.50 min.
11.0min. 12.0min.
MEOH
40%
90%
90% 40%
2.0mM Ammonium acetate
60%
10%
10%
60%
12.2.2.5Pressthe"Start"button.
12.3 InstrumentSet-up 12.3.1 RefertoETS-9-24.0formore details.
12.3.2Check thesolventlevelinreservoirasnd refiilflnecessary.
ETS-8-5.1 Analysisof Serum ExtractUsing ES/MS
Page 5 of 9
12.3.3 Check thestainlesssteelcapillarayttheend oftheprobe. Use an eyepieceto check thetip.The tipshouldbe flatwithno jaggededges.Ifthetipisfoundto be unsatisfactordyi,sassembletheprobe and replacethestainlesssteelcapillary.
12.3.4 SetBPLC pump to "On". Settheflow to 10 - 500 uL/niinor as appropriate. Observedropletscoming out ofthetipoftheprobe.Allow to equilibratfeor approximately10 minutes.
12.3.5 Turn on thenitrogen.A fineiiissthouldbe expelledwithno nitrogenleaking around thetipoftheprobe. Readjustthetipof theprobe ifno mistisobserved.
12.3.6 The instrumentusestheseparametersatthefollowingsettingsT.hese settingsmay change inorderto optimizetheresponse:
12.3.6.1Dryinggas250400 fiters/hour 12.3.6.2ESI nebulizinggas 10-15fiters/hour
I'@. 12.3.6.3 BPLC constant flow mode, flow rate 10 - 500 Wmin 12.3.6.4 Pressure <400 bar (This parameter is not set, it is a guide to ensure the
BPLC isoperatincgorrectly.)
12.3.7 Carefullgyuidetheprobeintotheopening.Insertprobeuntilitwillnotgo any furtherC.onnectthevoltagecablesto theprobe.
12.3.8 Printthetunepage,withitsparametersa,nd storeitinthestudybinderwitha copy tapedintotheinstrumentlog.
12.3.9 Using thecross-flowcounterelectrodientheES/MS sourceisrecommeride@ forthe analysiosf biologicamlatrices.
12.3.10CHckon starbtuttonintheAcquisitioCnontrolPanel(thismay varyamong MassLynx versionss,eeappropriatMeassLynx USEWS GUIDG). Pressthestart button.Ensure startand end saznplenumber includesallsample'sto be analyzed.
13.0 DATA ANALysis AND CA'LCULATIONS 13.1 Calculations:
13.1.4 Calculatematrixspikepercentrecoverieussingthefollowingequation:
% Recovery
Observed Result-Backyround Resultx 100 Expected Result
13.1.5Calculatepercentdifferencuesingthefollowingequation:
% Difference EKpectedConc.-CalculateCdonc. x 100
Expected Conc.
13.1.6CalculateactualconcentratioonfPFOS, or otherfluorochernicailn,matrix(gg/mL):
(ngof PFOS calc.from std.Curve x DilutionFactorj x I LLg anitiaVlolume ofmatrix(mL) + mL ofSur@ogateStandard) 1000 ng
FinalVolume (mL)
ETS-8-5.1 AnalysisofSenm ExtracUtsingES/MS
Page 6 of9
14.0 METHOD PERFORMANCE 14.1 Method DetectionLimit(MDL) and Limitof Quahtitatio(nLOQ) aremethod,analytea,nd
matrixspecificP.leaseseeETS-8-4.1,Attachment B, fora listinogf currentvalidated MDL and LOQ values.
14.2 Solvent Blanks, Method Blanks, and Matrix Blanks
14.2.1 Solventblanks,method blanks,and matrixblanksvaluesare must be below the lowest standardinthe calibratiocnurve
14.3 CalibrationCurves
14.3.1The r2 valueforthecalibratiocnurvemust be 0.980or better.
14.4 Matrix Spikes
14.4.1 Matrix spikepercentrecoveriesaremust be within 300/oof ihe spiked concentration.
14.5 Continuing CalibrationVerifications
14.5.1 Continuingcalibratiovnedficationpercentrecoveriesmust be 30% of the spiked concentration.
14.6 Ifcriterilaistedinthismethod performancesectionisn'tmet, maintenancemay be performed on the system and samplesreanalyzedor otheractionsas determinedby the analyst.Document allactionsinthe appropriatelogbook.
14.7 Ifdataare tobe reportedwhen performance criterihaave not been met, the datamust be footnotedon tablesand discussedinthe textofthe report.
15.0 POLLUTION PREVENTION AND WASTE MANAGEMMNT 15.1 Sample extractwaste and flammable solventisdisposedinhighBTU containersa,nd glass
pipettewaste isdisposedinbroken glasscontainerslocatedinthe laboratory.
16.0 REcoRD@ 16.1 Each page generatedfora studymust have the followinginformationincludedeitherinthe
headeror hand writtenon the page: studyor projectnumber, acquisitiomnethod, integratiomnethod, sample name, extractiodnate,dilutiofnactor(ifapplicable)a,nd analyst.
16.2 Printthe tune page,sample lista,nd acquisitiomnethod from MassLynx to includeinthe appropriatestudyfolder.Copy thesepages and tapeintothe instrumentrunlog.
16.3 Plotthe calibratiocnurve by linearregressionw,eighted I/x,thenprintthesegraphsand storeinthe studyfolder.
16.4 Printdata integratiosnummary, integratiomnethod, and chromatograms, from MassLynx, and storein the studyfolder.
16.5 Summarize datausingsuitablesoftware(Excel5.0)and storeinthe studyfolder,see Attachment A foran example ofa summary spreadsheet.
ETS-8-5.1 Analysisof Senun ExtractUsing ES/N4S
Page 7 of 9
16.6 Back up electronidcatato appropriatmeedium. Record instudynotebook thefilename and locationofbackup electronidcata.
17.0 TABLES, DiAGRAms, FLOWCHARTS, AND VALIODATioN DATA 17.1 AttachmentA: ETS-8-5.1 Data summary spreadsheet.
18.0 RFFERFNCES
18.1 FACT-M-4. compounds
1,"Extractionof Potassium Perfluorooctanesulfonatoer Other Fluorochemical from Serum forAnalysisUsing EPLC-Electrospray/NWs Spectrometry
18.2 ETS-9-24.0, "Operation and Maintenance of the Mcromass Atmospheric Pressure Ionization/MassSpectrometer Quattro H triplequadrupole Systerr&'
18.3 The validationreport-associatedwith thismethod isETS-8-4.0 & 5.0-V-l.
19.0 Amc7m
DocumNTs
19.1 ETS-8-4. 1, "Extractionof Potassium Perfluorooetanesulfonatoer Other Fluorochemical Compounds from Serum forAnalysisUsing BPLC-Electrospray/i\4assSpectrometry"
20.0 REvisioNs
Revision Number.
I
Reason For Revision Section 6.1.2 Clarificatioonf IHP 1100 system components. Section 11.1 Average of two curves, not standardvalues,are used for plottinglinearregressionand added the I/xweighting of the curve. Section 12.2.2.4Clarificatioonf solventramp. Section 17.1 Changed from attachment B to A.
Revision 04/02/99
ETS-8-5.1 Analysisof Senun ExtractUsing ES/MS
Page 8 of9
LaboratoryStudy
Study: TestMaterial: Matfix/FinaSlolvent: Method/Revision: AnalyticalEquipment System Number: InstrumentSoftwareNersion: Filename: R-Squared Value: Slope: Y Intercept: Date ofExtraction/Analyst: Date ofAnalysis/Analyst:
Group Dose
Sample#
Concentration mg/mT,
InitiaVloL mL
Dilution Factor
FinalConc. uatmt,
S@lope:Taken from linearregressionequation. Group/Dose: Taken from thestudyfolder. Sample#: Taken from thestudyfolder. Concentration(ugfmL): Taken from theMassLynx integratiosnummary. InitiaVlolume (mL): Taken ftom thestudyfolder. DilutionFactor: Taken from thestudyfolder. FinalConc. (ug/mL): Calculatebdy dividingtheinitiavlolume from theconcentration
Attachment A: Summary Spreadsheet
ETS-8-5.1
Analysisof Senun ExtractUsing ES/MS
Page 9 of 9
Fluorine Analytical Chemistry Team
Contact
Ki.Han9cm
8-6019
Detersitago6n ofPFOS inseraby ElectrosprayMass Spectrometry(ESMS)
Quantitation: LimitofDetectio(nLOD): LimitofQuantitatio(nLOQ) Range of C&Bration Curve:
1.0ppb 1.0ppb I.Oppb- 100ppb
Spechscity: RetentionTime: moiam9mion.
7.35 499 amu
Curve CorrelatioCnoefficient
0.999
PHASE
Let 1006 1007 1008 S009 solo soil W012 W013 W014
IEL-An*sisofpooledsem US 1!993
Avemp cone. St&
% Rowyery
PFOS (Dpb)@ Dev.
44
2
-27* 73
44
6
-14* 35*
43
2
65* 37*
26
8
82
92
28
7
-6* 27*
45
2
100 108
54
13
78
92
50
5
90
102
41
6
106
92
lrange ofAverage Concmbudon ofPFOS IinLot Smorram:
Avemge eme
LigL PFOS (ODb)@ RM
W015
41
3
W016
47
8
W017
42
3
-
fiffa6mppb to54 ppb
% Remvery
m
120
112
51*
92
-45*
65*
ResultsofQuantitatioonfMethod Blanks
Concentmdon
link Medwd Blank B20-1
PFOS (pub) <LOD
Method Blank MO-2
<LOD
MeffiodBlank,um-1 (1)
7
Method Blani@u.m-1 (2) Method Blank,mm-1 (3) Method Blank.3cm-2 (1)
<LOD -<LOD 4.OD
SamvW
QCI
QC2
QC3
QC4
QC5
[PFOSI rowyered
49 49
49-.50 53
[PFOSI emnew
49 49 49 49 49
% rewyery
100 100 100 102 108
Sy stem Reprodua*bilityand PrecisionChecks
producib
spampk uclb 31;00(67-23((22))
9_3 S009-3(2)
WO 12.3(2) W015-3 (2)
W017-3 (2)
PFOS (pob) 45 I1 54 33 37
L% 0.7% 0.40A 0.4% 1.80/0 0.8%
Prock1w..
Am*
1007-1(1) 1007-1(2) 1007-1(3) 1007-1(4) 1007-1(5)
Avemge Std.Dev. RSD
PFOS (npb) 47 55 49 47 49 49
I 211/o
'Reportedvaluesare theaverages concentratioPnFOS ofsampleseximctedinMplicate.
2QC sampki are extractsof blankseraspikedwithPFOS standar&. 3Reproducibilitsyamples are repeatinjectionosf lotsera extractsp,erformedafter every 15 imn plei
4Precision.samplesare 5 consecutiveinjectionsofthe same lotsera extract *QuestionableData. Sou= of ailotmm=tly undeAmiinecL 3M Envkommental Lab 5nlgg
PHASE.U
rtuorineAnalyticalChemistryTeam
in seraby ElectrosprayMass Spectrometry (ESMS)
Quantitd&@ LimitofDetectio(nLOD) LimitofQuantitatio(nLOQ)
Range ofCalibratioCnurve:
10 ppb 1.0ppb loppb -100ppb
Specificity: RetentionI"une:
MolecularIon:
6.90min. 413 amu' 369 amu@
Curve CorrelatioCnoefficien(tr@: 0.991
Comm:
K.J.Hansm 8-60191
Phase U: Analysisof pooled sem
Avenige con Std.
i,ot POAA (D]Db
Dev.
1006
<LOD
0
1007
<,OD
1
1009
<LOD
0
S009
<LOD
1
solo
<.OD
0
soil <WD
0
W012
<LOD
1
W013
<LOD
0
W014
<,OD
0
(POAA)
% Recovery
MS MSD
56* 96
53* 79
90
74
65*
68*
45* 570
71
67*
92
94
100 100
98
95
Range ofAverage ConcentrationofPOAA inLot Sera.-
Avcmge conc Std.
_LA POAA (IDub? Dev.
W015
<LDD
0
W016
<LOD
0
W017
<.OD
0
BOOI
<IOD
0
B002 <LDD
0
B003 -CLOD
0
B004 <,OD
0
B005 <DD
0
allvahm wm belowtheLODIOQ
% Recovery
MS
MD
100
101
83
.97
83
97
98
89
100
100
108
110
60*
94
94
89
(10ppb)
Resultsof QuantitationofMethod Blinks
Slmk Method Blank,B20-1 Method Bbu3k H20-2 Method Blank,scra-I(1)
MethodBlank,stra-1(2) MethodBlank sem-1(3) Method Blank sera-2 (1)
concentration POAA (IDD-W
<LOD <.OD <LOD <LOD -<LOD <.OD
Samew QCI QC2 QC3 QC4
QC5
[POAA] recovemd
94 91 91 .92 9.3
[JPOAA) emmcted
98 95 95 96. 97
% recoym
98
95@ 95 96 97
System Reproducibilityand PrecisionChecks
Reproducibilty':
Samiple 1006-3(2) S009-3(2) W012-3 (2) W015-3 (2) W017-3 (2) B003-3(2)
POAA (area) 7700 3100 6500 4700 4900 3100
RSD 0.9% 7.00/o o.oo/o 0.0% 5.801* 2.00/o
Sample1007-1(1) 1007-1(2) 1007-1(3) 1007-1(4) 1007-1(5)
Avmge Std.Dev. RSD
Peak 5$w 5600 6300 6300 6300 6100 300 5%
'IonnLIz-413usedforpurposes ofquantitation.
21onmlz-369 usedforpurposes ofverficatioonf compound identity. 'Reportedvaluesare theaveragesconcentratioPnOAA ofsmples c&wted intnplicate 4Qc samplesare extractsof blankseraspikedwithPOAA standards. sreproducibilitsyamples are repeatInjectionosf lotsera extractsp,erfonnedafterevery15 samples.
6Precisiosnamples are 5 consecutiveinjectionosfthesaw lotseraextract. *QuestionableData. Source of errorau=tly undetermined.
3M EnvironmentalLab 5nlgg
PHASE 11(POAA)
Y-1.Hanwn
Phase III
3/W8
3M EnvironmentalLab
Quantitative Analysis of PFOS in Ind*m*dual's Sera
Determination of PFOS in sera by Electrospray Mass Spectrometry (ESMS)
Quandtation:
Spedfidty:
LimitofDctwdon (LOD)
1.0ppb
Retudon Time: 7.35min.
LimitofQuandtodon (LOQ)
1.0ppb
MolecularIon:
499 amu
Range ofCabbradw Curve:
l.Oppb- 100ppb
CurveCorrelatioCn4efficie(nrt@: I
ResultsofQuantitationoflnd*m*duaSleraSamples
Avenkgecow.
Lot PFOS (opb)
198
58
298
41
398
46
498
32
598
67
698
S3
798
42
898
49
% RSD 41* 14 2
N-k
0 7 N-k 35*
Let 1798 1898 im
2099
2198 2298 2398 2498
998
39
11
2598
1098
54
5
2698
1198
60
11
2798
1299
37
1
2899
1399
45
NA
2998
1498
31
12
3098
1598
96
2
3199
1699
74
1
venkgceonc.
PFOS (vpb) % RSD
46
15
56
10
70
3
40
2
49
9
60
13
72
1
35
20
41
33*
53
11
57
15
33
N-k
65
7
67
50*
33
11
N.A- - No 0/" calculatedas therewu only enough smplc forI mabsis.
QuantitatiAvnealysiosfPFOS and POAA inInd*m*dualS'esra
DeterminatioonfPFOS/POAA inseraby lelectrosprMaayn
Quantitation:
LimiotfDetectio(nLOD):
LimitofQumdtadOn (LOQ): Rmp ofCalibradonCurve: CoffelatioCnoefficien(tr@:
Spedrakr.
1.0ppbtlo ppb 1.0ppb/10 ppb
RdenticeT'mc: bblecwwim
I.Oppb- 100ppb/10 ppb -100ppb
0.999/0.999
Spectrometz7(ZSMS)
7.35minJ6.9miil 499 awd4l3 Lwu.369 a=
Preliminary
Results
198 2F 2199181
398 498 598 698 798 899 999 1099 1198 1298 1398 1498 1598 1698
of Ouantitation of Indhid%W Som
Avlg.cone. Std.
S(lo Dev.
46
nd.
Avg. cosm 'FOAA (o
<LOQ
35
nd.
45
nd.
32
nd.
.167
nd.
53
4
42
nd.
49
17
37
ncL
:LOQ Is
10
<.OQ
<ZQ
gLOQ <.OQ -GLOQ
52
tLdL
CLOQ
39
nd.
37
nd.
CLOQ
4.OQ
45
nd.
28
nd.
96
3
CLOQ
<.OQ 10
73
tLd.
.4LOQ
Samples St4L
RM ME
zLd. 1798 nd. 1999 3 1999 nd. 2098 zLd. 2198 n.& 2298 nd. 2398 nd. 2498 nd. 2598 nd. 2698 ndL 2798 iLdL 28"0
nd. 2998 zLd. 3098
1 3198 nd.
Avemp mm PFOS (nimb4
41 52 71 40 45 54 71 23 30 47 51 30 41 41 36
Std. 2m nd. zLd. nd.
1 ;LdL zLd. zLd. nd. zLd.
1 nd. iLd. zLd. nd. iLd.
Avg. am& POAA (io
CLOQ
<LOQ
-<LOQ
<.OQ CLOQ
4.OQ 12
<.OQ -4,OQ
<.DQ <.OQ LOQ <IOQ LOQ <LOQ
St4L
um nd. iLd. zLd.' iLd. iLd. n.& nd. nd. nd. nd. zLd. iLd. nd. nd. nd.
Resultsof Quantitaflonof Method Blanbs
llmk
IPFOSI(pub)
iS7B Blank.Eao-l .4LOD
Method BILuk,Sao-1 (1) 4
MethodBlock=%-I (2) -4LOD
IPOALAI (DUM
Method Blxmk.MO-1
-4.OD
MethodBlock=*-I (1) -4LOD
IMetiodBlockum-1 (2) 4.OD
System ReproducibilityChecks
produdbw: sm2h 0198-2(2)
o1lr0o9t9.2(2) 2098-1(2) 2698-1(2)
PFOS (Dpb) 33
20 40 47
an 4.3%
3.6% 1.9% 3.0%
s QCI QC2 QC3
Rios] recovend
99% 93%
90%
VPOAA) .-.recovered
93% 87% 82%
POAA (area)
28W
0.0%
13M
0 .0%
1400 0.0%
2300. 6.1%
'R*portovdalumwvfivm a iftleawlysb mdow a MA dev.isbuffeated.
indon cam. 2 alliquotsof somple wo a amal>wd od evoogd.
2QC =MpeS We c&ac& ofblankmm ipikedwithPPOS4:'OAA amdar&
'Repro&cibifitmymples arerepeatinleefiomoflotjorac*wta pwfonmd
evoy 15 so**&
KJ. Hansen
Phne III
3M EwArannuntalLAb Quantitative Analysis of PFOS in Individual's Sera
Determination of PFOS in sem
Quandtadon: Limit of Detectkm (LOD) LimitofQwmdtwm OX)Q) Rmp ofCabUatkm Curve. CurveCorrelatioCnacffidwt(r@:
by Electrospray Man Spectrometry (ESMS)
specindly:
1.0ppb 1.0ppb
Remdon Time: MolocularIon:
7.35min. 4992ml
I.Oppb- lOOpIpb
I
ResultsofQwmtitation ofIndividuidSera Samples
Awrw came.
Iqt PFOS (opb) % 3M
198
58
410
299
41
14
399
46
2
498
32
NJL
598
67
0
6"
53
7
798
42
Nk
898
49
35*
"B
39
11
1098
54
5.
1199
60
11
1298
37
1
1393
45
N.A.
1498
31
12
1599
96
2
1 1698
74
1
Lot 1798 1899 1"3 2099 2198 2299 2399 2498 2598 2698 2798 2899
2998 3098 3198
verw cow. PFOS (nob)
46 56 70 40 48 60 72 35 41 53 57 33
65 67 33
% RSD is 10 3 2 9 13 1 20 33* 11 15 Nk
7 50* 11
Nfi- - No VJW calcubod as that was onlymougbisamplefor1 =absil
4/9/98
FluorineAnalyticalChemistry Team
Determination of PFOS in sera by Electrospray Mass Spectrometry (ESMS)
Quintitation: LimitofDewdon (LOD): LimitofQuantitado(nLM Rwp ofCahlwationCurve:
Specffldty:
1.0ppb
RetentionTime:
1.0ppb
MolecularIon:
I.Oppb- 100ppb
7.35min. 499 amu
CurveCorrelatioCn4cffwicn(tr): I
PHASE IUL-Analysisof individualserasamples,1993 US
Averageconc.
Lot PFOS (npb) % RSD
198
59
41*
298
41
14
398
46
2
499
32
N.A.
598
67
0
698
53
7
798
42
N.A.
898
49
35*
998
39
11
1098
54
5
1198
60
11
1298
37
1
Aymp cone.
L&L PFOS (pub) % RSD
1798 46
15
1898 56
10
1999 70
3
2098 40
2
2198 49
9
2298 60
13
2398 72
1
2499
35
20
2598 41
33*
2698
53
11
2793
57
15
2898 33
N.A.
1399
45
N.A.
1498
31
12
.1598
96
2
2998 65
7
3098 67
50*
3198
33
11
1698
74
1
N.A. = No 0/" mlmbod as them wu onlyewugh sampleforI anabsis-
contga. 8-6018
3M Ew&onmnud IAb
5nl9g
PHASEM
3M EnvironmentalLaboratory-FluorineAnalyticaClhemistry Team
KrisHamn - Sr.AnalyticaClhemist Muorine AnalyticaClmmisuy Team Building2-3E-09 612-778-6018
Phaie IV: PFOS analysis of US human sera samples collected in the 1970s
Slimmau: Twelve frozenserasamplesofvariousvolumeswem suppliedtotheEnvLro=cntal Lab by jeff
Mandel (3M Medical).One mL orno more thanone halfofthevolume ofeachsamplewas extracted usingan ion-pairmgreagentlle ewacts wereanalyzedqmumvcly fi)PrFOS by EEPLC-ESHO. Analyteidentificatwiaosnvcdfwd by comparisonofmoleculairon-EPLC retentiofnim oftheexuacted analyteand standardmataw. Sampleswerequantitativelvyaluateadgainsat VwWUy pmpuid extractecdurve.
The twelvesamplescontainedan averageconcenusfim of27 ppb PFOS =nzin from 2-48 ppb. Ile PFOS levelwsese sigmfi=* lowerthaninthe31 amples collectefdtom individualisno2/98and =bbited significantglmyatervariabiliitnyPFOS levelsthanthosesame samples.The percent abuddanceofthebranchedchainisomerwas 37.3+/-4.90/oc,omparedto33.7+/-70/ionthe1998 samples In standardsolutionosfPFOS, thebranchedchainaccountsfor21.7+/-3.1% ofthetotalconcmftadm A detailedsummary oftheresultissincludecl
The identitoyfPFOS inseveralrandomlyselectesdamplesinthisphasewas Tumed using EPLC-Esmsms. In allcasestheanalyteoxbbiteda cbaracwasdcretentiofnim, a characteristic primaryion,and fivecharacteristsiecondaryions.
Experimental=unwary:
SonplepreparationI:on-palyinegxtraction Ina pH controllendvironmentan ion-pamngreagenttcuabutyalmmomum (IBA),isusedtD
==a theanalytferom thematnx Ilm cabowc reagentwlectn* targetasmomc compounds,likePFOS and POAA. SubsequenttotheformationoftheTBA-anion pair,theambu istransferretdoa non-polm organicsolven(tethywletaw).dmd. and reconstitutiendmcftwl forhG analysis.
BPLC. CharacteristriectentioanmesforPFOS
InBPLC, an aliquootfthecKft2aisinjecteadnd passeddumigh a
column.
Based on theaffiwtyoftheandyteforthestationary-phaisnethecolumn relativteotheliquidmobile-
phasepassingthroughthecolumn,theanatytcisretainefdora chamuensticamount ofum. For
ekample,ina standardsolutionP,FOS may clutoat9.1minutes.Patentiontimesbetweena standard PFOS solutioannd theanalyteodmcted from seraintlusanalysiwserematched towithin1% on the
BPLC system.
ESCDS. Detectionand monitoringofthemolecularion AnalysisofPFOS standardisndicatetsha theprimaryioncb=Mrisfic ofPFOS isn* - 499
amu, correspondingtothemaw offt miionicmufamnt (CO17S%-)- ThisionWas monitoredWICC&dY
tomaximize sensitivitAy.scanofm/z-100 to1210 (negativoenly)was alsocohecte&
HPLCEY-MSAWS. Detectionand monitoringofcharacteristsieccondaryions ES-MSMS isverysimilartoESMS, exceptthatitadds-anadditionadlimensionofcertainttyo
compound identificatioAns.inESMS, achamcteristiiconisselectedA.fterselectiotnh,eES-MSMS
chamcteritmheionfiutkbrysmsithiintaparwtithhighenau pL AsamWt oftheuusb*nit secondairoynifcragmen(tdsaughtieornsd)w,wtuisfiocfthemoleculaem,amaw anddcmcm&
Forexamplef,orPFOS analysiiso,n499isselectaesdthecharacteripsrtiimcariyoilThisionis smashed intootherionssuchasgo -g-u(correspondintgoS031, 99 -u (correspondintgoFS%), 130 Amu (concvonding toCF2SO3), 180 i-mu (C2F4S%). and 230 amu (C@F&S%). Each ofthen m=ndary ftagmentsis&Aectcd atthedc=wr.
Qualitycontrolmmmary: Due tosample lumtationss,erasampleswon notodmcted induplicateFor thissome remn,
matrixspdm couldnotbe evaluatedforthesamples. Tinsteatdwo samplesof pooledserapurchasedftom Sigma were used forduplicatmeatrixspilmanalysis.hfcdmd Wanks wac analyzedbeforeand dber each sample toensurecompleteisolatioonfthe sample. A mid-lad qualitycontrolsample was analyzed afterthesixthserasample. The fourpowt extractedcurvewas analyzedbeforeand aft thesm3@pla. Quantitatioonf thesamples isbasedon the linea regmisionequationdaived hom theaverageofthetwo bracketingcurvm SpecifiQcC parameterswe availabloen theWoded resulttsalk
butmmental specwwj: HPLC system HewlettPa&ard Series1100LiquidChromatogfifm,nh-
Column:Kcystme BetasilCis 2 x 100 mm 5 pm particlseize
Flow rate: 300 pumin.
SolventA:
2.0mM Ammonhm Acetat
SolventB:
Methanol
SolventGradient
45 to 90 O/oBin 9.50 mins.
Hold at90 V*B for3.50mins.
Remm to45 0/aliBn 1.50mins.
Hold at45 O/oBfor3.5
injectiovnolume: 10 ;LL
Injection/ssample:I
EJechvspray nuissspectrometer Mcromass PlafformH API Mm Spectrometer
MassLynx 2.1 Softwarr. Cone volu4m: -20v,-60v
Mode: clecuospraynegative
Sourcetempuature:
115 OC.
Analy=r vacuum pre==: 0.000043mbar, 0.000079mbar
Ions:369, 413, 499 Elecb-ode:cross-flow
FluorineAnalytical Chemistry Team
Samples Received:
3/6/99
Samples Extracted:
3/9/98
Samples Analyzed: 3/11-3/12/98
Analysisby: CalibratioCnurve Ransc
1?ofCaUbratim Curvc LOQALODI:
PHASE IV: Analysis of historic samples, 197"Os
Conc. of PFOS
b+B40
P07-SE13
13
PG3-SEll
32
98SE774
30
98SE117
24
PG25
40
PGS
29
Sample IDD
CRAH 0003 3"1-0089-01 3"14)044-01
Will0002
Do= 0001 80-52-0514-01
COUC. OfPFOS (pob)
48 15 39 2 44 25
Average(ppb)
28
Std.Dev.
9
%RSD
32
KJHmun 77"018
ESM Ippb- 49ppb O.M 1 ppb
QC Results
QC Check-
CalibratiCohnadc (QCI) bo NW
% Recovery
1000/0 105% 105%
Branched Isomer Abundance Percentages
% Abund-n of % Abundanceof Branched Isomers Branched Isomers
Sample Pool
SUndakd Nfaterial IndividualSsampled in 1998 3M CMW GrovePlantWorkers
IndividualSsampled in 1970's ,PooledSem Samples
le) 220/o 34% 45% 370/o 31%
(St&DCV.) 3% 5% 4% 5% 5%
n (Msmoled inpool)
n/a 31 3 12
I -LOD/LOQ - LimitofDetwdon/Limit ofQuantitation
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PHASE rV
Pi@17090
phmrv
FUS
Is"&
3149101 hf$OH blmk 31 4nM gx&aow bmm -
3149M SWaaWbu@@blmk
3:115 me= blmk 3 49s,6 M@OH blmk
3149817 P074813
3149911 ?074813
3149119 P074813
31499211MOgbbak
3149921 P034811
31499= P034211
3149rM P034811
3149624 USCH blmk
3149M 9L4M"4
3149926 99SB774
3149W 99313"4
31
M*CH blmk
314grJg9MI17
3149= 9=117
314MI 98= 17
31
980117
31
Mo=bbok
31499M PWS
3149835 P025
3149M P025
314@ Us= bbmk
3149M Skd4-1.4"
3149639 3td4-1.4U
3149M Me= blmk
3149941 POS
314994 POS
3149M POS
3149944 POS
3149945 Me= blmk
3149946 GRABDO3
3149M GRAND03
3149M GRARD03
3149M Me= Wmk
31499" 80-01-0089-01
3149M W41-00041
3149LI28"1-008"1
3149953 M*OHbLmk
314995420-01-0""1
3149955 3"14044-01
3149Li68"14)044-01
3149M 30-41-004"1
31491= MOCH Wmk
3149959 S& 4-1.4LO ppb
3149M Me= bimk
3149Ul WiD 0002
3149= VIM OOM
3149M VIM 0002
3149864 WM OOM
31~ WM 0002
3149M MoM blwk
3149M DMWOMI
314ma DEUM 0001
49gd9 DEUM 0001
31.49lr7MOe= bimt
3149971 80-n45l4-01
3149M 80-524514-01
3149M 30-524514-01 3149974)@@bimk
3149675 kivOHblmk
3149976 B20 bimic-I
31498" B20 blmk.2
3149M M*ORbhwk
3149979 PoolsdL%wl
31
POOW sgw2
314MI MoOHWmk
3149M )M 19.9ppb
3149M MSD 19.9ppb
3l49U4 MoOHblmk
3149US )6WH bL=k
3149486 Exwootedb@ me
3149U? Ro@b..@Wmk
bl-k blmk
pfasippbMY04" OLDw.
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24.9
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32ZI
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Eb@ 778-Ml
3M EnvironmentaLlaboratoryF-luorinAenalyticCahlemishNTeani
KrisHansen-Sr.AnalyticCahlemist FluorineAnalyticalChemistryTeam Building2-3E-09 612-778-6018
Phase V and VI: QuantitativeanalysisofPFOS inhistorihcuman serasamples
and inhuman serasamples from ruralNorthern China
,Rilinmary:
Two setsof samples,thefim with 12 sampla inplastviical(sZ-seatn)dthesecondwith5
samplesinglassvials(M-M), wm suppliedtotheEwAmnmental Lab by JeffU@mM (3M Mefficala)n
March 20, 1998. For bothsok samplevolunkevariedfmm 0.2to1.0niLofhun"n =2 A volume
between0.4- 1.0mL ofeachsamplewas exuactedusingan ion-oft reapm Sixunmi inthe7,.sa
didnotcontainenoughvolumefororbacdm intheseca twosampla (e,&ZZA6 andZZAS) wac combinedand cxuactedasone=moo. lU cwactswereanalyzeqduanutatn* for -
mffonaw(PFOS)by high-pmmm liquidMIUDgWby-de=oWq mm Vwuomefty (EEFW-ESM.
Anabu idenflficatwiaosnvafflobdy
ofnwlecwu ion-EPLCretmdondm oftheextracted
analyteand standardmatuw. Sampleswerequantitativelvyaluateadgainsta speciallpyrqpare4frm@
pointextractecdam (zA2- 0.999).Eachsamplecc= wasanalyzetdwim Calibraticolnimb
analyzedevery5 samples,wem within6% ofexpectedvaluel
The identitoyfPFOS inseverarlandomlyselectesdamplesinUm phase(M-M only)was
confirmedusing13PLC-ESMSNO. In allcasestheanabu exhibiteadcharacterisztaitcentiotnime,a
characterisptriicmaryion,andfivedmderistic secondariyons.
Ristopiscamples Ile sem samplesintheM-set,collectferdom donorsintheUS inthe1960s,had an average
PFOS concentrationf33.4ppb;thesamplesrangedinIPFOSconcentratifornom Il..tt5o9.4.
Foreignsamples ne 9 samplesintheZ-set(includin3gcompositesamples)wen couacwd f3romdonorsinrural
China and weredeterminedtohavea much lowerconcentratiofnPFOS thanany him2n seradataset
analyzedpreviouslyS.ixsamplesdidnotcontainPFOS abovethe &Awdon limitofthisanalytical method(Ippb).M@e remaining3 samplesevidencePdFOS concenuationlseathan5 pyb,thelimitof quantiwon. With thewwmdon ofwe human =a samplecollectiendthe1980s(Will0002),thenm theonlybi,m-nsamplesdeterminetdocontailnessthan10ppbPFOS.
Experimentalsummarr.
SwnplepreparafioIno:n-paipinegxtraction
Ina pH controllewdamnment.an ion-pdnngreagentwtrabutyalmmonium adfiftCMA), is 'usedtoexU= theanabu fromthematrixAmomc compoun(klikethecauomc=agent selwuvely targetPsFOS andpeawrow=oate (POAA). SubsequenttotheformatioonftheIBA-anionpair,the anabu is=Ld@ffed toa non-polaorrganicsolven(tethyalcetated)n,e4 andn=nstium:d inmethanol
forMS analysis.
HPLC CharacteristriectentiohnmesforPFos InBPLC, an aliquootftheextracitsinjecteadndpassedthrougha chromatographiccolumm
Based on theafrimtyoftheanwyteforthestationary-phiansethecolumnrelativteotheliquimdobil-.Phase Passingthroughthecolumn,theanalytiesretainefdora characterisatmiocunt oftime.For example,ina standardsolutionP,FOS may cluteat10.5minutel Rdentiontin= betweena standard
05/07/98
PFOS solutionand theanalyteextractedfrom serainthisanalysiwsere niatchadtowithin 1% on the HPLC system.
ESlAa. Detection and monitoring of the mokcular ion Analysis of PFOS standards indicatesthatthe primary ion characteristicof PFOS is m/z - 499
ami@ corresponding tothe mass of the anionicmufactant(CsFl7SO3-).This ion was monitored selectively to maximize sensitivityA. scan ofm/z-100 to 1210 (negativeonly)was alsocobected.
HPLC ES-MSIMS.
Detection and monitoring ofcharacteristic secondary ions
ES-MSMS
is very sitnila to ESMS, except that itadds an additional dimension ofcmiaintyto
compound identificationA.s inESNM, a characteristiocnissdacte& Afterselectiont,he ES-MSNE
charactchm the ionfurtherby smashing itapartwith high-emgy ga& As a resultof the smashin&
secondary ionic fragments (daughter ions),characwmc
of the molecule, am created and deUM&
For example, for PFOS analysis,ion 499 isselectedas the characteristicprimary ion. lliis ion is
smashed into other ions such as 80 -gmu (convsponding to S03), 99 stirn(ucorresponding to Fsoi), 130
amu (coffevonding to CF2SO3), 180 qmu (C,2F4SI%), and 230 amu (C3F&%%). Each afthm secondary
ftagments isdetected at the doADoor.
Quality control summary: Due to sample hunt3uomL% sera samples were not exuacted in duplicate,with I exception. For
this same reason, matrix spikes could not be evaluated for the samples. Each sample exuad was analyzed in duplicate. One sample, M001278 contained enough material for two exuacdm& Tk presented rmft for thissample are based on duplicate analysis of each oftbe two extractions. NL-thanol blanks were analyzed penodicauy to ensure complete isolationof the sample. A nud-level (24 ppb) quality control
lewas analyzed every 5 samplel Because human sera without PFOS is not available,sampim of sem purchased from Sigma were pre-cKuact4 spflmd with a standard concentration ofPFOS, and
n-carwted. This pm-odmcted sera isunderstood to be very similn to the sample matrix This fin pomt extracted curve was analyzed before and afterthe samples. QuantLtation of the samples isbased on tborinea mgmssion equation derived from the average of the two bracketing curves (r"2 0.999). Specific QC parameters uc available on the appended resultstable
LimitofQuantitation
7U current analyticalmethod has be= used to evaluate a large range ofFFOS levels odmcted
fim sem ft method isnot optimized for pr=*SC low-lcvd (< 5 ppb) quantitaflon,but instcaifor
samples in the range of 20-60 ppb. Cnven the conccm=ons
chosen for Ons optimization of the standard
mm, while them is a sl-itmcal ddkrt= for samples evaluated from 5-100 ppb, them is no sudLsUW difference between samples quantitated from 1-5 ppb. The quantitationdoes not become MdWcany
defendable unth 5 ppb; thus thisvalue represents the limit ofquantitadon for this method. Samples designated <LOQ am estimated to contain 1-5 ppb PFOS. Nfurther accuracy and precision in
quantitatton of the low-kvcl Z-4 samples (samples lessthan 5 ppb) isrequired, a sp=W low-level
quantitation system will be required
Limit ofdetection
I'helimitofdetectiofnorthisanalyticmaelthodisbasedon analysrtecognitioonfthedistinct
peaksbapereswungfromPFOS aiwygs. PFOS =dud mataialand PFOS exuactodfrom scm
analyzed by the conditions reported hem, show new basdin resolutionof I brandied and I 'in= PFOS
isomer. lle apex of each peak in the BPLC-U=
o=im ata spedfic, reproducible retention fim Ew the
ratioof the branched peak to the linm peak ishtwy consisftt down to the low s=dard. 1.0 ppb. Thm
samples that a) had PFOS levelsevaluated at lessthan the limitof quantitationand b) evidenced the
distinctpeak shape, were designated < LOQ. Samples that a) have PFOS levels evaluated at less than the
limit of quantitation and that b) do not reflectthe unique PFOS peak shape, were designated < LOD.
The= samples are estituted to contain from 0-1 ppb PFOS.
05/07/98
2
Instnunestalspecirwi:
HPLC system Hcwkn Padeard Series1100 Liquid
Column:Kcimne Betod Cis 2 x 100 mm
5 limpardclesize
Flow rate:
300 gLAnin.
SolventA:
2.0mM Ammonium Acetm
SolventB:
Nlethanol
SolventGradient
45 to 90 %B in9.50minl
Hold at90 %B for3.50minl
Returntik45%B in1.50minl
BDid at45 %B for3.5minl
injecdmvob=: 10 ILL
Injecdm / nm&: 2
meefts'prayM= SWcftmeter bficromm Pb&rm I[A[M ItfawSpwftomam, "CMW
M&%sLy= 2.4Software Cone volbigm:--20v;-6ft Mode: clocamprayneptm
Source tmnperature: 115 OC. Analrw va=m pmmm: 0.000043mbar, o.oooo7gmbor Ions: 369,413, 499,427 Electrode:cmss-fiow
05/07/98
3
FluorineAnalytical Chemistry Team
XJHwmn 77"018
Samples Received: Samples Extracted: Samples Analyzed:
3/6/99 3/9/98 3/11- 3/12/98
Analysisby: CalibrationCurve Range: ?of CalibratioCnurve: LODL.-
LOQ2:
ESMS ippb.-49ppb 0.998 I pi)b
5 pyb -
PHASE V and VI: Analysisofforeign(ruralNorthern China) and historiscerasamples(1960)
Conc. ofPFOS
Sample M
ZZAI
<DD
ZZA2
<DD
ZZA3
ZZA4
<IOQ
ZZA5
<M
ZZA6 and & <,OD
ZZA7
<,OD
ZZA9 and 10 ZZAL I and 12
<.OQ
<,OD
Smple IID mDO1205 M001278 M01202
NMMI
MD01208
Cw- ofPFOS 0
24.4+/-0.4 48.4+/-1.5 23.2+1-0.2
11.8+/-O.l
59.4+/-O.l
QC Results
QC ChecILCahbmtionCheck (QC I) CaMradon Check(QC2)
% Recovery
1040/o 1060/o
Branched Isomer Abundance
Smple Pool StandardNiaterial WMduals Sampledin1998 3M CoftapGrovePlantWorkers Individual@sa@ed in1970's ,PooledSeraSamples
Percentages
% Abundanceof BranchedIsomers
(Averaw) 220/o 34%
45% 370/9 31%
% Abundanceof BranchedLomen
(StdD.ev.) 3% 5%
4% 5% 5%
I -LOD = LimitofDet=don 2-LOQ - LimitofQuantitation
a sampledInpool) nia 31
3 12 11
3M EnvironmentalLab 5nl9g
PHASE V &W VI
Quantify COMPOUOD SU@CY ASPOrt
P"e
\WJXLYM
3 M\
9
Last mo"tied: sun mar 22 14:33:39 It"
Method:
e: \.USLTNX\PRUBB. M\MTMCB\PM
Last mo"fiod: &at Mae 21 19:19!42 1996
saw a "St@ C:
","J,,
O"M"\012"
9
Job Code:
Printed:
Sun Mar 22 14:52:37 1998
Camqxnind 1: IPMS
t N@
1 03219801
2 03219402
Type AnalYto
Anslyto
3 03219803 4 03219804 5 03219005
Analyto Standard Standard
6 03219806 Standard
7 03219807 S 03219006 9 03219809
Standard Standard Standard
10 03219810 Analyto
11 03219011 Analyto
12 03219812 Analyto
13 03219013 Analyto
14 03219014 Analyto
15 03219815 Analyto
16 03219816 Anglyto
17 03219827 Analyto
If 03219011 Analyto
19 03219019 AnslYto
20 03219820 Analyto
21 03219821 Anslyto
22 03219822 Amlyto
23 03219923 OC
24 03219824 Malyt*
25 03219025 Analyto 26 03219826 Analyto
27 03229927 Analyto
28 03219826 Analyto
2:
0321::2:
A-alyto Analyt.
3 0321 3
31 03219031 AnalYte
32 03219632 Analytt
33 03219633 Analyto
3: 0321::3: Analyte
3 0321 3
36 03219836 AoCnalyto 37 03219837 Analyt*
38 03219838 Analyto
39 03219839 Analyto 40 03219440 Analyto
41 03219041 Analyto
42 03219$42 Analyto
43 03219043 Analyto
44 03219144 Analyto
45 03219845 Analyto
46 03219846 Analyto 7 0321::47 AAnnaallyyttoo
:8 0321 49
49 03219849 Analyto 30 03219850 Analyto
51 03219851 Standard
52 03219052 Standard 33 03219033 Standard
54 03219054 Standard 55 03219655 Standard
56 03219056 Standard
ample Text NoW Blank
U20 blank-I Sera blank-I
0.996 PPb re mi 4.90 PPb FC Mix 24.8 ppb FC Mix 49.0 ppb FC Nix 96.2 ppb FC Nix 142 ppb TC Mix M*(M Blank
M001203 M001205 12)
N001218-1 M001278-1 (2)
M001278-2 M001270-2 (2)
M01202 U01202 (2)
M001221 U001221 (2)"@-'
W001208
U001200 (2) Cal check, 24.4 ppb
NoW blank
ZZAI ZZAI (2)
ZZA2 ZZA2 9TA3 IZ13
(2) J21
ZZM ZZR4 42)
ZZIL5 ZZAS (2) Cal check, 24.0 ppb
MGM ZZAS ZZh6
and 1 and 1*(2)
ZZR'Y
ZZA7 (2) ZIA9 and 20 ZZA9 and 10
(2)
ZZRll and 12 ZZAII and 12 (21
AZ26-1 AZ26-1 (2) NoW blank K*OR blank
320 blank-I Sera blank-I 0.996 ppb IC Mix
4.90 ppb YC Kix 24.8 ppb TC Xix 49.0 ppb TE Nix
96.2 ppb FC Mix 142 ppb FC Xix
IPFW PMS
As"
4292 3239 2913
sots 10464 41137 74118 142*7$7
193769
3257 39673 380"
74992 79499 71794
72374
37934 37494 21224
23.018 $0087 $9709
41304 2021 3310 3397
3277
3300 5598 $721
7108 7038
3046 3340 41633
2900 4883 5071
4181 4207 6631
#4$0 5342
5262 44210
44259 2803 2744
3397 3223
Sall 10482 40948 75059
243153 203166
com.
0.26 0.00
0.00 0.76 4.53
25.72 49.51 95.94
131.18 0.00
24.71
24.15 49.11
50.16 46.90
47.45 23.32
23.20 11.94 11.02
St.S4 39.34 2S.94
0.00 0.00 0.00
0.00 0.40 1.17
1.25
2.21 2.17
0.80
0.99 25.20
0.00 0.67
0.80 0.19
0.20 1.08 1.78
0.99 0.93
27.25 27.18
0.00 0.00 0.00
0.00 0.81
4.54 25.39 49.16
96.21 137.66
wev news
bb bb
m -23 M
-8 M
4 mm -1 M
0m
-8 NU bb m
NK m
PK m
mm m
m mm m
m m 4m bb
m m
mm m m
xx mm
m m mm
6 34K bb
m m m Nk
mm
m m m
NK mm
mm m bb
w -19 m
-7 M
3M 0m 0m
-3 NNX
t
Quantity ciaLbiratLon Report
calibration, L"t =&tied: ftirttod*
Ct\oo&SZMM\PNAUS.M\CURV=S\pm am bar 22 14:49..38 logo fta mr 22 14:52:38 It"
@on-"undIname:PFOS Corretafiocnoefficienrt-: 0.999912,rl\2- 0.999823 ,Calibraflcounrve:1447.275720 0 x + 3910.409399 Responsetype:ExternalStd,Area lcurvetype:Linear,Origin:Exclude,Weighting:Null,Axis tms: None
2.O9e5-
ftes I
Response-
x
r 0-
one'
3M EnvironmentalLaboratory-FluorineAnalyticaClhemistry Teani
KrisHansen -Sr.AnalyticaClhemist FluorineAnalyticaClhemistryTeam Building2-3E-09 612-778-6018
]?hueV and VI: QuantitativaenalysiosfPFOS inhistorihcuman serasamples
and inhuman serasamplesfrom ruralNorthernChina
Sunnuary:
Two setsofsamples,thefLm with 12 mVIes inplastivcials(Z,.M)and thesecondwith5 samplesin glassvWs (M-ed),were affhad tothe rwmenftlLabby JeffMandel (3M h4adimo on March 20,1998. ForbothsM umple volumevariedfrom0.2to1.0mL ofhum2" am A volume between0.4- 1.0mL ofciaisamplewas extracteudsingan ion@ ream= Sixamples intheZeed
didnotcontainenoughvohm foradracdon;indme cum twosampla (e,&ZZA6 and ZZAS) vim
fm binedandckuactedwoneunq&. Tk odmcts wereanaly2Wquandbdvdy forpeifilinnnff,@tand
mffomw (PFOS)by hghvemm hqtud mmtogWby-clec@@ mm Vocametry (EPLC-P-SM.
Anabft identificatiwoans vatud by comparisonofmoleadu ion-HPLC retentiodnm oftheomacted
ambft and standardMatM2' Smpla wm quammv* evguftd aga= a Vmd@y pqmmd, frv-
pointumctw curve(irA-20."9). Each sampleacum wasanab-adtwice.Cahimadonchecks
anabmed evray5 samplm werewithin6% ofeq)ecievdaluel
The ulentitoyfPFOS inwvmal randomlyseladedmupla inthisphase(M-M only)was
confmned usingEPLC-ES&MO. Inallca theanalyteexhfl)itaecdharacteristriectentiotnime,
characteristpircimaryion,and Bm r
wns.
historicsamples Tli.-serasamples in theM-sek collectefdmm donm intheUS in ft 1960s,bad an average
PFOS concentratioonf33.4ppb;thesamplesrangedinPFOS concentratiofnrom II..tto59.4.
Foreign samples
The 9 samplesintheZ-W (indmung 3 =nposite samples)were coU=W from donorsinrural China and were determinedtohave a much lowerconcentratioonfPFOS thanany hlim2n seradataset anab7,edpreviouslySixamples didnotcontainPFOS abovethedftmon lumt ofdus analytical method (1pi)b)T.he remainin3g sampla awenced PFOS ednm=dm I= than5 ppk thelimitof
quantitagoilWith thecwmdon ofoneInim2nma samplecollecteidndw 1980s(Will0002),tlmm an theonlyhil-2nsampla determinedtocontainI= than10ppb PFOS.
entalxununary.-
S@vnplepreparationI:on-pairinegxtracdon
In a pH Controlle=dvironmn4 an ion-pdringrogmt =rabutylammonium mdfat(eMA), is
used tocxum theanabu from thematnx Amomc conip=W Wre thecationirceagent,wl=dvely
targetPsFOS and pefflwrooc=oate(POAA). SW=quent tothefimnationofthe7BA-mon pai4the anabu isMmsfeffedtoa non-polarorganicsoh=t (ethyalmtm), dn4 andn=nmuftd inmdmd
forNM analysis.
HPLC. Characterisdrcetenhonhmesfor PFOS
@ InBPLC, an aliqwtoftheext= isinjecteadndpassedthrougha chromatographiccolumil Based on theafftnitoyftheanalyteforthestationary-phaiwnthecolumn mWM totheliquidmobile. phasepassingthroughthecolumn.thea=lyw isretainefdora characterisatmiocunt ofdm For example,ina standardsolutionP,FOS may cluteat10.5inini . Reftntiontimesbetweena standard
05/07/98
PFOS solutionand the analyteextractedfrom serainthisanalysiswere matched towithin 1% on the BPLC systeal
E&MS. Detection and monitoring of the molecular ion
Analysis of PFOS standards indicates thattheprimaryioncharacteristoifcPFOS isM/z - 4" amu .,correspondintgothemassoftheanioniscurfacmt(CIF17SO3-).Thisionwas monitoredselecdvely toma)e@ sensitivitAy.scanofm/z-100 to 1210(negativoenly)was alsocouacte&
HPLC F.S-MSIMS.-Dewdon and monitoringofcharacteristsiecondwy ions
ES-MSMS isverysimOI2toESNC, exceptthatitad& an additionadlimensionofcutainty*to
compound identificatiAosn.inESW, a characterisitoincisselectedA.fterselectiont.heES-B(SM
characterimtheionfurthebry smashingitapartwithhigh-c=U ga& As a resulotf thesmashing
secondaryionicfragments(daughterions)c,harwm= ofthemolowle,arecreatedand debwte&
For example,forPFOS a=bi* ion499 isselecteadsthecharacterisptriicmaryim Thisionis
mnnr.lheidntootherionsa# n 80 jimu(correspon&mtoS%I, 99 amu (COIJL 22--tDFS03
130
amu (correspondintog CF2SO3), 130 -Qmu (C2F4SO3), and 230 amu (C3F&S%). Each ofthesesecondary
ftpients isdcwctedattheddector.
QuWft controlmmmary: Due tosamplelimitationsse,rasampleswerem extracteidnduplicatew,ithI exccpdm For
this== rema, matrixsp&w couldnotbe evaluatefdorthesamplesE.ach sampleam= was amb=d induplicateO.ne sample,MOO 1278 containedenough matmialfortwo exuacdon& Mm presentedresults
forthissample arebasedon duplicataenalysiosfeachofthetwo extractionsN.(ethanolblanks wei analyzedperiodicalltyoensurecompleteisolatioonfthesample.A nud-lcvd(24ppb) quaht3rcontrol
sample was anabrzodcvciy5 sampk& BecauseIhilim2snerawithoutPFOS isnotavailables,amplespf pooledserapurchasedf3romSigma wen pre-exbwted,sp&od witha sumdard concentratioonfPFOS, iimd
re-mmacte& Thisprt-uuactedseraisunderstoodtobe vay simil-t4othesamplematrix Thisfmc pointcxbww curvewas analyzedbeforeand afterthesamples.Quanti=on ofthesamplesisbasedon therinea regressioenquationderivedfrom theaverageofthetwobracketingcurves(rA2*='0.999). SpecificQC parametersareavailabloen theappended resulttsable.
Limitofquantitafion The currentanalyticamlethod hasbe= usedtD evaluatea bW mp'of PFOS levelsextracted
from wxa; themethod isnotopdndzed forpre*= low-kvd (< 5 ppb)quantitadon,butinsteadfor samplesintherange of20-60ppb. Given theconcentrationcshosenfx)trhisoptimizatioonfthe sbmdard curve,whilethem isa statistidciaflfcrc= fDrsamplesevaluatefdimm 5-100ppb,then isno statistical diffm= betweensamplesquanbuttedfrom 1-5ppb. The quantitatidoonesnotbecome MdWcaBy defendab]until5 ppb;thusthisvaluerepreantsthelimitofqwmtitation:btrhismethodl -qnmpks desizo2ted<LOQ areestimatedtocontain1-5ppb PFOS. Nfiutha accuracyand precisionin
tatioonfthelow-kvclZ,-sasamples(sampleslea than5 ppb)isrequireda,specialow-level quantitatiosnystemwillbe reqmrc&
Limitofdetection I'hehaut ofdetectiofnordus analyficamlethm isblsedon arwystrecogiiitioofnthedisd
peak shaperesultinfg3romPFOS angyns. PFOS standardm2tenn'and PFOS exuactodfrom sera analyzedby theconditionsreportedhere,show nearbaselinreesolutioonf Ibranched and I lines PFOS isomer Ile apex ofeach peak intheMC-u= o=us ata specifirce,prod=ble rdendon dm oW & ratioofthebranchedpeak tothe'*no peak ishirlyconsistendtown tothelow smda4 1.0ppb.Those samplesthata) had PFOS levelesvaluatedatI= thanthelimitofquantitatiaond b) evidencedthe distincpteak shape,were designated< LOQ. Samples,thata)havePFOS ImU evaluatedatlessthan the limitofquantitatioannd thatb)do not reflecttheuniquePFOS peak shape,were designated< LOD. These samplesareestimatedtocontainfrom 0-1 ppb PFOS.
05/07/98
2
instmmentaispecirwc
BPLC system
Howlen Padcard Series1100 Liquid
Column:Krimm Betug Cis
2 x 100 mm
5 pm pardde size
Flow rate: 300 gumin.
SolventA:
2.0mM Ammonium Acmo
SolventB:
Methanol
SolventGradient
45 to 90 O/oBin9.50minl
Ekid at90 %B for3.50minl
ReturntD_45%B in 1.50minl
EUd aC4S %B for3.5minl
injadm vobm. 10AL
Injecdm /sanvk:2
F-Jecbwpaymm specftmtzr
bfi=mass Platform]IAPI Man SpecUcmeW, -ChicL-
MassLynx 2.4 Software
Cone voltalp:.-20v-;60v
Mode: clecaospmynegatm
source
115 OC
Aulpw vacuum press=: 0.000043mbar,0.000079mbor
Ions: 369,413,499,427 Electrode:cros*41ow
05/07/98
3
FluorineAnalytical Chemistry Team
r@JHanwn
Samples Received:
3/6/99
Samples Extracted:
3/9/98
Samples Analyzed: 3/11-3/12/98
Analysisbr. CalibrathmCurve Range: 1?ofCalibrationCor-m LOD': LOQ2:
ESM lppb- 49ppb O."s 1 plpb 5 ppb
PHASE V and VI: Analysisofforeign(ruralNorthern China) and historicserasamples (1960)
Conc. ofPFOS
Sample ED
ZZA6
ZZA2 ZZA3 27A4 ZZAS and 8
<DD <,OD
<LOQ <A)Q <,OD <,OD
ZZA7
<A)D
ZZA9 and 10 ZZAII and 12
<A)Q <.OD
Smple ED mOO1205 IMDMO1270 127085 bo 2I12
COW. ofPFOS (pob)
24.4+/-0.4 48.4+/-I.S 23.2+/-0.2
lh=1203 59.4+1-0.1
QC Results
QC ChedLCalibratioCnhwk (QCl) CaM=tkm Cho* (QC2)
% BwAn"
104'Yo 106%
Bmnched Isomer Abundance
Samle Pad SUndard Matmial hdhidualsSampled in 1999 3M C4op Gwn PlantWorken IndividukSampM in1970's 1POoledSera Samples
Percentages
% Abmdazm of % Abmdana of
BrancbW Immm Brawbed Immm
(Averap)
(St4DLev.)
22%
3%
340/o
5%
45%
4%
37'Yo
5%
1
31%
1
5%
1
a (0@obd Inpoold nla 31 3 12
I -LOD - LimitofDewdon 2-LOQ - LimitofQuantitation
3M EwAmnmentd lAb 5nl"
PEULSE V Ed VI
Quantity ConvowA
9@ry
FAmpart
Sasple List: Lost modified:
moth",. Last modified:
Job Co":
C: Sun Mar 22 14.33:59 lose C: %whosLymx\pnuu. nw\mms\pm Set War 21 19:19:42 1998
Printed:
Sun Mae 22 14:52:37 Ito$
Compound 1: PM
0 m@
TY"
1 03219801 Analyto
2 03219002 An&lyto
3 03219403 Analyto 3219004 Standard
4s 00321980S Standard 0 03219806 Standard 7 03219807 Standard
8 03219608 Standard 9 03219809 Standard
10 03219810 Amlyto
11 03219811 Malyto 12 03219012 Malyto
13 03219913 Analyt*
14 03219914 Analyto
15 03219813 Analyt* 16 03219816 Analyto
17 03219917 Analyto
18 03219818 Analyto 19 03219919 Anslyto
20 03219620 Analyto
21 03219021 Analyto
22 03219822 Amlyto
23 :321:923 Qe
24 321 024 Analyto
23 03219825 Analyto 26 03219826 Auslyto
27 03219427 An&lyto
28 03215120 Analyto
29 03219829 Analyto
30 03219430 Analyto 31 03219431 Analyto
32 03219832 Analyto
33 03219833 Anslyto 34 03219034 Analyto
31 03219835 OC
36 03219036 Analyto 37 03219837 Analyto
38 03219834 Analyto
39 03219839 Analyto
40 03219040 Analyto
41 03219841 Analyt* 42 03219042 Analyt*
43 03219943 Analyte 44 03219944 Analyto
45 03219845 Analyto 46 03219940 Analyto
47 03219847 Analyto
1 03219840 Analyto :9 03219049 Analyto
50 03219050 Analyto 51 03219851 Standard
52 03219132 Standard
S3 03219853 Standard
5345 0321:::: Standard
0321
Standard
36 03219956 Standard
Semple Tmt N*M blank
H20 blank-I Set& blank-I 0.996 ppb FC xix
4.90 ppb fC Kix 24.1 ppb fC lUx
49.0 ppb IC KLm %.2 ppb FC kix 142 ppb rC Mix MOCK Blank M001203
MOO1205 (2) MOO1278-1
U001278-1 121 MOO2271-2
=01271-2 (2) U01202
*01202 (2) HOO1221 HOO1221 (2j,@, W0120t "-' =41206 121
Caa cbeek, 24.9 ppb PIM no= blank
ZZRI ZLU t2) ZZA2
IZA2 (2) --A'
ZZA3 (2) ZZh4 Z7A4 (2)
ZZAS ZZA3 (2) C" check, 24*$ ppb PrW
NoW ZZAG =4 9 ZZKG and $-(2) Z7A7 ZL%7 (2)
ZZRS and 10 &Zht and 10 (2)
ZZLII and 12 ZZPUI wW 12 (2)
AZ26-1 AZ26-1 (2) HOOK blank No= blank
22o blank-I Sera blazLk-I
0.996 ppb ]rCKix 4.90 ppb fC Kiz 24.8 ppb PC KLx
49.0 ppb IC Kix 26.2 ppb FC KLx
142 ppb rC KU
Area 4252 3239
2963 5013 104" 41137
74119 142707 193746
3287 39973 30848
74992 764"
71794 72378
37934 37494
21224 itoll 9M7
99709 41304
2221
3310 3397
3277 3300
3396 5721
7104 7054 soff
3340 4L$33 2900
4843 3072
4101 4207
9931 6488 S342
5241 44210
44250 2803 2744
3397 3223
sogi 10482 40946 7SOSS
143233 203144
cona. umv nave
0.29
bb
0.0
bb
0.00
m
0.76 -23 M
4.53 -8 NK
23.72
4m
46.31
-1 M
93.96
0m
131.18 -9 MM
0.00
bb
24.71
mm
24.15
m
49.11
m
so.is
m
49.90
m
47.43
NK
23.31
m
23.20
m
11.96
m
11.92
m
39.54
m
St.34
m
25.64 4 m
C."
bb
0.00
m
0.00
m
0.00
m
0."
m
1.17
m
1.23
m
2.21
m
2.17
m
0.80
m
0.
m
24.20 4 m
0.00
bb
0.67
m
0.80
m
0.19
m
0.20
m
1.08
m
1.79
m
0."
m
0.93
m
27.85
m
27.88
m
0.00
m
0.00
m
0.00
bb
0.00
m
0.81 -19 M
4.34 -7 M
23.39 3 M
49.10 0 m 96.21 0 M
137.
-3 OW -
1444%
guatley calLbv*LLOO ammm
emalbntlent
Lost ao"fiods ftletod:
fte Nw 22 14.49-.S@ 1999 am "W 22 14:32:301"9
ConipounIdnum: PFOS CorreWon coefficienrt- 0.999912,rft2- 0.999823 Calibradoncurve:1447-2757200 x + 3910.409399 ResponserM: ExUmal Std,Area Curve rM: Linew,Origin:Exclude,WeiShting:Null,Axis tram:None
2.O9c5-
Responw-
x x
c
3M EnvironmentalLaboratory-FluorineAnalyticaClhemistry Team
KrisHamn -Sr.ArWydcW Chemist FluorineAnalyticalChemistryTeam Building2-3E-09 612-778-6018
Phase VIOI: US Geographical Distribution Study - PFOS levels in human sera
Slimmm:
Fifty-fivseamples ofcoldhuman serain pwdc cenbiffigueiba were suppliedtothe
EnvironmentalLab by JeffMandd (3M Mefficalo)n Mamh 19 and Mu& 20, 1998. The samplm
collectefdrom sitesaroundtheUnitedSLite4containedsevew mTs ofsa2 One mL ahquob ofsua
viae renwved from each sampleand ekbuted vnthan ion-pamg ragod, nearlyallofft sampw were
pir-a@'- induplicatel.U ftm ckuam wem analyzedquanumvely for
mlfmft
(PFOS)by highprasm liquiddmmatogWby-el@@
== Vecftmetry(HPLC-ESW). AnW*
identificaflwoans verifiebdy comparisonofmolecularion-EPLC =tendon dm oftheacuictedanabu
and standardmaterial.Samplesvm qmntltum* evaluatedapum a spemauy prepar4 five-pomt
muzcted curve(rA2= 0.996).A matrixspikecahlrationcheck,analyzedinthemiddle oftheanalysis
sequence,was within1% of expectedvalues.
The sem samples in thegeographicdistributiosntudyhad an averagePFOS odwmtmtion of 28 ppb; the samplesranged in PFOS conmnbadon from 9 ppb to59 ppb. The percentabundance ofthe branched chainisomer was 41 +/-40/e.In standardsolutionosfPFOS, thebranched chainaccountsfor 21.7+/-3.1%ofthetotalconcenuadorl A detaileodnimaiy oftheresultissattached
The identitoyfPFOS inseveralrandomly selectesdamplesinthisphase W-M o*) was confmned usingHPLC-ESMSNO. In allca theanalyteodubited a cbaractmuticretentionhuac.a, characteristpircimaryion,and fivecharacteristsieccondaryions.
Experimental summary.
SamplepreparaftonI:on-pairingixtraction Ina pH controlleednvironmentan ion-panng reagent=,abutyl ammonium sulfateCIBA), is
usedtocxvw theanalytefrom thematrix Anionicconipminds,Mm PFOS and peawrooc=oate (FoAA), arewiwtn* targetebdy thecatiomcreagent subwquw totheformatlonoftheTBA-emon pair,thenabft istransferretdoa non-polaorrganicsolvent(ethyalce=), dn4 and m=Wbdcd in methanol forIHPLC-ESKA analysis.
HPLC CharacterisheretentionhmesforPFOS
In EPLC, an aliquotof theextractisinjectedand passedthrougha
column.
Based on the affinitoyf theanalyteforthestationary-phasienthe column relativteo the liquidmobile-
phase passingthrough thecolumn, the analyteis retainedfora characteristaimcount of fim. IFOR
example,ina standardsolutionP,FOS may aluteat 10.5minutes.Retentiond= between a standard
PFOS solutionand the analyteextractefdrom serain thisanalysiswere niawliedto within 1% on the EPLC system
ESMS. Detectionand monitoringofthemokcular ion Analysisof PFOS standardsindicatetshattheprimaryion characteristoifcPFOS ism/z - 499
amt% correspondingtothe mass of theanionicnufactant(CsFl7SO3-). This ionwas monitored selwdvcly tomaximize sensitivitAy.scanofm/z-100 to1210 (negativoenly)was alsocollected.
05/07/98
1
HPLC ES-M&MS.-Detwdonandmonitorionfcgharactersiesctoincdairoyns ES-MSMS isverysimiltaorESMS,exceptthaittaddsanadditiodniamlensiofncertaitnoty
compound identificatioAns. in ESMS, a characteristiiocnisselectedA.fterselectiont,he ES-MSMS characterizetsheionfurtherby smashing itapartwith high-energygas. As a resultof the-rm24thing secondaryionicfragments(daughterions),characteristoifcthemolecule,arecreatedand deuztc&
For example,fbrPFOS analysisi,on499 isselectedas thecharacteristpircimary ion. 1-nision is smashed intootherionssuch as 80 amu (correspondintgo S03), 99 amu (correspondingto FS03), 130 amu (correspondingto CF2SO@), 190 amu (U4SO3), and 230 2mu (C3F6SO31. Each of theseseoon&ry
fiagments isdetectedatthedewmr.
Qualitycontrolmmmary: In most cases theserasampleswere extractedin duplicatef;orthosesamples thatwere,standard
deviationvaluesareincludedinthetableofr=WtL Nb= spdm werepreparedforseveralsampla too.
Ifavalable,thematrixspikerecoverieasreincludedintheresulttsable.A nud-kvel (49ppb)quality
controlsample was analyzed,rwmry forthematrixspikewas &-Uwmmed tD be 1010/e. Be== h-man
sera-%ithouPtFOS isnota@@@le, samplesofpoolednm purchasedfrom Sigma were pro-exuwtmt
spikedwitha standardconcentratioonfPFOS, and re-c@
Thispre-axu=W seraisunderstoodto
be veryc*mila tothesamplematrix Thisfivepointexuactedcurvewas analyzedbeforemW dta the
samples. Quantitatioonfthesamplesisbasedon thelinm regressioenquationdaived from theavmp
ofthetwo bracketingcurves(rA2- 0.996).SpecifiQcC parametersareavailabloen theappended msdts
table.
Limit of Quanittation The currentanalyticamlethod has been used to evaluatea largerangeof PFOS levels=Uacted
from sera;the method isnot optimizedforpreciselow-level(< 5 ppb) quantitationb,ut insteadfor .
samples in the range of 20-60 ppb. Given the concentrationschosen forthisoptimization of the standard
mm while thereis a smmcal diffeam forsamples evaluated from 5-100 ppb, them is no sbbswd differencebetween samples quantitatedfrom 1-5 ppb IU quantitabon does not become mtmUcaUy defensibleuntil5 ppb, thus tlnsvalue representsthe limitof quand=on forthismethod. -Sampla d@edgnated <.OQ are estimated to contain 1-5 ppb PFOS. Iffurtheraccuracy and pro@mon in
quantitationof the low levelZ-wt samples (samples lessthan 5 ppb) is requiria a speciallow-lmd quantitationsystem will be required.
Limit of Detection The linutof detectionfor thisanalyticalmethod isbased on analystrecognitionof the distinct
peak shape rowtmg from PFOS analysis.PFOS standard materialand PFOS extractedftom sera
analyzebdy the conditions reportedhere,show near baselineresolutionof I branched and I linearPFOS
isomer The apex of each peak in the HPLC-U= occurs ata specificm,yroducfl)lcretentionum and the ratioof the branched peak to the linearpeak isfairlycondsw down to the low standard, 1.0 ppb. lUm samples thata) had PFOS Imb evaluatedat lea than the limitof quantitationand b) evidenced the distinctpeak shape, were designated< LOQ. Samples thata) have PFOS levelsevaluated at lessth4n the limitof quantitationand thatb) do not refled theunique PFOS peak shape,were desipated < LOD. These samples are esdmted to containfrom 0-1 ppb PFOS.
Instnimental specifics: HPLC system Hewlett Packard Series1100 Liquid Chromatograph
ColuzLn:Kcystone BetasilCis 2 x 100 mm 5 @mm particle size
05/07/98
2
Flow rate: Solvent A:
300 IAUmin. 2.0mM Ammonium Aettgo
SolventB:
Methanol
SolventGradient:
45 to 90 O/oBin 9.50mins.
Hold at90 'YeBfor3.30minl Return to45 YeB in 1.50minl
Hold at45 %B for3.5mins.
Injocdonvohme: 10 pL
Injwdons /sample: I
Electrospramyass spec&ometer
mcroman PlatformiiAPI Mm SpwUomeW, -ChicL-
ManLynx 2.4 Saftwm
Cone voltnw: .60v
.Mode: clewupny neptive
sou= wmpuviu@
115-C.
Analym vacamm presmu: 0.000043mbar,0.000079mBa
I=: 499,427 Electrode:amss4low
05/07/98
3
3M Eavi=vncnWLAb
FluorineAna"cal Chemistry Team
S@pin Reedved: Smapin Ezbm&M: Sompks Aambwd:
3/19/98 3/19M 3120-3/25/99
Ansirb brCW[brsdm C)uve Rmp: 3@ofCmubradm Cwve: LOD':
LOO':
PHASE VII Results: US geographical distribution study - PFOS Ineb in human sen
[P"
St&
sm*m
@
(ppb) Dev-
AKOI
21
0.4
AK02
31
1.2
AK03
25
NA
AK04
19
NA
AZO26
28
2.5
AZO27
37
6.4
AZMS
47
5.9
CA029
23
4.1
CA030
23
0.7
CA031
26
0.0
DE016
24
4.5
DE017
32
2.2
DEOIS
21
0.1
DED19
21
NA
DBO20
23
0.3
IA013
40
0.1
IA014
29
4.2
TAOIS
28
3.0
LA47
49
7.4
IA048
39
1.9
LA049
so
7.9
bOO3
31
NA
M3D4
is
NA
M105
22
0.9
bUO6
31
1.1
M007
24
4.9
moos
31
6.6
M009
35
0.6
msso
35
5.3
QC Results
QC C3wdr.
IC4h-WSdOnChWk(QCI)
% Recovery 101%
Branched Isomer Abundance Percentages
Somph Pool StandardMataial I"vkkmkb Sampled in 1"8 3M Cottap Grove PlantWorksm 1"9 k&vw"b SagAW in 1970s and SW PooledSam S=Wles from 1997-98 FOcciP Sam &=pit$. 1994 wW 1994 hAvWuak S=Vled inlate1950t US Coop2phied Su* Samples,iggs
% Abundsnce of
Branched homen
(Av
22% 34% 45% 370/o 31% na 39% 41%
I - LA)D - Lbnk of Dc"on 2 - LA)Q - LimitofQuantitafion
m
I Wb)
mssi
56
MS52
27
bff4l
26
Mr42
24
Mr43
is
NE21
20
NE22
12
NE23
27
NE24
9
NEZS
19
moio
27
NIOII
20
N1012
24
NV44
28
NV4S
25
NV46
X7
SB38
13
SM9
14
SBD40
16
SCM2
56
SCO33
47
SCO34
52
IX035
32
TX036
26
T=7
29
WY53
35
WYS4
13
WY55
20
% Abm@
Brmwl"
of
l@
(ML Da.) 3% 5% 4% 5% 5% na 4% 4%
a(#MPM) nta 31 3 12
11 na 5 55
Dw.
S.1 9.5 4.1 3.5 3.2 1.3 1.0 6.7 2.0 0.8 5.9 0.8 2.0 0.8 0.1 6.6 0.2 0.7 0.6 1.8 2.8 2.1 11.2 1.2 3.6-.-0.7 0.4 IJ
5/7/98
778-60io ESLO Ippb to248 ppb 0.9% I ppb 5.ppb
PHASEVU
Quantify C=Wound Sumary Report
BeAmple List; LAst modified:
Method: Lost Modified: Job Code:
C;\NUSLYMX\PHUZI -VW\BAWWM\PXMZI Thu Apr 09 09:39:18 It"
C: \MUSLYMX\PKAUI. PMD\MTMB\VM Thu Apr 09 10:00:36 is*@
Printed:
Thu Apr 09 10:11:30 1990
Compound 1: PTOS
N@
Type
1 04079901 Analyto
2 04079$02 Analyto
3 0407::03 Analyto
4 0407 04 Analyto 5 04079605 Analyt*
6 04079806 Standard
7 04079007 Standard
8 04079408 Standard
9 04079009 Standard
10 04079810 Standard
11 04079811 Standard
12 04079912 Standard
13 04079813 Standard
14 04079814 Standard
15 04079615 Standard 16 0:07::16 Standard
17 0 oll 17 Standard
10 04079118 Anslyto
19 04079419 Analyto
20 04079820 Analyt*
21 04079821 Analyto
22 04079422 Analyto
23 00 ::7::23 Analyto
24
7 24 Analyto
25 04079825 Analyto
26 04079826 Artalyto
27 04079027 Analyto
21 04079128 Analyto
2: 04:7::209 OC
3 04 7 3 Analyto
31 04079831 Anslyto
32 04079132 Analytt
33 04079633 Analyto
34 04079834 Analyt*
35 0407::3S Analyto
36 0407 36 Analyt*
37 0407::37 Analyto
30 0407 38 Analyto
39 04079839 Analyto
40 04079040 Analyto
41 04079041 OC
42 04079642 Analyto
43 04079943 AA&lyto
44 04079044 Analyto
45 04079945 Analyt*
46 04079046 Analyto
47 04079847 Analyto
48 04079849 Analyt*
49 04079849 Anslyto
50 04079850 Analyto
51 04079051 Analyto
52 04079852 Analyto
53 04079OS3 QC
34 04079954 Analyto 55 04079855 Analyto
56 04079856 AA&Lyto
57 04079857 Analyto
54 04079858 Analyto
59 04079859 Analyto 60 04079060 ArL&lyto
61 04079861 Analyto
62 04079642 Analyto
63 04079663 Analyto
64 04079064 Analyto
GS 04079665 Analyto 66 04079946 Analyto
67 04079847 Analyt*
04:7:::: Analyto
:39 04 7
Analyte
70 04079870 Analyto
71 04079871 Analyt*
72 04079872 )Lnalyto 73. 04079873 Analyto
74 04079874 Analyto
75 04079075 Analyto
76 04079076 Analyto 77 04079877 Analyto 78 04079870 Analyto
79 04079979 Analyto
10 04079800 Anslyto
81 04079@el Analyto
gmwle Text
Hoch Blank Water blank inj 1
Water blank inj 2 KS Blank inj 1 KS Blank inj 2
0.996 ppb inj-l 0.996 ppb inj-2 4.90 ppb inj-l 4.90 ppb Lnj-2 24.8 ppbinj-l 24.0 ppb inj-2 49.0 ppb inj-l 49.0 ppb inj-2 96.2 ppb inj-l 96.2 ppb ial-2 142 ppbLnj-2 142 ppbinj-l meah blank
St-11 RS04078 inj 1 39-11 US04079 lal 2 SE-12 U304079 inj 1 SZ-12 US04079 inj 2 SZ-13 K$04078 inj 1 SZ-13 9304070 inj 2 SZ-14 NS04076 inj 1
SZ-14 MS04078 Lnj 2 SZ-15 US04078 Lnj 1 SX-15 3304070 inj 2 24.8 ppb cal check aboob blank
3F,-16 M504078 inj 1 SE-16 RS040'18inj 2 SE-17 M304078 Lnj 1 SE-17 R504079 Lal 2 St-18 U504078 inj 1 SE-19 KS04078 inj 2 SE-19 U504070 inj 1 SZ-19 8304076 inj 2 39-20 MS04071 inj 1 SE-20 KS*4078 inj 2 24.Sppb cal check
mah blank SE-1 RS04070 lnj 1 SE-1 H304070 Lnj 2 SE-2 MS04076 inj 1 SE-2 H304078 inj 2 SE-3 KS04070 Lnj 1 SE-3 KS04079 inj 2 SE-4 K304078 inj 1 SZ-4 KS04078 inj 2
SE-5 NS04079 inj 1 SZ-5 NS04074 inj 2
24.8 ppb cal check "ch blank SZ-6 M304078 inj 1
SE-6 NS04076 lnj 2 SE-7 H304072 inj 1* SE-7 US04075 inj 2 SE-0 NS04079 Lnj 1 39-8 U3040-19 Lnj 2
39-9 K$04078 inj 1 St-D U504079 Lnj 2 SIC-10 R$04071 inj 1 $Z-10 R504076 Lnj 2 moh blank Water blank lnj 1
Water blank Inj 2 Sera blank Lnj 1 S*ra blank Luj 2
0.996 ppb lal-I 0.996 ppb iml-2 4.90 ppb inj-l
4.90 ppb Lal-2 24.4 ppbinj-l
24.1 ppbinj-2 49.0 ppb inj-l 49.0 ppb inj-Z 96.2 ppb inj-l 96.2 ppb inj-2 142 ppbinj-l 142 ppbxnj-2
a? 9.910
10.471 10.479
10.487 10.489 20.411
10.430 10.423 10.415
10.405 10.411
10.419 10.373 10.421
10.418 10.434
10.425 10.496
10.503 10.401 10.405 10.478
10.481 10.485
10.486 10.4$5
10.479 10.477 10.365
10.402 20.486
20.48S 10.424 10.479
10.487 10.477
10.437 10.420
10.411 10.43S 10.358
10.438 10.353 10.357
10.352
10.340 10.470 10.467
10.336 10.337 10.434
10.403 10.309
10.388 10.305 10.291
10.410 10.470 10.463
10.4ss 10.336
10.343 10.461
10.404 10.406 10.402 10.407 10.390
10.404 20.336
10.334 10.339 10.340
10.340 10.340
10.340 10.344
10.339 10.342
10.346 10.342
Area
5$375
3243 4594
5092 4829 5970
S750 11454 illes 41237
42564 73645
74906 132595
127206 192332
196237 4489
ssso 9246 7869 7340
9139 9473
7496 7116 7746
7431 12549
3709 7723
7611 3624
3633 5265 5330 4707
4569 3712
4203 12009
3757
9377 9822
9759
9610 10125 10474 0107
7985 9294
9300 11515 4037
8249 7947
10301 17578
7772
7839 022S
9132 20521 20053
4367 4524 4379 4342
4493 5875 5794
11191 11296 40768
41257
68332 66993
116061 115447
162113 165349
Cma. IDOV flags
36.04
bb
0.00
bb
0.00
bb
0.00
bb
0.00
bb
0.00 -100 m
0.00 -100 m 3.29 -33 NK
3.09 -37 MN
25.35
2 MN
25.59
3M
50.83
4m
50.29
3m
93.01 -3 M
$9.09 -7 M
137.26 -3 bbX
140.15 -1 bbX
0.00
bb
1.37
NK
1.66
m
0."
m
0.24
m
0.00
m
0.00
m
0.34
m
0.00
m
0.54
m
0.31
m
4.10 -93 MM
0.00
XK
0.53
im
0.44
m
0.00
m
0.00
m
0.00
m
0.00
m
0.00
m
0.00
m
0.00
bb
0.00
bb
3.70 -85 m
0.00
m
1.90
m
2.08
m
2.04
m
1.92
m
2.31
m
2.56
m
0.81
m
0.72
m
1.69
m
1.70
m
3.34 -$? M
0.00
bb
0.92 0..69
-m m
1 57
m
7.83
m
0.36
m
0.41
m
0.90
m
1..57
bb
10 ol
m
9.66
m
0.00
m
0.00
bb
0.00
NK
0.00
m
0.00
bb
0.00 -100 bb
0.00 -100 bb
3.10 -37 bb
3.17 -35 bb
25.00
1 bb
25.36
2 bb
45.42 -7 M
43.91 -6 m
80.77 -16 M
00.64 -16 M
114.11 -19 M
117.42 -17 M
fton I
2.91. LL;t: I C:\N"SLTIMVMAM
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3 03239403 AnslYts 3239404 Standard
M"@ US.c* lb@llomokk'-lI K20 0.996 PPb FC MIX
16 0.0332233:::: :1t1..1dgrdd 4.*41.: PpPp-b IrCc -IlnuLx:
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03223990: St@l",g
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Pl- VC KL142 ppb FC KLS
NOCW 916&k ::J::l
12
13 0323::13 A. lYt: 4 0313 14 An:@,
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S338 M Hwu IU-k
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20 0323::zo An lyt 21 0323 21
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22 0323::2 23 032
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22 A,
24 0323982 43 A..Iyrtt.
2: 003 31826 An.lyt.
2 12239024 A"Iyto
27 0323::27 Amlyt:
2: 032233,02291 Amlyt
23
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3310 00332233::3301 AAnnaallyyttoo
0323,432
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33 0323 :33 A"Iyt
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34 0313: 34 A"Iyt: 3: 032 3983S A"Iyt. 3 o3z39s34 Analyto
MV46-2 LA47 I
LA47:2
31 :3233::37 An&1 yto 30 2 34 Am lyt. 39 03239830 Ablyto 40 02239440 A"Iyto
LA47-M mm St@k
IA4::l 1^4 2
41 03239241 42 03239042
43 03231943 44 03239944
3 03231845
Anal A.'Ii-t. AMlyt*
A"Iyt: A..Iyt
LMS@2 NSWI
19250@2 msso-ms
:4 03239$46 A"Iyte
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47 03230147 A" Yt. 41 03230049 Am 1 Yto
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41 03231941 AD41yt* ns
50 03231430 Aalyt. "352-2
03239@Sl A..lyto
52 0323::3S2 Analyto
0323
53
3 Amlyto
54 033223::554 A"lyto
W"3-1 WV$3-2
WYSI-= MOCO Blank
3
4'.0 M&
KLX
0323965: OADCalyto M.Cm Blank
57 0323::37 )"Iyt VT3::l
5* 0323 54
.115 2
59 03239451 A"Iyte WY35:1
03239SGO A"Iyt. vns 2
61 0323:::l A-lyt62 0323 2 Analyto
AX03:1 AR04 I
63 03239063 Am iyt 64 03221964 Analyt:
IU03:2 KZ04
2
6S 03239165 An.lyt M104-SKINaak
66 03239666 An.lyt: ".=
I 03ZJ:::7 A"Iyt. :6: a0323 1 A-lyto
MDOO-1 "009-2
32 70 03233::7 71 03231671
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:JOU:L J012 z
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72 00323::732 A-1 Yt: 73 323 7 An"Yt
7I4S 03239974 A-1
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76 77
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40 032398$0
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105 032
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111 03239912 2ta."Cd
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Conipound I nwm: POAA Correlatiocnoefficienrt-: 0.997996,r^2- 0.995995 Calilradoncurve:319-335230 * x + 393.755503 Response type:ExternalStd,Area Curve type:Linear,Origin:Exclude,Weighting:Null,Axis transN:one
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Conc 14 .0
3M EnvironmentalLaboratory-FluorineAn
KrisHan= -Sr.AnalyticaClhmist FluorineAnalyticaClhem6try Team Building2-3E-09 612-'778-6019
Quantitative analysis of PFOS in hbtoric human serilsamples from Sweden
'eam
Two groupsoftenmm samplesinplastivcialswei supplietdotheEwAronmental Lab by kff NL-M&L (3M Medical)on March 20,1998.The two groups(sampla SE-1 toSE-10 and SEI 1-SE-20) repre*nttwo dlcaw ww penods.Both groupsofumpla onpuod inSweden and inallcans,sample volume variedfmm 0.5to1,0mL of taim2n.am An exactvolum% usualltyheanti=samplewas =uactod usingan ion-paW4 reagent.The =MM wa analyzedquantiftti%f*orPeffluOrOOCtIm milfougeCPFOS)by highpmmm liquidmmatopMby4e=ospmy massq=UomctrY (EMP-ESM. Analyftidentificatwiaosn vedftedby comparisonofmolecularion-HPLC reftndm time oftheexhacted anabu and standarmdgmg. Sampleswerequantift&* ewuated againsat VedWly preparedf.ourpointcxuactedmm (rA2- 0.992).Each sampleactradwas nab7od twice.Cah-brafm chocks6
analyzedevery5 samplm werebetween W106% ofexpectedvalues.
Descriptionofmnples groups.SE-1 toSE-10 and SE-1I to20 Sem samplesSFl throughSE-10 were coUacW from Swedishdonorsmore recentlythan
samplesSE-11throughSE-20. The avemp PFOS concentratioin ffifcirsgtroupswas determinedtobe 1.3ppb;them were threesamplesbelow thelimitofdetechollThe wmd setofsamplesbad an.aveiap concentratioonf 2.0ppb. Intwo ofthesesamples,PFOS conccnusdm was determinedtorboet 1I:=4:mtih@abntloe thedetectiolnimitofthemedw& Allsampla containePdFOS atlea than5 ppb. Itwas
deftmm theisimm ratiofdmc low levelamplel
icxperimentaslmmarjr
Samplepreparation:.Ion-paeixrtirnagction
CMA), is
Ina pH controlle=dWronment, an ion.-pairirnegagentf,tmbuty@ammonium sumft
usedtomtr= theangytefromthematnx Am=c wmpowW4 blwPFOS and peffluomwmoate
(POAA), am sdecdvtlytargetebdy thecationirceagenlSubsequentotheftmufm oftheTBA-anion
pair,ft andyw isftandwed toa nw-polarorpnic solven(tethyalcetat)d.rie4and r=zmdtuted in
methanolforMS anakysil
HPLC.- characteristircetentiotnimesforPFOS jacw and passedthrougha &romatograpbicCOIUMIL
InEPLC, an aliquootfthe=U-Ad is in
inthecolumn mbwm totheliquidmb*L-
Based on theaT2nityoftheanalyteforthestadonary-phase
phasepassin throughthecolumn,theanalyteis mWnW. fora cbamcw&& amount ofdm. For
example,ina standardsohitionP,FOS May cluteat10 5 mmML Rctention bm Wtwwn a smndud
PFOS solutionand theanalytextractefdrom serainWs analysiwsere matched towithin1% on the
BPLC rjstm
EZ&.
Detectioannd monitorinogfthemoleculaIron ArWysisofPFOS standardisndicattehsatheprimaryioncharacteriosftPiFcOS ismlz
4"
amu, correspondingtothemassoftheanionmiubcctant(Wl7So3-)-
ThiisonWasmonitorseedlectively
tomaximize sensitivitAy.scanofm/z-100 to1210 (nepdvi only)was alsoCOUcctc& In those=MPICB
04/20/98
thatwat determinedtocontainPFOS at identityof the anabft usingIRPLC-ESMSHO
1'rnagreaterthan10 ppb,isposuble0 vaffythe to MOWtOr fourchwAcWrWc fragmcn daughterion&
Qualitycontrolsummm7: Due toumple limitationsse,rasampleswere notwdmcted induplicateF.or thissame reason,
matrixspflm couldnotbe evaluatedforthesamplel Each sample =Uact was analyzed in&Vhcatr. bfetbanobllankswei analyzedperiodicaltloyensm complft isolatio(nifthesample.Two mid4md (2.98ppb and 4.95ppb)qualitcyontrolsampleswere analyzedbetweenevay 5 samplel Bacmisehuman mm witboutPFOS isnotavailables,amplesofpooledserapurchasedfrom Sigma we= pre-exbwft4 spiked@itha standardconcentrationfPFOS, and m-=ftacte& Thispm-=UwW sem isunderstoodto be vm similato the samplematnx. lbs fourpomt odmcted curvewas analyzedbeforeand afterthe samples.Quantitatioonfthenmples isbasedon thelinearegmssionequationderivedf3romtheavmp Ofthetwo bracketincgurves(zA2- 0.992).SpecifiQcC pamme= am availabloen thegpended results
table.
Limitofquanatation Thm low iavd sampleswac analyzedagainsta vemauy prqmcd low kvd =ve, As a rerdti6
confide= limitcsalculodaroundft =m valuesindicataequandflabldeiffc=m bctwm samples evaluatedat0 and 1 ppb. For thisanalysist,helimitofquwdtadon and thelimitofdetect*mare
Limitofdetecdon The limitofdetecuonforthisanalyticamletbod isbasedon analystrecogmtlonofthedadnct
peak shaperesultmgfiromPFOS analysisP.FOS ==lard ma=d and PFOS extmctedfrom sera amb7ed by theconditionrseportedhem show nearbasd resolutioOnf Ibmn'cbed and I li PFM iso=. The apexofeachpeakin theHPLC-U= occursata Wcific,reprod=Uc retentiodnm gndthe
ratiofthebrmdzd peaktothelineapreak ishirlyconsistendtown to thelow s=dard, 1.0ppb.Those
thata)have PFOS levelesvaluatedatlessthanthelimitofquantitadonand thatb) do notnfiect
the
PFOS peak shape,were designatebd.dl.O)dm &=don limit.Them samplesareestimated
tocontainlessthan 1 ppb PFOS.
2 04/20/99
Instnunentalspecifics:.
HPLC system HewlettPadmrd Series1100Liquid
Column:KcystoneBeUsil Cis
2 x 100 mm
5 @= particlsehe
Flow rate: SolventA.
300 gjkiin. 2.0mM Ammonium Acetate
Soh=t B:
Methanol
SolventGradient 45 to 90 O/oBin 9.50 minl
Hold at90 O/Z br 3.50mins. Returnto45 %B in 1.50m!nL
Hold at45 %B for3.5minl
Injectiovnohuw-. 10 JAL InjectionIsumple-. 2
Ekchvspray mass spech-ometer bficromassPhdorm n API Nfm Specftometer".ChW
MassLynx 2.4Saftwuc Cone volukm: -20v,-60v Mode: elccuwray neptive Source temperature: 115 OC. Analyzervacuum pre==: 0.000043mbar, O.OWM Ions: 369,413,499,427 Mccuvde: cross-flow
mbar
Elec&osprayM&?JS
mcromam QuattroItAPI MRA, -NbddW
MassLynx 3.1Software
Cone voltkges:-60v ConWon ps enew. 40
Mode: elecuDsPraYnqp*m
Sourcewmpcratm:
115 *C.
Anab= vacuum pressures0:.000043mbar, 0.000079 ud3ar
Primary Ion:499
Daughter ions:90,99, 130, 180,230
Mectmde: Zesom=
04/20/98
3
FluorineAnalytical Chemistry Team
SamplesReceived: Samples Extracted: Samples Analyzed:
4/6/98 4n4logIgg 4/094/13/98
Anabmb by. camrsuon CurveRange: iAofCalibratioCnurve:
LOW:
IAW:
Study of PFOS levelsin historicalSwedish human wxa smples
Sample ID
SE-1 SE-2 SE-3 SE-4 SE-5 SE-6 SE-7 SE-9 SE-9. SE-10
2 VPP+++FF(/1/O_L__I__S0L@00ID..II00@ b1LS0).'9
1.2++1/_-0O..1 l 1.55+++///_-0O,1l 1.0+/-0.L 1.0+/-O.l
bdd.1 1.22+/-0.0 2.8+/-0.0
b.c-dLL ! 21.066+/-0.9
ab.d.L
Sample ID
SE-11 SE-12 SE-13 SE-14 SE-15 SE-16 SE-17 SE-19 SE-19 SE-20
VPFOSI .=b
4.1+1-0.2 2.9+/-0.0 2.0+/-Ol 2.8+1-0.0 2.9+/-0.0 2.7+1-0.2 1.2+/-0.0 1.2+/-0.0
bd.L bd.L
778-6018
EShg lpybto 10 ppb 0.992 I ppb I ppb
QC Results
QC Chedc CalibratioCnheck 2.98ppb CalibraticCmheck 4.95ppb CalibratioCnheck, 2.98ppb Cahb@on Check,4.95ppb CalibratioCnheck, 2.98 ppb CalibmtionCheck, 4.95ppb
Reavery 106% 100% 100% 96% 89% 990/0
Brandied Isomer Abundanci Percentages
Sample Pool
SUndard MAWW IndividualSsampled in 1998
3M CottageGrm PlantWatkas, 1998 IndividualsSampled in 1970s and 803 Pooled Sem Samples fmm 1997-98 ForeignSem SampIM 1994 and 1994 IndividualSsampled inlate1950s US Geogmphical StudySamplm 1998
%Abundancoof BranciwdImmm
%Abuadmceof Brandiedboomn
.%22CL22%
400A 45% 37% 31% na 39% 41%
--(&&D".)
3%
n/a
5%
31
4%
3
5%
12
5%
11
na
na
4%
5
4%
55
I -LOD - LimitofDetection 2 -LOQ - LimitofQuantitadon
Pop I
Shooti
filenumber 4099807 4099808 4099809 4099810 4099811 4099812 4099813 4099818 4099819 4099820 4099821 4099822 4099823 4099824 4099825 4099826 4099827 4099828 4099829 4099830 40998Sl 4099832 4099833 4099834 4099835 4099836 4099837 4099838 4099839 4099840 4099841 4099842 4099843 4099844 4099845 4099846 4099847. 4W9848 4099849 4099850 4099851 4099852 4099853 4099854 4099855 4099856 4099857 4099858 4099859 4099860
sampledescriptionpeak area
0.998pp@ W 1
4654
2.98ppb inj1
sm
2.98ppb W 2
8247
4.95ppb inj1
11239
4.95ppb W 2
11381
9.8ppb inj1
17949
9.8ppb inj2
17582
Meoh blank
4466
SE- 11 HS04078 ini1 9659
SE- II HS04078 inj2 9265
SE- 12 HS04078 ini1 7886
SE- 12 HS04078 ini2 7794
SE- 13 HS04078 inj1 6507
SE. 13 HS04078 inj2 6735
SE 14 H.SO407,8'?n*j1 7684
SE-14 HS04079 inj2 7674
SE- 15 HS04078 ini1 7808
SE- 15 HS04078 inj2 7803
Meoh blank
4133
2.98 ppb calcheck
8173
4.95ppb calcheck
10721
Meoh blank
8844
SE- 16 HS04078 ini1 7766
SE- 16 HS04078 ini2 7411
SE-17 HS04078 inj1 5539
SE- 17 HS04078 ini2 5450
SE- 18 HS04078 ini1 5380
SE- 18 HS04078 ini2 5459
SE- 19 HS04078 ini1 4579
SE-19 HS04078 inj2 4335
SE-20 HS04078 ini1 4018
SE-20 HS04078 ini2 3971.
Meoh blank
3569-
2.98 ppb calcheck
7932
4.95 ppb calcheck
10483
Meoh blank
S377
SE. 1 HS04078 ini1
6330
SE- I HS04078 inj2
m
SE-2 HS04078 ini1
5773
SE-2 HS04078 inj2
6878
SE-3 HS04078 inj1
5197
SE-3 HS04078 inj2
5114
SE-4 HSD4078 ini1
5337
SE-4 HS04078 ini2
5127
SE-5 HS04078 ini1
4807
SE-5 HS04078 inj2
4937
Meoh blank
8416
2.98 ppb calcheck
7479
4.95 ppb calcheck
9904
Meoh blank
3219
[analytel
0.6
3.1
3.2
5.4
5.5
10.2
9.9
0.5 [PFOS]avg
4.2
3.9
t1
3.0
2.9
2.9
2.0
2.1
2.0
2.8
2.8
2.8
2.9
2.9
2.9
0.3
3.2
5.0
0.0
2.9
2.6
2.7
1.3
1.2
1.2
1.2
1.2
1.2
0.6
0.4
0.5
0.2
0.1
0.2
-0.1
3.0
t8
-0.3
1.1
1.2
1.2
1.4
1.5
1.5
1.0
1.0
1.0
1.1
1.0
1.0
0.7
0.8
0.8
-0.3
2.7
4.4
-0.4
St. Dev. 0.2 0.0 O..l 0.0 0.0 %Rec, QC o 106 100
0.2 0.0 0.0 0.1 0.0
100 96
0.1 0.1 0.0 0.1 0.1
89 88
Page I
Shooti
4099861
SE-6 HS04078 inj1
5421
1.2
4099862
SE-6 HS04078 W 2
5480
1.2
1.2
0.0
4099863
SE-7 HS04078 W 1
7673
2.8
4099864
SE-7 HS04078 inj2
7729
2.8
2.8
0.0
W39865
SE-8 HS04078 inj1
4556
0.6
4099866 SE-8 HS04078 inj2
4682
0.7
0.6
0.1
4099867
SE-9 HS04078 inj1
6497
10
4099M
SE-9 HS04078 inj2
8183
3.2
2.6
0.9
4099869 SE-10 HS04078 W 1 4312
0.4
4099870 SE-10 HS04P78 inj2 4710
0.7
0.5
0.2
4099871
Mooh blank
1555
0.0
4099872
water blankinj1
3813
0.0
4099873
water blankinj2
3891
0.1
4099874
serablank inj1
4273
0.4
4099875
seraWank inj2
4498
0.5
4099876
0.998ppb i,N-1
5199
1.0
4099877
0.998ppb inj2
5054
0.9
,4099878
2.98ppb inj1
7712
2.8
4099879
2.98ppb inj2
7792
2.9
4099880
4.95ppb iai1
10297
C7
4099881
4.95ppb inj2
10556
4.9
4099882
9.80ppb inj1
16807
9.4
4099883
9.80ppb inj2
16888
9.4
Page 2
3M EnvironmentalLaboratory-FluorineAnalyticalChemistry Team
Yds Hansen - Sr.AnalyticaClhemist FluorineAnalyticaClhemistryTeam Building2-3E-09 612-778-6019
Quantitative analysis of PFOS in historic human sera samples from the University of Minnesota
Summary: Ten samplesweresuppliedtotheEnvironmentalLab by JeffMan&l (3M Medical)on April14,
1998. The tensampleswere partofa group ofsamplesthat,afteruuaction,were pre-screenefdorPFOS levelsT.hese tensampleswere classifiaesd"low-lever(<10ppb);dW arenumbered 1,2A, 3A, 4,5, 6A, 7A, 9,9A,and IOA. Two-one mL portionosfthesampleswen extracteudsingan iontaidn rea t The === wereanab7jedquantLMaWy forpeifluorooctaanmemge CPFOS) usinghigh. pressureliquid hmmatog6i@by-elwftosprmaayss spwmmcay (EPLC-ESbffi).Ambft MaWfication was verifiebdy compuison@ofmolecularion-HPLC refttiontimeofthec&wW a=bU and standard
material.Sampleswem quandta&* evaluateadgainsta speciallpyrepu4 five@-poiawdractedcurve (rA2 = 0.987).Cahbratiduchecks,analyzedevery5 samples,we= between80-1086/o9fexpectedvalue&
Descfipiffofnswnples.In alltenofthesepre-screenesdampIM PFOS concentratiownas determinedtobe lessthanthc*
detectiolnimitof the method, 1 ppb.
Experimentalwammary:
SwnplepreparationI.on-pairinegxtraction In a pH controlleednvironmenta,n ioxl-paidnrgeagenttetrabutaymlmonium Mil (TJBA)i,s
used tow&= theanalytefrom thematrix Amomc compounds,likePFOS and pmguomocmnoate (POAA), areselectiveMlpyted by thecationirceagent Subsequenttotheformationafthe7BA-anion
pair,theanalyteiswanderredtoa non-polarorganicsolvent(ethyalce=), dnecland reconstltutiend methanolforMS analysis.
HPLC Charactenshc retentiohnmesfor PFOS
InBPLC, an allquotoftheuwda *5injecteadnd passedthrougha
coiunm
Basedon theafonityoftheanabftforthestagonary-pbaisnethecolumnrelativteo theliquidmobffo.-
phasepawing throughthecolumn,theanabu is retainefdora cbaracmmc amount ofwm. For
example,ina standardsolutionP,FOS may clutoat10.5minutm Retentiontimesbetweena standafd
PFOS solutioannd theanalytexuactedfrom serainthisanalysiwsere matcw towithin1% an the
EPLC systenl
F.SIZ. Detectionand monito?ingofthemolecularion AnalysisofPFOS standardisndicatetshattheprimaryioncbaracwas* ofPFOS ism/z - 499
amu, correspondintgothemass oftheanionicsurhctant(CsFl7SO3-)T.hisionwas monitoredselectively tonmxhniw sensitivitAy.scanofm/z--100to 1210(negatneonly)was alsocollected.
Qualitycontrolnummary: Scm sampleswereextracteidnduplicateM.ethanolblankswereanalyzedperiodicaltloyenmm
completeisolatioonfthesaxnpleand two mid-leve(l2.98ppb and 4.95ppb)qualitcyontrolmunpleswere analyzedbetweenevery5 samples.Becausehuman sem withoutPPOS ism availables,ampla of pooledserapurchasedfrom Sigma were pm-moacted, spikedwitha standardconoonuadon ofPFOS, and re-extracte&This pre-exuwtedseraisunderstoodtobe verysomila tothesample matrix Thisfive
04/22/98
1
pointexuactedcurvewas analyzedbeforeand afterft samples.Quantitadonofthemmi)l isbasedon thelinea regressioenquadonderivedfrom thenwap oftbetwo bmdmft curves(zA2- 0.9M. SpecificQC parametersareavailabloen theappendedresulttsome.
LimitofQuanhtahonILimit ofdetection These low level=Wles wen analyzedapmst a q=auy preparedlow levelcurve As a results,
confide= limitcsalmwod aroundthecurvevaluesindoca aquandfablediffmwmbdweensainples evaluatedat0 and I ppb. Forthis=&isi4 thelimitofqundbtbm andthelimitofdetectioanre equivalent-
speciries:
C system
HewlettPadmrd Series110014Wd
Column:Y.eystonBeetud Cis
2 x 100 mm
Flow rate: Solventk.
SolventB:
5,pm particlsein
360 PL/Mi&
2.0mM Ammonhm
Nfethan.01
Acetate
SolventGradienL
45 to90 O/oBin 9.50minl
Hold at90 O/Z hr 3.50mins.
PetUM tD45 %B in 1.50mins.
Hold at45 */&Bfor3.5mins.
Injectiovnolume: 10 pL
Injection/ssample:2
Electrospraymass spectrometer Mcromass PlatfbrmH API Mass Spwftometer,-OW
MassLynx 2.4Software
Cone voltaga:-20v,-60v
Mode: elccftvrayncpdm Sourcetemperature: 115 OC. Analyzervacuum pressures0:.000043mbar, 0.000079mbar
Ions:369,413,499 Electrode:cross-flow
04/22/99
2
FluorineAnalytical ChemistryTeam
Samples Received: Sampla Extracted: Samples Analyzed:
4/14/98 4/15/98 4/16-4/21/98
Analysisby: CalibratioCnurve Range: ?of CalibntionCurm LOD':
Analysis of PFOS in historicsamples of human sera (U of Al)
Sample IDD
I 2A 3A 4 5
<Lo @IFV<PIFAO)S] <LLLO40obD)@D ,If < LODS' < LOD < LODD < LODD < LODD
Simple M 6A 7A 9 9A 10A
IPFOS] (pob)
I < LOD
< LOD < LOD <LOD < LOD
K-fHanwn 77"018
E,%iS lppb tD 24.9ppb 0.997 1 ppb I ppb
QC Results
QC Check-. CahbrationCheck (QC1 at2.98ppb) CaMration Check (QC2 at4.95ppb)
% Recovm 30% 108%
I -LOD - LimitofDetection 2 -LOQ - LimitofQuantitation
4n2AS
3M EnvironmentalLaboratory-FluorineAnalyticalChemistry Team
KrisHamn - Sr.Analydol Chen2W FluorineAnalyticgCkmWq Team Budding 2-3E-09 612-778-6018
Phase 2C4 Part 2: PFOS levels in individual's human sera samples, a blind repeatability experiment
Summary: Fifteensamples of hitn-qnserain plasticentrifugetubeswen suppliedtotheEnvironmental Lib
by Jeffb&ndel (3M Nledicalo)n April15,1998. The Aftacm=mples werepartofa gmup ofminples tb4 afterextractionw,erepro-screenafdorPFOS levels.These fiftm sampleswere classifieads"andlevel"(>10 ppb and <100 ppb);theyarenumbered IA, 2B, 2C@ 4A, 5A, 5B, 6B, 7B, &A, 9B, 9C, IOB, 11, 12,and 13. sampic ofse@Afrom dim don= have be= anab-zedpreviouslbyy theFAcr. one mL ahquotsofserawere removedfrom eachample and extractewdft an wn-pamng ragmt; allofthe samples were extractedin duplicate.
Ilicseracxtwm were aiwyzed quantl=vely forp i-ifnirnooctaneswfonate (JPFOS)byhigh pressurehqtudchromatograpby-ekcummy mm V=Uometty (HPLC-LUB). Anabft identificatim was verifiedby comparisonof molecularion-EPLC rctmtlontime of theextractedanalyteand standard m@itmisal.Samples were quantitativeelvyaluatedagainsta Wedally prepar4 five-poimextractedcurve (rA2 = 0.996).MaWx sp&c calibratiocnhwjcs,anab7Ad inthemiddle ofthe analysisequence,wo within100/.ofexpectedvalues.
The presenceofPFOS in sevezw ofthesamples (IA tbmugh 6B) was verifieudsingEPLCESMMS. This techniqueprovidesan additionadlegme ofcertainttyo theanalytoidentdcationby.' specificalmloynitoringftginmts daughterions(m/z-80,99,130,190,230)characteristoifcthePFOS primaryion(m/z- 499).
The PFOS valuesin thisblindrepro&u*ilityanalysisme within11% ofvaluescollected previously.Specificrebmltasreattachedtothisreporl
Experimentalmmmarr.
Smple prepffadon:.Ion-,wifi=ntgraction la a pH controllednvironmenta,n ion-pairinrgeagenta,usbutylammonium mdfiftCMA), is
usedtowm-ad themmbft from thematrixAmomc compundi6 Ww PFOS and paflumowmoate (POAA), areselocawy targetebdy thecationirceagent Subsoqmw tothehrnmdon oftheIBA-anion poar,the analyteisuuns&rred toa non-polarorganicsolvent(aftlacetate)d,rnd, and reconstitutemd methanol forEPLC-ESMS analysis.
HPLC. Characte)4sfircetenfiodnmesfor PFOS In HPLC, an aliquotofthe aft= isinjectedand passeddvmgh a cdhbxmomato column.
Based on the atmiityoftheanalyteforthestadonary-phasien de coW= relativteotheliquidmobilpphase passingthrough thecolumn,theanalyten retuned fDra characteristaimcount of Wa. For example, in a standardsolutionP,FOS may cluteat 10.5minutm Rdention timesbetween a standard PFOS solutionand theanalyteextractefdrom serain thisanabsiswem matched to within1% on the EPLC systeul
05/07/98
ESAC. DetectioanndmonitorionfgthemokcularIon AnalysiosfPFOS standaridnsdicattehsattheprimaryioncharacteriosftPiFcOS ism/z- 499
amu,corresponditnogthemassoftheanionicMUhM=nt (C4Fl7So3-).Thisionwas monitoresdelectively tomaximize sensitivitAy.scanofm/z-100 to 1210 (negativeonly)was alsocollected.
ES&YSMS.- Confinnafionofanalyteidenfification sevem UMPICS indus setwen analyzedby ESUSO
tovm* theidentitoyfthePFOS analyte
ion.ES.NlcJv% isverysimil2toE,9W, exceptthatitadds an additionadlmmdon ofcertainttyo
con4ound identificatioAms inFSM, a compound specifiicm isselectedAlfterwlectiox@theselected ,onischwwwnzed ffirtbebry smashmg itapartwith highc=U gas-As a resultotfhesmashing Ionic
fragments,characteristoifcthemolecule,arecreatedand detecte&
For example,forPFOS analysisi,on499 issdww asthecompound sped& primaryim This ionissma bed intootherionssuch as90 amu (conwqwnding toS03), 99 amu (cmil11 " g toFS%),
130amu (oDntVondingtoCF2SO3), 190 skmu (C2F4S%l and 230,umu(C3F&SO3')I.fPFOS ispresent
inthe samples,each ofthesesecondary&Agments isddeaed atthe detecw.
Qualitycontrolmmmary! Each serasunple was extractedin duplicates,tandarddcvmon vahm areincludedin thetable
ofresultsT.wo mid-ILwd(25jo and 49 ppb) qualitycontrolumple wm analyzedbetween everyfmc samples;recoveryforthe= matrixsp&e analysiwsen detumined tobe within10'Yofcwud values. Because human sm %i&M "OS isnotavail&le,=,moles ofpwW sm pmrband km Sig= wm pm--e=@ spdmd witha standardconcenuabon ofPFOS, and re-odmcte& This pre-ccuactedserais understoodtobe verysirniltaothemunple matdx This fivepointexuactedmm was analyzedbefi= and afterthe samples.Quantitatioonf the samples isbased an the li regressionequationderivedfrom theavemge of thetwo bracketingcurves(e2 - 0.996).SpecificQC parametersare availablean the appended resultstable.
Limit of Quantitation As thesesamples we= pre-screened,itwas detanninedthatopdmizing instrumentaldetection
hnuts was not necessaryforacmwaw analysisofthese"imd-kvw samples. As a resultt,he limitof quantitatiownas 10 ppb. All sampleswere quantitatewdellabove thislevel
Instnunentalspecirics:
HPLC system HewlettPackard Senes 1100laquid
Column:Y.eystonBeemsflCis 2 x 100 mm 5 pm particlseize
Flow rate: SolventA:
300 ltT,/min 2.0mM Ammonium Ace=
SolventB: methool SolventGradient:
45 to 90 O/oBin 9.50mins.
Hold at90 O/oBfor3.50 mins.
Rctum to45 O/oBin 1.50 mins.
Hold at45 0/0 for3.5mins.
Injectiovnolume: 10 ;LL
Injection/ssample: I
Electrospraymass spectrometer bhcromass PlatformR API Mass Spe=meter.
MassLynx 2.4 Software
-Chick-
05/07/98
2
cone voltqw: -60V
Mode: decbwray neptivc Sourcetemperature: 115 OC. Analy= vacuum pressurm:0.000043mbar, 0.000079mbar
IDns:499.413,369 Electmde:crws-Ilow
EJec&wpray AME
hncrmm QuaMro H API Ntm Spectrometeurb,bddw
MassLynx 3.1Software
Cone voltna: -60v
CoUWon ps enerw.45 V
Mode: deWoWM neptin
SourceUmpuature:
115 OC.
An*= vacmim pmaum: 0.000043mbar, 0.000079mbar
Pdmuy I= 4"
Daugbier ions:W;199, 130,180,230
Electmde: Z-optay,.
05/07/99
3
inuorineAnalyticaClhemistryTeam
conw.
XJ. Hamen
8-6018
SamplesReceived: Samples Extracted: Samples Analyzed:
4/14/98 4/15/98 4/16-4/22/98
LOD':
LOQI:
Analysisbr. CalibratioCnum Rmg iAofCalibratioCnum10 ppb
10ppb
ESMS 10ppb to96 ppb
. 0.996
PHASE M part2: Blind repeatabiliteyxperiment
Somnvolmeme@110 1A 213 2C 4A -SX
SB 6B
7B SA
VPFOS] (pob) 28+/-0.3 50+/-3 38+/-0.2 47+/-0.4 62+/-l 54+/-2 44+/-4 54+/-4 78+/-S
ReportW Previoud
28 41 37""
45 S4 49 42 4S 67
VPFOS]
+Ob;ES9
9B
33V44+/-l
9c
477P+F/-9
10B
51+/-l
11
44+/-4
12 79 +I-4
13
70+/-S
14
79+/-26
16 37+/-2
17
80+/-14
Rqmrbd =gL 30 39 41 na. -n-.a. na. na. 32 73
QC Results
QC ChedLCalibratioCnhock, 24.9 ppb CalibratioCnheck, 49 ppb CalibratioCnheck, 24.9 ppb CalibratioCnheck, 49 ppb CalibratiOownk, U.9 "b Cdibmdon Cho& 49 Mb
% Recovery
96% 100% 92% 95% 90% 98%
I -LOD - LimitofDetection 2 -LOQ - LimitofQuantitafion
3M EnvironmentalLab 3/7/98
PHASE ICK part2
3M EnvironmentaLlaboratoryF-luorinAenalyticCahlemistrT-evam
KsisPranm -Sr.AnalydcdChernist FluorineAwlydol Ckmisuy Team IRiltildi2n-g3E-09 612-778-6018
Preliminaryresults:Analysisof POAA in human sera samples
Summary:
To date,datafrom nine phases of a su* offluorochemicianlhcinnan-sehmas been collected.
PHASE I:Semi-quantitativhermdgadon ofPFOS in sampla ofpooled Ihilimsskeimn PHASE U: QuantitativeanalysisofPFOS and POAA in samples ofpooled human US
sm samplc4 1997-1998 PHASE 13L-Quantiu&c analysisof PFOS 1998 PHASE TV Quantimm analysisofPFOS
and POAA in himumd
in sampla of Wdhidual's som US sem samplek 1970s-80s
PHASE V.'QuantitaCm analysisof PFOS-M@ l@6@ US am samples, 1960s
PHASF, VI: QuantiutiveanalysisofPFOS in samplesof sua fiam indi@
in rural
northem China, 1995-1997 PHASE VU: CieogVhicd disftflmdon:a quantitativaenalysisof PFOS in seracollected
around theUnited Suitt*,1998 PHASE VM: Quanti=w analysisof PFOS in butmud samplesftm SwedM specific date not suppliedto EnvirwTngntnl Lab PHASE M part 1:Quandtafm analysisof PFOS in historicaUlS samples, 1948-1951 PHASE M part2:PFOS levelsin indhidual'shuman serasampla; Blind RepeataWHty
yveriment
no analysisof perfluorooc=enffonate (PFOS) has be= theprimary focusin dww phases; quantitativdeataforpeinwmoctonoate (POAA) has alsobe= collectefdc)rseveralphasesof ft 0* Due totime constWnM we have not devoted the same attentiontothePOAA as we ba@v to the PFOS analysis The followingreportdescribesobsmvauons ofPOAA levelsin some of dw umples analyzed as partof thisongomg study Reportsdeudmg thePFOS analysislistedabovehave been issuedtoJeff Mandel inft 3M Medical Deputment LOQ forPOAA is10 ppb.
PHASE 11-OuantitattyetwalysisofPFOS and POAA Number of sampleswith POAA > LOQ - 0 Number of samples with POAA > LOD - 4 Total munber ofsamples - 12 Comnmu:
InLam lesofyooled human
PHA SE IffOuantitattvaenalys7sgL PFOS and POAA Number ofsampleswithPOAA > LOQ - 4 Total number ofsamples - 31 Comments: Data has not been ammmed cardbuy
inLiE@le_sofindividual'ssera
PHASE IV- QLantitghve anal@gl ofPFOS inhistoricaslera LeL/es Number of wimples vvithPOAA > LOQ - 0 Total number of samples - 10 Comments: Data has not be= preciselyquantiuded
1970s-80s
04/24/98
PFL4SEV OuantitatainvayelsisofPFOSInhistoriscearlammle_.s,1960s
NumberofsmiplewsithPOAA > LOQ - 0 Number ofsampleswithPOAA > LOD = 6 Totalnumber ofsamples- 6 Comments: Data hasnotbeenpreciselqyuantibod
PHASE P7 OuantitativaenalymsofPFOS in1WR_le__sof-le-fraom indtvi&alsinrural northernChina Number ofsampleswithPOAA > LOQ - 0 Number ofsampleswithPOAA > IA)D - 5 Totalnumber ofsamples= 9 Comments: Data has notbeen preciselqyuantibued
PHASE P71-Geographicaldistdbutiona: guantitafivaenahvisofPFOS
collecteadround theUnitedStates
Number of,samplawidiPOAA > LOQ - 2 (1at22 ppb, I at12pyb)
Number ofsampleswithPOAA > LOD - 20
Totalnumber of ..p.,la 55
Comments. Data hainotbeenan
on&gy
insera
PHASE VUl OuantitadavnvahsiOsLEM InhisoricsamlnvlefsromSweden Numberof=Wlw withPOAA > I.OQ- 0
Number ofsamplw withPOAA > LOD - 0
Totalnumber ofsainpla- 20 Comments: Data has notbeen preciselqyuandtacd
PHASE IX gga 1:Qu_antitaitaynealysisofPFOS InhistoricaUlS mW-I-e-s1,948-19s] Number ofsampleswithPOAA > IA)Q = 0 Totalnumber ofsamples- 20 Comments: Data has notbeen preciselqyuantitged
Experimentalsommarr.
SamplepreparationI:on-pairing'e2&action In a pE contmuedenviromncmta,n !on-pairinrgeagentwuabutylammom*unk m-1 CIBA),is
usedtoamracttheawlytefromthematnx Ammw wmpunds, Mm PFOS and (POAA), arewlecdvdy Wgded by thecadanicreagenl Subwqtumttothehonadon oftheTRA-anion pair,theanalyteisunnsfayedtoa non-polarorgamc sowm (ethyalcotgo)&,14 and reconsbuftdin methanolforNE analysi&
HPLC. Chffwterisfircetentiohnmesfor POAA
InBPLC, an aliquootftheckum n mjectedand passedOmagh a
00hunn.
Based on theaffiwtyoftheanabu forthesudonary-phaninthecohnnn rdada totheHquidnwbile-
phasepasung throughthecohmn, theanabu is remniedfora characunstimcmot oftune For
CULMplelina standardsolufimPOAA may elutoat10.5minutes.Rdmdon timesbetweena sumdard
POAA sohitm and theanalytocxbactedfromseram thisan*m weremached towithin1% on the
HPLC qftm
E&2& DetectioanndmonitonngofthemoleculaIron AnalysiosfPOAA stanaaridn-dcicatdeisaitheprimariyondkwacterisotfiPcOAA ismiz 413
amu, correspondintgothemass oftheanionicmubctant (C,7FsCOr).This ionwas monitoredwlecdvely toma2ritnisemidvity.Frap=tation ofthePOAA anioncanbe in&xw; ion369,cha=ctaistiocfthe
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2
dmftxylation productr,esultsB.oth ionswere monitoredinmostofthesu* phaseslisteadbove,A smn ofm/z--100to 1210 (negativeonly)was alsocollected.
EMDSUS.- Confirmationof analyteidentification Severalsamples inthissetwere analyzedby FSNLSI@M to verifythe identityof thePFOS anabu
ion.ES-NL%S isvery sumlar to ESNS, exceptthatitadds an addition&dimension of certaintyto compatmd identificatioArslinESNO, a compound spedficion issclectc&Afterscl=don, theselected ioniscbaracwdzed hwther by smashing itapartwith high energygas. As a r=Wt ofthesmasbinz ionic ftapients,characteristoifcthe molecule,arecreatedand dcu=te&
For example,for PFOS analysisi,on 499 isselectedasthecompound spwfficprimary ioillids ionissmashed intootherionssuchas 80 2mu (correspondingtoS031, 99 airnu(coffespon(Ungto FS03), 130 amu (correspondintgo CF2SO3), 180 skmu (C2F4SO31, and 230 2mu (C3F6S%). IfPFOS ispresent inthesamplm eachofthesesecondaryftp=U isdmcw atthe&ft=r.
Qualitycontromln=mt:
When possibles,eraumples w= cxuactedinduplicataend analyzedindupl=ft. Oftenthis was notpossg)lca,ssamplesnze and/orum were lumted. Methawl blanimwm analyzedperiodically toensurecompleteLwlationofthen@aple.)&d-levclqu-W* gonuol =Wles w= analyzedpuiodWaUy ihmgh each analyticasleque=, typicalleyveryfivesankplm tomoidtorbubument sbbffityB.e== bitirnsaenravatboutPFOS isnotavailables,amaplaofpooledserapurchasedfrom Sig= were proocuact4 spflwdvhtha standardconcentratioonfPFOS, and re-odracted.Thispre-exuacted8= b understoodtobe verysimil2tothesample matrix In allcasesPFOS was evaluatedvmw an ckuact* for,mostphasesofthissb*, POAA was alsospflwdand extractetdoform a sbuward curve In then cases quantitadonofthesimplesisbasedon thelinea mgmsdon equationderivedfrm theavmp of thetwo curvesbracketingthe samples.
Limitof Quantitaflon The currentanabtkml method has been used to evaluatea UM mp
of PFOS Imb axuwftd
from =a, themethod isnotoptimizedforprocim I(yw-kvd(< 5 ppb)quantimfim but insteadA)r
sampleswithPFOS concentrationisnthermp of20-60ppb. A speciallow4evelcurveh.as be= for prcclw quantitatievvealuatioonfPFOS kvds betwm 1-10ppb. As thePOAA levels
observedinnon-plantworka wra areverylow,in futm analysm POAA willbe.evaluateadgain a
special low-lcvtl curvr, sim,12 to thatpreparedforPFOS. Samples designated<.OQ containlessthan 10 ppb POAA. Iffiutheraccuracyand precisionin
quantitadonofthesm nmplas (sampleska dm 10 ppb) isrequireds,ampleswillbe re-evaluated
versusa speciallow-levelquantitativceurve,
Limitofdetecfion The hnut of d&Amon forthisanalyticamlethod n based on analystrempition of the distinct
peak shape resultingfrom POAA analysis.POAA stuxiardnu&jw and POAA extractedfrom nm analyzedby theconditionsreportedhoM show nearb@wji resolutiodn Ibranched and I lin POAA
isomer.The al= ofmch peak in theHPLC4r= o=rs ata qmdfic,reprod=ble rdmft dm Unlikc,PFOS, and theratiofthebranchedpeak tothelin peak isnot necessarilcyonsistent particularlaytlow level& POAA, when present,seem tobe presentatmich low levelsthataccurate
on ofthesmallerpeak (thebrandied isomer)isverydifficult.
Qu&Wicadons: Tiusdatawillbe consideredprelindnaryuntiltheanalyt cxbactedftm thesesampks can be
venfiedasPOAA usingLC-MShg whmques and untilunuumental senutivitcyan be ophnuzed tD MM clearlyidentiftyheangytc responw. The method used ADrtheanalysiosfdme ampla hasbeen validatebdy LC-MSNM previouslybut wn&=on ofPOAA forspeaficsamplesinthiseight-phan
0* has notbe= pedormed.
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3
InstnamentalSPCMCI:
BPLC system HewlettPadmrd Serie1s100Uquid
Column:KcysWne BdasilCis
2 x 100 mm
5 pm parficlseize
Flow rate: 300 itTImin
SolventA.
2.0mM Ammonhm
Solv=tB:
14ethanol
SolventCTrAffient
45 to 90 'Y*Bin 9.50 mins.
Hold at90 O/oBfor3.30minl
Returnto45 'YeBin 1.50
Hold at45 %B for3.5minl
Injectiovnolume:,10 )iL
Injecdm /nmpla: 2
Acebft
-Elecbwpay massVectrometer M=mam Plodom H APIMass SpecUomeM, -CWW
MassLynx 2.4Software Cone volUM: -20v,-&)v Mo&: elc=Mrq m-ga&c So= temperamm: 115 OC Analym vacuum pressures0:.000043mbar, 0.000079mBa Ions:369,413;499,427 ElecaWe: crawflow
EJec&osprayMSMS bfimmass Quawo H API Mass SpecuonitteIr&,ddine
MassLynx 3.1Software
Cone voltwo: -20v Collisiopns enaw. 45 V
Mo&: clechvspranyega&e Sourceten4)erAUm: 115 OC Aralyzervacuum pi mm: 0.000043mbar, 0.000079mbar
Pdm" I=- 413 Daugbter iom: 119,169,369 Mactrode: Z-spray
z
04/24/98
4