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Study Title
ANALYSISOF ENDOGENOUSFLUOROCHEMICALSINNORMALPOOLEDHUMAN SERUMAND
Data Requirement
40 CFR Part 792
Author
Mark E. Ellefson
Study Completion Date
13 November, 2002
Revised Report
9 December, 2002
Performing Laboratory
3M Environmental Laboratory
Building2-3E-09
935 Bush Avenue
St.Paul,MN55106
Project Identification
3M Environmental Laboratory Study Number E02-1039
Total Number of Pages 225
3M ENVIRONMENTAL LABORATORY
E02-1039 This page has been reserved for specific country requirements.
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3M ENVIRONMENTAL
LABORA TORY
E02-1039
GLP COMPLIANCE STATEMENT
Study Title:
Analysis of Endogenous Fluorochemicals in Normal Pooled Human Serum and Plasma
Study Identification Number: 3M Environmental Laboratory study Number E02-1039
This study was conducted in compliance with Toxic Substances Control Act (TSCA) Good Laboratory Practice (GLP) Standards, 40 CFR 792, with the exceptions listed below:
Exceptions to GLP compliance: 40 CFR 792.130(e): There is not an electronic audit trail of corrections. The authenticated hardcopy printouts are considered the original raw data.
mark E. Ellefson, Study Director //"
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-WilliamK. Reagan, Testing Facility Management
Date Date
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3M ENVIRONMENTAL
LABORATORY
E02-1039
QUALITY ASSURANCE STATEMENT
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Study Title: Analysis of Endogenous Fluorochemicals in Normal Pooled Human Serum and
Plasma
Study Identification Number: 3M Environmental Laboratory Study Number E02-1039
This study was audited by the 3M Environmental Laboratory Quality Assurance Unit (QAU). as indicated in the following table. The findings were reported to the study director and laboratory
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management.
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10/10/02 10/11/02 10/29/02- 10/30/02 10/31/02
Protocol In-phase Data FinalReport
10/10/02 10/11/02 10/30/02 11/1/02
10/10/02 10/11/02 10/30/02 11/1/02
QAU Representative
Date
Page 4 of 225
3M ENVIRONMENTAL
LABORATORY
E02-1039
TABLE OF CONTENTS
GLP Compliance Statement............................................................................................................... 3
Quality Assurance Statement ............................................................................................................ 4
List of Tables ...................................................................................................................................... 6
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List of Figures ..................................................................................................................................... 6
Study Information ............................................................................................................................... 7
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Executive Summary .................................
.........................................................................................
8
Summary ............................................................................................................................................ 9
Introduction.................................................................................................................................. ....... 11 i
Test Substance .................................................................................................................................. 11
,
Reference Substance ......................................................................................................................... 14
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Test Systems ..................................................................................................................................... 15
Method Summaries ............................................................................................................................ 15
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Preparatory and Analytical Method
15
Analytical Results ............................................................................................................................... 18
_
Data Summary ................................................................................................................................... 20
,
Statistical Methods and Calculations ................................................................................................. 31
Statement of Conclusion .................................................................................................................... 32
References ......................................................................................................................................... 33
List of Attachments ............................................................................................................................. 33
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Signature Page .................................................................................................................................. 34
Attachment A: Method ........................................................................................................................ 35
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Attachment B: Data Tables ................................................................................................................ 56
_
Attachment C: Chromatograms .......................................................................................................... 63
Attachment D: Prep Sheets and Traceability Information .................................................................. 125
Attachment E: Protocol and Amendment ........................................................................................... 208
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E02-1039
LIST OF TABLES
Table l.a. Endogenous levels of test substance in normal pooled human serum ........................... 9 Table 1.b. Endogenous levels of test substance in normal pooled human Plasma ......................... 9
Table 2. Characterization of the Test Substances ............................................................................ 11 Table 3. Characterization of the Reference Substances .................................................................. 14 Table 4. Description of Test Systems Used in this Study ................................................................. 15 Table 5.a. Endogenous levels of test substance in normal pooled human serum ........................... 20 Table 5.b. Endogenous levels of test substance in normal pooled human Plasma ......................... 20
Table 6. Accurate Mass Determination of Endogenous Test Substances ....................................... 21 Table 7. Daughter Ions of Endogenous Test Substances ................................................................ 21
LIST OF FIGURES '
Figure 1: NMR Certified99.5% LinearIsomer PFOA and Mixed Branchedand Linear Isomer PFOA Standards................................................................................................................. 22
Figure2:C7 Isomer Distribution......................................................................................................... 23 Figure3:C8 Isomer Distribution......................................................................................................... 25 Figure4:C9 Isomer Distribution......................................................................................................... 26 Figure 5: Clo Isomer Distribution........................................................................................................27 Figure 6: Cll Isomer Distribution........................................................................................................28
Figure 7:C12 Isomer Distribution........................................................................................................ 29 Figure 8: PFOS Isomer Distribution ................................................................................................... 30
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STUDY INFORMATION
3M ENVIRONMENTAL LABORATORY
E02-1039
Sponsor
William K. Reagen 3M Environmental Laboratory Bldg. 2-3E-09 935 Bush Avenue St. Paul, MN 55106 651-778-6565
Study Director
Mark E. Ellefson 3M Environmental Laboratory Bldg. 2-3E-09 935 Bush Avenue St. Paul, MN 55106 651-778-5405
Study Location
Testing Facility
3M Environmental Laboratory Bldg. 2-3E-09 935 Bush Avenue St. Paul, MN 55106 -
William K. Reagen, Laboratory Manager Stacy R. A. Hanson, Analytical Chemist Marlene M. Heying, Analytical Chemist Cindy M. Carlson, Analytical Chemist Ognjenka Krupljanin, Analytical Chemist
Study Dates
Study Initiation:10 October 2002
Experimental CInoitmiaptiolenti:o1n0: 3O1ctOocbteorb2e0r022002 Study Completion: 01 November 2002 Location of Archives
All original raw data and the report have been archived at the 3M Environmental Laboratory according to 3M Standard Operating Procedures. Remaining specimens pertaining to the analytical phase of this study will be archived at 3M Environmental Laboratory for as long as the quality of the preparation affords evaluation.
Page 7 of 225
3M ENVIRONMENTAL
LABORATORY
E02-1039
EXECUTIVE SUMMARY
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A screening study of three lots of commercial pooled human plasma, one lot of pooled human
,
plasma from central China, and four lots of commercial pooled human serum was undertaken to
quantify endogenous levels of perfluoroheptanoate (C7), pentadecafluorooctanoate (C8) (PFOA),
,._
heptadecafluorononanoate (C9), nonadecafluorodecanoate (C10), perfluoroundecanoate (C11 ),
perfluorododecanoate (C12), and perfluorooctane sulfonate (PFOS). Results from this study showed quantifiable levels of the linear isomers of C7, C9-C12 ranging
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from < 0.010 - 0.9 ng/mL (Tables la and lb). Low to non-detect levels of branched isomers
,
were observed for the C7 and C9-C12 compounds detected (Figure 1 - 10). PFOS was present
in the screened lots of commercial sera and plasma in concentrations ranging from 2.5 - 27
ng/mL and was present as branched and linear isomers. PFOA was present in the screened lots
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of commercial sera and plasma in concentrations ranging from 0.65 - 5.6 ng/mL and was present
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as branched and linear isomers.
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3M ENVIRONMENTALALBORATORY E02-1039
SUMMARY
Quantitativescreeningswere conductedon four lotsof pooledhumanserumand four lotsof pooled humanplasma to determineendogenouslevels of perfluoroheptanoate(C7), pentadecafluorooctanoate(C8), heptadecafluorononanoate(C9), nonadecafluorodecanoate (C10), perfluorodecanoate (C11), perfluorododecanoate (C12), and perfluorooctane sulfonate (PFOS) as described by the 3M Environmental Laboratory Study #E02-1039 protocol. The analytical screening data is summarized in tables 1.a. and 1.b.
Table1.a. Endogenoulsevelsoftestsubstancein normalpooledhumanserum
Test Substance
PFOS C12 Cll
C10 09 C8 C7
:Sigma TCR-689 (nglmL)
4.56 [0.018] [0.076]
[0.058] 0.265 1.60 [0.013]
Lampare TCR-688 (nglmL)
[2.49] [< 0.010]1 [< 0.010]1
[0.031] [0.068] 0.650 [0.025]
uioresource TCR-687 (nglmL)
17.0 [0.144] 0.295
[0.327] 0.605 2.95 [< 0.010]'
(3olOenwest TCR-690 (ng/mL)
27.0 [0.040] 0.320
0.203 0.900 5.60 0.190
[ ] Denotes values determined from concentrated spe method. _Value< LOQ.
Tablel.b. Endogenoulsevelsof testsubstancein normalpooledhumanPlasma
Analyte
PFOS C12 O11
Clo 09 Cs C7
L;hlnese
TCR-674 (ng/mL)
< 1.01 < 0.101 < 0.101
< 0.101 < 0.251 < 0.521 < 0.10'
Lampire
TCR-685 (ng/mL)
11.1 [0.036] [0.049]
[0.127] 0.435 2.61 0.100
Innovative
Research TCR-683 (ng/mL)
15.6 [0.022] 0.135
0.170 0.585 3.07 [0.016]
(5olOerlWest
TCR-684 (ng/mL)
18,3 [0.024] [0.071]
0.160 0.535 3.87 0.290
[ ] Denotes values determined from concentrated spe method. 1Value< LOQ.
Accurate mass measurements and elemental compositions were obtained for endogenous C7C11, and PFOS from a concentrated SPE extract of normal pooled human serum (see Table 6).
Characteristic daughter ions were observed for endogenous C7-C12, and PFOS from a concentrated SPE extract of normal pooled human plasma (see Table 7).
Qualitative analysis of chromatographically resolved branched and linear isomers of PFOA was accomplished using NMR certified standards of a linear isomer PFOA standard and of a mixed branched and linear isomer PFOA mixed standard. It was determined that the branched PFOA isomers elute within an approximate 0.2 minute retention time window and are baseJineresolved from the linear PFOA isomer. This finding of C8 isomer retention time resolution was
Page 9 of 225
3M ENVIRONMENTAL
LABORATORY
E02-1039
extrapolated to determine qualitatively the presence or absence of branched isomers for the higher homologues of C9-C12, and PFOS (see Figures 1 - 8).
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fRroemsu<lts0f.r0o1m0 -th0is.9stnugd/ymsLho(Twaebdleqsulaantaifniadblleb)l.evLeolswotfothneonli-ndeeater cistomleveerslsooffCb7r,anCc9h-eCd12isoramnegrisng
were observed for the C7 and C9-C12 compounds detected (Figures 1 -8). PFOS was present
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in the screened lots of commercial sera and plasma in concentrations ranging from 2.5 - 27
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ng/mL and was present as branched and linear isomers. PFOA was present in the screened lots
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of commercial sera and plasma in concentrations ranging from 0.65 - 5.6 ng/mL and was present
as branched and linear isomers.
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3M ENVIRONMENTAL LABORATORY
E02-1039
INTRODUCTION
The purposeof this study is to perform quantitativescreeningfor perfluoroheptanoate(C7), pentadecafluorooctanoate(C8), heptadecafiuorononanoate(C9), nonadecafluorodecanoate (C10), perfluorodecanoate (C11), perfluorododecanoate (C12), and perfluorooctanesulfonate (PFOS) in normal pooled human serum and plasma. This study did not have a typical test substance that is dosed onto a specific controlled test system as per a conventional GLP study. The study design is in compliance with US EPA Toxic Substances Control Act (TSCA) 40 CFR Part 792.
TEST SUBSTANCE
Preliminaryscreeningindicatedthatthe test substanceslistedbeloware present as endogenous material in normalpooled human serumand plasma. Informationpertainingto traceability,
source, physical description, and storage conditions is not available for these compounds as they exist in biological matrices.
Table2. CharacterizatioonftheTestSubstances
TEST SUBSTANCE
FORM ILA
Tridecafluoroheptanoate (C7) Pentadecafluorooctanoate (C8) Heptadecafluorononanoate (C9) Nonadecafluorodecanoate (C10) Perfluoroundecanoate C11) Perfluorododecanoate (C12) Perfluorooctane sulfonate (PFOS)
C_F_COO" CzF,sCOO CsF_COO" _F_oCOO" C_oF2_COO C.Fz3COO CsF,TSO_
The molecular structures are given below.
Name:
C7 Chemical Molecular
Name: Perfluoroheptanoate Weight: 363, as shown
F
F
F
O
F F_@@_0
-
F
F
F
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E02-1039
Name:
C8 Chemical Molecular
Name: Pentadecafluorooctanoate Weight: 413, as shown
F
F
F
0
F
F_O
F
F
F
F
Name:
C9 Chemical Molecular
Name: Heptadecafluorononanoate Weight: 463, as shown
F
F
F
F
O
Name:
O-
F
F
F
F
F
C10 Chemical Name: Nonadecafluorodecanoate
Molecular Weight: 513, as shown
F
F
F
F
O
F_ o-
F
F
F
F
F
Name:
C11 Chemical Molecular
Name: Perfluoroundecanoate Weight: 563, as shown
F
F
F
F
F
O
F 0-
F
F
F
F
F
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3M ENVIRONMENTALLABORATORY E02-1039
Name: C12 Chemical Name: Perfluorododecanoate Molecular Weight: 613, as shown
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F
F
F
F
0
F
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F
F
F
F
F
F
Name: PFOS Chemical Name: Perfluorooctanesulfonate
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Molecular Weight: 499, as shown
F
F
F
F
/F/F/F
tF
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.,.
F
F
F
F
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REFERENCE
SUBSTANCE
Table 3. Characterization of the Reference Substances
3M ENVIRONMENTAL LABORATORY E02-1039
Tridecafluoro heptanioc Acid Pentadecafluoro
octanoic Acid
Heptadecafluoro nonanoic Acid Nonadecafluoro decanoic Acid
Perfluoroun decanoic Acid Perfluorodo decanoic Acid
C6F_3COOH CTF15COOH
TCR-267 TCR-617
CsFlzCOOH TCR-618
CgF_gCOOH TCR-036
CIoFzlCOOH TCR-619
C,Fz_COOH TCR-037
Aldrich Oakwood
Products
Oakwood Products Oakwood Products
Oakwood Products Oakwood Products
Potassium Perfluorooctane sulfonate
08F17SO3K* TCR-018
SMM* 236-113-10
*Documentation of the method of synthesis is located at the source.
confirmed
isomers
**Reference substances
as linear
by NMR.
Clear Crystals White Crystals White Crystals
White Solid
White Crystals White Powder
White
Powder
98.2%** 99.5%** 98.02%** 98%** 96.4%** 99.7%**
86.9%
Frozen Ambient Temperature Ambient Temperature Frozen Ambient Temperature Frozen
Frozen
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TEST SYSTEMS Table4. Descriptionof TestSystemsUsedin thisStudy
3M ENVIRONMENTAL LABORA TORY
E02-1039
Pooled Human Serum PooledHuman Serum PooledHuman Serum Pooled Human Serum Pooled Human Plasma
Pooled Human Plasma Pooled Human Plasma
PooledHuman Plasma
Sigma-AIddchM,ilwaukeeW, l LampireBiologicaLlaboratoriesP,ipersvilleP, A BioresourcTeechnologyI,nc.,FortLauderdaleF,L GoldenWestBiologicalsT,emeculaC, A LampireBiologicaLl aboratoriesP,ipersvilleP, A
GoldenWestBiologicalsT,emeculaC, A InnovativeResearchI,nc.,SouthieldM, I
CentraCl hina
TCR-689L, ot022K0965 TCR-688,LotX324B TCR-687,Lot020821 TCR-690,LotG01406042 TCR-685L, ot22-60824A
TCR-684,LotG01410002 TCR-683,LotIR02-014
TCR-874,LotN087P27
Justification of the Test System. Based on preliminary testing, normal pooled serum and plasma contain endogenous levels of the test substances.
Identification of Test System. Samples were identified by the TCR number.
Collection of Test Systems. The commercial vendors indicated that three of the four lots of commercial pooled human serum and three lots of commercial pooled human plasma purchased for this study were collected from subjects residing in close proximity to the individualvendors (Sigma-Aldrich purchases blood products from blood banks located throughout the US). Hence, although limited to single lots of serum or plasma per location, analytical data from the purchased serum and plasma provide a benchmark of endogenous levels of fluorochemicals from different regions of the country.
METHOD SUMMARIES
Preparatory and Analytical Method
ETS-8-231.1, "Solid Phase Extraction and Analysis of Fluorochemical Compounds from Biological Matricies." A 2.0 mL aliquot of serum or plasma is transferred to a 50 mL screw-
capped polyethylene centrifuge tube. Spiking solution is added as appropriate, followed by
the addition of 8.0 mL of ASTM Type I water. The mixture is shaken and 40.0 mL of acetonitrile are added. The sample container was capped, mixed for 20 minutes, and centrifuged at 3,500 rpm for 20 minutes to clarify the supernatant. Following centrifugation, the supernatant is transferred to a 500 mL Nalgene container, diluted with 350 mL ASTM Type I water, and passed through a pre-conditioned Cla solid phase extraction (SPE) cartridge. The analytes of interest are eluted from the SPE cartridge using 2.0 mL of methanol.
Concentrated SPE Method, A modified form of the SPE method described by ETS-8-231.1, "Solid Phase Extraction and Analysis of Fluorochemical Compounds from Biological Matricies." used to concentrate analytes present at concentrations below the LOQ. A fivefold concentration is achieved by using 5 times more serum or plasma while maintaining the
foinr apllaeslumtiaontravnoslufemreredat t2o.0a m25L0mmeLthNanaolgl.enTehe cmoentthaoinderc.onSspisiktsingofsaol1u0ti.o0nmwLasalaiqdudoetdofasserum appropriate, followed by the addition of 40.0 mL of ASTM Type I water. The mixture is shaken and 200.0 mL of acetonitrile are added. The sample container is capped, mixed for 20 minutes, and centrifuged at 3,500 rpm for 20 minutes to clarify the supernatant. Following centrifugation, the supernatant is transferred to a 2.0 L Nalgene container, diluted with 1750 mL ASTM Type I water, and passed through a pre-conditioned C_8solid phase extraction
Page 15 of 225
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E02-1039
(SPE) cartridge. The analytes of interest are eluted from the SPE cartridge using 2.0 mL of methanol. Further sensitivity was achieved by doubling the injection volume of the standards used to calibrate the run.
Analytical Method
Liquid Chromatograph: Hewlett-PackardSeries 1100 Liquid Chromatograph Analytical column: KeystoneBetasilTMC182xl00mm, 51Jmparticle size Column temperature: 40 C Cycle Time: 17.0 minutes Flow rate: 300pL/min Injection volume: 10 pL (20 IJLfor concentrated SPE method only) Mobile phase components:
Solvent A: 2.0 mM ammonium acetate in water Solvent B: Methanol
system
Solvent Gradient:
Time (rain.)
0.00 10.00 11.00 11.50 12.50 13.00 16.00
%B
40% 90% 90 % 100 % 100 % 40 % 4O %
Mass Spectrometer: Micromass Quatro Ultima triple quadrupole mass spectrometer Software: Masslynx version 3.5.
Mass Spectrometer Acquisition Parameters:
(c7)
Channel Parent Ion
Daughter Ion
Collision Cone (V)
(m/z)
1
363.00
(m/z)
Ener.qv
{eV)
119.00
20
20
2 3 4
(c.)
Channel
1 2 3 4
363.00 363.00 363.00
Parent Ion (m/z}
413.00 413.00 413.00 413.00
169.00
20
219.00
20
319.00
20
Daughter Ion (m/z)
119.00 169.00
219.00 369.00
Collision Enerqv (eV)
20 20
20 20
20 20 20
Cone (V)
20 20 20 20
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Channel
1
2 3 4
(Ct0)
Channel
1 2
Parent Ion (m/z)
463.00
463.00 463.00 463.00
Parent Ion (m/z)
513.00 513.00
Daughter Ion (m/z)
119.00
169.00 219.00 419.00
Daughter Ion (m/z)
119.00 169.00
3M ENVIRONMENTAL LABORATORY
E02-1039
Collision EnemY (eV)
20
20 20 20
Cone (V)
20
20 20 20
Collision Enerqy (eV)
20
20
Cone (V)
20 20
4
(Ctl)
Channel
1 2 3 4
513.00
Parent Ion (m/z)
563.00 563.00 563.00 563.00
469.00
20
Daughter Ion (m/z)
119.00
169.00 219.00
519.00
Collision Ener.qv(eV)
20
20 20
20
20
Cone (V)
20 20 20 20
Channel
1 2 3
Parent Ion (m/z,)
613.00
613.00
613.00
Daughter Ion (m/z)
119.00
169.00
219.00
Collision Enerqv (eV)
20
20
20
4 613.00 569.00 20
Cone (V)
20 20 20
20
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E02-1039
PFOS Channel
2 3
Parent Ion (m/z)
Daughter Ion (m/z)
,0000 000 499.00
99.00
Collision Enerqv {eV)
45
499.00
130.00
45
Cone (V)
00 60
60
Capillary Voltage: 4000 V Gain = 1.0 EMV Mode: Electrospray Negative Gas Temperature: 250 C
DNreybinuglizGerasP:re8s.0suLr/em: i3n0. psig Analysis Type: Multiple Reaction Monitoring (MRM)
ANALYTICAL RESULTS
Data quality objectives outlined in the 3M Environmental Laboratory method were met (see Appendix A).
Regressions. Quadratic curve fit weighted 1/x was applied to calibration standards and sample data to improve quantitation over the concentration range appropriate to the data. All calibration curves had a coefficient of determination of 0.998 or greater.
Calibration Standards. Calibration curves were prepared from extracted matrix standards in
Chinese plasma for all plasma and serum quantitations. Reported values were not corrected
for endogenous levels of test substance in the Chinese plasma calibration curve (levels of all
endogenous test substances in the Chinese plasma were determined to be < LOQ). The
curves
a
points.
by
regresscioonnsaisntaeldysoisf usminingimthuempeoafknainreea(9s)of the anTahlyetee.qTuhaetioancwcuarsacdyeotefremaicnhedlevelwas
verified. Any level outside70% - 130% of nominalwas deactivated,and regression re-
ConctianluciunlgateCda. liAblrlalteiovnelsVsehroifwiceadtioanr.espFoonrsqeuagnretitaatteivrethdaentetwrmicienathtiaotnosf, tahembidla-lnekve. l matrix calibration check was analyzed at least every ten samples to monitor instrumental drift, with a limit of +25% deviation of the target concentrations.
Limit of Quantitation (LOQ). The LOQ was equalto the loweststandardin the calibration
curve,with a level of accuracywithin+30%. The levelof analyte in the LOQ was also greater than two times the response of analyte in the blank samples.
Demonstration of Specificity. The identification of analytes was substantiated by chromatographic retention times, characteristic primary ions, characteristic daughter ions, and isomeric proportions (where applicable).
Control of Bias. Two levels of matrix fortifications, prepared at knownconcentrations of the test substance and bracl_eting the anticipated range of the method were evaluated to determine recovery and to evaluate method performance. In serum samples, PFOS and C12 exhibited matrix effects identified by high (>150% recovery) or low (< 75% recovery. For all other analytes, and for all analytes in plasma samples, recoveries ranged from 75% to 105%. Reagent and matrix blanks were run with each set to evaluate the level of background interferences.
Page 18 of 225
3M ENWRONMENTAL
LABORA TORY
E02-1039
Blanks. Method blanks and matrix blanks were evaluated in the course of this study. The
method blanks showed no evidence of background contamination introduced in the sample
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preparation stage. The matrix blanks did show endogenous levels of the analytes. This was
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expected and such instances were noted in the raw data.
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3M ENVIRONMENTAL LABORATORY E02-1039
DATA SUMMARY
Quantitative screenings were conducted on four lots of normal pooled human serum and four lots of normal pooled human plasma for the determination of endogenous levels of perfluoroheptanoate (C7), pentadecafluorooctanoate (C8), heptadecafluorononanoate (C9), nonadecafluorodecanoate (C10), perfluorodecanoate (C11), perfluorododecanoate (C12), and perfluorooctane sulfonate (PFOS) as described by the 3M Environmental Laboratory Study #E021039 protocol. The screening data is summarized in tables 5.a. and 5.b. Matrix spike recovery information is contained in Appendix B.
Table 5.a. Endogenous levels of test substance in normal pooled human serum
Test Substance
PFOS O12
CtI C10 C9 C8 07
_51gma TCR-689 (ng/mL)
4.56 [0.018]
[0.076] [0.058] 0.265 1.60 [0.013]
Lamplre TCR-688 (ng/mL)
[2.49] [< 0.010] 1
[< 0.010]1 [0.031] [0.068] 0.650 [0.025]
Bloresource TCR-687 (ng/mL)
17.0 [0.144]
0.295 [0.327] 0.605 2.95 [< 0.010]'
(5olden west TCR-690 (ng/mL)
27.0 [0.040]
0.320 0.203 0.900 5.60 0.190
[ ] Denotes values determined from concentrated spe method. 1Value < LOQ.
Table 5.b. Endogenous levels of test substance in normal pooled human Plasma
Analyte
PFOS
012
unmese TCR-674
(nglmL) < 1.01
< 0.101
Lamplre TCR-685
(nglmL)
11.1
[0.036]
Innovative Research TCR-683
(ng/mL)
15.6
[0.022]
_olden west TCR-684
(ng/mL)
18.3
[0.024]
0C1 1t0 C9 C8
07
'<< 00.1.01101 < 0.251
< 0.521 < 0.10'
[00..014297] ] 0.435
2.61 0.100
00.1.315 70 0.585
3.07 [0.016]
[ ] Denotes values determined from concentrated spe method. 1Value< LOQ.
[0.107610] 0.535
3.87 0.290
Accurate Mass Determination, Accurate mass measurements and elemental compositions were obtained for endogenous C7-C11 and PFOS in a concentrated SPE extract of normal
pooled human serum purchased from Golden West Biologicals (TCR-690). Accurate mass measurements are presented in Table 6.
Page 20 of 225
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3M ENVIRONMENTAL LABORA TORY
E02-1039
Table 6. Accurate Mass Determination of Endogenous Test Substances
Test Substance Accurate Mass
Theoretical Mass
C7 C8
C9 PFOS C l0 C 11
362.9739 412.9637
462.9613 498.9280 512.9615 562.9542
362.9691 412.9659
463.9627 498.9297 512.9595 562.9563
Mass Deviation
(ppm) 13.3 -5.4
-3.0 -3.3 3.9
-3.8
Probable Formula
C702F13 C802F15 C902F17 C803F17S C loOzF 19
CI IO2F21
Daughter Ions of Endogenous Test Substances, Specificdaughter ionswere observedat characteristic retention times for endogenous C7-C11 and PFOS in a concentrated SPE extract of normal pooled human plasma purchased from Golden West Biologicals (TCR-684). Daughter ions verified in analytical standards of linear isomers. A summary of daughter ions observed is presented in Table 7.
Table 7. Daughter Ions of Endogenous Test Substances
Test Substance Cr C8 C9
C,0 Cll 612
PFOS
Parent Ion (m/z) 363 413 463
513 563 613
Dau_lhter Ions (m/z) 319 119 369 219, 169, 119 419 269, 219, 169, 119
469 319, 269, 219, 169 519 319, 219, 169, 119 569 419, 319, 269, 219, 169, 119
499
130 99, 80
Iesnodmogeersn,oTushefluporeroscehnecmeicoar lasbwseenreceqoufalditiasttirvibeulytiodnesteormf binraendcihnecdoanncdenlitnraetaerdisSoPmEeresxtorfacts of commercial lots of pooled human serum and plasma (Figures 1 - 10). Qualitative analysis of chromatographically resolved branched and linear isomers of PFOA was accomplished using NMR certified standards of a linear isomer PFOA standard and a mixed branched and linear isomer PFOA standard. It was determined that the branched PFOA isomers elute within an
approximate 0.2 minute retention time window and are baseline resolved from the linear PFOA
isomer. This finding of C8 retention time resolution was extrapolated to determine qualitatively the presence of branched and linear isomers for C7, the higher homologues of C9-C12, and PFOS.
Low to non-detect levels of branched isomers were observed for the C7 and C9-C12 compounds detected. PFOS and PFOA were present in the screened lots of sera and plasma as branched and linear isomer distributions. Figure 1 contains chromatograms of NMR certified linear isomer PFOA and mixed branched and linear isomer PFOA standards. Figures 2 - 8 contain
chromatograms of the corresponding standards of C7 -C12 and PFOS in solvent, an extracted calibration curve point (extracted calibration curve point consists of pooled human plasma from central China spiked with 10 ng of test substance/mL of plasma), and three concentrated SPE
Page 21 of 225
3M ENVIRONMENTAL
LABORATORY
E02-1039
extracts of commercial pooled human serum. Pooled human plasma collected in central China was used as the blank matrix to construct an extracted calibration curve because preliminary screening results indicated it did not contain quantifiable levels of endogenous test substances.
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Page 22 of 225
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3M ENVIRONMENTAL LABORATORY E02-1039
Figure 1: NMR Certified 99.5% Linear Isomer PFOA and Mixed Branched and Linear Isomer PFOA Standards
d021 106002 Sm (Mn, lxl)
1 00-
Unear k omer C8 standard
8.43 51249-
<= linear (gg.5%
MRM of 4 Channels ES-
by" NMR)
TI C 3.7 7e5
Area
%.
Lt_}
8.19
...._i
branched(0.5%
byNMR)=>
503___
0 ':'T'li" '_', .... ',...'. _... ;i..-.;'i"
, .... i .... i .... i .... i:.'"-";-I '-;'ff_"''
d021106001 Sm (Mn, lxl) 1 00-
8.43 153171-
MRM of 4 Channels E3TI C
<= linear(77.7%by NMR)
1.35e6
Area
!_'_
Branched & linear isomer PFOAstandard
_
! ,i
i;;:,j'
"._-_ _-i
=%. 8.18
50677
7 88
0-
Time
Summary of branched and isomer PFOA
2.50
5.00
7.50
1 0.00
PFOA Standards: NMR certified standard of the linear
99.5% linear isomers. NMR certified standard of mixed
contains 22.3% branched and 77.7% linear isomers.
12.50
15.00
isomer PFOA contains
branched and linear
0.5%
Page 23 of 225
Figure 2:C7 Isomer Distribution
3M ENVIRONMENTAL LABORA TORY
E02-1039
,r
_,,t -_i_
i 1
:"_
'.L }
_[ ;}
;
_"_" .
'
i ...:.
d021025069 Sm (Mn, lxl)
7 3 __ <= Unear
1: MRM of 4 Channels ES.
TIC
Solvent standard 30 ppb
7.1 | 116_:|
ranohed=, 1(_1 i i i i i i i i J i i i i i | ! i 2 678mj, | I l i l i i I I l l I I I ! 11 ,,1
d021025091Sm (Mn, lxl) 7.3
Chines e plasma 1Oppb
Area
2.09e5 1 | l I l i i I I I I I I i i i i i I ! i I | o 1: MRM of 4 ChannelsES. 2.66e5
Area
1 I1
(branched not obse2rv6e2.d9) .1i <=- Un. ear .
d021025098m (Mn, lxl)
Lampireserurn
_
--7_
< Unear
(branched not observed) IfLI1
111 ....
I ....
I ....
I ....
I .... I 1..../i_, I /..I..
I ....
I ....
d021025108 m (Mn, lxl)
S a serum
- 7 2 <- linear I,
(branched notobserveoj _=_,-
j.
TIC
1: MRM of 4 ChannelsES.
2.g8e4 Area
I ....
I ....
I ....
I' ''
TIC
1" MRM of 4 Channels ES.
.32e4
rea
d0210in25ill 10,2, S,,mi,,(Mn,i , lljxl),, _i ,in =i ,_ i, l,i
,, i= Ii,
i, ,i ,|,
, 1=,i MiR= M=, ofill 4i=Chli a,n'nels ES-
TIC
Golden West serum
Area
11%_
_'_54 <= Unear /_1
4.93e4
(branched not observed) "lJ_
._ L it,,_,
OJ'-.1,, .... ,,. : ,._, .',',":'_..'_,'."_....,
2.50
5.00
7.50
_','.":_,1"_,,",/'_/._,,, :.-:_,.,. ,-'-"T--im='e, 10.00 12.50 15.00
Summary of Cz Acid Chromatograms: Low to non-detect levels of the branched isomers of Cz acid were observed in these lots of Commercialpooled human serum.
Page 24 of 225
3M ENVIRONMENTAL LABORATORY E02-1039
,i
%
Lb
i; -. "';:_'::_ _,,
i
i
::.A
,
.....
b:."-
_:i!_
_,_ _,";!;_ i_;
;
i ....;
iJ,::}
Figure 3: Ca Isomer Distribution
d021024012Sm(Mn, lxl)
Sohtentstandard 30 ppb
<= Linear
2: MRMof 4Channels ESTIC
3 23e5 Area
8.22!
=== ii l= ==1 i= ii ill
Branched => 48tl
== i= i= =1 =l ill
ii =l
d021024034Sm(Mn, lxl)
B.47
69023
Chinese plasma lOppb
ll=
== i= ill
<=Unear
i= ii ii li=ll
,= l= ill
==
2: MRMof 4ChannelsESTI C
6.80e5 Area
8.21i
Branched =>
534| "%1
0" .... = .... = .... i .... i .... i .... , .... , .... i .... i .... i .... t .... i ....
d021024041Sm (Mn,11)
2: MRMof 4 Channels ES-
100-_
Lampire serum
/ 683.64045q1 <=Linear
6.3T0eIC5 Area
"1 Branche=d> 180.2118_|1 0 /
_ , i , _ _ _ i ' _ J = i I _ ' I I , , M ' i =% ' ' i '%' * = 1 _ = ' ' i ' = _ '*1 _ _ J _ i ' = = _ I _ = _ J I = , , _
d021024043Sm (Mn,lxl)
2: MRMof 4 Channels ES-
Sigma serum
79360 <= IJnear
8.1 4 /
1_1
Oi'"
"' I"''
Branched => 87.2458_i1tI
"i "" "'" I '' "--'%"1 ....
I ....
I ....
i .....
I ....
d021024045m(Mn, lxl)
8.40
8.1 385
Area
i ....
I ....
"I''-'_T
TIC
" :'-"
2: MRMof 4ChannelsESTIC
Golden west serum
Area
0" .... i .... , .... 2.50
I 7.aO
Branched=> 861.91
, .... , .... , .... ,_'",
5.00
7.50
'", .... 10.00
, .... , .... l .... , .... Time
12.50
15.00
Summaryof C8Chromatograms:Lowto non-detectlevelsof branchedisomersof C8were observedin theselotsof commercialpooledhumanserum.
Page 25 of 225
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3M ENVIRONMENTAL LABORATORY
E02-1039
Figure 4:C9 Isomer Distribution
d021025069 Srn (Mn, lxl)
Solventstandard 30 ppb
40551
<= Unear
2: MRN of 4 Channels ES.
4.0105 Area
(branched not observed)
....
! ....
I ....
I ....
I ....
d021025091 Srn (Mn, lxl)
I' '' '1 ....
I ....
0.1o
I ' '' 't ....
I ....
I ''''
I ....
2: MRM of 4 Channels ETIC
C hinese plasma lOppb (branched not o_erved)
.... t .... i .... I .... I .... i .... i ....
d021025098 m (Mn, lxl)
1<= Linear
i .... , .... f .... , .... I ''' '_-_1....
Area
2: MRM of 4 ChannelsES.
La mp ire se rum
_50 t_, _
888 I <= Unear
Area
0"-1,. :_._.... , .... ,...',...-:,.7.., d021025100 Sm (Mn, lxl)
Sigma serurn
: .... :','. , .................... 2: MRM of 4 Channels ES. TIC
g.04 7041 <
Area
_- _ ' _ t" * a _ I ' " ' ' I ' ' '' I _ _B_ r_anI c'-_he_d=' >I ' _ J_ ,'_,
I ' ' ' _t _ ' _ ' I
I-'" "'_t_'-t _' ' ''
d021025102 8m (Mn, lx1)
Golden wests erum
004
1_24
2: MRM of 4 ChannelsTEISC.
I
2.8605
Area
0 I' ' '--;-_f"
' ' ' I ....
2.50
188_t_I <=Linear
J[
Branched=>
'11 _
.-
It
1% ' ' ' I ' ; ' '' I ...."
"!_" ....
"_I ....
I _.."._. "*'-_"--_=" ....
I ...%. --'_"_1'_I ....
I ' ' ' T/IIIIU_._
5.00
7.50
10.00
12.50
15.00
Summaryof C9Chromatoqrams:Lowto non-detectlevelsof branchedisomersof C9were observedin theselots of commercialpooledhumanserum.
Page 26 of 225
__
Figure 5: Clo Isomer Distribution
3M ENVIRONMENTAL LABORATORY
E02-1039
::_3
i_'i
i
.+: _!_,:_ '_:"," _%i ..."...
i:!J
i:_.! '!
,_ I
_f_l
+.._..':_'_
'!
+:
--_' _:_ !'i.!_!
d021024012 Sm (t,,,lnl,xl) 1007
Solvent standard
"1
38 ppb
d021024034 Sm (Mn, lxl)
100-
9.91 _ 28022
3: _IRMof 4 Channels ES-
TIC
<=Linear
2.A87reea5
Branched => _. 930..7_/7
9.89 46914-j
3: MRMof 4 Channels ESTI C
<=Linear
4.97e5
%- Chinese plasma lOppb
O' ""'l .... i .... f .... d021 124041Sm (Mn, lxl)
100-_ Lampire serum
"l
0 [I '' II ''= '1 '= ''1
=' ''
d021024043 Sm (Mn, lxl)
i ....
I= '''Ill=
[ 9B3/
Area
era,-,o=h>edzo3|
+.... I .... I .... +.... , .... J.... ? .... I ....
3: MRMol' 4 Channels ES-
9.88
TI C
1745 qI,
9.701
.
<= Unear
2.A00reea4
Branched => 104
'1 =l ''i
II '= I= =l'
9.84
I' 'l =1 '= ==1 '' 'l I+' ''
3: MRMof 4 Channels ESTI C
1001 Sigma serum
2457"1_ <= Linear
2.A88reea4
II %_
= 9.691
0 ''_
,+_'--:"'-;-" "--, '-' - , .... , .... , .... , .... i .... , .... , .... , ....
d021024045Sm (Mn, lxl)
3: MRMo14' ChannelsES-
9.84
TI C
9223
1.00e5
l<=.+r Golden west serum
9.66 I
Branche=d>
10.86 12.30
0 . . .'., ,., ,'_q_',. .-_-. ,-, .... __, ._..... , .... , .... , .... , ....9_,4...9-__.
2.50
5.00
7.50
10.00
12.50
15.00
Area Time
Summaryof C_o,ChromatogramsL:owto non-detectlevelsof branchedisomersof C10 were observedin theselots of commercialpooledhumanserum.
Page 27 of 225
i,il,i
p
i
,i ,,,I,j ...._
:"]
_,i
: !:_i1 .... _iit _
3M ENVIRONMENTAL LABORATORY
E02-1039
Figure 6: Cll Isomer Distribution
ct021025069 Sm (t_ln1, 1)
100]
10.31 54214 q
3 MRM of 4 Channels EBTI C
5.7 2e 5
Solventstandard30 ppb
i "1
0""_ u u-, j , a u, j , , , u-j u'_ , , | .... j;3
d021 025091 Sm (Mn, lxl)
1 00_
_n ChineseplasmaIOppb
i
1o.o7/ lO31 II
<= Unear
Area
, , lu B, r,annj c="h, _e-,dj=,>= = ui-,-, u_, "_=jI,,, , , uTT]TT,-,-u j "g-=a n , i u_r'l' , = u
10.28 _ 43258
3: MRM of 4 Channels ES-
TI C
4.54e5
<= Linear
Area
96t
0 / .... ,'I''1
Branched=> 703 10.05
.... , .... I .... | .... I .... I .... I .... I .......
I .... I .... I .... I .... , ....
d021 02509fl Sm (Mn, lxl) 1
00q-
10.31 542 -_
3: MRM ef 4 Channels ESTI C
7 44e3
_ Lampireserum
=
I <= Linear
Area
d021 0251 00 Sm (Mn, lxl)
100
_ _] Sigmas erum
t%
0 _-.;., .... i .... , .... , .... ,'"
10.23
3: MRM of 4 Channels ESTIC
"1 3318| <= Linear
3.75e4
Area
Branched=> 10.0711
358,_1 , .... ,...-, :.'-t-'. ;., .... ,.... , .... ,..*"_.1.... _'....
d021 025102 Bm (Mn, lxl) 100-_
10.23 8903
"-_
3: MtRM of 4 Channels ETSI-C
9.71e4
_= linear
,Area
Goldenwest serum
0J .... , .... i .... , .... , ....
2.00
4.00
114111 10.07|
Branched=> '_ , .... , .... , .... i .... , .... I ....
8.00
8.00
10.00
, .... , .... 12.00
Summary of C,11Chromatograms:
Low to non-detect levels
observed in these lots of commercial pooled human serum.
| .... | .... , ..... Time 14.00
of branched isomers
of C_
were
Page 28 of 225
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i ..i
3M ENVIRONMENTAL LABORATORY
E02-1039
Figure 7: Clz Isomer Distribution
d021025126 Sm (Mn, lxl)
10
Solvent standard 30 ppb
10.75
o2a2e
2: MRM or 4 ChannelsES. TIC
<= Unear
8.0005 Area
(branched not observed)
' = '' I ' ' ' " I '' ' ' I' " '' I ' '' ' I ' ' ' 'I ' " ' ' I" " ' ' I ' '' ' I
'' t' ' ' ' I ' ' ' ' I ' w '=
d021025148 Sm (Mn, lxl)
lO.72
2: MRM of 4 Channels ES. TIC
Chinese plasma 10ppb
(branched not observed) !
,,,', =.... i r,.,, ; r,, r ,-.;,-i_,, _,, ;;, =, ,-,; i;,,, d021025155 Sm (Mn, lxl)
1007
1 Lampire serum ]
10.75307 ]
(branched not observed)
J
,_-_i;;,, 2: MRM
<= Linear I
T;-,-.,-i;,,
of 4 Channels ES.
Ic
6.9T6p.3.
Area
o ,', ,, ,, , , , .,, , w ,, o., ,, i, . ,=,1,
d021025157 Sm (Mn, lxl)
1 n_
Olu_
,, , , , ,,,. , , , , i, ,
lO.72
528 "i _)
, , ,, . , , , , ., , , , , , ,,
2: MRM of 4 Channels E.
<= Unear
TIC 1.01 e4
_ Sigmaseru m
,Zl
I
Area
0"_ ....
I ' ' ' ' I ....
I ....
I ' '' ' I ....
I ....
I ....
I ....
I ' ' '' [' ' ' ' I ' ' ' ' I' ' ''
d021025159 Sm (Mn, lxl)
lO.71 2: MRM of 4 Channels TEICS.
lo.m
A rea
1_1 ,G_ol-den wesi,t.,s-,e-rju,5m_ ,.............,...... , .... , ...1. 478, ..Q.. , <..=.. lin,e.a..r. , . ,'. 2T.3im50e4
2.58
5.00
7.50
10.00
12.50
15.00
Summary of C_ Chromatograms: Low to non-detect levels of branched isomers of 012 were observed in these lots of commercial pooled human serum.
Page 29 of 225
" -1
ii"!1_ i;'_'1
! :::i:_
; i i!_i':i
7:;}
.j
!]
]
;
_!
_
,.:L "'
:i
Figure8: PFOSIsomerDistribution
3M ENVIRONMENTAL
LABORATORY
E02-1039
d021lI25126 Srn (ran, lxl) 100-
Solvent standard 38 ppb
9.08 7 85187l
I
B.BI I
50373 /
<= Unear
1. M_M of 3 Channels ESTIC
9.15e5 Area
0 ....
I ....
I ....
I ....
I ....
d0211125M8 Srn (Mn, 1)1) 100-
Chinese plasma 10pph
o ..............
dO21(25155 Sm (Mn, lxl) 1go-
, .........
Branched =>
I ....
I ....
I ....
, .....................
378B5_
I ....
I ....
I ....
I ....
I ....
I ....
I ....
I ....
590.70974_/
i
i
8.79 |
<= Linear
1: MRM or 3 Channels ES6.64T0I5C Area
8.55 228
9.09 _ 94485 I
,.......
<= Linear
, ........................
1: MRM of 3 Channels ESTIC
1.2385
" Lamp|re serum
Branched =>
ii 785158|813'
8.57
Area
O ' ' ' ' I ....
I ....
i ....
I ....
I ....
I ....
I ....
T' ' '_' I ....
I ....
I ....
I ....
I ....
I ....
t ....
C10211)25157Sm (Mn, lxl)
1: MF_Mof 3 Channels ES-
9.05
TIC
Sigma serum
'!1" ' ' ' ' I ....
I ....
I ....
I ....
{3021ll25159 Sm (Mn, lxl)
10O-
%-
Goldenwest serum "
0 , , ...,...,.'_..'.....,..,. . .... 2.00
,,
_
4.OO
Branched=>
I ....
l ....
I ....
18e363 /
tl 851
21 |0q<8:7n7ear 514oj| _ ....
I ''_ ' ' I ....
I ....
I ....
9.04
707835]
5584.73899 II <= Unear
8.52II
18417
, B, r,a,n.c..h. ed i: )
; _" _1 _ ......,..............L...... ,
6.00
800
1000
12.00
I ....
I ....
I ....
,,e Area
1: MRM ot 3 Channels ESTIC
867e6
Area
,
;
,
14.00
Time
Summary of PFOS Chromatograms: Branched isomers of PFOS were observed in these lots of commercial pooled human serum.
Page 30 of 225
i_!ii
'_! I
!:!,,,] _i[_
ii!1i _i]
3M ENVIRONMENTAL
LABORA TORY
E02-1039
STATISTICAL METHODS AND CALCULATIONS Theoretical concentrations of analyte in final eluate:
Concentration = (Concentration of Analytical Standard x Amount of standard added) / EV Observed result to original sample result: Original sample result = Observed result x DF
Spike percent recoveries:
%Recovery
Observed Result - Same Sample, Unspiked
=
Theoretical Concentration
x 100
EV= Eluate volume DF = Dilution factor Relative standard deviation:
Standard Deviation
Relative Standard Deviation =
x 100
Mean
% Deviation
Means and standard
= Theoretical TheCoornetci.ca-l CCalocnucla. ted Conc. x 100
deviations were calculated using Excel software.
i
:I I? i
Page 31 of 225
3M ENVIRONMENTAL
LABORATORY
E02-1039
STATEMENT OF CONCLUSION
Resultsfrom this study showed quantifiablelevels of the linear isomers of C7, C9-C12 ranging
from < 0.010 - 0.9 ng/mL (Tablesla and lb), Low to non-detect levelsof branched isomers
:_"_
were observed for the C7 and C9-C12 compounds detected (Figures 1 -10). PFOS was present
!!l
in the screened lots of commercial sera and plasma in concentrations ranging from 2.5 - 27
ng/mL and was present as branched and linear isomers. PFOA was present in the screened lots
_<.!
of commercial sera and plasma in concentrations ranging from 0.65 - 5.6 ng/mL and was present
as branched and linear isomers.
Accurate mass measurements and elemental compositions were obtained for endogenous C7C11, and PFOS that are consistent with theoretical mass and elemental composition.
The presence of confirmatory daughter ions at characteristic retention times of target analytes in matrix are consistent with the linear isomer analytical standards.
<
i
..J
,t cJ
Page 32 of 225
3M ENVIRONMENTAL LABORATORY
E02-1039
REFERENCES
i
None
LIST OF ATTACHMENTS
AttachmentA: Extractionand AnalyticalMethods
AttachmentB: Data Summary Tables
AttachmentC: Sample Chromatograms
,
Attachment D: Sample Prep Sheets, Test Substance Information and Notes to File
Attachment E: Protocol, Protocol Amendments and Deviations
't ':i
REPORT REVISIONS
I
':...1
Semi-quantitative estimates for THPFOS and THPFDS were removed from tables la, lb, 5a, and
5b because the data was intended as quantitative and only screening estimates could be
:'
obtained. References to THPFOS and THPFDS were removed from the list of test substances
table 2 (page 11), chemical structures (page 13), reference substances table 3 (page 14), mass
spectrometer acquisition parameters (page 18), and control of bias (page 19). References to THPFOS and THPFDS were also removed from the accurate mass determination discussion
(page 20) and accurate mass determination data table 6 (page 21), daughter ion discussion (page 21) and daughter ion data table 7 (page 21), isomer discussion (page 21), and isomer figures 8 and 9 (pages 30 and 31). Wording in the Executive Summary (page 8), Summary (page
ii_
9re),mIonvtraoldoufctthioens(epmagi-equ1a1n)t,itaantidveSteastteimaetnetsofoCr TonHcPluFsOioSn a(pnadgTeH3P4F) DwSas. mSeovdeifrieadl tytoporegfrlaepcht itchael
errors were also corrected, including William K. Reagen's phone number (page 7), formulas for
the anionic forms of THPFOS and THPFDS in table 2 (page 11), and the units designator for
%_
mass deviation, table 6 (page 21).
A protocol amendment was written to address the removal of THPFOS and THPFDS from the
study.
I
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Page 33 of 225
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SIG NATU RE PAG E
3M ENVIRONMENTAL
LABORATORY
E02-1039
,_
We certify that this report is a true and complete representation of the data for this study:
M_k I_.Eliefson Study Director
....
William K. Reagen
Testing Facility Management
Date Date
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Page 34 of 225
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ATTACHMENAT: METHOD
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E02-1039
Page 35 of 225
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E02-1039
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Record of Deviation
I. Identification
Study/Project No.
Deviation Tj_pe:
(Checkone)
E02-1039
r=]soP: .... I'-IProtocol
......................
_victhod E]EquipmentProcedt_e [3 Other:
.................
Document Numl_eri i_'_S-8-23 I_i ....... . ..... Date(si of 0eeu_ene-- i0 C)et 02 to"2_i_Det-'02---
II. Description:
Required Procedure/process: ETS-8-231.I section 9.6, "Quality Control (QC) Sample" see method for details.
Ae_all'rocedure/proe_sssi_Tlecontinued accuracy of the calibration curve was monitored through the re-injection era curve point after no more than I0 samples and at the end of the run, not by preparing additional samples. The QC samples described in the method were prepared to monitor extraction efficiency. The QC samples were only spiked at 2 levels, 0.5 and 5ppb. In addition, only 2 QC samples were prepared for each matrix. It was possible, therefore, to distinguish between the continued accuracy of the calibration curve and the
.extractio n effiy!en_ey.in eachma__.tested. _................................
DuHngthe course 0f flaestudy 2/3 of thi,-Qc sanapi-esprepm:ed in the sarne mah:ix-_-the ...... icalibration curve were within +9-5% of expected values, All of the 5ppb spikes passed, but only 3 of 9 low s_pikespassed.
IlL Actions Taken:
..............................
(s.uch_._.a..men d__m_e_nstued,_So_P..r.e vision,..et_c..:.)...........................
No addit!onal..a.ctign wi!l.b_e.ne_ed__e.._..d.............................................................
.............. ........
i? .........................................]7.....71......... i................
Date:
Recorded By:,
IV. Impact on Study/Project
tt
ThiSstudy.deviatdioorets n0t adversely affect the quality o-fthe data in the"context-o-f-the current .......... _'_._-_|t
Authorized By: (Study Di_ior//Pro-j_-fiej(d)
...........................
Date: .......-./ _ ..........
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3M Em,ironmental Laboratoly
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Deviation No.
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(assignedby StudyDirectororProjectLeadat the endofstudyor project)
Page 36 of 225
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3M ENVIRONMENTAL
LABORATORY
E02-1039
.-
Method Solid Phase Extraction and Analysis of Fluorochemical
Compoundsfrom Biological Matrices Method Number: ETS.8.231.1
Adoption Date1: 1/13/_/
Revision Date: ._//_t/o2..
EffectiveDate.:_/#l/oz
Approved By:
Willliam K. Reagen
Date
,4
$
ETS-8-231.1 Solid Phase Extraction and Analysis ot'Fluorochcmical
Compoundsfrom Biological Matrices
Page I of 19
Page 37 of 225
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E02-1039
1 Scope and Application
This =trothedescribestheextractionof ta._.'t analytasfrom fish,rat liver, ratscra,mouseliver, andmouseserausing solidphaseextraction(SPE). This methodmayalsobe extendedto otherbiologicalrnaciccsprovideddmtthe dam qualityobjectivesam met.
2 Method Summary
An amount of biological ma),'rial,dctcnnmed by tic analyst.,is prepared(t_dds diluted and tissues homogenized) at a 1/6 dilution, or other dilution as dcte_ned by the analyst using reagent grade water. An aliquot of the dilution/homogcnatics spikedwith tic appropriatesurrogateor anal.ytm ixture. Acctonitzile(ACN) isaddedasan extractionsolvenatndalsoservetso p_cipitatcthe proteins.The sampleis capped,mixed'andputonthe cenn'ifice to Clarifythe supemata_._ supcrra,tam istransferredto a cleanrobe,dilutedv_thwater, andpassedtkrougha proeondifionedC,s SPE carCidgc.Finally, theu_aiytcsofintercs_amelatedfrom theSPE cartridgeandanalyzedby high pcrf.oml_cc liquid chromatography-clectzosptraanydemmassspccUometz(7HPLC-ES/MS/MS).
3 Definitions
3.1 Dilution
A dilution expressedas 1:5or 1/6 is definedas: ! mL of.sample+ 5 m[J of.diluentfor a total of 6 mLs combined, unlessotherwls= noted.
3,2 SPE cartridge
A columncontaininganopensolventreservoirat oneendandpackedwith bondedsilicasorbentsat the other end. It is designedto retain the compoundsof"inter_t under some solventconditionsand elut= them under others. A separation is thus achieved; compounds can b removed from difficult biological mamccs and introduced into appropriatesolvents for analysis.
3,3 Reagent grade water
Water with no detectableconcentration(so)f the targetanalyt(s).
3.4 Quality control sample
Sampleused re monitor_c cxwacdone_cicncy (-',_a matrixspike)andm _rif T rhccondnuedaccuracyof"_ minal calibration curve (as a continuingcalibration verification).
4 Warnings and Cautions
4.1 Health and Safety Warnings
Always wear appropriate gloves, eyewear, and clothing when working with solvents, _mples and/or equipmenL
Use caution with the voltage cables tbr the pr'ob. When engaged, the probeemploys a voltage of approximately 5000 volts.
4.2 Cautions
Take cam not to allow the SPE column to run to dryness after the methanol and water washes. After washing is complete, add sample then allow all of the liquid to pass through the SPE column to dryness.
ETS-8-23 I.I SolklPhase Extraction and Analysis of Fluorochemieal
Conlpottndfrsom Biological Matrices
Page2 of19
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Dbaor,ntehteoHpPerLaCtewsilol linvietinaptto-raauptosamboavtiecschauptadcoitvymof. 400 bar (5800 psi)back pressure, if the back pressure exce_is 400 Do notmn solventpumpsto dryness.
5 interferences
To minimize interferencesT, eflon shouldnotbe ascdfor samplestorageor any partof instrumentationthatcomesin
contactwith the san_[cor cxtracL
6 instrumentationS,uppliesa, ndMaterials
The following instrumentation,supplies,and materialsarc used while performing this method. Equivalent instrumentations, upplies,andmaterialsmayI_ usedin placeof thoselisted. 6.1 Instrumentation Vortex mixer, VWR, Vortex Genie2 URra-TurraxT25 tissuehomogenizer
va,,mP
SPE ExtractionManifold Centrifuge,Mistral !000 or IEC Shakcr,EbcrbachorVWR Balance(+/- O.lO00g) Micromess, Quattro II or Ultima triplequadrepolc Mass Spectrometerequipped with an electro.sprayionization source
HP l 100 or Agilent low pulse solvent pumping system, solvent degasser,column compartment, and autosampler 6.2 Supplies and Materials
Eppendorf or disposable pipettes, plastic or _Jass Dissecting sealpcts Polypropylenc bottles, capable of holding 50 mL to I L (Nalgene) Volumetric flasks, glass, type A
40 mL glass vhals (/CH_ Plastic sampul vials, Wheatoth 6 mL (or other appropriate size) Centrifuge tubes, polypmpylene, 15 mL and 50 mL Labels
GSyraridnugaetse,dcappipaebtlteeso, fgmlaesassuring 5 I.tLto 1000 I.tL Bottle-Top Dispenser (capable of'dispensing 5mL of solvent) SPE oxtmction cartridge, l g, Sep-Pak 6 cc tri-funetional C,, (Waters) 75 mL sample reservoir (or other appropriate size)
Crimp cap glass autovials and caps
ETS-8-23 I.I Solid Phase Extraction and Analysis of Fluorochemical
Compounds from Biological Matrices
Page 3 of I9
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Crimpers HPLCanalyticaclolumns, pecifictso bedeterminebdytheanalysatnddocumenteindtherawdata.
7 Reagents and Standards
ReagengtradewaterM, illi-QTM,NanopumI1,orequivalent Acctonitr/lH, TLCgrac_orequivalent Methanol,H'PLCgradeor _[uivalent Ammoniumacetater,eagentgradeor equivalent
Biologicaflluidsortissuesfr,ozenfromsupplier
7.1 Reagentspreparation
2.0 mM ammoniumacetatesolution:Weighapproximate0ly.300g ammoniumacetateP. ourintoa 2000 mL volumetricontainecrontaininrgeagengtradwater,mixuntilallsolidsaredissolvedb,ringto'volumeusing==agmt gradewater.Storeatroomtemperature.. Notet Whenpreparingdifferentvoluracsthanthoselistedinreagentspreparation,targetanal],,smtandardpreparation, andsurrogatsetandarpdrepacatioand,jusatccordingly.
7.2 Target analytestandardpreparation
Prcparetargcat nalytestandard(sfo) rthestandardcurve.MulticomponeanntalytestandardasreacceptableT.he followingis anexamploenlyandmayormaynotbeappropriaftoerallstandarpdreparations. Weighapproximatelyt00 mg of targetan'ak_ intoa I00 mL volumetricflaskand recordthe actual weightin the aandardlogbookorotherappropriatleocation.
Bringto volumewithmethanolfora stockstandardof approximately1000ppm(gg/mL).
caIculat_onth.'eDilLsittoeck|000_._i.LSn'utin,w2(ithmL0/,0_thanlmL-'rwors_tai.n._gg,0/mL.
s_Lrldard'
slution of" approxilff3_tely ,0 ppilz F._J_amp I e
Diluteworking standard1 withmethanolto producea workingstandard2 solutionof approx.5,0 ppra. Example
cDail/cttumlawtioornk:5in0gIs.ttga/nmdaLxrd1I0mwiltJhl0m0emthLan=o5l.t0opp.rgo/dmuLcea workingstandard3 solutionof approx.0.50 pp_ Example calculation:50 lag/mLx 1.0mL/100aft.,= 0.5 I,tg/mL
7.3 SPrueprraoresguarrtoegsattsaetannddaarrdd(spT)r.heepfoallroawtiinoginsanexamploenlyandmayor maynotbeappmpdatfeorall surrogato
standardpreparations. Weighapproximately90-110mgofsunogatestandardintoa 100-mLvohunetrieflaskand recordthe actualweight. Bringtovolumewithmethanolfora surrogatestandardstockof approximatel9y00 - I 100ppm.
volumetricflaskand bringtovolumewithmethanolfora workingstandardof90-110ppm.Recordthe actual volume tral'isferred and standardconcentrationins the standardslogbookorotherappropriatelocation. Preparea sun'ogatestandardworkingstandard.TransferapproximatelyI mL of surrogatestandardstack toa 10-mI..
Prcparainternalstandard(s).The followingis an exampleonly andmay or maynot be appropriateforall internal
7.4 Istnatnedranrdaplrepstaarantidoanrs.d preparation
Weighapproximately90-1I0 mgof internal:;tandardintoa 100-mLvolumetricflaskandrecordthe actualweight.
ffrs-8-231.1 Solid Phase Exwactionand Analysisof Fluorochemieal
Compounds fromBiologicalMatrices
Page 4 of 19
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Bring tovolumewith methanolfor an internasl tandardstockofapproximatel9y00 - I 100ppm.
Preparean internalstandardworking standard.Tranffcr approximately1 mL of internalstandardstockto a 10-mL volumetricflask andbring to volumewith methanolfor a workingstandardofg0-110Fpnt Recordtheactualvolume transferredandstandardconcentratiomin thestandardsIogbeokor otherappropriatelocation.
8 Sample Handling
i
All smnplesam receivedfiozenandtram be keptfrozenmad[theextractionis performed.
Allow samplestothaw toroomtemperatureprior toextraction.
Typically fi-e_ matrix standardsarc preparedwith eachanalysis. Extractedstandardsand samplesarc storedin
cappedautovialsuntil aral_is,
/
If analysiswill be dela)cd,_lracted stand='d.a_nd _amplesmaybe refiige_ted at approximately4C indefinitelyor may be storedat roomtemperatmuntil anal_iscanbeperformed.
9 Quality Control
9.1 Blanks 9.1.1 Solvent Blank
An aliquotof methanoils usedasa solventblank. Solventblanksate notextracted.
9.1.2
Method Blank
An aliquot of 1.0 mL of water, or other appropriateamount, is used as a method blank. Four method blanks am extracted and analyzed with each sut following this procedure (two are spiked with surrogate and two am not spiked),
9.1.3
Matrix Blank
An aliquot of 1.0 mL or 1.0g of matrix(diluted orhomogenized) is used as a matrix blank. Other amounts may be used, as appropriate. Matrix blanks am l:_parcd fromone of throe source,s: l) a study control matrix from a study control animal received with a sampl set; 2) a commercially obtained sampl," of the same species as the study animals; or 3) a surrogate n-am'ix,also obtainedcommemiidly, but of a different species than the study animal. (g.
if rat is used to gencrat standard eta'yen and CCVs for a mouse study). The matrix to use is dependent on the
9.1.3.1 matriSxtuusdeydcfoonrttrhoelmcuartvreix, curve- if the studycontrolmamxisusedfor the curve,preparefour(4) matrix blanks using the study control matrix(two spiked with surrogateand two not spiked).
99..11..33..23
curve, prepare four (4) zmlzix blanks using the same commercially available matrix (two spiked with surrogate and two not spiked).
CSuormromgaetreciamllaytrioxbtcaui_rvde -(siafmaesusrpreocgiaetse) mmaattrriixxicsuu_see-d fiofrththee ccoumrvme,eprcmiaplalyr_ofbotuairn(e4d) m_mattrriixx ibslaunskeds ufosirntghethe same commercially available matrix and prepare four (4) matrix blanks using a commercially available matrix of
9.1.3,4
If limited matrix is available, the number of method and matrix blanks troy be adjusted and will he noted in tthheessatmudeysppreoctioecsoalsotrhienstthuedryaawnidmaatali.s(_.va spiked with surrogate and two not spiked).
9.2 Sample Replicate
Samples replicates arc preparedaccording to each study protocol or project outline.
ETS-8-231.1 Solid Phase Extraction and Analysis of Fluorochemical
Compounds from Biological Matrices
Page 5 of 19
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3M ENVIRONMENTAL
LABORA TORY
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9.3 Surrogate standard
If surrogatestandardis a componenot f thestudy,all samplesarespiked with surrogatestandardprior to extractionto obtain a concentrationin the mid-rangeof the calibrationcurve,with the cxccptionof blank sampleaas described above.
Typically sumogatstandard_ spikedintotl_ 1.0mL diluted/homogenizesdampleremovedfor extraction.However, surrogate may be spiked din:ctly into the matrix prior to dihdng with water, into the diluted/homogenJznd sample priorto removing the 1.0 mL smnple, or into _ 1.0 mL di[uted&omogeniz=dsample removed for extraction.
9.4 Internal standard
If internal standard is a component of thest-,_y, all samples arespiked with internalsnmdardafter extraction to obtain a concentration in the mid-hingeof thecalibration curve.
Typically internal stand',a'idsspik_ into the 2.0 mL of exact in the 15 rnLcentrifuge tube, before transferringto the autovial.
9.5 Lab Control Sample
Lab control samples arcnot a component of this method.
9.6 Quality Control lOG) Sample
Preparequality control(QC) samplesto monitorextractionefficiencyand to vexi_ the continued accuracyof the initial calibration curve. Typically 1.0 mL, c.rother appropriateamount,ofthe same matrix used to prepare the initial calibrationcurveis usedforeachQC sampM.
Twelve (I 2) quality controlsamples(QC) will be preparedforeachmatrixduringtbe courseof a study. A minimum of 3 QC samples must be prepared (one at e,',,'hlevel) on each day of sample extraction. (e.g. If the study is such that samples will be extracted on throedifferentdays then four QC samplesmust I_ prepared on each day of extraction for a total of twelw.)
QC samples will consist of four samples at each of three levels of analyte` The levels listed below may be used and
mLoawy rleevperle: s3eXnsttoam5XpltehceoLnLcOenQt,rationdsilutedintothe rangeof thecalibrationcurve: Mid-level: equivalentto a point neartic middleof thecalibrationcurve,
High level: 80% of the ULOQ Two QC sample levels am analyzed aR=- every tenth sample injection starting after tim last calibration standard injection, with a minimum of three QC pea"analysis. Solvent blanksare not considered samples but may be included as such for determining wlmn QC samplns will Ix:analyz.cd.
QC samples extra, ted with a particularsample set must be analyzed in the same analytical am. Any QC samplea extracted during thecourse of the study may he includedin subsequent analyses, If samples from multiple extraction dates are analyzed in one analytical ran, then QC samples from the same sample
extraction dates must be included in that analysis. 'EachQC isexpectetdoshowanaccuracoyf75-125%ofexpactcdA. minimumoffalo3fallQC samplesmustmecr this criteria, and a minimum of I,'2of the QC samples at each level must mect this criteria. If not. the set must either
bc re-analyzedor re-extracted.
Any sample with an area greater than that of the highest acceptable standard will need to be diluted into the range of
9.7 StheacmalpiblraetioDn icluurtvieo. nIf samples are diluted into the range of the curve during analyses and enough sample remains, a
post-run dilution validation will be peffonned to verify sample values.
To perfbrm the dilution validation, one sample will be separated into two representative samples (i.e. two I.O mL aliquots for fluid samples or two 1.0 breamamounts for tissoe samples, or other amonnt as detcnnined by the analyst
ETS-8-231. I Solid Phase Extraction and Analysis of Fluoroehemical
Compounds fi'omBiological Matrices
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anddocumentedina notetofilet)hendiluteudsingtwoproceduresT.he firsptrocedurceonsistosfdilutintghe samplewithadditionmaaltrixpriotro extracti(ofnluiadddingfluidw)h,ilethesecondprocedurceonsistosfdiluting thecx_actwithsolvenptost-cxa'ac(tmico_n.2noeixtracatddingadditionmaelthanoslolvcnt.J
Iftherelatipvercendtifferenicsenotwithin15% forthesetwosamplesa;dditiontaelstinwgillbe requiretdo dctcnninewhichva[ucis acorrectrepre.sen_',ioonf thesampleconcentration.
10 Calibration and Standardlzatlon
10.1 InstrumentCalibration
Onecalibrationcm-vcwill be preparedfromextractedmatrixstandardsi,n tim samematrix asthe samplesp, er study.
Itwillcomistofa minimum ofnino(9)l_cls.Additioncaallibratoiuornvcsmay beexaacteodn scpamm sample extraction dates, as determinedby the analystand documented in a note to file. Transfer 1.0 mL, or other appropriateamount, of diluted control fluid or homogenized control tissue to a 15 mL centrifugetube usinga disposableplasticpipette. This will be repeatedwhilepreparingaliquotsfor the standard
creumrovveed. .Be sum to mix or shakethe controlmatrix containerbetweenaliquotsto ensurea homogenoussample is
RecordeachstandarvdolumeontlmwcightA,oluns,h_eeotrextraction wo_
as appropriam.
Four 1.0 mL aliquots, or other appropriateamount, of control matrix serveas matrixblanks.
Tho standarcdoncentratiaondsspikinagmountslisteind Tablel may be used,when appropriateo,spikeone standarcdurve.A totaolf9 standardfso,urmatribxlanksa,ndfourmethodblankas_ prepareidnadditiotnotheQC
samplcaand testsamples.The numberofstandardasndblanksmay be adjusteadsdeterminebdy theanalysatnd documentedina notetofile.
Use A:tachmcnt C, or other appropriatefonn, as an aid in calculating tic concentrations of the working standards. Refer to section 12 to calculate the actual concentration ofanalyto in each calibration standard and QC sample.
Typically the target nnnlytestandardis spi_.'d into the I.OmL d/luted/homogenizedsampleremoved for extraction. However, it may he spikeddirectlyinto the matrixprior to diluting with water,into the diluted/homogenizesdample. prior toremovingthe l.O mL sm'npleo,r intothe 1.0mL diluted/homogenizesdamplerr.n_vcd forextraction.
Analyzethe extractedmatrix standardcurvepriorto eachsctof extracts.The curveequationwill be determinedby regression analysis using the peak areasof the target analyte(s) using MassLyax or other suitable soRwar.
Any level outside 75% - 125%of nominal lr_St be deactivated, and regression rc.-calculatcd, except the LLOO which must b within 3_A ofnominaL All levels must show a response greater than twice that of the blank. A n-aximum of thr_e (3) levels may be deactivated in any one set, or the set wilt be re-analyzed.
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ETS-8-23 L !
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Solid Phaso Extr,zction and Analysis of Fluorochcmica!
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Compounds from Biological Matrices
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Working standard (approximate concentration)
0.500 u_)mL 0.500u_/mL 0.500u[/mL 0.500 u[/mL 0.500 u_/mL . 5.00u[,'mL 5.00u_mL 5.00u_mL 5.00u[/mL 5.00u_/mL
550..000uus_//mmLL 50.0 u_/mL Surrogate Std 100 ug/mL
11 Procedures
Approximate final cionncMenattrriaxtiondiluofteadna1l:y5t
Blank
1.5
5.00 ng/g or ng/mL
3.0
I0.0ng/gorn[/mL
8.0
25.0ng/gorn_/mL
16
50.0 ng/g or ng/mL
32
100 ng/g or ng/mL
5.6
175ng/gorns/mL
8.0
250 ng/gorng/mL
16
500 n_/_orn_mL
24
750 n_/gorn_/mL
32
I000n_/gorn[/mL
54.00
11520500nn[_]/_,oorrnng[//mmLL
6.0
1750 n_ or n[/mL
I0
6500 ng/g or ng/mL
Approximate final
Blank 0.375 ng/mL 0.750ns/mL 2.00n_/mL 4.00 ng/mL 8.00 ng/mL 14.0n_mL 20.0n_mL 40.0n_/mL 60.0n_/mL 80.0n_/mL
112050nn[_/mmLL 150 n_/mL I 500 ng/mL
11.1 TissueSamplePreparation
Obtain fi-ozentissue smnples
Cut approximately 1.0000 g of tissue (+/- 0.1000 g), or other appropriate amount, using a dissecting scalpel. of the procedure is bestperformed quickly, not allowing the tissue to thaw. Weigh the tissue directly into atared plastic sampuin vial.
This part
Record the weight on the weight/volume shccl, extraction werksheet, or other appropriate location.
Return unused tissue to the freezer afierextraction amounts have been removed. Add 2.5 mL of reagent water to sampule vial, or other voJume as determined by the analyst and documented in a note to file. Homogenize the sample. Put the Ultra-Tumm grinder probe in the sample and grind for approximately 2 minutes, or until the sample is homogeneous. Rinse the probe into the tube containing the sample with 2.5 mL of reagentgrade water, or other volun_ as determined by the analyst and documented in a note m file, using a pipette.
Take the grinder apart and clean it with metlumoi alter each sampte. Refer to ET5-9-52 for more information. If an amount other than 1.0000 g (not within +/- 0.1000 g) is removed for an initial weight, adjust the water volume"
ratio as determined by the analyst and documented in a note to file.
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ETS-8-231.1 Solid Phase Extraction and Analysis of Fluoroehemical
Compounds from Biological Matrices
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11.2 Fluid Sample Preparation Obtainfi'ozcnfluidsampleandallowit tothawat roomtemperatureor in lukewarmwater.
Label a 15 mL polypmpylenece.ntrifogctube with the studynumbers, ampleID, extractiondateandanalystinitials. Seeattachedworkshcct(AttachmentA or similarworkshect)for documentingtheremainingsteps. Vortex mix thefluid sampleforapproximately15 secondsth, entransfer1.0mL of fluid,or otherappropriateamount to a plasticsampulcvial,or otherappropriatecontainer. Returnunusedsamplesto fi'ccz=ar .Rcrextractionamountshavebeenremoved.
Add 5.0 mL of reagentwaterto the 1.0mL of tluidfor a 1/6 dilution,or otherdilutionas determinedby the analyst anddocumentedin a notetofile.
If a volume other than l.O mL is removed for an initialvolume, adjustthe water volume accordingly to maintain the same dilution as above.
11.3 Tissue and FluidSample Extraction
ARer tissue or fluid samples have bccn prt:pamd according to sections l 1.1 and 11.2, vortex mix or sMke by hand the diluted/homogenized sample for approximately [5 seconds then transfer 1.0 mL, or other appropriate volume, to a clean ! 5 mL polypmpylcne.cntrifugetube. Rcmmunuseddilumd/homogcnizcdportionsto the freezeraRe.rextractionamountshavebccnremoved. Recordthe volumeremovedonthe extractionworksheet(,AttachmentA orsimilar worksheet). Spikeblankss,amplesa,ndstandardrse,adytbr extractiwointhsurrogastteandaradsdescribeidnthimsethod. Spike each calibration standard marx with the appropriate amount of standard as described in this method for the calibration curve standardsand c'achQC sample. Vortex mix the standard curve samples and QC samplasfor approxilmtcly 5 seconds.
To cachsmnpleandsmndsrda,dd5.0mL ofacctonitrcialpc,,andvortexmixorshakeby handappmximazel1y5 seconds.
Place all samples on the shaker at anappmpr/ate speed for 20 minutes to adequately mix (a setting of approximately 300 rpmon themodelslistcdinsection6.1). Rcmov_ from the shakerand centrifogeat anappropriatespeedfor 10 minutesto adequatelypellet the precipitate(a setting of approximately 2000 rpm onthe models listcd in section 6.1). Add 40.0mL ofreagengtradewatertoa clean50 mL centrifutguebe.Remove samplesfromthecentrifuagned decantthesupernatainnttotimwaterinth,5-0 mL tubet,akincgam nottointxoduacneyofthematrixsolidisntothe solutionC.ap andmix by inwrthlsgcvratliffinIsn.thistopelmonlcrofadditiomnay bcctmngcd(i.et.imsarnpt
AnxttaaycbhethpeutriensteorvthoiercteontthriefuSgPeEtucbaertzainddgethanend tahtetawcahtethriasdredseedr)v. oir/cartridgeunit to a vacuum manifold.
flow of 5-7 mL/min. Flows ,nay vary thmul;h cartridgcsand the kPA =naybe raised for slow tubes and deying aRcr most hav beendrown down. NPr_cTpEar: Wtbeh_SnPEmncnarintrgidthgee _baynwuaushmins_g_tttwh_icveawciuthumacplpmromxbimcraatetlayp5_.0r_mxiLmoaftem_ey_t_haknPoAl, -fot_llogwive_dabnya_apppmrxoixmimaarte_luytti_wo
Aflcr washing is complete, pour the samph: into tim reservoir/cartridgeunit and allow all of the liquid to pass 5th.0romugLhaltiqhueoctosluomf wn ateord, rtyankeinssg. care not to :allow the column to run to dryness after each wash. Run die vacuum on high for approximately 5 minutes to adequatelycityeach SPE cartridge. Place a collection 15 mL polypropylcn-"centfifiagtube under each cartridgeand eiute with 2.0 mL of methanol
Spike cxtractcd blanks,samplcsa, nd standardswith internal standard as dcscribcdin this method.
ETS-8-23 I.I Solid Phase Extraction and Analysis of Fluorochcmical
Compoundsfrom Biological Matrices
Page 9 of 19
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3M ENVIRONMENTAL LABORATORY
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Labol each glass autovial, as appropriate, with the study number, vial rite archive number, animal numbcr/gendcdtiroepoint or LIMS number, matrix, final solvent, analyt components (if needed), extraction type, extraction date, and analyst(s)pcrfmming the extraction. Transfer each oluant to a glassautovial and cap.
11.4 Extract Analysis
11.4.1 Software set-up
On the MassLynx main page, set up a sample list name. Save the list as instrumentdesignatorletter, last 2 digits of test year-month-day, and a letterthat will increase throughthe alphabet with each additionallist for thatday.
F..xamplcSample List:FfYMMDDa or A020204a 1= Initial of the insmuncntname (A: "Amelia")
YY = Testyear(02) MM ,, Testmonth(02)
DD-,o da,O,) a ",F'irstsample list (run)ofthe day (thenext sample list will end with _', the next 'c',
and so on.)
Assign a filenanm using the instrumentdesignator letter, the last 2 digits of the tc_ year-month-day, and a 3-digit sequential file numberthatstartswith I and iacma_s by one foreach filenamc.
Example filcname: IYYMMDD/fl#?or A020204001 I = Initial ofinstmmcm name
YY = Test year MM - Test month
DD: Test day ### : 3-digit sequential file numberstartingwith I through999 (001) Also, as part of the samplclist,assign a method (MS) for acquiring, an inlet file, a bottle number,an injection volume, and sample dcscfiptiot_. To create a mothod, click on Method Editor button in the MS Status Pane and select SIR (Single Ion Recording) or MRM (Multiple Reaction Monitoring). Set Ionization Mode as appropriateand mass to 499 or other appropriate mass(s). Also set the acquisition start mad stop times. Save acquisition method. If MS/MS insm.zmentaax_
employed, additional product ion fragmentationinormadon may bc collected. See Microm,x_MassLynx "Guide to
Typically the analytical batchrun
I:cgins with system suitability,so|vent blanks, and a set of extractedmatrix
standards. Data Acquisition," for additional iafotmatiOnoseuqMueRmMcc.
Sample extracts are analyzed wifl_two QC samples injectedafter every tenth sample injection. Solvent blanks should. be analyzed periodically to monitor possibl," analyte carryover and am not considered sample extracts but may be
included as such.
--_ ._'l [ '_ "_ :L_'X
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ETS-8-23 [. I Solid PhascExtraction and Analysis of FluorochcmicaJ
Compotmds from Biological Matrices
Page 10 of [9
Page 46 of 225
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E02-1039
11.4.2 HPLC set-up Set up sampletray accordingto the samplelistprepar_l above.
Sct up theHPLC othe followingconditionsor at conditionstheanalystconsiderasppropriateforoptim._lresponse. Recordactualconditionsin d' immanentlogbook,orotherappropriatelocation:
Samplesize= !0 HL injection Inject/sample= I
Cycle ti,ne = 10.0 minutes
Flow rate = 300 g/./min
Mobilephase:SolvenAt ==2 mM Ammonium AcetateS,olvenBt=,Methanol
Solventgradientprogram:
Time
% Solvent B
5.5O
95%
7.50"
8.00'
10%"
11.4.3Instrumenset t-up
Rogerto ETS-9-24, "Operation and Mainteaance of the Micromass QuattroII Triple Quadrupole Mass Spectrometer Fitted with anAtmospheric PressurIoenization Source.fo,r"details.
Checkthesolvent level in HPLC resewoirsand refill if necessary. Check the stainless steel capillaryat the end ofthe probe. Use aneyepiece to check d_etip. The tip should be fiat with no jagged edges. If the tip is found to be unsatisfactory,disassemblethe probe and replacethe stainlass steel capillary.
Turnon tlcnitrogen. Open the mr,page. Click on operate to initiate source blockand d_olvation heaters.
Open th_ Inlet l_dJtor.
SDeotwthneloflaodwthteo/-I1r0p-L-5c0m0ueUthmodinaonrdaisnaidpaptreosporlivaetent flow to begin s3,stemequilibrium. SetI-[PLpCump to "On" Observderopleotrsmis_comingoutofthetipoftheprobe.A finmeistshouldbe
expelled with no nitrog_ leaking around thedp of theprobe. Readjust
g/
_ -4 ._ _ "x_ ,,.a ._ t
Allow to equilitbhreattiepfoofrthaeppproroxibne_itfenlyo mI0ismt iisnuotbess,erved Typical instrument panuncters include:
Drying gas 250-400 liters/hour
ES nebulizing gas IO-15 litcrs/hour
u_._ _;_
ETS-8-231I. Solid Phase Extraction and Analysis of Flnorochemical
Compounds from Biological Matrices
Page II of 19
Page 47 of 225
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HPLC constanftlow mode,flow rate10-500I.Z[Jmin Pressure<400 bar(thisparameteris notset,it isa guidetoensurethe
HPLC is operatingcon_ctly.) Sourceblocktcmpcratureapproxin_tcly150"C Desolvation temperatureapproximately250C Thes,o set, rigsmay change in orderto optimize theresponse Print the tune page, sample list, and acquisition method from MassLynx and store it in the study binder with a copy taped into the instrument log. Click on start button in the Acquisition Control Panel (the location of the start button may vary among MassLynx versions, rcfcr to appropriateMossI.,ynxUser's Guide).
t2 Data Analysis and Calculations
12.1 Calculations
If othercalculationsareusedthanthoselisted,theywill be documentedinthe rawdata.
Calculate the matrix amount containedin thc initial dilution using the following equation:
Matrix Amount (g/mL or mL/mL) =
IW (g) (or IV (mL))
(IW(g)(orIV(mL))+DV (mL)
Calculataectuaclonccnu'atioofnasnalytiennalibmfisotnandarudssingth_followienqguation:
Conccnrcation (ng/g or ng/mL) = Spike Concentration (ug/mL)x Spikcd.Amount(mL)xlO00 ng
SV (mL)x Matrix Amount (g/mL or mL/mL)
Iug
IW = Initial weight (whom 1.0 g = 1.0 mL ) IV = Initial volurns
DV _ Diluent volume (rw..agcnt grade wamr)
AR = Analytical resultfrom MassLynx maunmry SDVF =,- DSialumtipolnevfoalcutomreremovedforcxtracdon(typlcally1.0mL) FV = Final volume
MA ='Matrixamount 3 curve= MA oftissuc/fsltuainddarcdurvea,ssumedtobe lg orImL/5mL water
3 sample = MA of tissuc/fluid sampleC....,).r.m.Lg of sampld5 mL water)
Calculate spike percent recoveries using the tbllowing equation:
'Y,,Recovery
ObservedResult - Matrix Blank Result
=
Spiking Level
x tO0
ETS-8-231.1 Solid Phase Extraction and Analysis of Fluorochcmical
Compmmds from Biological Matrices
Page 12 of 19
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3M ENVIRONMENTAL LABORATORY
E02-1039
Calculate relative standard deviation using the following equation:
Standard Deviation
RcladveStandard Deviation =
x 100
Mean
Calculate portent deviation using the foUowiag equation:
%Deviation
= Expected Cone.- Calculated Cone. x 100 ExpectedCone.
Calculate actual concenmafionofanaJytein _uid (gg/mL):
AR.(ng/mL) x DF x _ curve (mUm[.) x FV fmL) in Curve x 1.0 leg o3sample (mUm/..) FV (mL) in Maaix 1000 ng
= (lag/g)
Calculam actual conccotration ofanalytin tis,_ _g/g): AR (ng/g)x DF x 3 curve(E/mL_x FV (mL'_in Cuw x _
asample(g/mL) FV(mL)inMatrix 1000rig
= _g/g)
13 MethodPerformance
13.1 SystemSuitability
System suitability will be determined prior to the start and at the completion of each analytical run. Prior to the calibration curve and aRer the last sample of the run throe (.3) mid-lcv=l unextractcd calibration standards will be" a,mlyzcd. As applicable, the peak area precision, mtendon time pt_-cision,resolution, and peak asymmetry will be monitored at thc beginning and the end of the mn separately. The peak area precision must b equal to or less than 5.0% RSD, the precision of the retention tin_ must be equal to or l_s than 2.5% RSD, the resolution must be > 2.0, and the peak asTmmctry (fconting or tailing) must be 0.5<AF<2.0, where AF is the a_. nmetry factor.
sIyfsatenmy istuemitaboiflittyhesasmysptleems asnuditatbheilistyystfeamilss,usiytastbeimlitymmauinsttepnaasnscbeefmoureststbaertcionmg tpbleetceadlibprraiotironto. mIf'nsynsitnegmasuseitcaobnidlityseftilolsf at the completion of a run,the sample set must be manalyzcd.
The coefficient of determination value for the calibration curve, plotted by regressionusing the peak areas of the analyt_s), must be 0.990 or better.
All active calibration curve points must bwithin 25% of the theoretical value with the exception of the LOQ point, which may deviate up to 30%. Calibration standards with peak areas less than two times the curve lm_x bhnk will be deactivated to disqualify' a data range that may be affected by backgroundlevels of tl_ analyt, A valid calibration curve must contain at least 6 active points above and includingthe LOQ. If the curvecannotmeetthesecrkcr/a,thesamplesetmustbc reanalyzcdor rccxtractcd.
13.3 Accuracy
TWOthirds ofall quality control samples and }/2 ofcach quality eonWol sample at each level amexpcctcd m show an accuracy of 75-125%.
ETS-8-231.I Solid Phase Extraction and Analysis of Fluorochcmical
Compounds from Biological Matriccs
Page 13 of 19
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;i
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Surrogates and internal standards must have a percent deviation < 50%. Deviations outside this range will be
_i!J
reanalyzed re confirm. If the second analysi;_conarms the original, the dcvistion wifl be documented in the raw data.
Ifthc second analysis is within 50%,then the second value will replace the original value.
!
14 Pollution Prevention and Waste Management
Samplewasteisdisposedof in noninFcc_oubsiohazardwastecontainers. Flammablesolventwasteisdisposedof in highBTU' containers. Glass pipette waste is disposed of in broken glass containers located in tl_ laborato_.
;,,:_
15 Records
,.) j
Completethe extractionwork_hectattachedtothismethod,or otherapplicableworkslcct andstorewith thestudyraw
-_
data.
;
"
J
Each page generated for a study mu.contain the following information (if applieabl,.): study/project or instrmnent
number, acquisition method, integration method, sample ntur, extraction date, dilution factor (if applicable), and analyst. Other information may be added if applicable to the study.
'
Print the tune page, sample list, and acquisition method from MassLynx to include with the study raw data. Copy
__j
these pages and tape into the instrument rtmlog.
Plot the calibration curve by the appropriateregression. Print these graphs and store with the study raw data.
Print data integration stmamary,integration method, and chromatograms from MassLynx, and store with the study raw data.
Summarize data using suitable so.cam (Excel 7.0 or LIMS) and store in the study folder. Back up electronic data to appropriate medium. Record in study notebook the tile nanm and location of backup
_!!
electronic data.
16 Attachments
_z_,
Attachment A: -ExtractionWorkshcet
Attatchrlncnt B; Sample We[_tFv'o|urlrze WOlkSheet
Attachment C, Calibration Standard Concentration Worksheet
--
_-i
17 References
....
ETS-9-24, "Operation and Maintenance of the Micromass Quattro lI Triple Quadrupole Mass Spectrometer Fitted
'_
with an Atmosphere Pressure Ionization Source"
u._
ETS-9-52, "Operation and Maintenance of a Tissue Grinder"
18 Affected Documents
'_
ETS-8-231.1
Page 14of19
i
Solid Phase Extraction and Analysis of Fluorochemical
Compounds from Biological Matrices
Page 50 of 225
r!,,,_" 4_:i
'11:13
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....
19 Revisions
R_visJon Numbcr
I
RevisionDescHnfion
MinorformattingchangesA.ddeddetailedinformatiotno all secdoncsoncernintghe
extractionprocedurea,nalyticaplrocedurea,ndcalculatioN.Addedattachmenatsnd references.
Revision .D.ate
02/18/02
r
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ETS-8-23I.I
Page [5 of 19
Solid PhaseExtractionand Analysis of Fluoroche,nical
Compoundsfrom BiologicalMatrices
Page 5I of 225
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3M ENVIRONMENTAL
LABORATORY
E02-1039
Study Number: Prep Date: Analysts initials: Box#:
Attachment A - Extraction Worksheet
Method Revision:ETS-8-231.1 Matrix:
Sample Timepoint:
SampleNumber
Sample
Number Volumeof
Amounat nd
or dilutedsample Amounatnd surrogatsepike Typeofcolumn Elutlonsolvent
description removed spikemixused mixused usedandlot andvolume
Comments
....
.o,
....i
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Blankmatrix
TN-A-
;Amounwt eighedlaliquoted:
g/mL
21.. HAoliqmuoog1temnLizsoeafdmilpulteedmatrixinto15mL polypropylenttd,be
3. Spike samples accordingly
4. Add N-- mL of ACN (TN-A-
) to each diluted sample and shake or vortex mix
5. Shakesamplefor20 min@
rpm(Shaker
)
6. Centrifugseamplefor10rain ___
rpm(Centrifuge1.
)
7. Add40 mLof --
waterto50 mLpolypmpdencaentrifugteube.
8. Decantextractinlocentrifugteubeswithwater 9. Shakesampleslicjhttytoensurepropemr ixing
1I. Conditioncolumnwithtwowashesof-5 mL MeOH(TN..A-
) - donotallowcolumntogotodP/ness
12. Washcolumnwithb.,vwoashesof-5 mL__
water- donotallowcolumnto goto dryness
1130.. AFitlttaecrsha6mmpLleCt1h8roSuPgEhccoanrdtriitdiogneesacdnodl7u5mmndL, irsecsaerdrvinofgiirltstoravtaecuummanifold
14. Allowcolumntogotodryness.Afterdrippingstopsd, rawa highvacuumthroughcolumnforat least5 minutes.
15. Elutecolumnwithsolvent(
TN-A-___)
intoappropriat1e5mLcentrifugteube
16. Spikesampleswith--
uLofinternasl tandard#
17. Transfersampleintoappropriatelyabeledautoviaal ndcap
__
conc.
Note: Invacuumstepsabovesetthevacuumchamberat ar_proximate1l5ykPA-thisshouldgiveapproximate5ly-7mL/mlnelutlonflow
Flowsmayvarythroughcart,ridge-skPAmaybe raisedfor,';lowtubesanddPjingaftermosthavebeendrawndownandshutoff.
ETS-8-231.1 Solid Phase Extraction and Analysis of Fh.torochemical
Compounds from Biological Matrices
Page 16of19
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3M ENVIRONMENTAL LABORA TORY
E02-?039
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i i Attachment B - Sample Weight/Volume Worksheet
Prep Date(s):
_!
Analyst(s):
Sample Matrix: Method/Revision:
Study Number: Equipment Number: Final Solvent & TN Number:
i
Sample ID
Initial WtdVnL
Water Vnlume added
Vnlume Removed
_nmments
_mlLA'f..,
(mL)
(mL)
,{
.... i
.;
Form Completion Verified By:.
ETS-8-231.1 Solid Phase Extraction and Analysis of Fluorochemieal
Compoands from Biological Matrices
Pag* 17 of 19
Page 53 of 225
3M ENVIRONMENTAL
LABORA TORY
E02-1039
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Prep date(s): Analyte(s): Sample matrix: Method/revision:
AttachmentC: CalibrationStandardConcentrationWork,sheet
Standard number: Equipment number: Final solvent and TN: Blank Tissue or Fluid/identifier:
AnalySe mix std approx. 0.500 ng/mL: AnalySe mix std approx. 5.00 ug/mL:
AnalySe mix std approx. 50.0 ug/mL: Surrogate std approx. 100 ug/mL:
Actu tl concentrations of standards in the analyremix
AnalySe Std cone ug/mL
0.500 0.500 0.500 0.500 0.500 5.00
5.00 5.00 5.00 5.00 5.01} 50.0
All Am't spiked
mL
0.0015 0.0030 0.0080 0.0160 0.0320 0.0056
0.0080 0.0160 0.0240 0.0320 0.0400 0.0(15
All Final Volume: lr_
2.00 2.00 2.00 2.00 2.00 2.00
2.00 2.00 ZOO 2.00 2.00 2.00
All Initial Fluid Dilution mL/mL 0.1667 0.1667 0.1667 0.1667 0.1667 0.1667
0.1667 0.1667 0.1667 0.1667 O.1667 O.1667
All Initial Tissue Density g/mL 0.1600 0.1600 0.1600 0.1600 0.1600 0.1600
0.1600 0.1600 0.1600 0.1600 O.1600 0.1600
50.0
0.006
2.00 O.1667
O.1600
Calculated concentrations of standards in relation to the final 2.0 mL solvent and initial matrix
2.0 mL Final Volume
Fluid Matrix
Tissue Matrix
Analyse Final cone.
ng/mL
0.375
Surrogate Std cone ng/mL
1O0
AnalySe Final cone.
ng/,nL
5.00
Surrogate Std cone ng/mL
100
AnalySe Final cone.
ng&
5.00
Surrogate Std cone ng/mL
100
O7. 50 2.00 4.00
Surrogate Final cone
IO.O 25.0 50.0
Surrogate Final oanc
I O.O 25.0 50.0
Surrogate Final cane
8.00
n_'mL
14.0
0.500
100
ng/mL
I00
175
6500
175
n_l _ 6500
20.0
250
250
_
4o.0
500
500
60.0. 80.0 , I O0
125
150
750 I000 1250
1500
1750
750 I000 1250
1500
1750
ETS-8-231.1 Solid Phase Extraction and Analysis of Fluorochcmical
Compot,nds from Biological Matrices
Page 18 of 19
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3M ENVIRONMENTALLABORATORY E02-1039
Study: DBioluxtNiounmDbaetre:/Analyst:
Sample Number
or Description
1/
Attachment D: Dilutions Summary Works, heet SolventfrN Number: MExattrraixct/TioinmDeaptoei/nAt:nalyst:
1/ I/
11 1/
Dilutions 1/ 1/
Comments
Verified By:
I__,,
N1/o1t0esd: ilution =
of sample +
of solvent
_ __ ___
ri
, :,
Form Completion Verified By:
ETS-8-231.1
Page 19 of 19
SoLidPhaseExtr,xctionand Analysisof Fluorochemical
i
CompoundsfromBiological Matrices
Page 55 of 225
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ATTACHMENT B: DATATABLES
_7
3M ENVIRONMENTAL
LABORATORY
E02-1039
t
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Page 56 of 225
Human Serum Data
Quantitated with Chinese Plasma Calibration Curve
Alldataisin unitsn_/mL
Lampire Serum
PFOS
sample 1 < LOQ
sample 2 < LOQ
low spike < LOQ
IISigma Serum
High spike] sample 1 sample 2 . low spike
5.47
4.74
4.38
4.75
Ct=
< LOQ
< LOQ
0.65
5.70
< LOQ
< LOQ
0.45
CIt
< LOQ
< LOQ
0.82
7.02
< LOQ
< LOQ
0.69
Ct0
< LOQ
< LOQ
0.68
6.34
< LOQ
< LOQ
0.60
C9
< LOQ
< LOQ
0.79
5.91
0.19
0.34
0.84
C=
0.73
0.57
1.39
6.81
1.60
1.59
1.86
_z
< LOQ
< LOQ
0.75
6.51
< LOQ
0.15
0.65
High spike 9.06
3.74
5.45 5.17 5.91 6.64 5.78
lGolden West Serum
I
] sample I sample 2
25.64
28.41
< LOQ < LOQ
0.31
0.33
< LOQ
< LOQ
0.96
0.84
5.54
5.65
0.23
0.15
low spike 24.16
0.46
0.85 0.60 1.30 4.64 0.41
High spike 26.10
3.65
6.42 5.20 6.62 9.12 4.91
Biorasource Serum
sample 1 16.79
< LOQ
0.28 < LOQ 0.63 2.83 < LOQ
sample 2 17.26
< LOQ
0.31 < LOQ 0.58 3.06 < LOQ
High spike 18.78
2.65
4.94 4.32 4.95 7.39 1.47
Analyte ... PFos
Clz C, C1= C9 Cs C7
Calibration Range, nglmL 1.01 - 30.2
0.104 - 31.1 0.103 - 30.9 0.252 - 30.3 0.101 - 30.4 0.258 - 31.0 0.102 - 30.7
Ch!neese Plasma_ Serum Data Cal Curves
_ystem
Suitability
Samples,
CCV #_
CCV #2
CCV #3
R= 0.999596
%RSD 2.48
recovery, % recovery, % recovery, %=
52%
3%
""
0.999621 0.999767 0.999471 0.9997 0.998816 0.999569
0.99 2.46 1.45 2.94 6.73 2.37
77% 105% 86% 91% 94% 87%
52% 105% 90% 105% 87% 95%
*" 99% "* 102% ** 93%
Matrix Blanks < LOQ
< LOQ < LOQ < LOQ < LOQ < LOCI < LOQ
"None performed
Low spike 16.44
< LOQ
0.96 0.73 1.11 4.03 0.18
0 t_
Human Plasma Data
Quantitated with Chinese Plasma Calibration Curve
All datais in unitsng/rnL
Chinese Plasma
PFO5
sample I < LOQ
sample 2 < LOQ
low spike 1.30
High spik 4.78
IILampire Plasma
_ sample I sample 2
9.89
12.34
Clz
< LOQ
< LOQ
0.52
5.02
< LOQ
< LOQ
Ctl
< LOQ
< LOQ
0.65
5.18
< LOQ
< LOQ
C10
< LOQ
< LOQ
0,40
4.88
< LOQ
< LOQ
C9
< LOQ
< LOQ
0.59
4.91
0.37
0.50
low spike 13.15 0.48 0.46 0.49 0.78
Ca7
<< LLOOQQ
<< LLOOQQ
<0.L2O8 Q
45..7218
20..3200
<2.L9O1 Q
30..3542
High spike 16.19 4.53 4.42 4.01 4.88
75.,3413
Golden West Plasma
sample I 16.20 < LOQ < LOQ 0.15 0.42
sample 2 20.32 < LOQ 0.10 0.17 0.65
low spike 13.56 0.44 0.52 0.57 0.72
03..4456
40..2183
30..3342
High spike 20.34 4.80 4.95 5.29 5.11
Ilnnovative I _ sample I
15.61 < LOQ 0.13 0.19 0.68
Research Ptasma
sample 2 15.55 < LOQ 0.14 0.15 0.49
low spike 17.32 0.58 0.84 0.78 0.84
75..9344
<3.L0O4 Q
<3.L0O9 Q
30..8468
High spike 21.63 5.66 6.16 6.08 6.00
96..1164
Analyte PFOS
C_z Cll
Cl0 C9
.Cs ICT
Calibration Range,
nglmL 1.0 - 30.0 0.10 - 31.0 0.10 - 30.9 0.10 - 30.3 0.25 - 30.4 0.52 - 31.0 0.10 - 30.7
Chineese Plasma i Plasma Data Cal Curves
_ystem
Suitability
Samples,
CCV #1
CCV #2
Matrix
R2 0.999721
%RSD 2.20
recovery, % recovery, %
102%
84%
Blanks < LOQ
0.999759 0.999585
5,87 1.21
101% 90%
84% 78%
< LOQ < LOQ
0.999695
2.76
0.999847
5.07
91% 97%
83% 80%
< LOQ < LOQ
0.999736 0.999695
2.85 5.85
81% 102%
89% 75%
< LOQ < LOQ
'-o
O0 0
Human Serum Data, 5x Sample Scale-Upwith 20uL Injection Volume
Quantitated with Chinese Plasma CalibrationCurve
All data is in units ng/rnL
Lampire Serum
Sigma Serum
PFOS C_= C. Ct0 C= C= C7
Sample 1, Corrected
Sample 1, on-Column for Concentration
Concentration
Factor
24.859 < LOQ < LOQ 0.313 0.675 11.734 0.250
2.486 < LOQ < LOQ 0.031 0.068 1.173 0.025
Sample 1, onColumn
Concentration
ULOQ (30.2) 0,177
" 0.760 0.575 1,234 13,396 0.126
Sample 1, Corrected for Concentration
Factor
Golden West Serum
Sample 1, onColumn
Concentration
ULOQ (30.2) 0,018 0,076 0.058 0.123 1.340 0.013
> ULOQ (30.2) 0.402 2,473 2.025 3.533 26.245 < LOQ
Sample 1, Corrected for Concentration
Factor
ULOQ (30.2) 0.040 0.247 0,203 0.353 2.625 < LOQ
Bioresource Serum
Sample 1, on-Column Concentration
ULOQ (30.2) 1.444 2.856 3.272 2.657 26.245 < LOQ
Sample 1, Corrected for Concentration Factor
ULOQ (30.2) 0.144 0.286 0.327 0,266 2.625 < LOCi
Human Plasma Data, 5x Scale-Up with 20uL InjectionVolume
Quantitated with Chinese Plasma CalibrationCurve
All data
PFOS _'_z C11 C_0 CD C= Cl
is in units of n_/rnL Lampira Plasma
Sample 1, on-Column Concentration ULOQ (30.2) 0.364 0.486 1.270 3.799 36,207 < LOQ
Sample 1, Corrected for Concentration Factor
> ULOQ (30.2) 0.036 0.049 0.127 0,380 3.621 < LOQ
Golden West Plasma Sample 1,
Scruple 1, on- Corrected for
Column Concentration
Concentration Facto=r
ULOQ (30.2) ULOQ (30.2)
0.236
0.024
0.711
0.071
2.112
0,211
3.436
0.344
ULOQ (31,0)
ULOQ (31.0)
< LOQ
< LOQ
Innovative Research Plasma Sample 1,
Sample 1, on-
Corrected for
Column
Concentration
Concentration
Factor
ULOQ (30.2) 0.219
ULOQ (30.2) 0.022
1.400 2.169
0.140 0.217
4.016
0.402
37.170 0.160
3.717 0.016
Chineese Plasma Calibration Curve for Scale-Updata, 10uL InjectionVolume
Analyte PFOS
Calibration Range, ng/mL
1.01- 30.2
R= 0,999539
System Suitability Samples, %RSD
4.21
CCV #1 recovery, %
155%
Matrix Blanks < LOQ
t'_
Ct=
0.104- 3t,1
0.999696
3.94
114%
< LOQ
tJI
CH
0.103- 30.9
0.999526
6.34
95%
< LOQ
CI0 C0
C=
iC_
0.101- 30.3 0.254 - 30.4 0.103 - 31.0
0.102- 30.7
0.999907 0.999812 0.999441
0.999903
4.02 4,16 5.99
6.21
94% 92% 92%
106%
< LOQ < LOQ < LOQ
< LOQ
,i
:_:i!i
_ ! ,
_'!_i_ili '_"
i:::i
' -_i
_:iiii !!i_
Matrix Spike Recovery for Human Serum Data Quantitated with Chinese Plasma Calibration Curve
Analyte PFOS
C12 C11 Clo
CC9s 07
Lampire Serum
Average Endogenous Concentration,
ng/mL < LOQ
Low Spike Recovery, %
< LOQ
High Spike Recovery, %
< LOQ
ISigma Serum
I
Average
[ Endogenous
I Concentration,
I
ng/mL
4.56
< LOQ < LOQ < LOQ
129% 164% 136%
114% 140% 127%
< LOQ < LOQ < LOQ
<0.L6O5Q
115488%%
111283%%
01..2670
< LOQ
150%
130%
0.15
Low Spike Recovery, %
39%
90% 138% 120%
High Spike Recovery, %
90%
75% 109% 103%
15135%% 100%
111031%% 113%
_,nalyte PFOS
i Clz
IC11
IC10
IIC9
C8 C7
GoldenWest Serum
Average Endogenous Concentration,
ng/mL 27.02
< LOQ 0.32
Low Spike Recovery, %
-573%
92% 106%
< LOQ
120%
0.90 5.60 O.19
80% -191% 44%
High Spike Recovery, %
-19% 73% 1221o
104%
114% 71% 94%
BioresourceSerum
Average Endogenous Concentration,
nglmL 17.02
< LOQ 0.30
Low Spike Recovery, %
0%
530% 93%
< LOQ
864%
0.61 2.95 < LOQ
86% 91% 294%
High Spike Recovery, %
3288% < LOQ
6%
146%
49% 624% 36%
_i I
i
Page 60 of 225
'_'__
'"_!: _-_t
i
i :i
,( :,;J :_i
;i,_!!:l
Matrix Spike Recovery for Human Serum Data Quantitated with Chinese Plasma Calibration Curve
Analyte PFOS
Ct2 Cll
Clo C9 Cs C7
Chinese Plasma
Average Endogenous Concentration,
nglmL < LOQ
Low Spike
Recovery, % 260%
< LOQ < LOQ
104% 130%
< LOQ < LOQ
< LOQ < LOQ
80% < LOQ
< LOQ 56%
High Spike Recovery, %
96%
100% 104%
98% 98% 94% 106%
ILampirePlasma
Average Endogenous Concentration,
ng/mL 11.12
< LOQ < LOQ
< LOQ 0.44 2.61 0.20
Low Spike Recovery, %
407%
96% 92%
98% 69% 147% 64%
High Spike Recovery, %
102%
91% 88%
80% 89% 94% 105%
Analyte PFOS
C12 Cll C1o Cg C8 C8
Golden West Plasma
Average Endogenous Concentration,
nglmL 18.26
< LOQ 0.10 0.16 0.54 3.87 < LOQ
Low Spike Recovery, %
-940%
88% 84% 82% 37% -106% < LOQ
High Spike Recovery, %
42%
96% 97% 103% 92% 81% 125%
Innovative Research Plasma
Average Endogenous Concentration,
ng/mL 15,58
< LOQ 0.14 0.17 0.59 3.07 < LOQ
Low Spike Recovery, %
348%
116% 141% 122% 51% 159% " 1438%
High Spike Recovery, %
121%
113% 121% 118% 108% 122% 183%
Page 61 of 225
.. : :I '_,:!
_;,i_,:i :!=.J
i
I "
ii i :
_...:.,_ ::,_
i
,' !
,..!
3M ENVIRONMENTALLABORATORY
E02-1039
PFOS Telomer Analysis Summary 3M Pharmaceuticals Analytical Research and Development
LC/MS analysis of a pooled human sera sample obtained from Golden West Biologicals (#E02-1039) was performed using an Agilent 1I00 quaternary I-IPLC system coupled to a Micromass Q-Tof2 quadrupole time-of-flight mass spectrometer. The sample was run as submitted using the following parameters listed in Table 1:
Table 1
Inject: Analog wavelength
output: PDA Wavelength Range:
Recorded Mass Range: Flow Rate:
Column Temp: Column:
20 gL
NA 190-600 nm 100-800 Da. 0.3 ml/min ambient Betasil C 18,
Run Time (rain.)
1:I20w/2raM N_CI-I3CO2
MeOH
0
90
10
7
0
100
12.5
0
100
13.0
90
10
17.0
90
10
IonizatioMnode: Resolution:
50x2mm ESI(-) 7,000
Accurate mass measurements and elemental compositions obtained in this analysis are summarized in Table 2:
TabRleete2ntion
Time
5.8 min 6.3 min 6.5 rain 6.69 min 6.71 min 6.72 min 6.8 min 7.1 min
Accurate Mass
Theoretical
Mass
362.9739 412.9637
526.9693 462.9613 498.9280 512.9615 426.9734 562.9542
362.9691 412.9659
526.9610 463.9627 498.9297 512.9595 426.9674 562.9563
Mass
Deviation
(ppm) 13.3
-5.4
15.8 -3.0 -3.3 3.9 14.1 -3.8
Probable
FormuIa
C702F13
CsO2FIs
CI0H403FITS
C902FI7 C803F178
C i002Fl 9 CsH403FI3S C1102F21
Page 62 of 225
!.i _,_.,_
ATTACHMENT C: CHROMATOGRAMS
3M ENVIRONMENTALLABORATORY E02-1039
]:!:ii_i !
,iiJi:
=i"
Page 63 of 225
(
plasma
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InilJaJ Date
goldenwestplasma5x scaleup 10/23/02ok
3M Environmental
Lab
d021030005 273 (7.408) Sm (Mn, 2x1.00); Cm (272:274)
100-
74.459
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d021030005
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363 219 2.80e3
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032 ltno_ 192 \ _ 349403 ":'v 552 "';" 898 _._o -7.77_9
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7.36
363 169
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d021030001
100-
8.37
Davey070799
30-Oct-2002 11:28:58 2: MRM of 4 Channels ES-
TIC 5.78e6
|%. d021030001
8.08 8.40
1: Daughters of 413ESTIC
5.51 6.09
L
I,
_,t 8.98
10.43
12.21
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4.00
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10.00
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14.00
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golden west plasma 5x scale up 10/23102 ok 3M Environmental Lab
d021030001 288 (8.395) Sm (Mn,2xl.00); Cm (284:297)
100
168.768
.o
davey 070799 30-0ct.2002 11:28:58 1: Daughtersof 413ES-
8.08e5
%
218.992
369.289
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118.651
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golden west plasma 5x scale up 10/23/02 ok 3M
d021030001
100
-
8.3
Davey070799 30-Oct-2002 11:28:58 2: MRM of 4 Channels ES-
413 > 369
= %-I
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413 > 219 9.47e5
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/
5x scale up 10123/02 ok
1001
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3M Envb'_msBtal Lab
dD2IO3000t 288 (8 _a5| Sm(Mn. ;b;t.00_;Cnt (214_=1)
100
I_.?U
golden,,,,t p",,= =*,,l, upI=Z=SoOk=
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Davey070799
30-0ct-2002
11:28:58
2: MRM of 4 Channels ES-
413 > 369
5.21e5
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8.37
413 > 219
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2: MRM of 4 Channels ES413 > 169
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1
2: MRM of 4 Channels ES-
_
8.37
413 > 119
0
" 2.26e5
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8.17
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8.3;
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020--_-2-1-7- solvent standard 10ppb 3M Environmental Lab
d021030011 286 (8.339) Sm (Mn, 2xl.00); Cm (281:288)
100-
168.768
davey 070799 30-Oct-201)2 14:21:04 1: Daughtersof 413ES-
1.90e5
218.255
368.797
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119.082
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d021030011 8.32
Davey07079 30-Oct-2002 14:21:04
2: MRMof 4 ChannelsES413 > 369
I%
10001"_-,"_-;'"'l_- J;-";' I_ _ d021030011
:': 100
6.13 a" -' "-'_ ...._, , , ^,
8.67 9,28 _''_'_-i_'_'__
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; _-_'..-:5'.9,6e4 2: MRM of4 ChannelsES-
413 > 219
9.42e4
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1 1 ' ' ' I , ,'I , i,,
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4134>.631e659
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6.32
413 > 119
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02048.21.7 solvent standard 10ppb 3M
d021030011
100
o2048-21s-7olvensttandar1d0ppb
3M Envkonmental Lab
002103001 "_ 286 15.33g) Sm |Mn, _:x1.00); Cm [281:2t_)
100
160.768
%
davey0707SS
30-Oct-2002 14:21:04 '$;Daughte_ _| &I3_ES-
1._3e5
8.32
d02103001 _
_,.. 1001
218.255
:3M,TP7
8.67 9.2S 8.32
Davey070799 30-Oct-2002 14:21:04
2: MRM of 4 Channels ES41 3 > 369
5.96e4
2: MRM of 4 Channels ES413 > 219 9.42e4
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5.s.7=l4
f sO..._.'I_
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413 > 169
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ae
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10.06 9.21
2: 3M0R-OMcto-2f 04D0C2ahvane1ny2e:0l5s75:0F0TS27IC-99
8.32e5
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10.02
1: Daughters of 463ESTIC
11.04
A _ lO.89 . 12.o9
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14.35 14:87
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0
golden west 3M d021030006
100
plasma
5x scale
up 10123/02 ok
10.06
Davey070799 30-Oct-2002 12:55:02 2: MRM of 4 ChannelsES-
463 > 419
d021030006 100
9.21
"
A
92.1
8.28e5
2: MRM of4 ChannelsES463 219
2.83e5
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golden west plasma 5x scale up 10123102 ok 3M Environmental Lab
d021030006 10C
316 (9.206) Sm (Mn, 2xl.00); Cm (314:321) 168.522
218.992
_ _*_ _' _
davey 070799 30-Oct-2D02 12:55:02 1: Daughters of 463ES-
8.07e4
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418.552
462.836
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119.105
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m:_
279.220 329:050
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1 00"
golden west plasme 6x scale up 10/23/02 ok
3M Environmental Lab _021030006 316 (9.208) Sm (u_. 211 .O0);Cm (314:321)
100-
1M 522 2111.(i02
clayey0707.
_ct.2002
t2:55:02
I: Diugl_em of 43ES-
8"02ro4
I1%
10.06
DaveyOlO799 30-Oct-2002 12:55:02
2: MRM of 4 Channels ES-
463 > 419
8.28e5
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Davey070799 30-Oct-2002 15:46:28
2: MRM of 4 Channels ESTIC
4.98e5
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02048-21-7 solvent standard lOppb 3M Environmental Lab
d021030016 1 ]0-
312 (9,095) Sm (Mn, 2x1.00); Cm (308:318) 218.869
218.25.=. %
davey 070799 30-0ct-2002 15:46:28
1: Daughters of 463ES7.22e4
168.399 o/
268.896
418.982
_:/
102.598
152.659
443.305
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Davey070799 30-Oct.2002 15:46:28
2: MRM of 4 ChannelsES-
9.10
463 > 419
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1 00"
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9.10 _ 140.15
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Davey070799! 30-Oct.2002 15:46:28
2: MI_M of 4 Channels ES463 > 419 6.95e4
12.30 13.21 14.14 2: MRM of 4 Channels ES-
2.04e5
2: MRM of 4 Channels ES463 > 169 2.18e5
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7.74e3
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10:53
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golden west 3M d021030003
100
plasma
5x scale up 10123102 ok
I1%-
Davey07079fl 30-Oct-2002 12:03:28
2: MRM of 4 Channels ES-
9,88
TIC
3.59e5
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1: Daughters of 513E$-
13.46 13 64 ""
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2.00
4.00
6.00
8.00
10.00
12.00
14.00
16.00
ExactCopyof Original
Init_l
Date
CO
o
(3 '_ _ _
golden west plasma 5x scale up 10123/02 ok 3M Environmental Lab
d021030003 327 (9.869) Sm (Mn, 2xl .0C); Cm (325:330)
100-
169.19
218.739
268273 268.870 /
194.714
davey 070799 30-Oct-2002 12:03:28 1: Daughters of 513ES-
6.65e4
466.288
(69.303 /
513,307 512.651.
413.53t
,_
319.229
;;'_
422250
\
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279.504
349.213
112.331152.45;
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_ 495.097
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'-_
50 75 100 125 150 175 200 225 250 275 300 325 350 375 400 425 450 475 500 525 550
_
Exact Copyof 0dgina!
Iniliai
Date
golden west 3M d021030003
100
plasma
5x scale up 10123102 ok
DaveyO7079S 30-Oct-2002 12:03:21]
2: MRM of 4 ChannelsES-
9.88
513 > 469
9.10e4
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9.88
513 > 219
1.64e5
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9.68
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._
9.66
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6.92e3
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2.00
4.00
6.00
8.00
10.00
12.00
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lnit_ Date
golden west plasma 5x scale up 10123102ok 3M
d021030003
100
golden west plasma 5x scale up 10/23/02 ok
davey 070799
9.88
3M Environmental Lab
30-Oct.2002 12:03:28
Davey070799 30-Oct-2002 12:03:28
2: MRM of4 ChannelsES_13 > 489
I
0021030003 327 {9.869}Sm [MrL2xl.00); C_ _:_30)
1:4__u.2__htm o_513E_-
9.1 084
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9.88
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413.531
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1.64e5
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02048-21-7 solvent standard 10ppb 3M
d021030013 100-
Davey070799 30-Oct-2002 14:55:16
2: MRM of 4 Channels ES-
9.74
TIC
4,23e5
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4,17e7
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13.28
8.92
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0204B-21-7 solvent standard lOppb 3M Environmental Lab
d021030013 324 (9.765) Sm (Mn, 2x1.00); Cm (322:326) 1(30
218.799
268,990
davey 070799 30-0ct-2002 14:55:16
1: Daughters of 513ES1.10e5
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1_,354 168,892
/
118.61(}
319.169
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10ppb
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9.74
513 > 469
1.24e5
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d021030013 o2o48-2s1o.7lvesnttanda1r0dppb
1 00 7
3M Environmental Lib d0210:_013 324 _.765) ,S,'n{Mn.2x 1.1_; Cm (322:326)
dave0y707,
30-0_-2002 14:55:1S 1:Da_mrs o1513ES-
9.74
Davey070799 30-Oct-2002 14:55:16
2: MRM of 4 ChannelsES513 > 469
1.24e5
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i
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10.34
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10.34
2: MRM of 4 ChannelsES30-Oct-20D0a2vey5106373:10>275:9119(9]
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_
Date
golden west plasma 5x scale up 10123/02 ok 3M Environmental Lab
d021030007 320 (10.328) Sm (Mn,2xl.00); Cm(319:322) 169.073
1001
I
218.957
davey 07079S 30-Oct-2002 13:12:1[
1: Daughtersof 563ES5.56e4
318.866 %-
96.702
168.29,_ \
266.374 253.323
295.464
518.889
563.636
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1130
1690"/3
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6.56e4
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10.34
10.14
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2: MRM of 4 Channels ES563 > 519
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d021030017 319 (10.300) Sm (Mn. 2x1.00); 100-
Cm (316:322) 269.007
-
davey 0707991
30-0ct-2002 16:03:301
1: Daughters of 563E$- I
1.28e51
518.231
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319.285 318.38E
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100
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golden west plasma 5x scale up 10123/02ok 3M Environmental Lab
d021030004 316 (10.910) Sm (Mn, 2x1.00); Cm (314:318) 100-
269.341
davey 070799 30-0ct-2002 12:20:37
1: Daughters of 613ES613.862 5.12e4
568.519
219.192
..
295.037 319.180
360.130
418.715
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209.292 "0 118.313 168.373 O_
474.731
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368.593
I 493.084
643.893
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100
150
200
250
300
350
400
450
500
550
600
650
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ExacCt opoyf Odgina]
Init_ Date
golden west plasma 5x scale up 10/23102ok 3M
d021030004 100-1
-
4
%-I
d021030004 100
10.92 10.92
Davey070799 30-Oct-2002 12:20:37
2: MRM of 4 Channels ES613 > 569 2.41e4
2: MRM of 4 Channels ES613 > 219
l 0.78
1.8_2
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0.85
4.57
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100-
plasma 5x scale up 10/23102 ok
llloldlm west plasma Ilx scala lip 10/23._2 Ok 3M Envllonme_ttal I"b d02103Q004 318 [10.910) Sm (Mn. 2xl.G0); Cm (314:818)
100-
%1
O..J
clayey 0707l!1 30-0t-2002 12:20:31 1: Daughters ot 613ES-
et3.M2. 6.12e4
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10.92
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2: MRM of 4 Channels ES613 > 569 2.41e4
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10.92
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0.85
,
10.92
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1 I'0_.99r"147
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4.00
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02048-21-7 solvent standard 10ppb 3M d021030014 100-
I1%-
10.76
Davey07079S 30-Oct-2002 15:12:19
2: MRM of 4 ChannelsES-
TJC
1.09e6
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10.75
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02048-21.7 solvent standard 10ppb 3M Environmental Lab d021030014 312 (10.754) Sm (Mn, 2xl.00); Cm (309:318)
100
318.703
Z2 !'.
davey070799 30.Oct.2002 15:12:19
1: Daughters of 613ES-
569.293
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216.536
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168.431 \
368.951
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338.970 l
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100
150
200
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300
350
400
450
500
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600
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02048-21-7 solvent standard 10ppb 3M
d021030014 100
d021030014 3, 100'
%.
d021030014
1001
d021030014 100
10.76 10.76 10.76 10.76
Davey0707991 30-Oct-2002 15:12:19
2: MRM of 4 Channels ES613 > 569 5.70e5
2: MRM of 4 Channels ES613 > 219 2.41e5
2: MRM of 4 Channels ESo 613 > 169 2.53e5
2: MRM of 4 Channels ES613 > 119 2.19e4
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02048-21.7 solvent standard 10ppb 3M
d021030014
100
0201s-=1-=7mwm=t=,da,=loppb
0021030014 312 (10.754) Sm (Mn. 2zl.00)_ Cm (30_):315) 100-
3M Envhonrnmnla! Lsb
_=,._ _707_
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10.76
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613 569
5.70e5
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2.41e5
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2.53e5
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2.19e4
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golden west plasma 5x scale up 10123102 ok
d021030008
3M
.9.08
Davey070799
2: MRM of 3 Channels ES-
304_-2002 13:29:2T3IC
100II1%
8.811
1.12e7
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i '_= i_:
_
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goldenwest plasma5x scaleup 1012310o2k 3M EnvironmentaLl ab
d021030008 329 (8.884) Sm (Mn, 2xl.00); Crn (323:334)
100-
79.695
davey070799] 30-Oct-200213:29:23i
1: Daughters of 499ES1.67e6
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0021030008 337 (9.100)sm (Mn,2xl.00); Cm(334:343) 100- 79.695
davey 070799 30-Oct.2002 13:29:23
1: Daughtersof499ES499.1442.02e6
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79.695
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davey 070799 30-0ct-2002 13:29:23 1: Daughters of 499E_.
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2: MRMof 3 ChannelsES-
8.81
499 > 130
2.45e6
9.08
|
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dsvly 0707St 30-0t-2002 13:29:23
8.8'
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30-Oct.2002 13:29:23 2: MRM of 3 Channels ES-
499 > 130 2.45e6
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d021030018
Davey070799 30-Oct-2002 16:20:35
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dO21030018 329 (8.886) Srn (Mn, 2x1.00); Cm (321:334) 79.695
davey 070799 30-0ct-2002 16:20:35
1: Daughters of 499ES6.00e4
129.679 168.663
180.093
498.117
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d021030018 337 (9.102)Sm (Mn. 2x1.00);Cm (335:342)
100-
79.760
98.586
davey 070799 30-0ct-2002 16:20:35
1: Daughtersof499ES1.20e5
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d021030018 337 (9.102) Sm (Mn,2xl.00); Cm (322:342)
100
79.695
davey 070799 30-Oct.2002 16:20:35
1: Daughtersof499ES8.55e4
98.585
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168.663
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Davey070799 30-Oct.2002 16:20:35
2: MRM of 3 Channels ES499 > 130 6.92e4
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02048-21-7 solvent s=nd;Ird _gppb
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,
dJvl 0707_ 30-0ct-2002 16:20:35 1: Oaugll_ mol 490E_q-
8.84
Davey070799 30-Oct-2002 16:20:35
2: MRM of 3 Channels ES499 130
6.92e4
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3M ENVIRONMENTALLABORATORY E02-1039
i. I
ATTACHMENT D: PREP SHEETSAND TRACEABILITYINFORMATION
i
t
i
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Page 125 of 225
3M E_IVIRONMENTALLABORATORY
i
E02-1039
,I
:: 1
:
*, :__r i
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SPE Columns
Extraction
o:.
Worksheet
Prep Date: Analysts initials:
Sample Number or description i
Blank milli-q Lampire Serum Sigma Sem..m GoldenWest Serum Biomsource Serum Lamp.irePlasma
'GoldenWest Plasma Innovative Resourcets Plasma
10123/2002 OK
/O ,_.-_ C__ _)/_
Method Revision: ETS-8-231.1 Study Number: E02-1039
Volume ot sample
filtered (ml)
Type of column Used
2000 ml 2000 ml 2000 ml 2000 ml 201711ml 2000 ml
Waters, 19, 6ml Waters, 19, 6ml Waters, 19, 6ml Waters, 19, 6ml Waters, 1_, 6ml Waters, 19, 6ml
I::luUon
Amountand spike mix used
. .. NA ...NA
NA NA HA NA
solventand volume
Comments
of MIOH TN
,.,al_
2n1_M MIOH TN
_13
2ml_ MIOH
rCR._ea
TN,
_13
rcR.6a9
2ml d MeOH TN.
A-6313 2ad _ MeOH
_13
_ OfMeOH
,.=13
2n11of MeOH
TCR-890 TN,
rc_._7
TN
TCR-a_
"IN
2000 ml Waters, 19, 6ml 2000 ml Waters, 1_, 6ml
NA
_Jofu.oN=T"N63m1R3.sa4
NA
_
mR.sa3
,,,
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,;,._
_x_c0ndltion column with MeOH; x_wash with milIi-qwater;,_x_filter sample; ;
....!.
_x_vacuum dry the column; _.x_elutecolumnwith _lvent;
_'',
%
. ",. Additional comments:
i
10mlofsera dilutedwith40ml ofmilll-qand200mlofACN.Sampleswer_ shakenfor20 minat 300rpm.thencentrifugedfor 10rain @ 3500rpm/4C
Samplewas transferredinto1750mlof milll-qandfilteredthroughconditioneSdPE
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Page 126 of 225
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Norf"GLP SPE Columns Extraction Worksheet
Prep Date: Analysts initials:
_}_ 1011112002 'c. la.o'_
OK
OL/--J
Method Revision: E-T-S..;_Q-I _) Study Number:.E 02-1039
Sample Number
description
'H
_
31ank,milli-q-1
Blank milll-q-2
rabbit serum blank
rabbit serum curve-0.1ppb rabbitserum curve-0.25ppb
Volume of
Elution
or sample Type of column Amount andspike solvent and
filtered (ml)
used
mix used
volume
Comments
'"
2 ml'of MeOH
400 ml Waters, 19, 6ml
NA
TN-A-=10
2ml ofMeOH
400.ml Waters, 1_],6ml
NA
r.-^_lo
I ml_ MeOH
400 ml Waters, lcj, 6m!
NA
rN_._o
TCR.See
| mlof MeOH
400 ml Waters, 1_, 6ml 2ul of 02050-14 rN-A-aam rCR._8e
400 ml Waters, 1,cj.6ml
5ul of 02050-14 rN.*-=_o
! ndol MIOH
rCR-aee
rabbit serum curve_-0.5ppb
irabbit serum curve-O,.75pFb
,.
rabbit serum curve:lppb
I rabbit serum curve-2.5ppb
i
I rabbitserum curve-Sppb .
: rabbitserum curve-.10ppb
;.._
'"
rabbit serum curve-_30ppb
Lampire serum blank-1 Lampire serum blank-2
Lampire serum MS K)..5ppb
Lampire serum MS-Sppb
400 ml 400 ml 400 ml 400 ml 400 ml 400 ml 400 ml 400 ml 400 ml 400 ml 400 ml
Waters, 1_],6ml Waters, 1j_6ml Waters, lg, 6ml Waters, 19, 6ml Waters, 19 6ml Waters, 1_, 6ml Waters, 19, 6ml Waters, lcj, 6ml Waters,,.lg, 6ml Waters, 1_ 6ml Waters,lg, 6ml
10ulof 02050-14 rI n_d-oaf 3MrIOoH
15ul of 02050-14 r_a3m 2 nd,_ MAVDH
20ul of 02050-14 50ul of 02050-14
T_a_o
2 mlof MIOH
TN-A_tO
2 mlof MIOH
100ul of 02050-14 _A-ealo
2 mlot MeOH
200ul of 02050-14T,-A_o
2 mlof MeCH
600ul of 02050-14 r.-_.3_o
2ml of MIOH
NA
rN-_-_m
2ml _' kteOH
NA
rN-A-_m
Z ml,V MeOH
lOul of 02050-14 r,-*.-._o
| mlol MeOH
100ul0f.02050-14 rN.A._o
rcRaes rcR-aSe rcR.eaa rcR.ses TCR-_88 TCR.680 TCR-888 TCR.SSa TCR.SaB TCR._a TCR.eaa
Sigma serum blank-1 Sigma serum blank-2
400 ml 400 ml
Waters, 1_16, ml We!ere, !g, 6ml
NA
rtrr.n.l,o_f aMeaO,Ho
TCr_S
12mlof MeOH
NA
TN-_-_I0 rcR.ea9
,
t Sigma serum MS-0.S ppb " Sigma serum MS-5ppb
Gold.enWest serum blank-1
400 ml 400 ml 400 ml
Waters, lcj, 6rot Waters, 1_, 6ml Waters, lcjt 6ml
'TN-A-11O
10ulO__r,_o_. 22mml_f|Moel_MH eOH 100ulo2_-_hTN-_-e=_O
2 rnl _ _lldOH
rCR-68g
rca.ae_
NA
_.._o
rCR_O
Golden West serum blank-2
GoldenWest serum MS-0.Sppb
GoldenWest serum MS-5ppb
",.
Bioreseource research serum blank-1
Bioreseource research serum b,L lank-2
Bioreseource research serum,MS-0:5ppb Bioreseource research serum MS-5ppb
400 ml 400 ml 400 ml 400 ml
400 ml 400 ml 400 ml
Waters, 1_16, ml Waters, 1_ 6ml .waters, 19_6ml Waters, lg, 6ml
.Waters,19, 6m!. Waters, lg, 6rnl Waters, lg, 6ml
NA
"rN-A-_m 22 mmllOoI t kM_eOOHH
lOul of 02050-14 T,-_a_o
100ul of 02050-14 =_m.^lo_o_U,OH
! mt ol Me,OH
NA
TN-._-6310
2 rill OfMeOH
NA
TN-A" -6310
2 mlO| MeOH
10ul of 02050-14 T.-^-_=_O 2 ml Of MIOH
100ulof 02050-14 !Ta-x-ea_o
rCR._gO rcR-ego ,IrCR.e e TCR..887*
TCR-ea7 TCR-687 TCR.887
ii_
Extraction Steps (initialwhen/if done):
'"
_x condition column with MeOH; _.x_washwith milli-qwater; _x_filter sample;
_xvacuum dry the column; _x._elute column with solvent;
_"
:"
Additionalcomments:
hC'_ _ .A.-_/_C_ c'_ ,c,,._,?
ExactCepyofOr_ginal
_
_(b"t_._
InYdaJ Data
2ml of seraJplasma diluted with Bml of mil[i-q and 4Qml of ACN. Samples were shaken for 20 rain at 300rpm, then centrifuged for 10 rain @ 3500rpm/4C
Sample was transferred into 350ml of milll,q and filtered through conditioned SPE
_,-,_"_" v_- _ C:c7% ,-',_;_'-"='-_'_\_'_H "_ _._c'_'_ _.;_;/a'Y.YJ-
Page 127 of 225
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pO__.l 'JP'10/10/2002
--/'"
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It.;/6'.o,_' C,p__.
Method Revision:SPE validation Study Number:,E 02-1039
'" Sample Number
,, description
Blank milU-q-1...
Volume ot
Elution
or sample Type of column Amount and spike solvent and!
filtered (ml) ii m
used
mix used
volume
2ml ol MeON
400 ml . Waters, 19, 6ml
NA
m-A._lo
Comments
Blank milli-q-2
Chinese plasma curve-0.1ppb C,hinese plasma curve-0.25ppb.
Chinese plasma curve-0.Sppb
'
'
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Chinese plasma curve-0.75ppb
Chinese plasma curve, -lppb
!
I Chinese plasma curve-2.Sppb
i Chinese plasma curve-Sppb
,
] Chinese plasma curve-10ppb
_I, Chinese plasma curve-30ppb,
Chinese plasma blank-1
Chinese plasma blank-2
Chinese plasma .MS-0.Sppb ,.,
i C,hineseplasma MS-Sppb
400 ml IWaters, 19, 6ml
NA
2rNml-o_f 1M0IIOH
Zml cffMeOH
400 ml 400 ml 400 ml
Waters, 19, 6ml Waters, 19, 6ml Waters, 19, 6ml
2ul of 02050-14
5ul of 02050-14
10ulof 02050-14
rN-A.6310
ZmlotMeOH
rN-A._0
2ml oIMeQH
r_,.A.=_0
ImlolMeOH
TCR-674 rCR-_74 TCR-(174
400 ml 400 ml
Waters 1_18, .ml Waters, 19, 6ml
15ulof 02050-14 20ul of 02050-14
r....,,_rQ
2 ml of MeOH
_-A-._a
2 ml OtMIOH
rcR-e74 TCR-6"/4
400 ml 400 ml
Waters, lg, 6ml Waters, 19, 5ml
50ul of 02050.14 _-,_._t0 2rid _ MIOH
100ulof 02050-14 :..A-ela
2 mlo( MIQH
TCR-874 TCR-e74
400 ml Waters, 19, 6ml 200ul of 02050-14 m.A_31o TCR.874 2nd oiMeOH
400 ml
Waters, 19, 6ml 600ul of 02050-14 m-A._o
2ml el MIOH
TCR-874
400 ml Waters, lg, 6ml
NA
r..A.=_o TCR-874
Z mlofMlOH
400 ml Waters, lcj, 6ml
NA
rN_._to
/'CR.674
Z ndot MeOH
400 ml
Waters, 19, 6ml
10ul of 02050-14 m.A-=_0
l ml of MeOH
rcR.e74
.... 400 ml _Waters,lcj, 6ml 100ulof 02050-14 _A._',o
TCR-674
Lampire Plasma blank-1
'
i Lampire Plasma blank-2
! Lampire plasma MS-0.Sppb _ Lampire plasma MS-Sppb I Golden West Plasma blank-1
400 ml 400 ml
400 ml 400 ml 400 rnl
!Water , 19, 6ml Waters, lcj, 6ml
Waters, 1_, 6ml Waters, 1_, 6ml Waters, l_h 6ml
NA NA
10ul 100ul NA
rN-A-_m
t ml of MeOH
m-A.=to
| ml ofMIOH
rN-A-=,o N..,'.-_0
_ml of MeOH
rN_tO
TCR-e_ rCR-68S
rCR-88S rcR-eas rcR-ell4
GoldenWest Plasma blank-2 Golden West Plasma MS-O.Sppb
Golden West Plasma MS-Sppb.
400 ml 400 ml 400 ml
Waters, lcj, 6ml Waters, lg, 6ml Waters, 19, 6ml
NA 10ul of 02050-14 100ulof02050-14
IrnNdo.(_MmeOoH
_nd_ M_OH
rN-A-(_tO
_ml _ MIOH
N..-_lo
_ed _ MeOH
rcR.ea4 "rCR-M4 rCR._
InnovativeResearch Plasma b!.ank-1
....
t Innovative Research Plasma blank-2
i
400 ml 400 ml
Waters, 19, 6ml Waters, 19, 6ml
NA
r...._o
rcR-s_
t ml of MeOH
NA
TN.A..6.110 TCR-eB3
r2 ml _ MIIOH
i Innovative Research Plasma MS-0.Sppb_ 400 ml Waters, 19, 6ml 10ulof 02050-14 _'N_'^_"_.OO._ rcR-_a3
' InnovativeResearch Plasma MS-5ppb
400 ml Water,s,,lg, 6ml 100ulof 02050-14 TN-_,H$310 TCR-683
,,,
Extraction Steps (initialwhen/if done}:
_xcondition columnwith MeOH; _x_wash with milli-qwater;, _x_filter sample;; _x_vacuum dry the column; _x._elutecolumn with solvent;
ExacCt opyof Original
_.iY1C /O/_( ](_r-2.....
A('d,:_d.i-tpio.n_a=l_comme,_n,t's_:-'_ C' 2 I1_-_,$_;_,'- , ,;_ _ _.._: V_j,_ _(_. (__,_ C_/(.:C_.
2mlofsera/plasmdailutedwith8mlof milli-qand40mlofACNS. amplewsareshakenfor20minat 300rpmth, encentrifugefodr10rain@ 3500rpm/4C Samplewastransferreidnlo350mlofmillJ-qandfilteretdhrougchonditionSePdE
k'_ _A "_/_t
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Project or Study Number: E02-1039 Associated Study Number:
Forsamplesthat werepreppedon 10111/02t,hat areBioresourceResearchSerumMS 0.Sppband ._PP.,O_m_ .o_Cmw.-Pa_.]_Lnw_r_em._.aeem__n!'y, .sw_n_P,..........................
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Test Control and Reference Substance Log
I Substance trade name IHuman plasma from China
or reference #
IITCR Substance #
TCR-674
ISnaumbset:ance/chemicaI ILotJbatch#: 13M#
(Human p,asma IN087P27 I
ITCR# IReceived from:
TCR-674 Northwest Bioanalytlcal
Expiration date:
I1
Avoml)o: unt received (wt. or 7x-lOml
IlnitJals:
IOK
Date:
0912512002
Number/size of containers:
I17-15 ml centrifuge tubes
Shipper:
FedEx
]Condition:
Iliquid, Biohazard
MSDS (y/n)
'=..)Y N
IRetain
I
Date of Retain
1.7.,_.'.-.-.......i[.._ .-_U_.:...-_-.-.._.-.-._;.__.--T_::...--..',.,:_--_.-._!_..,:_.=__-.:';
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Gross wt/vol
Purpose (enter standard number
Balance Balance Initials
Date
,:,!
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Substancetrade name IPooled HumanPlasma In Sodium
3r reference#
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TCR Substance#
IITCR-683
1
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[nSaumbes:tance/chemical [Pooledhumanplasma
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:3M#
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Expirationdate:
09130/2007
nitials:
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[
Date:
I10/02/2002
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Dateof Retain
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USE LOG
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110ml
after withdrawal t0B=-a-lIance ID 1
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Test Control and Reference Substance Log
I Substancetradename Sodium Citrate PooledHuman
TCR Substance#
TCR-684
J
or reference#
P asma
ILoUbatch#: (3M #
I ,ra,on
Ilnitials:
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3M L_NVIRONMENTALLABORATORY
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E02-1039
5odium Citrate Pooled Human Plasma
...i._,
;_ooledhuman plasma
.i
"CR-684
USE LOG
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I Before
withdrawn
after
or reasonfor removal)
ID
jBa,a,JBal cej l,o,,,a,s, I withdrawal (massorvol) withdrawal
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I[GBraolsasnWcet/JDVo1l.I BalAanmcnetI.D 2 IGBraolsasnwcet/IvDo1lJ Purpose(enterstandardnumber
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E02-1039
Test Controland ReferenceSubstanceLog
Substance trade name or reference #
Substance/chemical name: Lot/batch #:
3M#
Expiration date:
Initials: Number/size of ;ontainers:
Condition:
Pooled Human Plasma From Lampire
IPooled Human ILamp|re
122-60824A
I
II10108/2007
{OK
11-250mplalstic I
Plasma bottle
From
jFrozen
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1
,
IITCR Substance #
TCR-685
ITCR #
I
JReceived from:
I
Amount received (wt. or vo ):
TCR-685 Lampire 10Oml
IDate:
101t012002
JShipper:
I IMSDS(y/n)
UPS _.) Y O N
IDate of Retain
I
Punly:
I
I
Records received:
I Disease Screen
I
fabrication, or derivation
Lreoccoardtiso:n of synthesis,
I Lampire
I
Std Location/Storage:
I Frozen F19
I
Molecular Formula:
I
I
Comments
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I
Attachment(s)
I
I
ExacCt opyofOriginal
_
Datll
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E02-I039
_ooled HumanPlasmaFromLamplra _ooledHumanPlasmaFromLamplre
USE LOG
I I Before withdrawn after
I withdrawal (mass orvol) withdrawal I BalanceID 1 BalanceID 2 BalanceID 1
orreasonforremoval)
1"
11Oral
I"
E02-10"19
I
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I ID
2 Ina ha ' IOK 11023/Z002,
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Page 139 of 225
3M ENVIRONMENTAL LABORATORY E02-1039
I
USELOG
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_oolad Human Plasma From Lamplre
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_CR-685
_--!
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after
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2
.
GBraolsasnWcet.NDo1l. I BalAanmcnetI.D 2 BGarolasnscwetI/Dvo1l I Purpose(enterstandardnumber IBal_ce I BalanceI IniUals I
Date
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18ml
I"
IE02-1039,validation
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11011012002
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Test Control and Reference Substance Log
JIoSrurebfsetraenncceter#adename
name: ILot/batch#:
{J3ME#,p,,Ua,oen:
I
Ilnitials:
PBoloorleesdouHrucme anSerum From
roo,...oo. .ru
1020821 I
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JOK
ITCR Substance,
i.c .
IReceivedfrom:
ITCR-687 IBloresource
IAmo, ueniv,e,oI,OOm,
VO):
IDate:
110/11/2002
Ncounmtabienre/srisz:eof
15O0mpl tasticbottle
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lRecordsreceived:
I
I
Ifabricallon,or derivation
[ILreoccoartdiosn:of synthesis,
1Sioresource
I
IStd Location/Storage: I FrozenF19
I
IMolecularFormula:
I
I
IComments
JAlso assignedTN.A-62841011110O2 K
I
IAttachment(s)
I
I
r",
(_
ExaCtCopyof Original
'nEz.Vj._.___e._
!_J
Page 141 of 225
3M ENVIRONMENTAL LABORATORY E02-1039
I
ooled Human Serum From Bloresource
_!_i
_>ooled Human Serum
USE LOG
BaracI,.'o'IIvG",w="0w'.'B,"u.v",n.=o'orOn,,.IoVO,I",'"/'Or"Ia0""
11Oral
I"
IE02"1039
F
J"
I0K' 110/23/2002
Exact Copy of Original
_,W(1 I,,/,/0_
Page 142 of 225
3M ENVIRONMENTAL
LABORATORY E02-i039
i
I
ooled Human Serum From Bioresource
_,.
Fooled Human Serum
;_,I
FCR.687
USELOG
I Before I withdrawn
after
or reason for removal)
":i
I withdrawal I (mass or vol) withdrawal
I Balance ID 1 I Balance ID 2 Balance ID 1
[-
Is'"
I"
E02.1039, validation
I"
l"
IOK
110111/2002
!
,t
IL.
ExacCt opoyfOriginal
_
Date
;
Page 143 of 225
3M ENVIRONMENTAL
LABORATORY
E02-1039
_' i I
Test Control and Reference Substance Log
':""_ or reference # , !
Substance
t,ade
name
IPooled
Human
serum
from
Lampiro
TCR Substance,
TCR-.688
I
I i, _I
Substance/chemical
jPooled Human serum
TCR #
TCR-688
name:
JI
3M# I Lot/batch #:
IX324B
"
I I Received from:
ILampire
J
Expiration date:
(0812912007
I
Avoml)o: unt received (wt. or 1, 250ml
I
Initials:
IOK
Date:
It 0/11/2002
containers:NUomf ber/size ,JZSOml Nalgene bottle
Shipper:
UPS
I
Condition:
JFrozen
USDS (y/n)
_. } Y t_ N
I
Retain
J
Date of Retain
I
[
'
( 5"ArchivedlSubstan_eNotA_iia_,e_
::")
Purity:
J
I
Records received:
J
J
I I ' i
Location of synthesis,
I Lampire
J
t
fabrication, or derivation
'-.,;
records:
Std Location/Storage:
JFrozen F19
J
i
Molecular Formula:
J
I
,
Comments
JAlso assinged TN-A-6286 10111102ok
I
Attachment(s)
J
I
_i,:!i:
ii_ii
'i
ExactCopyof Origiac,l
J
Page 144 of 225
;
i:i
1
)ooled Human serum from Lempira
i
_)ooled Human serum
,;
I_'CR-6B8
3M ENVIRONMENTAL LABORATORY
E02-1039
USE LOG
-i
I Before
withdrawn
after
or reason for removal)
ID
:
_ withdrawal (mass or vol) withdrawal
1
I GBroalsasnWcet.NIDol1. I BalaAnmcenLID 2 t BGarolasnscewtI/Dvo1l
Purpose (enter standard number
Balance I Bali)nce I IniUals I
Data
I"
18ml
i"
E02-1039, validation
I"
_"
IOK 11011112002
'S= i !, . J
i J
!i'?
_
i
,,ii ii
o
Exact Copy of OHglnal
i
Page 145 of 225
3M ENVIRONMENTALLABORATORY
.....
E02-1039
"'i
I
USELOG
I
I pooled Human serum from Lamplre
[
_ '_
pooled Human serum
'i
Ircr.68e
:" i
Before
withdrawn
after
or reasonforremoval)
,t
withdrawal (massorvol) withdrawal
Balance D 1 BalanceID 2 BalanceID 1
l"
1O1 ral I"
[E020-:t19
I" I" ]oK 11012_:z00:'I
i :i
:1 I
i_
Exact Copyof Original
!",'L 1
Page 146 of 225
i ,,._
--,_
_'_
.' ._ ' '_!
::': ! '_
!;.:";
:_":r_: -::_, ,, :' '_ ;
3M ENVIRONMENTAL
LABORATORY EO2-'103g
Test Control and Reference Substance Log
I Substance trade name JMale Human Serum from Sigma
or reference #
IITCRSubstance #
TCR-689
Substarlce/chemJca,
name: Lot/batch #: 3M # Expiration date:
Initials: Number/size of containers:
Condition:
Ii_t_ale Human
serum
1022K0965
I
I10712412007
IOK
1-100ml plastic bottle
Ifrozen
J'l'CR,
I
JReceivedfrom: I Amount received (wt. or
vo):
IData: [Shipper:.
I
IMSDS (y/n]
TCR.689
Sigma 100ml 10/11/2002 UPS
_Y N
_Rem!n................................!_._.
IDate of Retain
i !-; ArchwedlSubstance Not Avadab] e '1
!Purity:
I
Records received:
]
......
]
]
fabrication, derivation
Lreoccoartdiosn: of synthesiS,or
I Sigma
I
Std Location/Storage:
I Frozen F19
I
Molecular Formula:
I
I
Comments
I AIso assigned TN-A-6250 10/11102 OK
]
Attachment(s)
I
I
ExactCu;;,.:.:,?_,.. ,,;
:i?i
Page 147 of 225
3M ENVIRONMENTALLABORATORY
E02-1039
I
USELOG
1
/ _AaleHuman Serum from 51gma
]
' i"ii
pale Human serum
!
irCR.6a9
....
'/lJBGwarilBtashensWdfcoretar'INewDal1"l I (BmwaaliAatshnmsdconreraLIvDwon2l) BGwariltasahnsfdtcwereratI/Dwva1ll I Purporsree(eanstoenrfsotrarnedmaordvnaul,mber IBal_ce I Bajl2IaDnceI Initials.
Date
I
I-
le_nl
I"
1E02-10v3a9n, datlon
I"
J"
IOK 110/111202 I
j q
_,,_
Ng!,',
!i . ,!
., !
ExacCt opyofOriginal
Page 148 of 225
1 I
")
I
pale Human Serum from Sigma
'__i
pale Human serum
.i,
FCR.e89
3M ENVIRONMENTALLABORATORY E02-1039
USE LOG
/
;i
I Before
withdrawn
after
or reasonforremoval)
'
I withdrawal (massor vol) withdrawal
I BalanceID 1 BalanceID 2 BalanceID 1
["
[lOml I"
[E02-10,19
PF
IOK [10123/Z002 l
i_,':,=I ,]
r)
"y_-4
'_";"_i
i
! t:;.:!]
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i
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3M ENVIRONMENTALLABORATORY E02-1039
TestControal ndReferencSe ubstanceLog
Substancetrade name 3r reference#
Substance/chemical aame: Lot/batch #:
3M #
Expirationdate:
Pooled HumanSerumfrom Golen ,West Pooled Human Serum
G01406042
0712512007
Initials:
Number/sizeof containers:
Condition: Retain
OK 1-500ml blastic bottle
frozen
TCR Substance#
TCR.690
TCR # Receivedfrom:
TCR-690 Goldenwest
Amounrteceived(wt.or 500ml
_ol):
Date:
1011112002
Shipper:
UPS
VISDS(y/n) Date of Retain
_.) Y N i
!:..(.".'- Archived/Sbbsta, nCe.N.oi.;Av_iia..l._[ie::.,.: .;:
Pu_/:
I
I
Recordsreceived:
I
I
I I Locationof synthesis,
I Golden West
I
fabricationo, r derivation
records:
Std Location/Storage: IFrozenF19
I
MolecularFormula:
I
I
Comments
I AlsoassignedTN-A-62511011110o2k
I
Attachment(s)
I
I
!;_;;_
I
ExacCt opoyfOriginal
_
Dtlto
Page 150 of 225
3M ENVIRONMENTALLABORATORY
i
E02-'1039
!
'
I
: '_i
p_o'ooolleeddHuman Serum from GolenWest
_rCR-690
USE LOG
-:"
Before
withdrawn
after
or reasonforremoval)
withdrawal (massor vol) withdrawal GBraosasnWcet.DNo1l. I BalAanmcnetI.D 2 I BGarloasnscwetI/Dvo1l
Purpose(enterstandardnumber I Bal_ce I Bal_)nceI Initials I
Date
I"
1lml
I"
E02-1039
l"
F
IOK I10/2312002
z r:7
li_i__,
!i:iJ i:cli!
L
_ i
ExacCt opYofOriginal"
Page 151 of 225
i? _.i
:'_"'i,,, ,, i : _:i
3M ENVIRONMENTALALBORATORY E02-I039
I
USE LOG
I
I _ooled Human Serum from Golen West
I
_PooledHuman Serum
_rCR-690
Before withdrawal GBraoasnscWe t.NDol1.
["
withdrawn (mass or vol) I BalaAnmcenltD. 2
[8ml
after withdrawal J BGarloasnscewlDt/vo1a
l"
or reason for removal)
Purpose (enter standard number E02-1039, validation
f Bal_ce [ Bal_nce I InlUals I
Date
["
_"
IOK
11011112002
._:._,_
ExacCt opyofOriginal
Page 152 of 225
Standardcurve trackingsheet
P,ep date: Analyst:
10/7/2002 OK
/(.._'C_t/
]
'C-./"%J
Type ofthe cun_e: Target analytes:
Solventcuwe forSPE sera validation
C6, C7, C8, C9, C10, C11, C12, THPFOS,THPFDS, PFOS
Standard mix usedforpreparingthe curve:
02002-63
StudyNumber. FinalSolvent&TN-A#:
Sera SPE validation MeOH/6308
[FinalVolumeofeach point:I
25l
.... j:
Curvepointnumber 02048-21-1 02048-21.2 C)2048-21-3
02048-21-4 ....... 02048-21-5 02048-21-6 02048-21-7 02048-21-8 02048-2t-9
02048-21-10
Amountofmix
used(ul) 5 25 50
125 250 375 500 750 1000
1500
C6 0.100 0.500 1.00
"C7 0.102 I 0.511 I 1.02
2.50 5.00 7.50
10.00 15.00 "20.01
2.55 5.11 7.68
10.21 1513'7 20.43
30.0,1 I 30.64
C8 0.10:3' 0.517 1.03
"2.58 5.17 7.75 10.33 15,50 20.66
31.00
Analyte concentrationin every point (ppb)
C9 0.101 0.807 1.01
C10 0.101 01505 t.01
Cll 0.103 0.515 ..... 1.03
C12 0,104 0_518' 1.04
2.54 5.07 7.61
10.14 15.22 20.29
2.53 5.05 7.58
10.10 15.15 20.20
2.58 5.15 7.73
10.31 15'.,_6 20.81
2.59 5.18 7.77
10.38 15.54 20.72
'30.43 I 30.30' ' 30.92
31;,08
THPFOS 0.102 0.512 1.02
2.56 5.12 7.68 10.24 15.37 20.49
30.73
THPFDS ' 0.100
0.501 1.00
2.51 5,01 7.52 10.02 15.03 20.04
I' 30.06 I
PFOS 0.101 0.503 1.01
2.52 5.03 7.55 10.06 15,09 '20.12
30.18
01(/
co O
_
Q
ExacCt opyof Original
_
/-
Ildtlal Date
,,_
......
"T" "': ....
..--r,.=..?...............
."=_-,.'.,'.-'T--_-
........
_" " " "- ....
3M ENVIRONMENTALLABORATORY E02-1039
....i '_
I; "_ ',
:
i
,
:
!ii
: ;
Standardmix trackingsheet Sere Super mixfor 8PE lOX MDV
Prepdate: Analyst:
10/7/2002 OK
Exp. 11/13102 0,_., /0' _'C_
Typeofthemix: sere supermix Targetanalytes: C6. C7. C8. C9. C10. C11.C12.
THPFOS. THPFDS.PFOS
Standardnumberforthe mix:
02002-63
StudyNumber:. FinalSolvent&TN-A#: jFtnalVolumeof the mix:
Analyto
C(]
C7
'C8 C9 C10 C11 C12 THPFOS
THPFDS PFOS
concenlratloonf amountof concentratioonfthe
Analytestandard enalyteIn standardstandardused analytaIn themix
number
mg/mJ(ppm}
(ul)
ng/ml(ppb)
02040-44
1042
12
500
02040-58
1344
9.5
511
02040-4,5
1230
10.5
517
02040-46
1266
10
507
02022-90
1010
12.5
505
0204065
1356
9.5
515
02040-55
1126
11.5
518
0204042
1348
9.5
512
02040-49
1002
12.5
501
02022-56
1048
12
503
Sere SPE validation MeOH/8308
I
25
ExactCopyof Origtnal
Page 154 of 225
3M E_VIRONMENTALLABORATORY E02-1039
SINGLE COMPONENT PREPARATION LOG
' :_
Date: I0, I_0- 0 _J
!!
Analyst:
0
BookNo. 02 050 PageNo. 14
I
DescflpUon:
Ji:::}CT_p
"_L#"_ :_ bL_,I"x _ _ 5?
'i 1
='.','
StoCkNumber:.C)oQO- _3) _-- -_ _:=
i,.
,....I.
Weightor Volume
Used:
2_ _
-i
BalanceID:
/_.)t_
Concentratioonr Purity:
EO0,_.
0_' _
,ziL.
CorrectedWeight:
_I/_
OtherCorrecffon Factors:
tJ/%
SolventandTN-A Number:. _eO
-A " _ I_)
._ _" _ ._ ' I
F,..,
Volum.:
FinalConcentration:
_)Off_
,f.
d::!
ExactCopyof 0rig[na/ ( _,lnc t_c/:t_lOL-
Inltlal Data
Reviewed /'Signat'_,"" _ 7/
jo
Date(
Page 155 of 225
3M ENVIRONMENTALLABORA'TORY
....
E02-1039
v=
_,L,:l
1
SINGLE COMPONENT PREPARATION LOG
,1
o,,e/o:.)c,_P.)
BookN02o0. 50
';4: ,;t.j
, j
:::i
wo,,,,o,_o,u.3o7.0. %. -,(.4 ,.,...,o. f//t
/
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-_tl
f)
ii;',!.,,:_ oo.-.w.,0/v.,A.
_ij
.,.,v._.. -_,-;_g
,.aJ
+
Storage Lo=ilon:
_:_UOJ
(_,
:. !
;.J
L."JD
Other CoFrarecctotirosn:
//_/4
_,v..u.m,._,e.__.O. ///ql,' _ceJo I
.,.._,.o....o, _ 7'-;xH_6-
ExpimUon Date:
tl.i;.o_J
ExacCtopoyfOriginal
L'i_c ICI',_)O-L.'- Inl_ g_
b Reviewed
Sig_'natdia
,,,'-"_Z
_ _'* ,_ /
ioJ,/o
Date
Page 156 of 225
I
II
II__
_I
,,
....
A
II II
I
I
llEl
...-
3M ENVIRONMENTAL LABORATORY
E02-1039
"lq
SINGLE COMPONENT PREPARATION LOG
I
Date: ]C ]C"C_
Book No. 02 050
Do,c,,,,o,- O.P
ix
i
-:!
Analyst:
C_)
Page No. 16
I
-!
i :/
Stock Number:.
IO,gC,t'_. ,_ _ "_
I
;
Weight or VoUlusmede: ,
I o_ "_" ] ,{,.,_
Balance ID:
M/'_
"
J
ConcentraPtiounritoyr: ,
,_
'=
_"CC////_TrI_)
I!
Other CoFrarecctotirosn:
/_///'31
_;_J
"-
'
....:
Fl.l_l,I V(il.IJITU_:
_ _ i_t.l_
Storage Location:
_I,_ I_ t_ }"
Final ConP,:entltlltton:
Expiration Date:
Li'7)._.. C_" _
I"I
//'/_"
_'__)
!
ExacCt opyofOriginal
Initial Oa_
Reviewed by.,,#',vi"'--_'"S/X,,-'_'_ I_'_//_
''_A
Page 157 of 225
_._ __,_ i__. C
_.....
_
"" ":
l
l
IBm.
lif
i
l
i
m
i
m
m
m
i
R
_
R
l
_
Description: Date Prepared:
Prepared By:
OO_Ue "E_'P,j ._-'2A6T_Co-r3M_L_O--_;-K
-ic---C-_ _-/,'_ Io.:/.o2,jStorage Location:
(J_Z,.._
Expiration Date:
_Ot _ ,_(_ /I.r6,- C_/;_.
MULTI-LEVEL PREPARATION LOG
Book No. 02 048
PageNo.
21
Solvent:
A[_-_--)/_
3M Trace #:
7"A_-A-L_ _'_.-._,,_.
Standard ID #
02048-21.1 02 048-21.2 02 048-21-3 02 048-214 02 048-21-5 02 046.21.6 02 048-21-7 02048-21-0
''='_'____ Description
,., Description Compo ,_ntStandards
ID # .. . Conc
_/_O
Expiration Date
a. 1 Std 1
_. _" Std 2
(
_. 5"
5-
7. '_
),_
Amount of Component Standard Added _,J_-
Std 3
Std 4
Std 5
Std 6
Std 7
/:_Std 8
CV<,
........
L
_
_=,V=,__on.,(_ _'_
_
,_ ,...... -........-"."-.'-'>
i
-= FlnalConcentratlon.,,.-__@_..2... O. ( .
O" _
|
_."_
_
__
IC'
J._"-
Standard IO #
02049.2'1-9 02 04s-21-t0 02 048.21-1t 02 0411-21-1=02 048.21-1302046-21-14(}2N0.21-15 02 04s-21-1=
_,
._
-
,,.
,-._, Descri.,p. tion, -,.
_O
_ C_
_..__---.- ----,-,,',------ _---'Tb,.,-,:-_'_-.:
Component Standards
-
"Expiration
Amount of Component Standard Added _
....
"
Description
ID #
Conc
Date
Std 9
Std 10
Std 11
Std 12
Std 13
Std 14
Std 15
Std 16
__
C_
FinalVolume
.j_S"- _"_
-"--'-----.
_"
bO
to
_
t:3
Reviewed
/
._ /
.....,
3M ENVIRONMENTAL LABORATORY
E02- f 039
,-_
.,.:I
MULTI-COMPONENT PREPARATION LOG
Book No. 02 002
Page No.
63
52"I
. Oeac,p.o",_,:c"R'_.,2H/_'_ "-_'_A _'P _ so.,e.,t:/4_CH .!
Date Prepared:
_O- _'" C*,_
3M Trace #: TN-A- (_ "_?
i
' _
Prepared By:
_")K_
storage,o=,.,:_,q_,j_.
i
Expiration Date:
H" I :;_"C*-_
Standard.It:)#
i iii
02 002-63 i i i m
"...
%
Component=Standard
'..l
Corrected FinalConcentration
':--
Description
ID #
CPounrti,toyr ExDpiaratetion WVeoilguhmi'oer BalanceID Weight
Tf,_.O
|
ii
,.-
,,,'
:i
C_.Ac_'b
4_ _.PTY
..
C._ Ac;_ Cs ACi,_
_- r.r_
I
'tO _2c_-
t_ _ _o_-, _.2.o3 12.,;kJ,
-, _og-
C_ /_c.;'_ 7__F-c,_5
iO.2CA-o- #u2._ _'.),q'_3 _1._/
:;5 it'-'-' . ,.
4-2.
-_ ...
'
%- r_.,_
'
_=
T,t4?fib 5
_. Tf_
...
o _.
.... '
_vv:,
__- 'c4_i',,._,.o_I,z>_i
>-o2_ -,i
,,,.1,
L:Q,i.il
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-/_ _-c'2
Concentrationof the mix
.
..,_
.
- _,/ "Si0_nature.
"
_
"D_at' a/
Page 159 of 225
, :
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i
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3M ENVIRONMENTAL LABORATQRY E02-1039
Test Control and Reference Substance Log
I Substance trade name TDHA
or reference #
TCR Substance #
TCR-99131-025
I
Substance/chemical
Trldecafluoroheptanolc Acid
TCR #
TCR-267
name:
{Lot/batch #:
PUI07219EU
IRecelved from:
Aldrich
|
I3M #
NA
I
J
IIExpiratJondate:
01/01/2005
I Amount received (wt. or ZS g, 37.1357 g gross wt.
l
VO ):
{Initials:
SRP
[Date:
12/2111999
I
I Number/size of
1130 mL plastic container
[Shipper:.
Courier
]
containers:
I
[Condition:
clear crystals
IMSDS(y/n)
Y'(.) N
1
IRetain
10'._3994_
{Date of Retain
92115/2000
I
i.(_)'ArchivedlSfil_si_ance :N0t_Avaiiabie t
, . ......
. . : :. -: 2 ..;J." .
[Pudty: Records received:
99.5% LAG 4/24101 MSDS KJD 311100
Location of synthesis, fabdcation, or dedvation records:
Std Location/Storage: Molecutar Formula:
Comments
NA
F19, Frozen C6F13COOH Standard has been moved to Freezer 19 in room 347 KJD 06/07/00 Standard was stored at room temperature prior to 06107/00 LAC 12/22/00
Shipping comments: Corrosive, No 3M ID# - must ship ground small quantity sxcepUon (30 mug or less per vial). I.AS 10102/02
Attachment(s)
I,_
L_
ExactCopyof Odglnal Data
Page 160 of 225
_-; i
_..,.. .t
J J
=
L I i
i
i 1 ....
!I?,_i
i;_
I
,
:
JAN 26 2808 89:48 FR ALDRZCH QC
_':" 3M EtT_I_,_Sf_I980RA
TC_,,,_4,,04 E02-I039
CERTIFICATEOF ANALYSIS _--,_,.=_
3H ENVZRONHENTfd_OT'r P_T
PQ NBR:
PRODUCT NUH_ER: 34204.-
LOT NUMBER: O'tRi?EU
PRODUCT N_E_ TRt'_EC._FLUOROHEPT_NQIG ACZI), 99K
FORMULA; G'rHFi30=
FL_HULA WKZGHT: :364.06
_NFR_R1E;D8P_TRUH
PLUORZNK Nf_ GAg LZQUZD _HROMATOGRalH-W _JALZTY P_J'INTROL A_CIEPTC_NE:ED_TE
CONFORH_ TO b'FRUCTURK #=bid_L'AId]>_ A_ ILLUSTRATED tin PAGE 7?BB OF DZTZON ._, VOI.UHE t OF "TIE ALDRZGH LZBRARY OF FT-ZR _PEC11_".
ONF_IRM.5TO 6TRUCTURE,
79._ X
JUNE 1999
ExacCt opoyf0dgfnal
AL1DRtCH CHKM_C_L L'J]CPNCf
,..I._UARY26 _ 2000
_
ch'umis_ helpingohamlscsin n_.searoh& Indusb3t /J-m_C_N_=r_tl_p_=_=_=_=_._._l
b at: 4u__cl Axnm_a,
i_,_mr mu__
_4
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Page 161 of 225
3M ENVIRONMENTALLABORATORY E02-1039
J
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USELOG
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p'ridecafluoroheptanoicAcid
;
_IrDCHRA.99131-025
I
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Date
[
135.9s19g lO.OeSSg J35.a9_g IstandaOrdZO4O-Se
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p _'/..._J" ,,_'.J'"
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Ba,,.,=o,:_ P'/"/
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3M ENVIRONMENTAL
LABORATORY E02-1039
SINGLE COMPONENT PREPARATION LOG
.-' ..... Date: ,?'/_,6:,.
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Book No. Page No.
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3M ENVIRONMENTALLABORATORY E02-1039
""
3M SPECIALTY MATERIALS MANUFACTURING DIVISION ANALYTICAL LABORATORY
To: From:
Lisa Stevenson - (8-5568) - ET&SS - 2-3E-09 Tom Kestner - (3-5633) - SMMD Analytical Lab - 236-2B-11
Request # GID:71638
Subject: Date:
Characterization of TCR-99131-025 by 'H-NMR and '_-NMR Spectroscopy October 30, 2002
SAMPLE DESCRIPTION:
TCR-99131-025, lot PU/07219EU from the Telomer project.
Nominal )roduct = CF3(CFz).-CO2H, where average n = 5 (white solid).
Sample
Spectra#'s
ExperimenDt escriptions
TCR-99131-025
H71638.GID.401
400MHz ID 'H-NMRin a CFClj/acetone-ds_olventmixture+p-HFXcross integration/internasltd.
TCR-99131-025
F71638.GID.401
376 MHzID IgF-NMRin a CFCl3/actone-dso_lventmixture+ p-HFXcross intqFation/intemasltd.
'
TCR-9913!-025 F71638.GID.COSY.502 470MHz2D t_F-NMRCOSY(correlatedspectroscopye)xperimenint a
CFCIv'acetonc-dso_lventmixture.
OBJECTIVE:
This sample was subjected to a combination of IH-NMR and 'gF-NMP,,spectral analyses to determine the purity of the nominal product. Special emphasis was also placed on attempting to identify and quantify any impurity components.
EXPERIMENTAL:
A portion of the sample was accurately weighed, spiked with a known amount of 1,4-bis(trifluoro-
meixthtuylr)ebefnozresnuebse(pq-uHenFtX)a,naalnydsisthbeny NtoMtaIlLly dIin,;itsioallvoednei-ndiamCenFsCio1n3/adleu(1teDr)at4ed00acMetHonze tH(a-cNetMonRe-darn)d s3o7l6venMtHz )gF-NMR spectra were acquired at room temperature using a Varian UNITYplus 400 FT-NMR
spectrometer. A two-dimensional (2D) WF-NMR correlated spectroscopy (COSY) experiment was also acquired using a Varian UNITY INOVA 500 FT-NMR spectrometer to facilitate assignment of tgF signals
associated with various impurity components. This sample preparation method permitted the p-HFX to be
used as either I) a IHftgF-_R.
intemal stamlard to allow the calculation of the absolute weight percent
concentrations of specific components, or 2) a 1H/19F-NM'Rcross integration standard to permit the cross correlation of the relative _H and 19Fsignal intensities for evaluation of the overall sample composition.
RESULTS:
- ".% The tH-NMR and tF-NMR spectral data indicated this sample was a relatively high purity form of the nominal product, CFa(CFz),-COzH, where the average value ofn = 5.05. Small amounts of a few impurity components, including probable isomers, were also assigned. A IH]IgF-NMR cross integration analysis technique was then used to calculate the relative weight percent concentrations of the identified components. The qualitative and quantitatiw," compositional results that were derived from the single trial IH/I'_F-NMR cross integration analysis are summarized below in TABLEd. The relative weight percent concentrations shown in TABLE-1 should be very close to their respective absolute weight percent values
assuming no water was present in the sample. Trace amounts of numerous other unassigned components were also detected in the NMR spectra, but additional work would be needed in an effort to identify or
quantify some of these other components.
ExactCopyof Original
Pagel of 2
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Page 164 of 225
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3M ENVIRONMENTALLABORATORY E02-1039
October 30, 2002
31VSl MMD AnalyticalLab Request # GID:71638 .TCR-99131-025, Lot PU/07219EU: Telomer Project
Copies of the NMR spectra are attached with the paper copy of this report for your reference. If you have any questions about these results, please let me know.
Tom Kestner
: MarkEllefson RickPayfcr RonPurcell WilliRacmagcn
FilReefc_nIcseT:I63_.GID.TCR-L9a9Pt1U3I10-7O22159TEeUlom?erroject.DOC/lO|
TABLE-1
Sample: TCR-99131-025, Lot PU/07219EU from the Telomer project.
OverallCompositionRaelsultbsy II-I/tgF-NMRCrossIntegratiAonnalysis
ComponentStructurtes
IHflgF.NRM
,
Relative Weight% Concentrations
(single trial analysis)
""
CF_(CFz),-CO2H
(where average n = 5.05)
Probable internal branched isomers
CF3(CFz)x-CF(CFa)-(CFz)y-COzH (where x_-0and assume x..+y= 3.05 for calculation purposes)
Probable terminal isopropyl branched isomers (CF3)2-CF-(CF2)n-CO2H
(assume n=3.05 for calculation purposes)
A probable ether/acid as possible
..
O-[CF2CF2-CO2H]2 ....
98.24% 0.87% 0.52% 0.13%
" F F F' o
0.11%
F.A--(--o/ .
Probable
FF
C,H2,+2 saturated aliphatic hydroe_bons and functional aliphatic components, C,H2,+t-X,
--0.11%
where -X can be possible ether and ester functional groups.
_ '....
Possible CF3(CF2),-COzCH3
0.021%
".
(where average n = 5.05)
1. Traceamountsof numerous otherunassignedcomponentswerealsodetectedin the JgF-NMR spectrum.
ExaCctopoyfoaginat
_
Dal_
Page2of2
Page 165 of 225
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3M ENVIRONMENTALLABORATORY E02-1039
Certificate of Analysis
Nominal Product: CF_(CF2),-CO2H,where average n _ 5 Tridecafluoroheptanoic acid
Product Code: TCR.-99131-025, Lot PU/07219EU October 30, 2002
The sample of TCR-99131-025,. Lot PU/07219EU was analyzed using a combination of t9F-NIVIRand
tH-NMR, spectral analysis techniques. The overall qualitative and quantitative compositional results that were derived from these combined analyses are summarized below in TABLE- 1.
TABLE-1
S ample: TCR-99131-025, Lot PU/07219EU
Overall Compositional Results by Combined 19F/IH-NMR Spectral Analyses
'
Component Structures i
UH/19F_NMR
Relative Weight*/, Concentrations
....... ...... CF3(CFz).-CO2H
(sing!_etrial analysis) <98.2%
(where average n = 5.05) "' Probable internal branched isomers
Purity 0.87%
CF3(CF2)x-CF(CF3)-(CF2)),-CO2H
(where x_-Oand assume x+/= 3.05 for calculation purl_oses) Probable terminal isopropyl branched isomers
.... 0.52%
(CF3h-CF-(CF2).-CO2H (assume n=3.05 for calculation purposes) ..
A probable 'e'ther/aeidas possible
O-[CF2CF2-CO2H]2
0.13%
F v F .O. '
0.11%
F_o_
Probable
FF
c.H2.+2 saturated aliphatie hydrocarbons and
_0.11%
_---..
functional aliphatic components, C.H_.+I-X,
where -X can be possible ether and ester functional .groups.
Possible CF3(CF2),-CO2CH3
0.021%
(where average n = 5.05)
1. Traceamountsof numerousotherunassignedcomponentswerealsodetectedm'theNMRspectra.
"=
Tom Kestner
ExactCOpyof Original
r
Page 1 of I
FileReference:Cola TCR-99131-025Lot PU-07219EU.doc
Page 166 of 225
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3M E-ZNWRONMENTAL LABORATORY
E02-1039
Test Control and Reference Substance Log
Substance trade name _r reference # Substance/T:hemical _ame:
Pentadecafluorooctanoic acid Pentadecafluorooctanoic acid
.ot/batch #: :3M #
1210002 I
Expiration date:
Initials: Number/size of containers:
J
I
IOK Jl-t0ml I
amber glass vial
Condition: Retain
_white crystals . t
TCR Substance #
.....
TCR #
TCR-617 TCR-817
Received from:
Oakwood Products
Amount received (wt. or 5g _ol):
Date: Shipper:.
0711912002 Courier
VISDS (y/n) Date of Retain
t Y t. ) N
! (,_ :Aibhived/Substance. Not:/(_ailable"1
... ?_.; :..
.
,, :.... ...'--, . .,.-_:.'__:_;'/:.-
Purity:
99.51%, updated 10130102OK, NMR analysis
Records received:
MSDS
I'ocation of synthesis,' fabdcation, or derivation
records:
Certificate of Analysis I_AS 07/25102 Oakwood products
Std Location/Storage: Molecular Formula:
Comments
Room Tamp, TCR-C01 C8HF1502
Corrosive Solid LAS 07119/02
Shipping comments: No 3M ID# - must ship ground small quantity exception or less per vial). LAS 10102/02
Attachment(s)
L_
TCR-617.pdf
, ..
(30 mL/g
ExactCopyof Original
""
Cwlc _olal!
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Oakvcood Products, Inc. I741 Old Dtmbax l'Load
West Colambia, SC 29172
]rhone I1_03) 739-8800
Fax(803)739-6957
."
CERTIFICATE OF ANALYSIS
Date: XS-ltflo02
Material:
Pentadecaflum'o oc tanoic add
..
Cat.No.:
1319
Cas No.: [335-67-:1]
]Lot No.: 210002
Assay:
97+% by NaOH tilxation
.;:'.-..
.,.'
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Appeaxa_e:
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Melting Point:. 59-61_'C
.:
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Page 168 of 225
3M ENVIRONMENTAL
LABORATORY E02-1039
I
....
entadecafluorooctanoi acid
,
JPentadecafluoroocta nolo acid
I
_CR'617
USE LOG
_-_
J Before
withdrawn
after
or reason for removal)
ID
ID
I withdrawal (mass or vol) withdrawal
1
2
IGBroalsasncWet.INDol1. BalaAnmcent.ID 2 BGarlaonscsewtI/Dvo1l I Purpose (enter standard number I Balance I Balance I Initials I
Date
Ils.._asg Io.oslrg Ils.48eee Istanda0rd2040-45
t914, l"
IRww Ioa/ls/2002
:/i
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:
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*
3M ENVIRONMENTALLABORATORY E02-1039
SINGLE COMPONENT PREPARATION LOG
BooNko.020,0
Page No.
45
.
=,,
Stock Number:. TC_-
_"//
:i
,I
....i .- Weight or Volume
;'"_
U,ed.: _. Ol/-._.2
Concentration or Pudty:
_. _
!!
Corrected Weight:
_),' D_//.S"_ /
B_l__nDo:o. 7 : '7/'
Other Correction
Factors:
/4-//
Solvent and TN-A Number: ,_C_, ' _/.'_/7_,_,--/'_
-/__.2--.'i2
I',:,.:
Final Volume:
5-o I _
,..,
Final Concentration: L2.._":,_,.,, :
StorageLocatlon: 9_2 :/f:.._,[-"-.//2o.,._.,._.,'I
i
i
L'_._
Expiration Date:
_?S'S'_._
ExacCt opyofOriginal
8kjnaturo,
Dato
"
Page 170 of 225
3M ENVIRONMENTALLABORATORY E02-1039
3M SPECIALTY MATERIALS MANUFACTURING DIVISION ANALYTICAL LABORATORY
_::i
t
To___2
Lisa Stevenson - (8-5568) - ET&SS - 2-3E-09
Request # GID:71638
From:
Tom Kestner - (3-5633) - SMMD Analytical Lab - 236-2B-11
Subject: Date:
Characterization of TCR-617 by IH-NMR, 19F-NMR, and LC/MS Analyses October 28, 2002: Updated R,:port - LC/MS Analysis for Impurities
:if_
!
...._ I
i_!:_];-iJ ' ii_ I!':!_ '_ _
i :_
i .?!
SAMPLE DESCRIPTION: TCR-617, lot 210002 from .theTelomer project.
Nominal product = CF3(CF2)r-CO2H, where average n _ 6 (white powder).
Sample
Spectra#'s
ExperimenDt.escriptions
TCR-617 TCR-617
UPDATE:
HT1638.GID.501 500 MHz'H-NMRinaeetone-dsnolvent+p-HFXcrossintesration/internasltd. F71638.GID.501 470MHz t_F-NMRinaeetone-d_solvent+ p-HFXcrossintegration/internasltd.
'
After the initial NMR compositional analysis report was issued to you on 10-24-02, Joel Miller performed a
!
qualitative LC/MS analysis to assist in the assignment of some of the impurity components in the sample of
i
TCR-617. This updated reported summarizes the new information regarding the identifies and
:_t
concentrations for some of the impurity components. You will notice that the tentatively assigned olefin
:
structure from the original report is now replaced with a probable (C6FI30)-CO2H ether acid.
r
OBJECTIVE:
This sample was subjected to a combination of _H-NMR and 19F-NMR spectral analyses to determine the purity of the nominal product. Special emphasis was also placed on attempting to identify and quantify any
i
iinmpthueritayssicgonmmpeonntenotsf. impTuhreitysamcopmlepownaesntasl.so JgoievlenasktoedJotehlatMIiilnlecrorfpoorraatqeuatlhietaqtiuvaelitLaCti/vMe Sinafonramlyastiisonto farossmist
his LC/MS analysis in this updated report.
"'
FT-NMR EXPERIMENTAL:
'i:t .;[ :
_ ....". ; .I
";
A portion of the sample was accurately weighed, spiked with a known amount of 1,4-bis(trifluoromethyl)benzene (p-HFX), and then totally di.,molvedin deuterated acetone (acetone-d6) for subsequent analysis by NMR. A 500 MHz _H-NMR spectrum and a 470 MHz 'gF-NlVlRspectrum were acquired at room temperature using a Varian UNITY INOVA 500 FT-NMR spectrometer. This sample prel_aration method permitted the p-I-I'FXto be used as either 1) a IH/IF-NMR internal standard to allow the calculation of the absolute weight percent concentrations of specific components, or 2) a IH/19F-NMR cross integration standard to permit the cross correlation of the relative tH and 19Fsignal intensities for evaluation of the overall sample composition.
RESULTS:
The combined )H-NMR, 19F-NMR, and LC/MS analyses indicated this sample was a high purity form of the nominal product, CF_(CF2),-COzH, where the average value ofn = 6.02. Small amounts era few impurity components, including probable isomers, were also assigned. A tI-UmF-N'MRcross integration analysis technique was then used to calculate the relative weight percent concentrations of the identified
components. The qualitative and quantitative compositional results that were derived from the combined single trial IH/J'_F-NMR cross integration analysis, and the qualitative LC/MS analysis, are summarized below in TABLE-1. The relative weight percent concentrations shown in TABLE-I should be very close
to their respective absolute weight percent values assuming no water was present in the sample.
PageI of 2
[xa_ Copyof Orfginal
,o_au.o
Initial n,_.
Page 171 of 225
i
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3M ENVIRONMENTALLABORATORY E02-1039
:'i , _
,:i
l :! i : _i !
I
October 28, 2002
3M SMMD Analytical LabRequest # GID:71638 Updated Report - LC/MS Analysis for Impurities in TCRgil7, Lot 210002
RESULTS (cont.):
Trace amounts of a few other unassigned components were also detected in the NMR spectra, but additional work would be needed in an effort to identify or quantify these other components.
Copies of the NMR spectra are attached with the paper copy of this report for your reference. If you have any questions about these updated results, please let me know.
Tom Kestner
c: JRoicekMlPiallyefrcr RonPurcell WilliamReag=n
FileReferencIes;71638.OlO.UlgRla,.t,eudlts_TCR-61271..0.L0o0t2TelomePtrojeeLDO0CI /I
TABLE-1
Sample: TCR-617, Lot 210002 from the Telomer project.
Overall Compositional Results by IH/19F-NMR. Component Structures I
CROSISnte_ation and LC/MS Analyses NMR Relative Weight% Concentrations
......
(single trial measurement)
CF3(CF2)n-CO2H where average n = 6.02 by lgF-NMR.
LC/MS showed n=6 (major), n=5, n--4 (minors). Probable (CFa)2-CF-(CF2)n-CO2H
99.52% 0.39%
assume n----4for calculation pro'po, ses Probable (C6FI30)-CO2H aeyelic ether acid
as possible CF3CF2-O-CF(CF3)-CFzCF2-CO2H
Possible CF3(CFz)x-CF(CF3)-(CF2)y-CO2H where x;_0,y_0 and assume x+y : 4 for calculation purposes
Possible (CF3)3-C-(CF2).-CO.,H
assume
n=3 for calculation
purposes
PossibleC.H:.,2 saturatedaliphatichydrocarbons
1. Traceamountsof otherunassignedcomponeaatwserealsodetectedin theNMR.spectra,
0.057% 0.019% 0.013%
0.0079%
\
-"%.
,i
Page2 of 2
ExactCopyof Original
tel :_ll(,ft..-
_
_a_i--
Page 172 of 225
..=..
3M ENVIRONMENTAL LABORA TORY
:
E02-1039
i
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Certificate of Analysis
Nominal Product: CFj(CF2)n-CO2H, where average n _ 6 Pentadecafluorooctanoic acid
Product Code: TCR-617, Lot 210002 October 28, 2002
Tom Kesmer and Joel Miller
The sample of TCR-617, lot 210002 was analyzed using a combination of 19F-lqM_, IH-NMR, and LC/MS analysis techniques. The overall qualitative and quantitative compositional results that were derivedfromthesecombinedanalyseasre summarizedbelowinTABLE-I.
TABLE-1
Quantitative
Sample: and Qualitative Compositional
Component Structures t
TCR-617,Lot210002 Results by Combined 19F/IH-NMR and LC/MS Analyses
IH/19F__vl_q. Relative Weight% Concentrations
(single triaalnalysis)
CF3(CF2),-CO2H
where average n = 6.02 by IOF-NMR. LC/blS showed n=6 (major), n=5, n=4 (minors).
Probable (CF3)z-CF-(CF2),-CO2H assume n=4 for calculation purposes Probable(C6F,30)-CO2Hacyclic etheracid
as possiblCeF3CF2-O-CF(CF3)-CF2CF2-CO2H PossiblCeF3(CFz)x-CF(CF3)-(CF2)r-CO2H
where x;_0,yea) and assume x+7 = 4 for calculation purposes Possible (CF3)3-C-(CF2)a-CO2H
<99.51% Purity 0.39% 0.057%
0.019% 0.013%
a_surne n=3 or calculation purposes
Possible C.H2.+2 saturated aliphatio hydrocarbons
1. Trace amounts of other unassigned components were also detected in the NMR spectra.
0.0079%
#,
--
Page I of I
File Reference: CofA_TCR-617_Lot 210002.doc
Exa_Copoyf Orfglna)
i_
Oato
Page 173 of 225
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3M ENVIRONMENTALLABORATORY E02-1039
Test Control and Reference Substance Log
!Substancetrade name Heptadecafluorononanoicacid
TCR Substanc#e
TCR-618
or reference# Substance/chemical name:
Heptadecafluorononanoicacid
TCR #
TCR-618
]Lot/batch#:
3M_
Expirationdate:
Initials:
H7588
NA
OK
IReceivedfrom:
I
Amountreceived(wL or Ivo):
IDate:
OakwoodProducts 5g 0711912002
Number/sizeof containers:
1-50ml plasticjar
IShipper:.
I
Courier
Condition:
_hite crystals.
JMSDS(y/n)
Y (.) N
I
Retain
JDateof Retain
I
i(_i,Aichived/Sub'starice_oi:-_vai,i-_.i_
:Purity:
198.02% updated1013010O2 K, NMRanalysis
:Recordsreceived:
MSD$
Locationof synthesis, fabrication,or derivation records:
Certiflcatof Analysis LAS07/25102 Oakwood Products
Std Location/Storage:
( RoomTemp, TCR-C01
MolecularFormula: Comments
IC9HFt702 :Shippingcomments: Corrosivesolid, No3M ID# - must ship groundsmall quantity exception(30 mug or lessper vial). LAS 10102/02
Attachment(s)
_._
TCR-618.pdf
__
ExacCt opoyfOr/g_nal
':: ]
i L
Page 174 of 225
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' :_ '
Oakwood Products,
1741 Oht Dunbar Road _'VesCt t_[uu,.biaS, C29172 ['hone {8t_3)"Dg-SSO0 Fax (803) 730-6957
Ir_c.
CERTIFICATE OF ANALYSIS
:: ""'
Date: 27-Nov-01
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Cat.No.:
2263
CaS No,:
Lot No.:
[375-95-2]
H7568
Assay: 99*% by NaOH titration
.,,,
,,._..-, :
"
' Appearance:
Off-white _olid
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:,::'.:":., Melting Polxtt:
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eptadecafJuorononanoic acid
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_eptadecafluorononanoic acid
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3M ENVIRONMENTALALBORATORY E02-1039
USE LOG
o,.o,,w,.,__on,,.. withdrawal
Balance ID 1
(mass or vol) Balance ID 2
BOwaliathn,dc'reaow|Da,l1',I,,,",,,.v,ro,,,=o,on'e,'sI="",a,,,',_c,o,',,""a,,,a"nor_,',:n"",,=1,,
20.8649g
0.0677g
120.7972g Istandard02o4o.4s
_14 l" IRWW Io511_00Z
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,7,1
_!(i
ExacCt opyof Original
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Page 176 of 225
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3M ENVIRONMENTALLABORATORY
i
E02-1039
7
SINGLE COMPONENT PREPARATION LOG
I
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!
_ookNoo2.o,o
'
Page No.
46
Analyst: #vIJ
i
i
Description:..I1;,,7_ olaf,//,<o..,,,/__.,,.,,;,2..i/.o,<.7,7,.(>"i,si'_,l_-,c,_o,#
:'", L,t
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;
Weight or Volume
Concentration or Purity:
#/_
.5
Corrected Weight:
#/_,, O_dc/#
h:G
FinaVlolume:
! ,_.)'--#;"t
Other Correction Factors"
A//_"
Solvent and TN-A Number:. tlL'/l,'_.,'.,//_-'ll/,-#.l#,__._,2.._._.., .
FinalConcentration:L .2 6 ,_ ,,F,#
ExacCt opyofOriginal
....
Initial Date
Reviewedby:,..._._.%A, c' Signature,
il_/r)_.
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Page 177of 225
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3M ENVIRONMENTALLABORATORY
E02-1039
3M SPECIALTY MATERIALS MANUFACTURING DIVISION ANALYTICAL LABORATORY
To: From:
Lisa Stevenson-(8-5568) - ET&SS- 2-3E-09 Tom Kestner - (3-5633) - SMMD Analytical Lab - 236-2B-l 1
Request # GID:71638
Subiect: Date:
Characterization of TCR-618 by IH-NMR and 19F-NMRSpectroscopy October 28, 2002
SAMPLE DESCRIPTION: TCR-618, lot H7568 fromthe Telomerproject.
Nominal.product = CF3(CF):,-CO2H,where average n _ 7 (white solid).
, Sample
Spectr#a's
ExperimenDtescriptions
TCR-618 H71638.GID.402 400MHzIH-I_MiRnacetone-dso_lven+t p-HFXcrossintegration/intexsntd_. TCR-618 F71638.GID.402/.403376M_Izv_F-NMiRnacetone-ds_olven+t p-HFXcrossintegration/intersntda.l
OBJECTIVE:
t
This sample was subjected to a combinationof IH-NMR and IgF-NMRspectral analysesto determine the purity of the nominal product. Special emph:tsiswas also placedon attemptingto identify and quantify any
impurity components. EXPERIMENTAL:
A portion of the sample was accuratelyweighed, spikedwith a known amountof 1,4-bis(trifiuoromethyl)benzene (p-HFX), and then totallydissolved in deuteratedacetone (acetone-de)for subsequent analysis by NMR. A 400 MHz _H-NMRspectrum and 376 MHz tgF-NMRspectra were acquired at room temperature using a Varian UNTI'Yplus400 FT-NMR spectrometer. This sample preparation method permitted the p-HFX to be used as either 1) a IH/=gF-NMRinternal standard to allowthe calculation of the absolute weight percent concentrationsof specific components,or 2) a 1H/tgF-NMRcross integration standard to permit the cross correlationof therelative IHand 19Fsignal intensitiesfor evaluationof the overall sample composition.
RESULTS:
Thv IH-bTM17,.and 19F-N'DtI_ spectral data indicated this sample was a high purity form ofthe nominal
product, CF3(CF2)a-CO2I-wI,here the average value ofn = 6.953. Small amounts of a few impurity components were also assigned. A II-I/I_F-NMRcross integration analysistechnique was then used to
calculate the relative weight percentconcentrationsof the identifiedcomponents. The qualitative and quantitative compositional results that were derived from the single trial H/19F-NMRcross integration analysis are summarized below in TABLE-1. The relative weight percent concentrations shown in -". TAB LE-1should be very close to their respective absolute weight percent values assuming no water was present in the sanaple. Trace amounts of a few other unassigned componentswere also detected in the NMR spectra, but additional work would be needed in an effort to identifyor quantify these other components.
Copies of the NMR spectra are attachedwith the paper copy of this report for your reference. If you have any questions about these results, please let me know.
ExacCt opyofOriginal.
Page 1 of 2
_
l_ats
Page 178 of 225
!?! I
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' __ : ',,,,)_,_ .... '::_I _:_) :]
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October 28, 2002
3M ENVIRONMENTALLABORATORY E02-1039
".. 3M SMMD Analytical Lab Request # GID:71638 TCR-618, Lot I-I7568:Telorner Project
Tom Kestner
e: RickPayfer RonPurcell WilliamReagen
Fil,R":ferencIes:TI6311.GID.TCR-1611785_6LT8oetlomPerrojectDOC./100
TABLE-1
Sample: TCR-618, Lot H7568 from the Telomer project.
Overall Compositional Results by tI-I/19F-NMRCross Intesration Analysis
Component Structures t
NMR Relative Weight% Concentrations
(single trial measurement)
CF3(CF2),-CO2H
where averase n = 6.955 Probable H-(CF2)a-CO2H
assume n = 8 for calculation purposes
Probable CF3(CF2)n-CO2CH3 where average n = 6.955 A probable cyclic ether F O "C'F4
98.02% 1.10% 0.65% 0.20%
F
F
as possible F t_ or similar
Total inorganic fluoride (at least 3-t_pes), including some possible HF
Possible C,H2n+2saturated aliphatie hydrocarbons
0.021% 0.014%
1. Traceamountsof othermmssignedcomponentws er,e alsodetectedintheNMRspectra.
Page 2 of2
ExactCopyof 0 rigihal -._)_C_ lo/.L._.O-L."
blit[al Date
Page 179 of 225
3M ENVIRONMENTALLABORATORY E02-1039
:i
i i ._i
, _
!
!_ ': i
i_
,:! .... J
Certificate of Analysis
Nominal Product: CFa(CF2)a-CO2H,where average n _ 7 Heptadecafluorononaaoic acid
Product Code: TCR-618, Lot H7568 October 28, 2002 Tom Kestner
The sample of TCR-618, lot H7568 was analyzed using a combination of 19F-NMR and IH-NMR spectral analysis techniques. The overall qualitative and quantitative compositional results that were derived from these combined analyses ate summarized below in TABLE-1.
TABLE-1
,
Sample: TCR-618, Lot H756g
Quantitative Compositional Results by Combined 19F/tH-NMR Spectral Analyses
Component Structures '
'H/19F.NM R
Relative Weight% Concentrations
(sinl_le trial anal)sis)
CFa(CF2),-CO2H
where average n = 6.955 Probable H-(CF2),-CO2H
assume n = 8 for calculation purposes
Probable CFa(CF2)n-CO2CH3
where average n = 6.955
A probable cyclic ether
F0 F F
"C4F9 F
F
<98.02% Purity 1.10%
0.65%
0.20%
as possible F F orsimilar
Total inorganic fluoride (at least 3-type:Q,
0.021%
ineludin_ some possible H-F
Probable C, H2,+2 saturated aliphatic hydrocarbons
0.014%
,.
1. Trace amountsof otherunassignedcomponentws erealsodetectedintheNMRspeclra.
ExactCopyof Original
Pagel of I
FileReference:CofA_TCR-618_LoHt7568.doe
Page 180 of 225
i!
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I
3M ENVIRONMENTAL LABORATORY E02-1039
Test Controland ReferenceSubstanceLog
Substance trade name or reference #
Substance/chemical name:
_lonadecafluorodecanolc acid Nonadecafluorodacanolc acid
TCR Substance # TCR #
SD036 TCR-36
Lot/batch #: 3M #
IR11 K ]10#2284
jRecelved from: I
IOakwood Products Inc 4/2/99
I
I
I
Expiration date: niUals:
Number/size of containers:
12/0112010 IJCP
111120mL plastic bottle i
voAmunrte)c:eived (wt.or 25g,43.3264 g gross wt.
I
jDate:
104/27/1999
I
I JShipper:
N/A
,
I
Condition:
Jwhlte solid MCH 07122J99
JMSDS (y/n)
Jg Y _..) N
J
Retain
j0.1874g
[Date of Retain
11011811999
I
"(:')/_rchived)_ubstance Noti:Avaif_,_le_j
Purity:
198.01%,updated t0/30102 OK NMR analysis
I
Records received:
IMSDS,Certificate of Analysis
I
oc,ooolu,.,on.o o.s I fabrication, or derivation
ecords:
iStd Location/Storage:
JF19, Frozen
I
Molecular Formula:
I C9F19COOH
I
Comments
TN-A-2451 prior to 4/27199 JCP 04/27199
Standard ha,= been moved to Freezer 19 In room 347 KJD 06/06/00
Standard was stored at room temperature prior to 06/06100. LAC 12/19/00
Attachment(s)
_
sd036msds.pdsf d036cofa.pdf
EXaCt Copy of Original .
Iiddai Oats
Page 181 of 225
.... =
_,_ i!,,<!
i
'..,._.j.. ,, ,_ i ;-,_
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3M ENVIRONMENTALLABORATORY E02-1039
3M SPECIALTY MATERIALS MANUFACTURING DIVISION ANALYTICAL LABORATORY
To: From:
Lisa Stevenson - (8-5568) - ET&SS - 2-3E-09 Tom Kestner - (3-5633) - SMMD Analytical Lab - 236-2B- 1!
Request # GID:71638
Subiect: Date:
Characterization of SD036 by tH-NMR and tgF-NMR Spectroscopy October 28, 2002
SAMPLE DESCRIPTION:
SD036, lot R1 IK from the Telomer project.
Nominal product = CF3(CF2),-CO2H, where average n _ 8 (white powder).
Sample
Spectra #'$
ExperimentDescriptiom
SD036 SD036
H71638.GID.403 400 MHztH-NMRin aeetone-d_solvent+ p-HFXcrossintegration/imernn/std. F71638.GID.404 376 MHz "F-NMRinacetone-d,solvent+p-HFXcrossintegration/internasltd.
OBJECTIVE:
This sample was subjected to a combination of tH-NMR and _gF-NMR spectral analyses to determine the purity of the nominal product. Special emphasis was also placed on attempting to identify and quantify any impurity components.
EXPERIMENTAL:
A portion of the sample was accurately weighed, spiked with a known amount of 1,4-bis(tfifluoro- ' methyl)benzene (p-HFX), and then totally dissolved in deuterated acetone (acetone-d6) for subsequent analysis by NMR. A 400 MHz JH-NMR spectrum and a 376 MHz 19F-NMR spectrum were acquired at room temperature using a Varian UNITYplu_ 400 FT-NMR spectrometer. This sample preparation method permitted the p-HFX to be used as either 1) a IH/_gF-NMR internal standard to allow the calculation of the
absolute weight percent concentrations of specific components, or 2) a IH/tgF-NMR cross integration standard to permit the cross correlation of the relative tH and 19Fsignal intensities for evaluation of the overall sample composition.
RESULTS: The II"I-F_,fRand 19F-N'M'Rspectral data indicated thls sample was a relatively high purity form of the
nominal product, CF3(CF2)n-CO2H, where the average value ofn = 7.85. Small amounts of a few impurity
components, including probable isomers, were also assigned. A tH/tgF-Nl_fl_,cross integration analysis technique was then used to calculate the relative weight percent concentrations of the identified components. The qualitative and quantitative compositional results that were derived from the single trial
,
IH/19F-NMR cross integration analysis are summarized below in TABLE-1. The relative weight percent
-'" concentrations shown in TABLE-1 should be very close to their respective absolute weight percent values
assuming no water was present in the sample. Trace amounts era numerous other unassigned components were also detected in the IF-NMR spectrum, but additional work would be needed in an effort to identify
or quantify some of these other components.
Copies of the NMR spectra are attached with the paper copy of this report tbr your reference. any questions about these results, please let me know.
If you have ExactCopyof Original
Page l of 2
Page 182 of 225
'!
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3M ENVIRONMENTAL LABORATORY
E02-1039
October 28, 2002
3M SMMD Analytical Lab Request # GID:71638
SD036,LotRI 1K:TelomerProject
Tom Kestner
c: RRoicnkPPuarycfeelrl
William Rcagen
I=il Reference:
Is71638.GID.SD036_Lot
RI I K..Tclomer
PmjccLI:X3C/I
OI
TABLE-I Sample: SD036, Lot R11K from the Telomerproject.
Overall CompositionalR.esu!tsby 1I-I/19F-NMCRr.oss Integration Analysis
Component Structures t
NMR Relative Weight% Concentrations
(single trial measurement)
CF3(CF2).-CO2H where avera[[en = 7.85
98.01%
,
Probable CF3(CF2)x-CF(CF3)-(CF2)y-CO2H
wherex_0 andassumex+y = 5.85for calculationpurposes
Probable (CF3)z-CF-(CF2)n-CO.,H
assume n=5.85 for calculationpurposes
Probable
1.41% 0.36% 0.12%
F
F
F I
assume n=3.85 Pfororbcaablcleulationpo urposes
F
II
F
FF
0.060%
FF
B
F CF OH
assume n=2.85 for calculationpurposes
Probable CnI-Iln+2 saturated aliphatie b7dmcaxbons
Total inorganicfluoride
0,026%
_0.0095%
1. Trace amounts of numerous otherunassigned components were also detected in the J'JF-NMRspectnm_
,'
ExacCt opyof Original
J
Page 2 of 2
Page 183 of 225
Ot::_KWIP3R0D013UCTS Fax:803-?39-6957
Feb3_ EZ_(_oN,_'m- LAe_"_",,R,_Y
-I
:,.]
...'.
i.' I
,., _
,!?'
_,
,_i
17_ Old _b_ bad
WestColumbia,$C 2g_l._.
i,i,.ot_(sos)
(_
Oa3_ood l'roduets,Inc.
CERTIFICATE OF ANALYSIS
Date: 11-Feb-00 Material: Nonadec_luorodecanoi add Cas No.: [335-76-2] Lot No.: RI::I..K
Ashy:
Products mare volatile than I'etfluorodecanoi,' aJcd <1%
Per1uomdet_onlc acid
98/orain.
Products less volatile _an Perfluo_decanoic acid
<1%
Appea_anc_
White solid
Melting Point= 83-85"C
EXacCt opyofOdglnal
_
i_Lm..
Page 185 of 225
3M E'hlVlRONMENTALLABORATORY E02-1039
I
USE LOG
]
" ";
_lonadecafluorodecanoicacid
,',
' __SoDna0d36acafluorodacanoicacid
I
Before
withdrawn
after
orreasonforremoval)
IO
withdrawal (massor vol) withdrawal
2
Balance D 1 BalanceID 2 BalanceID 1
J33.9944g ]0;:i'19Sg
J33.8784g ]standard02022.90
J914 J.
[RWW [07102/2002
I
t
,
ExacCt opyof 0dginal
N
Page 186 of 225
'",_I
_,=,:,
i..i
3M ENVIRONMENTALLABORA TORY
E02-1039
Date:
,Z..
,_,,=ys_. ,/,_j _
SINGLECOMPONENTPREPARATIONLOG
De..,,,o,.P F/J._ _ /_, /L
BookNo. 02 022
F',_eNo. 90
sto=.u.,be_. ,.5/) d3_
Weight orVolume Used:,.
f'_/,_
Concentrationor
BalanceID:
_/_-/
Other Corre_on
_!t
..... Co.,,_e,_W/e__Ig.,_D_'I
Solventand TN-A
Number./_I,-,_/,Zx.,,z.-..,_#-,,_z.
."
Final Volume: .
/_.
/
,,o,._,,o. =,o,z.:.jF/_.,,
!
:_,_.i
...:..
Final Concentration:
/Z_/_ ," .tt'_
_,,,,,o,o,,,.,. /_/D,_
ExacCt opyofOriginal InJr/el Date
U S_nature,
/1
Date
Page 187 of 225
!i:'I
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3M ENVIRONMENTAL LABORA TORY E02-1039
Test Controland ReferenceSubstanceLog
Substance trade name =erfluoroundecanoic acid
TCR Substance #
TCR-619
or reference #
Substance/chemical name:
Perfluoroundacanoic acid
TCR #
TCR-619
Lot/batch #:. 3M #
JU11N JNA
Received from:
Oakwood products
I
I
Expiration date:
_1
vol):Amruencteived (wt. or 5 g
I
Initials:
IOK
Dale:
107119/2002
I
I Ncounmtabienre/srisz:e of
1-10ml amber glass vial
Shipper:.
IjCourier
I
Condition:
Iwhits crystals.
MSDS (y/n)
I(ID Y (..) N
'1
Retain
I
Date of Retain
I
I
! .("_ArchivedlSubstanc:e,'i_0At;vaiiab'lei:J
Purity: Records received:
Location of synthesis, fabrication, or derivation records:
Std Location/Storage: Molecular Formula: Comments
I >99% LAS 07125/02 MSDS Certificate of Analysis
Oakwood products
I,AS 07/25102
I Room Tamp, TCR-C01 I C11HF2102
Shipping comments: Harmful solid, No 3M ID# - must ship ground '(30 mug or less per vial). LAS t0/02/02
small
quantity
exception
Attachment(s)
L_
TCR-619.pdf
Exact Copy of Orlgl_
Page 188 of 225
3M ENVIRONMENTALLABORATORY E02-1039
j
".,
3M SPECIALTY MATERIALS MANUFACTURING DIVISION ANALYTICAL LABORATORY
:I
,,
To:
Lisa Stevenson - (8-5568) - ET&SS - 2-3E-09
Request # GID:71638
From:
Tom Kestner - (3-5633) - SMMD Analytical Lab - 236-2B-I 1
S,ubject: Date:
Characterization of TCR-619 by IH-NMR and 19F-NMR Spectroscopy October 29, 2002
SAMPLE DESCRIPTION:
TCR-619, lot U11N from the Telomer project.
Nominal product = CF3(CF2),-CO2H, where average n = 9 (white powder).
i
s .a.mple
Spectra#'s
..
ExperimenDt escriptions
i
TCR-619 H71638.GID.404 400 MHzJH-NlVlRin acetone-drsolvent+ p-H.FXcrossintegration/internasltd.
TCR-619
F71638.GID.405 376 MHzJgF.NMRin aectone-d_solvent+ p-HFXcrossintegration/internasltd.
OBJECTIVE:
This sample was subjected to a combination of IH-NMR and 19F-NMRspectral analyses to determine the purity of the nominal product. Special emphasis was also placed on attempting to identify and quantify any impurity components.
EXPERIMENTAL:
A portion of the sample was accurately weighed, spiked with a known amount of 1,4-bis(trifluoro-
methyl)benzene (p-HFX), and then totally dissolved in deuterated acetone (acetone-dr) for subsequent
analysis by NMR.. A 400 MHz IH-NMR spectrum and a 376 MHz WF-NMR spectrum were acquired at
room temperature using a Varian UN1TYplus 400 FT-NMR spectrometer. This sample preparation method
permitted the p-HFX to be used as either 1) a tH/19F-NMR intemal standard to allow the calculation of the
_t
absolute weight percent concentrations of specific components, or 2) a II-I/I_F-NMR cross integration
standard to permit the cross correlation of the relative IH and 19Fsignal intensities for evaluation of the
overall sample composition.
_i_
RESULTS:
The
IH-N'IvIR
and
19F-.-"q'IWII_
spectral
data
indicated
this
sample
was
a relatively
high
purJt-y
forna
o the
nominal product, CF3(CF2),-CO2H, where the average value ofn = 8.63. Small amounts of a few impurity components, including probable isomers, were also assigned. A II-/./t9F-NMR cross integration analysis technique was then used to calculate the relative weight percent concentrations of the identified components. The qualitative and quantitative compositional results that were derived from the single trial _ ]H/19F-NMR cross integration analysis are summarized below in TABLE-1. The relative weight percent "" concentrations shown in TABLE-I should be very close to their respective absolute weight percent values
assuming no water was present in the sample. Trace amounts of numerous other unassigned components were also detected in the 19F-NMR spectrum, but additional work would be needed in an effort to identify
or quantify some of these other components.
Copies of the NMR spectra are attached with the paper copy of this report for your reference. If you have any questions about these results, please let me know.
-
ExactCopyof Or/g_nal
Pagel of 2
lnlUal
Page 189 of 225
,
i-?-.i_ I
fJ
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!=i,i_ i! i=.! -1
i_] !i:_
3M ENVIRONMENTAL
LABORA TORY
E02-1039
October 29, 2002
3M SMMD Analytical Lab Request # GID:71638 TCR-619. Lot U11N: Telomer Project
Tom Kestner
e: Mark EIIcfson Rick Payfer Ron Purcell
William Reagen
Fil Reference: 1571638.GID.TCR-619_Lot
U 11N.. Tdomcr Project.DOE/I OI
TABLE-1 Sample: TCR-619. Lot U11N from the Telomer project. Overall Compositional Results by IH/tgF-NMR Cross Inte[_ration Analysis
Component Structures'
NMR R(esliantgilvee trWiael igmheta*s/u, reCmoenncte)ntrations
CF3(CF2),-CO2H
96.4%
,
(where average n = 8.63)
Probable internal branched isonzers
2.6%
CF3(CF2)x-CF(CFj)-(CF2)c-CO_H . (where x;e0 and assume x+y = 6,63 for calculation purposes).
Probable trans-olefins of general form: trans-CF3(CF2)x-CF=CF-(CF2)y-CO2H
0.89%
(assume x+y = 6.63 for caleulat!on pl .U'l_.OS)eS Possible terminal isopropyl branched isomers
(CF3_z-CF-(CFz),-CO2H (assume n=6.63 for calculation purposes)
0.12%
Probable C.H2,.2 saturated aliphatic hydrocarbons Total inorganic fluoride
0,032% >0.0017%
1. Trace amounts of numerous other unassigned components were al_o detected in the 'gF-NMR spectna_
Page 2 of 2
ExacCt opyof 0riginal Page 190 of 225
3M _NVlRONMENTAL LABORATORY
,,
E02-1039
i:i
,_,_! i
i
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..... ii
ii
i_J _
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i] _:;
!?_,_'_
',_;_ !_
(:_
i,L..
i >
tLJ
Certificate of Analysis
Nominal Product: CF3(CF2)n-COzH,where average n _ 9
Perfluoroundccanaociicd Product Code: TCR-619, Lot UI 1N
October 29, 2002
The sampleofTCR-619, lotUIIN wasanalyzeudsinga combinatioonfZgF-NMR and IH-NMR _cctral analysitsechniquesT.he overalqlualitati,vaenqduantitaticvoempositionraelsulttshatwerederivefdrom thesecombinedanalyseasresummarizedbelowinTABLE-I.
TABLE-1
Sample: TCR-619, Lot U1 IN
,
OverallCompositionaRlesultbsy Combined19FInH-NMRSpectraAlnalyses
Component Structures i
II.{/19F.NIk/IR "
Relative Weight% Concentrations
(sinGle trial analysis)
. CF3(CF2).-CO2H
(where average n = 8.63) Probable internal branched isomers
CF3(CFz)x-CF( CF3)-(CF2)y-CO2H (where x_0 and assume x+y = 6.63 for calculation purposes)
Probable trans-olefins of general form:
trans-CF3(CF2)x-CF=CF-(CF2)y-CO2H (assume x+y = 6.63 for calculation purposes) Possible terminal isopropyl branched isomers
<96.4% Purity 2.6%
0.89%
0.12%
(assume (nC=F63.6)23-CfoFr-(CcaFlc2u)l.-aCtioOn2Hpurposes)
Probable C.I'-I2.+2 saturated aliphatie hydrocarbons
O.O32O/Jo'"
"'
Total inorganic fluoride
>_0.0017%
1. Trace amounts of numerous other unassigned components were also detected in ttm '9F-NMK speettl, lrcL,
-,,. Tom Kestner
ExactCopyof Original
oate
Page 1 of I
File Ref:rence: CofA_TCR-619_Lot UI IN.doe
Page 191 of 225
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OaLkwoodProducts, Inc.
1741 Old Dunbar Road
West Columbia, SC 29172
Phone(803)7"39-8800
:.
Fax(8031739-6957
CERTIFICATE OF ANALYSIS
Da{e: 15-Jui-02
..
Material:
Perfluoroundecanoic acid
:
Cat.No.:
2265
'
Cas Na.: Lot No.:
[4234-73-5] UIlN
Assay: 99+%by NaOH titration
Appeaxance;
_hlte
solid
Melting Point: 92-98_C
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Page 192 of 225
3M ENVIRONMENTALLABORATORY
', '
E02-1039
USE LOG
J
......
l_erfluoroundecanoicacid
;
PrCeRrf-l6u1o9roundecanolcacid
I
-_
I Before
withdrawn
after
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withdrawal (massorvol) withdrawal
I BalanceIO 1 BalanceID 2 BalanceID 1
J15.S264g 10.0691g
]15.4573g _standard02040-65
[914 I"
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3M ENVIRONMENTALlABORATORY E02-1039
Data: Analyst"
SINGLE COMPONENT PREPARATION LOG
2..-
/__
.
RookNo. 02 040
Description: ft'e//..,,-b/.t.J/.,.,c
._;J
)I
Weight or Volume
"
Used:
<_ _'* _,_ ..
BalanceIO:
._ I C/
Concentrationor purity:
__,, /,//4
o_ecr o=aeon Faro,,: ,_ ,d-
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ExpirationDate: ,_ ___/OJ_
,
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'
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Page 194 of 225
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3M ENVIRONMENTALLABORATORY
E02-1039
Test Controland ReferenceSubstanceLog
Substancetradename orreference#
Substance/chemical name:
ILoUbatch#:
13M#
Perfluorododecanoicacid
Perfluorododecanoiacid
R24K [D#2266
TCR Substance# TCR # Receivedfrom:
SD037 TCR-37 OakwoodProducts Inc 4/2/99
'Expirationdate: Jlnitials: Number/sizeof containers: ICondition: IRetain
12/01/2010 JCP II120 mL plasticbottle
white powder MCH07/22/99 ).2159g
vol):Amreucnetived(wt.or 25g, 43.4548 g gross wlL
Date:
04/2711999
Shipper:.
NIA
MSDS (y/n) Dateof Retain
lid y (._)N 1011811999
J_; .)!Ar cfiiVed/Subs{a:nceiN0t.Available_l
Purity:
99.65% updated 1013010O2 K, NMRanalysis
Recordsreceived:
MSDS,Certificateof Analysis
Locationof synthesis,
Unknown
'
fabrication,or derivation records:
Std Location/Storage:
iF19, Frozen
MCoomlemcuelnatrFsormula:
CTNl 1-AF.2234C5O3 pOrHiorto 4/27/99 JCP 04/27/99 Standardhas been movedto Freezer19 in room 347 KJD 06/06/00 Standardwas storedat room temperaturepriorto 06/06/00. LAC 12/19100
Shippingcomments: Irritant, no shipping information- ship as small quantity exception. LAS 10102/02
Attachment(s)
_ sd037msds.pdf
_ sd037cofa.pdf
L_ NMR SD037.pdf
;_i...,
ExacCt opyof Original
_
Da_
Page 195 of 225
3M ENVIRONMENTALLABORATORY E02-1039
_,_ i
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3M SPECIALTY MATERIALS MANUFACTURING DIVISION ANALYTICAL LABORATORY
To:
Lisa Stevenson - (8-5568) - ET&SS - 2-3E-09
Request # GID:71638
From:
Tom Kestner - (3-5633) - SMMD Analytical Lab - 236-2B-11
Subieet: Date:
Characterization of SD037 by tH-NMR and tgF-NMR Spectroscopy October 28, 2002
SAMPLE DESCRIPTION: SD-037, lot R24K from the Telomerproject.
Nominal product = CF3(CF2),-CO2H, where avera[e n = 10 (white powder).
I Samples
Spectra#'s
ExperimenDt escriptions
SD037 SD037
HT1638.GID.405 400 MHz'H-NMRin aeetone--dsnolvent+p-HFXcrossintel]xation/internsatld. F71638.GID.406 376MHz 19F-NM_ in acetone-dosolvent+ p-HFXcrossintegration/internasltd.
OBJECTIVE:
This sample was subjected to a combination of tH-NMR and tgF-NMP,,spectral analyses to determine the purity of the nominal product. Special emp.hasis was also placed on attempting to identify and quantify any impurity components.
EXPERIMENTAL:
A portion of the sample was accurately weighed, spiked with a known amount of 1,4-bis(trifluoromethyl)benzene (p-HFX), and then totally di,;solved in deuterated acetone (acetone-dr) for subsequent
analysis by NMR. A 400 MHz _H-NMR spectrum and a 376 MHz 19F-NMR spectrum were acquired at room temperature using a Varian UNITYplus 400 FT-NMR spectrometer. This sample preparation method
permitted the p-HFX to be used as either 1) a IH]IgF-NMR internal standard to allow the calculation of the absolute weight percent concentrations of specific components, or 2) a tH/tgF-NMR cross integration standard to permit the cross correlation of the relative IH and 19Fsignal intensities for evaluation of the overall sample composition.
RESULTS: The |H-N'MR and 19F-N1MIR spectral data indicated this sample was a high purity form of the nominal product, CF3(CF2)a-C02H, where the averag0 value ofn = 10.042. Small amounts of a few impurity components, including probable isomers, were also assigned. A tH/t 9F-NI_L-Rcr.oss integration analysis technique was then used to calculate the relative weight percent concentrations of the identified components. The qualitative and quantitative compositional results that were derived from the single trial _.-.. _H/_'_F-NMRcross integration analysis are summarized below in TABLEd. The relative weight percent concentrations shown in TABLEd should be very close to their respective absolute weight percent values assuming no water was present in the sample. Trace amounts of a few other unassigned components were also detected in the NMR spectra, but additional work would be needed in an effort to identify or quantify these other components.
Copies of the NMR spectra are attached with the paper copy of this report for your reference. If you have any questions about these results, please let rae know.
ExactCopyof Odg[nal
Page1 of 2
Dat.a
Page 196 of 225
3M ENVIRONMENTALLABORATORY E02-1039
_
October 28, 2002
3M SMMD Analytical Lab Request # GID:71638 SD037, Lot R24K: Telomer Project
'_
Tom Kestner
e: RickPayfer Ron PurcEll WilliamRezgen
FileRcfenmceb:71638.GID.SDO37.R_I2._4KTlomcPrrajeetDOCllOI
TABLE-1
Sample: SD037, Lot R24K from the Telomer project.
Overall Compositional Results by 1I-{/19F-NMRCross Integration Analysis
Component Structures i
NMR Relative Weight% Concentrations
...i.,.
(single trial measurement)
':ii
CF3(CF2)n-CO2H
99.65%
where average n = 10.02
"_
Probable (CF3)2-CF=(CFz)n-CO2H
O.13%
'I
.;
assume n=8 for calculation purposes
Possible CF3(CFz)x-CF(CF_)-(CF2)y-COzH
0.088%
:
where x_0, _t-_0and assume x+y = 8 for calculation purposes
Probable chlorinated impurity, CI-CF2CF2-Rt;
0.049%
possibly as CI-(CF2)II-CO2H Possible methyl ester impurity as
0.048%
CF3(CF2)n-CO2CH3
where average n = 10.02
Probable C.H2.+2 saturated aliphatie hydrocarbons
0.016%
iii'
1. Trace amounts of other unasTsiognlueednceomponents werealso detected in the NMR spectra. 0.015%
t
ExactCopyofOriginal
Page 2 of 2
Page 197 of 225
3M ENVIRONMENTALLABORATORY E02-1039
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C erti [icateo fA na lysis
Nominal Product: CF_(CF2).-CO2H, where average- n _ 10 perfluorododecanaociicd
ProductCode:SD037,LotR24K October28,2002 Tom Kestner
The sample of SD037, lot R24K was analyzed using a combination of 19F-NMR and IH-NMR spectral analysis techniques. The overall qualitative and quantitative compositional results that were derived from these combined analyses are summarized below in TABLE-1.
TABLE-1
'
Sample: SD037, LotR24K
Quantitative Compositional Results by Combined 19F/tH-NMR Spectral Analyses
Component Structures _
_H/19F-NMR
Relative Weight% Concentrations
(single trial analysis)
CF3(CP2),-CO2H whereaveragen = 10.02 Probable(CF3)2-CF-(CFz),-CO2H
assumen=8 forcalculatipounrposes Possible CF3(CF_)x-CF(CFj)-(CF2):CO2H where x;t0, y_0 and assume x+y = 8 for calculation
purposes Probable chlorinated impurity, CI-CF2CF2-Rf,
possibly as CI-(CF2)H-CO2H Possible methyl ester impurity as
CF'_(CF2)n-COzCH3
<99.65% Purity 0.13%
0.088%
0.049% 0.048%
where averase n = 10.02 Probable C,,H2,+2saturated aliphatic hydrocarbons
0.016%
Toluene
1
0.015%
1. Trace amountsof otherunassignedcomponentswerealsodetectedin theNMRspectra.
%.
ExactCopyof0rfg[nal
Page I of I
FileReference:CofA_SD037_LoRt24K.doc
Page 198 of 225
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OAKWOOPDRODUCTS Fax:803-739--6957
Feb _/t I_JRON_I_ri'AL
I...AfJ_'t_TORY
_
Oa]_vood]Pxod_ts, Inc.
17_1OldDunba_ Road West Columbia, $C 29172
Phont (S0_)739-eeoo Fax(8o3)_39-_957
CERTIFICATE OF ANALYSIS
Dat_ 11-FeIMJ0
i
Materia]: Perflaorododecanoic add
J
i
Cat.No.: 2266
"
Lot No.: Assay:
R22K
J
Products more volatile than Ferfluorododecanoic acid < 2%
Feffluorododecar_ acid
196%rain.
l_roducts less volatile than Peffluorododecanoic acid' <2%
Appearance:
WRite solid
Melting Point: 107-I09C
!
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ExacCt opoyfOriginal
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Page 199 of 225
3M dNVlRONMENTAL LABORATORY E02-I039
:
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useLOQ
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_erfluorododecanoicacid
...:._!
_I$eDrf0lu3o7 rododecanolc acid
1
I j Before
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:
IGBraolsasnWcetI.DNo1l. I BalAanmcnetI.D 2 IGBroaslasnwcte/IvDol1l
Pulpose(enterstandardnumber
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142.5752g 10.0796g '' 142.4956g. tstandard02040-55
_914 _.
IRVVw .,,108/29/2002
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Page 200 of 225
3M ENVIRONMENTALLABORATORY E02-1039
Analyst: //4_A,_
Page No. 55
StockNumber:. _",/_ _.J_
.. i
Weight orVoluma
_._'
Used:
_ _:p,..,r"_,,_'_
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BalanceIO:
_/q
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Page 201 of 225
.
3M ENVIRONMENTAL
LABORATORY
E02.1039
i
Test Control and Reference Substance Log
Substance trade name PFOS
TCR Substance #
SD018
:i or reference #
'
Substance/chemical
Potassium Perfluorooctane
I"CR #
rCR-18
name:
Sulfonate FC-95
Lot/batch #:
217
IReceived from:
lugDickes 8/10198
I
3M # date: 98-0211-0888-S
I,,morouonto(w,vo,eI.Ir'd"O.Oo'rOo'.g
II
VO ):
I
I
Initials:
PMR
IDate:
104107/1999
I
containers:Nuomfber/size t/175 mL glass container
ijShipper:
!lUnknwn
I
ICondition:
white powder MCH-07122/99
IMSDS (y/n)
_ll Y (.) N
I
Retain
0.1733g
tDate of Retain
110118/1999
1
/_i
?::' '
i i _'
-
("_ ArchivedlSubstance NotA_ailable_J
Pudty:
86.9% LAG 09119100
IRecords received: I
NMR Results/Charectedzation #53030, MSDS KJD 02/29100 Interim final report from Centre and Certificate of Analysis. LAG 04126/01
[Location of synthesis, Ifabfication, or derivation Irecords:
98-0211-0888-5
_Std LocatJonlStorage: Molecular Formula:
Comments
F19, Frozen C8F17SO3-K+
Environmental Lab Traceablitity numberwas TN-A-2130 PMR 04/07199
Moved to cold storage (< OC) on 05116/00 LAC 05116/00 Standard has been moved to Freezer 19 in room 347 KJD 06/06100
Standard was stored at room temperature prior to 05116100. LAC 12/19/00 Shipping Codes: FC-S000-0185-6(<30 g on dry Ice) LAC 06/14101 Shipping Comments: Dangerous goods in excepted quantity of Class 6, UN281t.
REGULATED-TOXIC 98-0211-0888-5 (>30. g (1 oz sample)) Not on dry ice. LAG 01/08/02
sdO18msds.pdf sdO18nmrreq53030.pdf sdO18nrnrreq61517.p(
,v:,,_,
E00-1682-COA-SD018-PFOS-Rev3
ExactCopyof Original
Page 202 of 225
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3M ENVIRONMENTALLABORATORY E02-1039
_lkV._'_'_k'_mli. '_P'O_'_ll=._Phone:
Cntr Analgtical Laboratories, Inc.
3048 ResearchDrive State College, PA 16801
www.centrelab.com
(814)231-8032
Fax:(814) 231-1253 or (814) 231-1580
INTERIM CERTIFICATE OF ANAL YSIS
Revision 3
Centre Analytical Laboratories COA Reference 3M Product: PFOS, Lot 217 Reference #: SD-018
#: 023-018A
Test Name Purity I
Purity: 86.9%
Specifications
i
i
Result 86.9%
Appearance Identification
NMR
Metals (ICPfMS) I. Calcium
2. Magnesium 3. Sodium 4. Potassium 2
White Crystalline Powder'
Conforms
Positive
I.O.O05wt./wt.% 2. 0.001 wtJwt.% 3. 1.439wtJwt.% 4. 6.849wt./wt.%
5. Nickel 6. Iron
7. Manganese Total % Impurity (NMR) Total % Impurity (LC/MS) Total % Impurity (GC/MS) Related CompoundsPOAA
Residual Solvents (TGA).
56.. <O0..O00015wwt.t/.w/wt.t%.% 7. <0.00lwt./wt.%
1.91 wt./wt.% 8.41 wt./wt.%
None Detected
0.33 wt./wt.% None Detected
PInuorirtgyanbicy DASniCons (IC) 1. Chloride 2. Fluoride 3. Bromide 4. Nitrate
5. Nitrite 6. Phosphate 7. Sulfate 4 Organic Acids _(IC)
Not Applicable _ 1. <O.O15 wt./wt.% 2. 0.59 wt./wt.% 3. <0.040wtJwt.% 4. <O.O09wtJwt.%
5. <0.006wt./wt.% 6. <0.007 wt./wt.% 7. 8.76 wt./wt.%
2. PFPA
3I. THFFABA 4. NFPA
Elemental Analysis*: 1. Carbon 2. Hydrogen 3. Nitrogen 4. Sulfur 5. Fluorine
1. Theoretical Value = 17.8% 2. Theoretical Value = 0% 3. Theoretical Value = 0% 4. Theoretical Value = 5.95% 5. Theoretical Value = 60%
2. <0.1 wt./wt.% 31.. <0.01.01wwt./tw./wt.%t.% 4. 0.28wt./wt.%
l. 12.48 wt./wt.% 2. 0.244 wt./wt.% 3. 1.74 wt./wt.% 4. 8.84 wt./wt.% 5. 54.1 wtJwt.%
__ =_ v, " o
u__ _l
COA023-018A
Page I of 3
Page 203 of 225
"L'."
3M ENVIRONMENTALLABORATORY i E02-1039
...i.:
_la_k_'_i_
Centre Analgtical Laboratories, Inc.
3048 Research Drive
State College, PA 16801
www.centrelab.com
'_e'O"_._Phone:
(814)231-8032
Fax:(814)231-1253or(814)231-1580
,'_
INTERIM CERTIFICATE OF ANAL YSIS
"_i
Revision 3
Centre Analytical Laboratories COA Reference #: 023-018A
Date of Last Analysis: 08/31/00
Expiration Date: 08/31/06
Storage Conditions: Frozen _<-10C
._
Re-assessment Date: 08/31/06
. _,_
IPurity = 100% - (sum of metal impurities, 1.45%+LC/MS impurities,8.41%+Inorganic
i
Fluoride, 0.59%+NMR impurities, 1.905%+organic acid impurities, 0.38%+POAA,
0.33%)
Total impurity from all tests = 13.07%
Purity = 100%- 13.07% = 86.9%
2potassium is expected in this salt form and is therefore not considered an impurity.
3Purity by DSC is generally not applicable to materials of low purity. No endotherm was
_
observed for this sample.
4Sulfur in the sample appears to be converted to SO4 and hence detected using the inorganic anion method conditions. The anion result agrees well with the sulfur
determination in the elemental analysis, lending confidence to this interpretation. Based
on the results, the S04 is not considered an impurity.
.,,
I-IFBA
Heptafluorobutyric acid
NFPA
Nonafluoropentanoic acid
PFPA
Pentafluoropropanoic acid
6Theoretical value calculations based on the empirical formula, CsFt7SO_'K+(MW=538)
__
;
Tlfis work was conducted under EPA Good Laboratory Practice Standards (40 CFR 160).
:ii
COA023-018A
Page 2 of 3
Page 204 of 225
'
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3M ENVIRONMENTALLABORATORY E02- f 039
CEntPGAnalytical Laboratories, Inc.
k ' 3048 Research Drive
State College, PA 16801
www.centrelab.com
hone: (814) 231-8032
Fax: (814) 231-1253 or {814) 231-1580
INTERIM CER TIFICA TE OF ANAL }'SIS
Revision 3
Centre Analytical Laboratories COA Reference #: 023-018A
LC/MS Purity Profile:
Impurity C4 C5 C6 C7
Total
wt./wt. % 1.22 1.33 4.72 1.14
8.41
Note: The C4 and C6 values were calculated using the C4 and C6 standard calibration
curveu, respectively. The C5 value was calculated using the average result from the C4
and C6 standard curves. Likewise, the C7 value was calculated using the average result from the C6 and C8 standard curves.
Prepared By:
/o _,/o/
_
Charles SimO_
D
"_
,
Scientist, CentreAnalytical Laboratories
._.
o
,
Reviewed By:/_hn Flaherty
/
Date
Laboratory Manager, Centre Analytical Laboratories
COA023-018A
Page 3 of 3
Page 205 of 225
3M ENVIRONMENTAL LABORATORY E02-1039
J
USELOG
FOS
....]
Fotasslum Perfluorooctane Sulfonate FC-95
-_i
_SD018
Before
withdrawn
after
or reason for removal)
withdrawal (mass or vol) withdrawal
BraolasnscWet.INOol1. I BalaAnmcneLIO 2 I BGarolasnscweUIDvo1l I Purpose (enter standard number I Bal_nce I Ball_nce J Initials I
Date
I
1140.44eOg [0.0814g [140.36680 Istandar0d2022-56
]914
I"
[RWW 10,5/13/2002 I
i
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21
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Page 206 of 225
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3M ENVIRONMENTAL LABORATORY E02-1039
Date: Analyst:
SINGLE COMPONENTPREPARATIONLOG
,_., #(_112A)
pp >J .s'b<.g
Book _o. 02 022
Page No.
56
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StockNumber. ,.5/) 0/_
u,=t: Weight orVolume /__..o_
Concentratioonr
Pu_s:. El, 9 _
CorrectedWeigh_
_"_,
J_ r,,,=
#"
B=,..Ico.: ?/
OtherCorrection
Factora/:), 92 7J-
Solvent aNndumTbNe-rA. /6_? _,ff/._'A/,;-A -_OZoJ'J/
FinalVolume:_ _-0_-. /
:. ;j
:,;
Slorage Location:
/i_ / _,
',]
RmllConcentration: l _DI./_',_/_,, ......
ExplmUon Date:
( [k3/_
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ExactCo_yof Original Initial Dats
5_r_llum;
Dil
Page 207 of 225
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ATTACHMENET: PROTOCOL AND AMENDMENT
3M ENVIRONMENTALLABORATORY E02-1039
:_: :21
Page 208 of 225
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3M ENVIRONMENTALLABORATORY
E02-1039
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STUDY PROTOCOL
STUDY TITLE Analysisof EndogcalouFsluomchcmicailns NormalPooledHumanSerumandPlasma
SPONSOR William K, Reagen,Ph.D
DATA REQUIREMENT 4.0CFRPart792
TESTING FACILITY 3M EnBvuirioldnimngen2-t3aElL-a0b9oratory
935 Bush Avenue
St Paul, MN 55106 LABORATORYSTUDY IDENTIFICATION 3M Environmental StudyNumber E02-1039
NUMBER OF PAGES 10
ExacCt opyofOdginal
Page 209 of 225
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Anatyslso( EndogenousRuotochemicaltt
3M ENVIRONMENTAL
LABORATORY
E02-1039
E02-1039
STUDY IDENTIFICATION Analysis of Endogenous Fluorochemieals in Normal Pooled Human Serum and Plasma
SPONSOR Srt1_rDh_CrOR TEst FAazdza,
William Reagen, Ph.D. 3M Environmental Laboratory 935 Bush Avenue, Building 2-3E-09 St. Paul, MN 55106 (651)778-6565
Mark E. Ellefson 3M Environmental Laboratory 935 Bush Avenue, Building 2-3E-09 St.Paul,MN 55106 (651)778-5405
3M Environmental Laboratory 935 Bush Avenue, Building 2-3E-09 St. Paul, MN 55106
Experimental StarDtate
10 October 2002
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Experimental Termination Date
01 November 2002
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AnalysoisfEndogenoFulsuoroctlemicale
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1.0 Introduction and Purpose/Objective
1.1 The purpose of this study is to quantify perflunrohexanoic acid (C6), perfluoroheptanoic acid (C7), pentadecafluorooctanoic acid (C8), heptadecafluorononanoic acid (C9), nonadecafluorodecanoic acid (CI 0), perfluorodecanoic acid (CI 1), perfluorododecanoic acid (C12), tetrahydroperfluorooctan sulfonate (THPFOS), tetrahydroperfluorodecane sulfonate (THPFDS), and perfluorooctanesutfonate (PFOS) in normal pooled human serum and plasma. This study does not have a typical test substance that is dosed onto a specific controlled test system as per a conventional GLP study.
2.0 Regulatory Compliance
2.1 This study will be conducted in accordance with the United States Environmental Protection Agency Good Laboratory Practice Regulations for the Toxic
i]
Substances Control Act, 40 CFR 792.
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3.0 Test Substances
3. l Preliminary screening indicates that the test compounds listed below are present
as endogenous material in normal pooled human serum and plasma. Information
pertaining to traceability, source, physical description, and storage conditions is
not available for these compounds as they exist in biological matrices.
_,:_
Test Substances
Tee!Substance
,:_,
PerfluorohexanAocicid
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TetradecafluoroheptAancliodc
PentadecafluorooctaAncoiidc
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HeptadecafluotononaAncoidlc NonadecafluorodecaAncoidlc
PerfluoroundecaAncoildc PerfluomdodecaAnocid
1H,2H,3H4,H-perfluorooctanesulfonate
1H,2H.3H.4H-per_uomdescualnfoenata
i
PotassiumPerfluorooctanesulfonata
Formula
CsF.COOH
,,
CaFI=COOH CTF_=COOH C=F_rCOOH CoFI_=CGOH
CloF_tCOOH CuFz=COOH
C=H=FI=O=S C_oH=F_IO=S C=F_TSO_'K
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4.0 Reference Substances
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Reference Substances
SRuebfesrteannccee
For.mula
Trace#ability
Source
Perfluorohexanoic Acid
Tet dec no,
heptanioc AcJd
Pentadecafluom octanoic Ar.Jd
Heptadecafluoro nonanoic AcJd
C=F_ICOOH TCR-047
SMM* 236-1B-10
c,,COOH TCR-267
,,,,,
C_FnCOOH TCR-617
Oakwood Products
C.F_K_OOH TCR-618
Oakwood Products
NdoencaadneocicafAlucoidro
C_._COOH
TCR-038
OParokdwuocotds
Perfluomun decanoic Acid
C,_=_COOH TCR-619
Oakwood Products
dPecearfnluooicroAdcoid
1H,2H,3H,4Hperfluorooctane
sulfonate
Ct_Fz._COOH
,,,,
TCR-037
,, ,
C=%FI=O=S TCR-343
OParkowduocotds
SynQuest Labs
1H,2H,3H,4Hperfluorodecene
sulfonate
C_0H=F_70=S TCR-627
Pace Analytical
Potassium Perfluomoctane
sulfonate
C,F_SO='K
*Documcatution
of the method ofsynthc_is
TCR-018
SMM* 236-1B-10
hi located at the source.
DPehscyrsipictaiol n ,, J,,,,, Colorless Liquid iear Crystals
White Crystals
White Crystals
White Solid
Purity TBD**
99.5% 97% > 99% 98%
White Crystals PWowhidteer
,,
> 99% 96%
White Powder
TBD
White Crystals
White Powder
94.7% 86,9%
CSontodriatigoens Frozen
Frozen Ambient Temperature Ambient Temperature Frozen Ambient Temperature Frozen
Frozen
Ambient Temperature
Frozen
**A sample of the reference substance ha=been sent for characterization
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5.0 Test System
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Test Systems
Pooled Human Serum
Sigma-Aldrich, Milwaukee, WI
TCR-689
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Pooled Human Serum
Lampire Biological Laboratories,
TCR-688
::
Pipersville, PA
Peered Human Serum
Bioresource Technology, Inc., Fort
TCR-687
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Lauderdale, FL
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Pooled Human Serum
CA
TCR-690
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3M Environment_Laboratory
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Analysis of Endo_genous Fluorochemical.s
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PooledHumanPlasma PooledHumanPlasma
LampireBiologicaLlaboratories, PipersviUeP,A
GoldenWestBioCloAgicalsT,emecula,
PooledHumanPlasma _ InnovativRe eseaMrIchI,nc.iSouthleld,
PooledHumanPlasma
CentralChina
TCR-685 TCR-684 TCR-683 TCR-674
5.1 Justification of the test system. Based on preliminary testing, normal pooled serumand plasma contain endogenous levels of thetest analytes.
5.2 Identification of Test System, Samples shall be identified by the study number, date of initial preparation, test substance or test system, sanaple number, replicate number (if applicable), analyst(s), and project leader.
6.0 Surrogate Matrix Surrogate Matrix
RabbitSerum J Sigma-Aldrich
TCR-686
6.1 Justification of the Surrogate Matrix. Based on preliminary testing, normal
pisoothleedrebryabsbuititasebrluemforcounsteaianss avseuryrrologwateemndaotrgixen. ous levels of the test analytes and
6.2 Induemntbifeirc,atidoante oof finSuitriarol gpareteparMataiotrnix, . tesStasmupblsetsanschealolrbseuirdroegnatitfeiedmabtryixt,hesasmtupdlye number, replicate number (if applicable), analyst(s), and project le'ader.
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7.0 Analytical Methods
7.1 Analysis of the test and reference substances will be conducted in the 3M Environmental Laboratory. The analyses will be conducted as described by 3M
Environmental Laboratory Method ETS-8-231, "Solid Phase Extraction and
Analysis of Fluorochemical Compounds from Biological matrices",
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Analysis of Endogenous Fluorochemicals
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8.0 Data Quality Objectives
8. I Absolute Recovery:
8. I. I
The absolute recovery of the method will be evaluated separately in human serum and plasma and rat serum. For each matrix, the samples will be fortified at two levels of(500ppt and 5ppb). All samples will be
extracted through the method, and analyzed by comparison with external calibration of non-extracted standards. The non-extracted standard
calibraticounrveswillbe prepareidnmethanola,ndwillconsisotf a minimum ofnine(9)levelsi,ncludinagmethanolblank.The best appropriarteegressiwoinllbe usedtodescribtheis curve(forbest accuracyatalllevelosfthestandards).
8.1.2 The accurac(y% recoverya)ndprecisio(n%CV oftherecoveriewsi)llbe deterrninactdeachlevela,ndforalllevelcsombined.Thereisno control
limiftoraccuracyp;recisiomnustbebettetrhan15% ateachlevel.
8.2 CalibratioCna:libraticounrveswillbepreparefdromextractemdatrixstandards, inChineseplasmaandrabbisterum.The curveswillconsisotfaminimum of nine(9)levelasnda matrixblank.The equatiownillbe determinebdy regression analysiussingthepeakareasoftheanalyteT.he accuracoyfeachlevelwillbe vcrificdA.ny leveloutsid7e5% -125% ofnominalmustbe deactivateadn,d regressiorne-calculateexdc,epttheLLOQ whichmustbe within30% ofnominal. Alllevelmsustshow a responsgereatetrhantwicethatoftheblank.A maximum of four (4) levels may be deactivated in any one set, or the set will be re-analyzed.
8.3 Limits of Quantitation (LOQ): The lower limit of quantitation (LLOQ) will be determined for each analyte. The level determined as the LLOQ must show a
recovery within 75% - 125% for the analytes and must show a response greater
than twice that of the blank. These limits will be determined during the course of the study and documented in the raw data. Should the LLOQ level calibration be de-activated in a particular set, the practical limit of quantitation for this set will be raised to the next acceptable level. Samples below the practical LOQ of that set will be reanalyzed until quantitated in a set including the validated LLOQ.
The upper limit ofquantitation (ULOQ) will be determined in serum and plasma. The level determined as the ULOQ must show a recovery within 75% - 125% for the analytes. These limits will be determined during the course of the study and documented in the raw data. Should the ULOQ level calibration standard be deactivated in a particular set, the practical limit of quantitation for this set will be lowered to the next highest acceptable level.
Arty sample with an area greater than 110% of the highest acceptable standard
will need to be diluted into the range of the calibration curve. If samples are diluted into the range of the curve during analyses and enough sample remains, a post-ran dilution validation will be performed to verify sample values. To
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perform the dilution validation, one sample will be separated into two representative samples (i.e. two I mL aliquots for fluid samples or two I gram amounts for tissue samples) then diluted using two procedures. The first procedure consists of diluting the sample with additional matrix prior to extraction (sere adding sera), while the second procedure consists of diluting the extract with solvent post-extraction (methanol extract adding additional methanol solvent).
If the values are not within 15% of each other additional testing will be required to determine which value is a correct representation of the sample concentration.
8.4 Use o f Confirmatory. Methods
Confirmatory methods are typica!ly not needed with LC/MSIMS analysis.
8.5 Demonstration of Specificity 8.5.1 The identification ofanalytes will be substantiated by chromatographic retention time, by the characteristic primary ion, the characteristic product ion, and isomeric proportions (where applicable).
7.6 Controi of Bias
Two levels of matrix fortifications, prepared at known concentrations of the test substance and bracketing the anticipated range of the method will be evaluated to determine recovery and to evaluate method pcrformance. P.eagent and matrix blanks will be run with each set to evaluate the level of background interferences.
9.0 Statistical Methods and Calculations
9. l Statistical methods for the analytical results will be limited to the calculations of means, standard deviations, and relative standard deviations (as appropriate).
10.0 Report
A report of the results of the study will be prepared by 3M Environmental Laboratory.
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The report will include, but not be limited to, the following, when applicable:
10.1.1 Name and address of the facilities performing the study, 10.1.2 Dates upon which the study was initiated and completed. 10.1.3 A statement of compl:iance by the Study Director addressing any
exceptions to Good Laboratory Practice Standards. 10.I.4 A copy of the protocol, and any amendments and deviations. 10.1.5 A description of the methods used to conduct the test(s). The report will
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contain updated methods incorporating any changes or improvements.
10.1.6 A description of the test system.
10.1.7 A description of any circumstances that may have affected the quality or the integrity of the data.
10.1.8 The name of the Study Director and the names of other scientists, professionals, and supervisory personnel involved in the study.
10.1.9 A description of the transformations, calculations, or operations performed on the data, a summary and analysis of the analytical chemistry data, and a statement of the conclusions drawn from the analy ses.
10.I. 10Statistical methods used to evaluate the data, if applicable.
I 0. I. IIThe signed and dated reports of each of the individual scientists or other professionals involved in the study, if applicable.
10.1.12The location where raw data and the final report are to be, stored.
10.1.13A statement prepared by the quality assurance unit listing the dates that study inspections and audits were made and the dates of any findings reported to the Study Director and Management.
10.2 If it is necessary to make corrections or additions to a final report after it has been accepted, the changes will be made in the form of an amendment issuedby the Study Director. The amendment will clearly identify the part of the final report that is being amended, provide the reasons for the amendment, and will be signed by the Study Director.
11.0 Quality Assurance
11.1 The 3M Environmental Laboratory Quality Assurance Unit will review the protocol and audit study conduct, data, and the final report to determine
compliance with Good Laboratory Practice Standards and with 3M
Environmental Laboratory Standard Operating Procedures. The Quality Assurance Unit will report all findings to the Sponsor Representative and the Study Director.
t2.0 Location of Raw Data, Records, and Final Report
12.1 Original data or copies thereof, will be available at 3M Environmental Laboratory. When the final report is completed all original paper data, including those items listed below, will be retained in the archives of 3M Environmental
Laboratory following signing of the final report.
12.2 The following raw data and records will be retained in the study folder in the archives according to 3M Environmental Laboratory SOPs.
12.2. I Approved protocol and amendments
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12.2.2 Study correspondence 12.2.3 Shipping records 12.2.4 Raw data 12.2.5 Approved final report (original signed copy) 12.2.6 Electronic copies of data 12.3 The following supporting records will be retained separately from the study folder in the archives according to 3M Environmental Laboratory SOPs: 12.3.1 Training records 12.3.2 Calibration records 12.3.3 Instrument maintenance logs 12.3.4 Standard operating procedures, equipment procedures, and methods
t3.0 Sample Retention
13.1 A portion of the reference substances used in the study will be retained in the laboratory for a period ofnot less than 2 years after a report is issued.
13.2 Sample extracts will be retained and refrigerated for a period of not less than three months from the time of analysis.
14.0 Protocol Amendments and Deviations
14.1 Amendments and deviations to the protocol will be in the form of written amendments signed by the Study Director and the Sponsor Representative. Amendments will be considered as part of the protocol and will be attached to the final protocol. All changes to the protocol will be indicated in the final report. Any other changes will be in the form of written deviations, signed by the Study
raw
Director and filed with the data. 15.0 Attachments
None
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Protocol Signature
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Mar_:E (Eliefso_n
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3MEnvironmentalLa_tory
0_. Date:
Protocol Approval
Sponsor.
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WilliamtC Reagen,Ph.D.
3M EnvironmentaLl aboratory
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3M Envlronmenl_lLaboratow
Date:
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3M ENVIRONMENTALLABORATORY
E02-I039
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Study Title
Analysisof EndogenouFsluorochemicailns NormalPooledHumanSerumandPlasma
PROTOCOLAMENDMENTNO. 1
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Amendment Date:
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Performhlg Laboratory
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3M En,lironmentalLaborato_,
Building2-3E-09
935 Bush Avenue
St. P_ml,MN 55144-1000
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Laboratory Pro]ect Identification 3M EnvironmentalLaboratoryStudyLIMS#E02-1039
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Protocol #E00-1311 Amendment 1
This amendmentmodifies the following portion(s)of the protocol:
1. PROTOCOLREADSS: ECTION8.1.I: Theabsoluterecoveryof themethodwill beevaluatedseparatelym human serum and plasma and ratserum. For each matrix,the samples will be fortified attwo levels of(500ppt and 5ppb). All samples will be extracted throughthe method, and analyzed by comparisonwith externalcalibration of nonextracted standards. The non-extractedstandardcalibration curveswill be prepared in methanol, andwill consist of a n_nimum of nine (9) levels, including a methanol blank. The best appropriateregression will be used to describe this curve (for best accuracy at all levels of the standards).
AMEND TO READ:The absolute recovery of the method will not be evaluated as the matrixeffects render this type of comparison limited in its usefukm, ss.
REASOn: A planned change in the stady's direction.
2. PROTOCOLREADS:SECTION8.2: Calibration:Cal_ration curves will be preparedfTomextracted matrix standards, in Chinese plasma and rabbitserum. The curves will consist era minimum of nine (9) levels and a matrix blank. AMENDTO READ:Calibration: Cal_ration cu.,_,eswill be preparedfrom extra, tedmatrix standardsin Chinese plasma. The curves will comist of a minimum of nine (9) levels. Reasons fornot using one or more of these standards in the construction of a calibrationcurve are up to the discretionof theanalystand will he documented in the raw data.
REASON:The samples were run against 9 extracted standards withouta blank, but not all of these standards were used to construct the curve. Additionally rabbit curves were not included in the data forthis study.
3. PROTOCOLREADS:SECTION7.1: Analysisof the test and reference substances will be conducted in the 3M
Enviromncntal Laboratory. The analyses will be conducted as described by 3M EnvironmentalLaboratory'Method ET8-8-23I,"SoliPdhaseExtractiaonndAnalysiosfFluorochemicCaolmpoundsfromBiologicmaaltrices".
AMENDTOREAD:Analysis of the test and referencesubstances will be conducted in the 3M Enviromnental
Laboratory.
The analyses
will be conducted
as described
by 3M Environmental
Laboratory
Method ETS-8-231.
"Solid Phase Extraction and Analysis of Fluorochemical Compounds fromBiological matrices". Selected ion
monitoring will bc used to detect the prcscnc_of the targetanalytes. The masses scannedwill be documented in the raw data and in the final report.
REASON:Add clarity.
%,
4 PROTOCOL READ.S:SECTION8_.A.nysamplewithanareagreatetrhan1i0% ofthehighesatcceptable standarwdillneedtobediluteidnttoh,r_a"ngeofthecalibratciuornveI.fsampleasrediluteidntotherange
ofthecur',d'u,rinagnalyseasndenoughsampleremainsa,post-rudnilutivoanlidatiwoinllbeperformetdo verify sample values. To perform the dilution validation, one sample will be separated into two representatsiavmeples(i.et.woI mL aliquotfsorfluisdampleosrtwoI gramamountsfortissuseamples) thendiluteudsingtwoprocedureTsh.,:firsptrocedurceonsisotfsdilutitnhgesamplewithadditional matrix prior to extraction (scra adding scra), while the second procedureconsists of diluting the extract with solvent post-extraction (methanol extract adding additional methanol solvem). If the values are not within 15%of each other additional testing will be required to determine which value is a correct representation of the sample concentration.
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Protocol #E00-1311 Amendment 1
AMEND TO RF.AD: Any sample with an area greater than 110% of the highest acceptable standard will be reported as >ULOQ.
REASON: The purpose of this study is to demonstrate the presence of the target analytes in pooled human serum and plasma. It is more important to show that endogenous Icvels are detectable than to show specifically what those levels are.
5. PROTOCOl. READS: SECTION1.1 The purpose of this study is to quantify perfluorohexanoic acid (C6), perfluoroheptanoic acid (C7), pentadccafluorooctanoic acid (C8), heptadecafluorononanoic acid (C9), nonadecafluorodecanoic acid (C10), perfluorodecanoic acid (CI 1), perfluorododecanoic acid (C 12), tetrahydroperflunrooctano sulfonate (THPFOS), tetrahydroperfluorodecane sulfonate (THPFDS), and
perfluorooctanesulonat (PFOS) in normal pooled human serum and plasma. This study does not have a typical teat substance that is dosed onto a specific controlled test system as per a conventional GLP study.
AMEND TO READ: The purpose of this study is to quantify pexfluoroheptanoic acid (C']), pcatadecafluorooctanoic
acid (C8), heptadecafluorononanoic acid (C9), nonadecafluorodecanoic acid (CI0), perfluorodecanoio acid (el 1),
,
perfluorododecanoic acid (CI 2), tetrahydroperfluorooctane sulfonate (THPFOS), tetrahydroperfluorodecane
sulfonate (THPFDS), and perfluorooctancsulfonate (PFOS) in normal pooled human serum and plasma. This study
does not have a typical test substance that is dosed onto a specific controlled test system as per a conventional GLP
stud'.'
IIEASON:.Thc C6 compound was eliminated from the study.
6. PROTOCOLREADS: SECTION3.1
Test Substances
Test Substance Perfluo rohexanoic Acid
Pentadecafluorooctanolc Acid Tetradecafluoroheptanloc Acid Heptadecafluorononanoic Acid
Nonadecafluorodecanoic Acid
ii
PerfluoroundecanoicAcid
Perfluorododecanotc Acid
-
1H.2H.3H.4H-perfluorooctanesulfonate
""
1H.2H.3H,4H-perfiuorodecane sulfonate
Potassium Perfluorooctanesulfonate
AMRNI) TO READ:
Test Substances Test Substance
Tetradecafluoroheptanioc Acid
PentadecafluoroocAtacnidoic
3M Environmental Laboratory
Formula CsFt1COOH
CIFtsCOOH Co, FtaCOOH CeFoCOOH C#toCOOH Ct0FzICOOH CuFz=COOH
CaHsFnOaS CmHsF_70_S C_FtTSO3"K"
Formula
C_FlaCOOH
CIFnCOOH
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Heptadecafluorenonanoic Acid Nonadecafluorodecanoic Acid
Perfluoroundecanoic Acid Perfluomdodecanoic Acid 1H,2H,3H,4H-perfluomoctanesulfonate 1H,2H,3H,4H.perl]uorodecane sulfonate Potassium Perfluomoctanesulfonate REASON: The C6 compound was efimL,mted from the study.
3MENVIROnmENLtAABLO_rOm"
E02-1039
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Protocol #E00-1311
Amendment
1
CBF_TCOOH CoF_COOH C_oF2_COOH C.F=_COOH CeHsF_30_S C_oH_tTO_S C=Ft_SOzK
7. PROTOCOL READS: SECTION 4.0
Reference Substances
RSuefbesretannccee
,
,,
Perflu_,rohexanoic Acid
Formula CsFtlCOOH
Traceability #
TCR-047
' Tetradecafluoro heptantcc Acid
CaF_3COOH TCR-267
Pentadecafluoro octanoic Acid
C1FtsCOOH TCR-617
Heptadecafluoro nonanoic Acid
CaFITCOOH TCR-618
NdoencaadneocicafAlucoidro
CgFI=COOH TCR-036
Source SMM* 236-1B-10 Aldrich Oakwood Products Oakwood Products OParokdwuocotds
Physical Descdptlon
i,
Colorless Liquid Clear
Crystals White
Crystals White
Crystals
White Solid
Purity
,,
TBD'"
Storage Conditions
Frozen
99.5%
Frozen
97%
Ambient Temperature
Ambient
> 99% Temperature
I
=
98%
Frozen
Perflucroun decanoic Acid
CtoFalCOOH
TCR-619
Oakwood
, I Products
White Crystals
99%
Ambient Temperature
dPecearfnluooicroAdcoid
1 H,2H,3H,4H-
perfsluuolfroonoactteane
1H,2H,3H,4Hpedsluuolfroondaetceane
Potassium Perftuorooctane
sulfonate AI_I END TO READ
Ct_F=3COOH TCR-037 CaHsF_O=S TCR-343 CloHd=lTO_S TCR-627 CsF_zSO3"K* TCR-018
OParokd'wuocotsd
SynQuest
Labs
Pace Analytical
SMM* 236-1B-10
PWohwidteer
White
Powder
96% TBD
White Crystals
White Powder
94.7% 86.9%
Frozen Frozen Ambient Temperature
Frozen
Reference Substances
Reference Substance
Formula
Tetradecafluoro heptanioc Acid
C6FI_(_OOH"
Pentadecafluoro octanoic Acid
CtF,_COOH
Traceability #
'TCR-267
TCR-617
Source
Aldrich .,
Oakwood Products
Physical Description
Purity
Clear
99.5%
Crystals ....
White Crystals
97%
Storage Conditions
Frozen .
Ambient Temperature
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3M ENVIRONMENTAL
LABORATORY E02-1039
Protocol #E00-1311 Amendment 1
Pentadecafluero octanoic Acid
Heptadecafluoro nonanoic Acid
NdoencaadneociacflAucoimd Perfluoroun
decanolc Acid Perfluorodo
decancic Acid
CtFlsCOOH
TCR-617
CoF17COOH
ml,
CeFI=COOH
TCR-618 TCR-036
C_oF=ICOOH TCR-619
ClIF_COOH
"rCR-037
Oakwood Products
Oakwood Products
OPraokdwuocotsd Oakwood Products Oakwood Products
White Crystals
White Crystals
White Solid
White Crystals White Powder
> 97% 99% 98%
99% 96%
Ambient Temperature
Ambierlt Temperature
Frozen
i
Ambient Temperature
Frozen
1H,2H,3H,4Hperfluorooctane
sulfonate
"' 1H,2H,3H,4H-
C_sF_=O=S TCR-343
SynQuest Labs
Pace
While Powder
While
TBD
Frozen Ambient
perfluorodecane sulfonate
CloHsFtTO_S TCR-627
Analytical
Crystals
94.7% Temperature
'
Potassium
SMM"
White
Perfluorooctane sulfonate
CeFITSO='K TCR-018 _36-1B-10
Powder
86.9%
Frozen
RE,_St)N: The C6 corn )omzd was criminated from the study.
8, PROTOCOl, READS: SECTION 6.0
Surrogate Matrix
Rabbit Serum
I
Sigma-Aldrich
TCR-686
6.4
Justification of the Surrogate Matrix. Based on preliminary testing, normal pooled rabbit serum contains
6.5
vIdeernytifliocwatioenndogeonfoSuusrrolgeavteels oMfattrhiex.tesSt aamnapllyetsesshaanldl ibsethideernetbiyfiesduitbaybltehefostruudsye nausmabseurr,rodgaatete omf aintritiixa.l
preparation, test substance or surrogate matrix, sample number, replicate number (if applicable), analyst(s),
and project reader.
,AMENI) TO READ: None REASON: Itwas decidednottouserabbitserum curvestogeneratedataforthisstudy.
9. PROTOCOl. READS: SECTION 8.3 Limits of Quantitation (LOQ): The lower limit of quantitation (LLOQ) will be determined for each analyte. The level determined as the LLOQ must show a recovery within 75% - 125% for the
analytes and must show a response greater than twice that of the blank.
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3M ENVIRONMENTALLABORATORY E02-1039
Protocol #E00-1311 Amendment 1
A_ _ TO READ: Limits 0f Quantitation (LOQ}: The lower limit of quantitation (LLOQ) will be determined for each analyte. The level determined as the LLOQ must show a recovery within 70% - 130% for the analytes.
R_,_SON: Since this is a screening-type study it was appropriate to relax the acceptable recovery levels in order to avoid re-running sample sets.
Amendment Approval
WilliamK. Reagen, Sl:onsorRepresentative
Date
/
Mar/cE. Ell@on. Study Director
Date
i
f
i %,
'i
:,._] 'd
3M Environmental Laboratory
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Protocol E02-1039 Amendment #2
Study Title Analysis of Endogenous Fluorochemicals in Normal Pooled Human Serum and Plasma
PROTOCOL AMENDMENT NO. 2
Amendment Date: 6 December, 2002
Performing Laboratory 3M Environmental Technology & Safety Services
3M Environmental Laboratory 935 Bush Avenue
St. Paul, MN 55106
This amendment
Laboratory Project Identification ET&SS E02-1039
modifies the following portion(s)
of the protocol:
PAGE 3, SECTION 1.1, PROTOCOL READS: The purpose of this study is.to quantify, perfluoroheptanoicacid (C7), pentadecafluorooctanoic acid (C8), heptadecafluorononanoic acid (C9), nonadecafluorodecanoic acid (C10), perfluorodecanoic acid (C1 l), perfluorododecanoic acid (C12), tetrahydroperfluorooctane sulfonate (THPFOS), tetrahydroperfluorodecane sulfonate (THPFDS), and perfluorooctanesulfonate (PFOS) in normal pooled human serum and plasma. This study does not have a typical test substance that is dosed onto a specific controlled test system as per a conventional GLP study.
AMEND TOREAD: The purpose of this study is to quantify perfluoroheptanoic acid (C7), pentadecafluorooctanoic acid (Clq), heptadecafluorononanoic acid (C9), nonadecafluorodecanoic acid (C 10), perfluorodecanoic acid (C 11), perfluorododecanoic acid (C12), and perfluorooctanesulfonate (PFOS) in normal pooled human serum and plasma. This study does not have a typical test substance that is dosed onto a specific controlled test system as per a conventional GLP study.
REASON: THPFOS and THPFDS were removed from the list of analytes in the revised report because the data was intended as quantitative and only screening estimates could be obtained. In addition, THPFOS and THPFDS were removed from the list of test substances, section 3.0, page 3 and the list of reference substances, section 4.0, page 4.
Amendment Approval
William K. Reagen, Sponsor Representative
Date
Mark E. Ellefson, Study Director
/'"
/
Date
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