Document jyRBQBOpvDOGy4e7194v7LDON
3M Medical Department Study: T6316.1
3M Medical Department Study: T-6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
Study Title
104-Week Dietary Carcinogenicity Study with Narrow Range (98.1%) N-Ethyl PerfluorooctanesulfonamidoEthanol in Rats
Analytical Laboratory Report Title Determination of the Presence and Concentration of PFOS, PFOSA, PFOSAA,
EtFOSE-OH, M556, and PFOSEA in Serum and Liver Samples of Crl:CD@(SD)IGS BR Rats Exposed to N-Ethyl PerfluorooctanesulfonamidoEthanol
Data Requirement
Not Applicable
Author
3M Environmental Laboratory
Study Completion Date JuAntes0ig6n,in2g001
Performing Laboratories
Liver and Serum Analyses 3M Environmental Laboratory Building 2-3E-09, 935 Bush Avenue
St. Paul, MN 55106
Project Identification
3M Medical Department Study: T-6316.1 Covance In-Life Study: 6329-212 Analytical Report: FACT TOX-001 3M Laboratory Request No. U2103
Total Number of Pages #3#1#0
3M Environmental Laboratory
3M Environmental Laboratory
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3M Medical Department Study: T6316.1
3M Medical Department Study: T-6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
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3M Environmental Laboratory
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3M Medical Department Study: T6316.1 3M Medical Department Study: T-6316.1
GLP Compliance Statement
Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
Analytical Laboratory Report Title: Determination of the Presence and Concentration of PFOS, PFOSA, PFOSAA, EtFOSE-OH, M556, and PFOSEA in Serum and Liver Samples of Crl:CD@(SD)IGS BR Rats Exposed to N-Ethyl Perfluorooctanesulfonamido Ethanol
Study Identification Numbers:
T-6316.1, FACT TOX-001, LRN-U2103
This study was conducted in compliance with United States Food and Drug Administration (FDA) Good Laboratory Practice (GLP) Regulations 21 CFR Part 58, with the exceptions in the bulleted list below.
Exceptions to GLP compliance:
0 There were two study directors in this study. This study was designed as two separate studies. The in-life phase study was considered to end at the generation and shipment of specimens. The analytical study was considered to start at the receipt of these specimens for analysis. This resulted in having two separate study directors, one for each phase of the same study. However, since the technical performance of each phase was entirely separate, no effect is expected from this exception.
0 Sample storage stability will not be determined. 0 Characterizationof the analytical standards is underway, but has not yet been
completed (21 CFR 58.105 (a)). Lot No. 59905 of the surrogate, THPFOS, will not be characterized for purity since quantities of this standard are exhausted. 0 The electronic data systems in use have not been validated and there is not an electronic audit trail of corrections currently available (21 CFR 58.130 (e)).
Authenticated hard copies of chromatograms and associated documents will be
considered as the original raw data. 0 Some changes in the raw data entries were not all made in accordance with 21
CFR 58.130 (e). 0 Some reagents and solutions did not have expiration dates on the labels, as
required according to 21 CFR 58.83.
(See next page for signatures)
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3M Environmental Laboratory
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3M Medical Department Study: T6316.1
3M Medical Department Study: T-6316.1
GLP Compliance Statement (continued)
Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
7L2.
-
John L. Butenhoff, Ph.D., Stud$ Director
6
.-' 7 C L
Marvin T. Case, D.M.V., Ph.D., Sponsor Representative
&/ m/
Date
!bq
Date
05\31 /O/
Kristen'J. Hansen, Ph .D., Principal Analytical lnvestigator
Date
William K. Reagen, Ph.D., Laboratory Manager
Date
3M Environmental Laboratory 3M Environmental Laboratory
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3M Medical Department Study: T6316.1
3M Medical Department Study: T-6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
GLP Study-Quality Assurance Statement
Analytical Laboratory Report Title: Determination of the Presence and Concentration of PFOS, PFOSA, PFOSAA, EtFOSE-OH, M556, and PFOSEA in Serum and Liver Samples of Crl:CD@(SD)IGS BR Rats Exposed to N-Ethyl Perfluorooctanesulfonamido Ethanol
Study Identification Numbers: T-6316.1, FACT TOX-001, LRN-U2103
This study has been inspected 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 management.
Inspection Dates
I Phase
Date Reported to
Management I Study Director
4 / 7 / 0 0 4 1 1/00
In-phase
5/8/00
5/8/00
1/15/01-2/4/0 1
Data
2/5/0 1
2/5/0 1
I I 1 3/23/01, 3/26/01-3/30/01
3/26/01-3/27/0 1, 3/29/01-
I I I 3/30/01,4/2/01-4/5/01
Data Data
3/30/01 4/6/01
3/30/01 4/6/01
4/3/01-4/6/0 1, 4112/01-4113101, 4/17/0 1
Data
4/18/0 1
4/18/0 1
5/3/01,5/7/01-5/10/01 , 5/15/01-5/16/0 1
Draft Report
5/16/01
5/16/01
QAU Representative ~
Date
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3M Environmental Laboratory
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Table of Contents
Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
GLP Compliance Statement ............................................................................................. 3 GLP Study-Quality Assurance Statement ...................................................................... 5 Study Personnel and Contributors.................................................................................... 8 Introduction and Purpose.................................................................................................. 9
Test System ................................................................................................................. 9 Specimen Collection and Analysis ............................................................................... 10
Specimen Receipt and Maintenance................................................................................ 10 Chemical Characterization of the Reference Materials..................................................... 12
Dose Confirmation Analyses ........................................................................................ 12 Method Summaries........................................................................................................... 13
3M Environmental Laboratory ...................................................................................... 13 Preparatory Methods............................................................................................... 13 Analytical Methods .................................................................................................. 14 Analytical Equipment............................................................................................... 14
Data Quality Objectives and Data Integrity ....................................................................... 15 Data Summary. Analyses. and Results............................................................................. 15
Summary of Quality Control Analyses Results for PFOS. PFOSA. PFOSAA. M556.
EtFOSE-OH and PFOSEA........................................................................................... 16 Statement of Data Quality............................................................................................ 18 Summary of Sample Results........................................................................................ 19 Statistical Methods and Calculations ................................................................................ 19 Statement of Conclusion................................................................................................... 19 References ....................................................................................................................... 19
Appendix A: Chemical Characterization and Control Matrices.......................................... 20
Appendix B: Protocol, Amendments and Deviations......................................................... 21 Appendix C: Extraction and Analytical Methods ............................................................... 12025 Appendix D: Data Summary Tables.................................................................................. 12835 Appendix E: Data Spreadsheets....................................................................................... 13968 Appendix F: Example Calculations ................................................................................... 23784 Appendix G: Interim Certificates of Analysis..................................................................... 32885 Appendix H: Report Signature Page................................................................................. 33190
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3M Medical Department Study: 1-6316.1
List of Tables
Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
Table 1.Test System Population Demographicsfor Study 6329-212 .............................. 9
Table 2. Specimen Collection for FACT TOX-001 ............................................................ 10 Table 3. Characterization of the Analytical Reference Standards in Study FACT
TOX-001 .............................................................................................................. 12
Table 4.Target Ions Monitored in 3M Laboratory Analyses.............................................. 15
Table 5. Matrix Spikes-Sera .......................................................................................... 17
Table 6. Matrix Spikes-Liver ........................................................................................... 18
Table 7. Characterizationof the Control Matrices Used for Sera Analyses in Study FACT TOX-001.................................................................................................... 20
Table 8. Characterizationof the Control Matrices Used for Liver Analyses in Study
FACT TOX-001.................................................................................................... 20
Table 9. Characterization of Test Article in Study FACT TOX-001 ................................... 20
Table 10. FACT TOX-001 Data Summary of PFOS Concentration-Serum (pg/mL) .......21486 Table 11. FACT TOX-001 Data Summary of PFOSA Concentration-Serum (pg/mL).....21587 Table 12. FACT TOX-001 Data Summary of PFOSAA Concentration-Serum (pg/mL) ..21688 Table 13. FACT TOX-001 Data Summary of EtFOSE-OHConcentration-Serum
(pg/mL) ................................................................................................................ 12879
Table 14. FACT TOX-001 Data Summary of M556 Concentration-Serum (pg/mL)........12980
Table 15. FACT TOX-001 Data Summary of PFOSEA Concentration-Serum (pg/mL) ..2191
Table 16. FACT TOX-001 Data Summary of PFOS Concentration-Liver (pg/g)............. 13902 Table 17. FACT TOX-001 Data Summary of PFOSA Concentration-Liver (pg/g) ..........13193 Table 18. FACT TOX-001 Data Summary of PFOSAA Concentration-Liver (pg/g) ........13294 Table 19. FACT TOX-001 Data Summary of EtFOSE-OH Concentration-Liver (pg/g)...31395 Table 20. FACT TOX-001 Data Summary of M556 Concentration-Liver (pg/g) .............31496 Table 21. FACT TOX-001 Data Summary of PFOSEA Concentration-Liver (pg/g) ........13957
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3M Medical Department Study: T6316.1 3M Medical Department Study: T-6316.1
Study Personnel and Contributors
Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001
LRN-U2103
Study Director John L. Butenhoff, Ph.D.
3M Corporate Toxicology - Medical Department
3M Center Building 220-2E-02
St. Paul, MN 55144-1000
651-733-1962
Sponsor Marvin T. Case, D.V.M., Ph.D. 3M Corporate Toxicology - Medical Department 3M Center Building 220-2E-02 St. Paul, MN 55144-1000
Analytical Chemistry Laboratories
Liver and Serum Analyses 3M Environmental Laboratory Kristen J. Hansen, Ph.D., Principal Analytical lnvestiga tor
3M Lab Contributing Personnel
David R. Barnidge, Lisa A. Clemen Lisa A. Dick, Ph.D. Rhonda S. Dick* Kelly J. Dorweiler* Mark E. Ellefson Sara E. Estes* Tina M. Galloway Barb A. Gramenz* Sarah A. Heimdal*
Cari S. Hewitt*
Ph.D.*
"Contract lab professional service employees
Marlene M. Heying* Joy D. Jenkins Harold 0. Johnson Ognjenka Kruplijanin* Sally A. Linda* Ian A. Smith* Kathleen M. Stock* Kelly J. (Kuehlwein)*Swartout Anh-Dao Vo Bob W. Wynne*
Richard D. Youngblom*
Location of Archives
All original raw data, protocol, and analytical report have been archived at the 3M Environmental Laboratory. The test article and analytical reference standard reserve samples, as well as the specimens pertaining to the analytical phase of this study are archived at the 3M Environmental Laboratory.
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Introduction and Purpose
Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
The purpose of the study is to determine the presence and concentration of PFOS, PFOSA, PFOSAA, EtFOSE-OH, M556, and PFOSEA in serum and liver specimens collected from Covance Study No.: 6329-212 titled: 104-Week Dietary Carcinogenicity Study with Narrow Range (98.1%) N-Ethyl Perfluorooctanesulfonamido Ethanol in Rats. The Covance in-life study was initiated on January 21, 1998. The analytical phase of the study was initiated on April 9, 1998.
Test System
A total of 410 males and 410 female rats were used as the test system. Table 1 outlines the rat population demographics and dosage levels for study 6329-212.
The test system species and strain selected was the Crl:CD@(SD)IGS BR rat received from Charles River Laboratories, Inc., identified using an implanted microchip device. At the initiation of treatment the rats were approximately 45-51 days old and weighed between approximately 100-31 0 g.
Table 1. Test System Population Demographicsfor Study 6329-212
a Groups 5 and 7 were terminated during week 8 of treatment due to toxjcily. Group 6 was plxedon recoveryafter 52 weeks of treatment.
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Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
Specimen Collection and Analysis Specimens were collected by Covance (study 6329-212) and sent to the 3M Environmental Laboratory for analysis. Table 2 lists the sampling intervals and types of specimens that were collected for this study.
Table 2. Specimen Collection for FACTTOX-001
The total number and type of specimens collected for analyses in the analytical phase of this study are presented below.
Specimens Collected from Study Groups 1through 5 (through 2/01/00): Serum Specimens-524 specimens (423 samples were analyzed.) Liver Specimens-265 specimens (All 265 samples analyzed.)
Specimens Collected from Study Group 6 (Recovery) on 2/01/00: Serum Specimens-22 specimens (All 22 samples analyzed.) Liver Specimens-22 specimens (All 22 samples analyzed.)
Liver and sera specimens were shipped to the 3M Environmental Laboratory frozen and on dry ice.
Sera and liver samples were extracted beginning on April 23, 1998 using an ion pairing reagent
and either ethyl acetate or methyl-tert-butyl ether (MtBE). Liver samples were homogenized prior
to the extraction procedure. Sample extracts were analyzed using high-pressure liquid chromatography-electrosprayAandem mass spectrometry (HPLC-ESMSMS) in the multiple reaction monitoring mode. PFOS, PFOSA, PFOSAA, EtFOSE-OH, M556, and PFOSEA levels were evaluated by external calibration using extracted curves. Analytical details are included in this report.
Specimen Receipt and Maintenance
The 3M Environmental Laboratory received liver and serum specimens collected at predeterminedtime points during and at the end of the in-life phase of Covance Study 6329-212 from February 1998 through February 2000 from Covance. All specimens were received frozen on dry ice and were immediately transferred to storage at -20C *IO"C.
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Analytical Report: FACT-TOX-001 LRN-U2103
3M Medical Department Study: T-6316.1
Analytical Report: FACT TOX-001 LRN-U2103
Control matrices used in liver and sera analyses performed during TOX-001 were obtained from commercial sources and are presented in Appendix A (see Tables 7 and 8).Samples analyzed at the 3M Environmental Laboratory will be maintained for a period of 10 years and will be stored at the laboratory at -20Ck10"C to -80Ci2O"C.
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Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
Chemical Characterization of the Reference Materials
Chemical characterization information on the analytical reference materials used in this study is presented in tabular form below.
Table 3. Characterization of the Analytical Reference Standards in Study FACT TOX-001
Reference Standard/ Formula
Potassium Perfluorooctanesulfonate CeFi7S03-K+
N-Ethyl Perfluorooctanesulfonamidoethyl alcohol C~FI~SOZN(GH~)CHZCHZOH Sodium Perfluorooctanesulfonylamido(ethyl) acetate CEFI~SOZN(CH~CH~KHZCOO-N~ Perfluorooctanesulfonylamido(ethyl)acid CEFI~SO~N(CHZCH~)CHZCHOO-
Perfluorooctanesulfonylamide CeFi7SOzNHz
Perfluorooctanesulfonylethylamide CsFi7SOzNHCHzCH3 M556 C8Fi7S02N(H)CH2COOH lH, lH, 2H, 2HTetrahydroperfluorooctanesulfonic acid CEH~FI~SO~H
'This lot is exhausted and cannot be characterized. N R - N o t recorded N A - N o t applicable TBD-To be determined
Acronym
Source Expiration Storage
Chemical Physical
Date
Conditions Lot Number Description
Purity
3M Oml/O1
Ambient temperature
KPFOS"
3M
2010
Ambient temperature
171
'ght
86.4%
powder
193
W hte
88.0%
crystals
Ambient
3M
2010
temperature
215
Whitepowder
TBD'
3M EtFOSE-OH
3M
I I I 1 1 1 3M
PFOSMb
I I I t$:!zre I I I 3M
201 0 11/26/01
Ambient temperature
Ambient temperature
01/01/2010 $t$er
936 Unknown (SD013)
617
Amberwaxy solid
Amberwaxy solid
NA* 88.9%
TBD'
01/01/2010
NB112999-99 Tanwaxysdid
TBD'
Ambient
3M
01/01/2010
temperature
E353
Amber to brown waxy
sdid
TBDC
PFOSA 3M
201 0
Ambient
NR
NR
temperature
(TN-A-1886)
TBD'
I I I I PFOSEA
3M
01/01/2010 temAmpebriaetnutre
3M
01/01/2010 temAmpebireantut re
L15709 529
Light YdlW
TBDc
I ""zidWI waxysdid TBD'
M556 THPFOS
3M
01/01/2010
temAmpebireantut re
NB113047-80 White powder
TBD
ICN
01/01/201 O
Ambient
temperature
Ambient
ICN
01/01/2010 temperature
59909 53406
Brownpowder
Brownwaxy Solid
NA* TBDc
"rarget analyie is C8Fl7SO2{(CH2CH3)(CH2COO])
'Unless othemise indicated, at the time of quantitation, the purity for all analyies was
assumedto be 1W/.
Dose Confirmation Analyses
Dose preparation methods and analysis were performed by Covance, using a validated analytical method provided by the Sponsor (MP-M312-MA), and are reported separately (Reference Covance 6329-212).
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Method Summaries
Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
Following is a brief description of the methods used during this analytical study by the 3M Environmental Laboratory. Detailed descriptions of the methods used in this study are located in Appendix C.
Data collected prior to November 1999 was reworked in 2000 to accommodate improvements in data reduction methods. Both the original and "reworked" data are archived; reworked data is presented in the final results. The improved methods are documented in the form of method modifications.
As the present study progressed, more advanced methods evolved and these methods were used with deviations until amendments to the protocol were written. Protocol and method deviations are located in Appendix B of this report.
3M Environmental Laboratory
PREPARATORMYELHODS
FACT-M-1.O. "Extraction of Potassium Perfluorooctanesulfonateor Other Anionic FluorochemicalSurfactants from Liver for Analysis Using HPLC-Electrospray/Mass Spectrometry." This method was used for week 4, week 8, and week 14 samples.
FACT-M-3.0, "Extraction of Potassium Perfluorooctanesulfonateor Other Anionic FluorochemicalSurfactants from Serum for Analysis using HPLC-Electrospray/Mass Spectrometry." This method was used for week 4, week 8, and week 14 samples.
ETS-8-4.1, "Extraction of Potassium Perfluorooctanesulfonate or other Fluorochemical Compounds from Serum for Analysis using HPLC-Electrospray/MassSpectrometry." This method was used for week 27, week 53, and week 105 samples.
ETS-8-6.0, "Extraction of Potassium Perfluorooctanesulfonateor other Fluorochemical Compounds from Liver for Analysis using HPLC-Electrospray/MassSpectrometry." This method was used for week 53 and week 105 samples.
An ion-pairing reagent was added to the sample and the analyte ion pair was partitioned into
ethyl acetate (FACT-M-1.O and FACT-M-3.0) or MtBE (ETS-8-4.1 and ETS-8-6.0). The
extract was transferred to a centrifuge tube and put onto a nitrogen evaporator until dry.
Each extract was reconstituted in 1.OmL of methanol, and then filtered through a 3 cc plastic
syringe attached to a 0.2 pm nylon filter into glass autovials.
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Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
ANALYTICAL METHODS
FACT-M-2.0, "Analysis of Liver Extracts for Fluorochemicals Using HPLC-Electrospray/Mass Spectrometry".
FACT-M-4.0, "Analysis of Fluorochemicals in Serum Extracts Using HPLC-Electrospray/Mass Spectrometry".
ETS-8-5.1, "Analysis of Potassium Perfluorooctanesulfonateor other Fluorochemicals in Serum Extracts Using HPLC-Electrospray/MassSpectrometry".
ETS-8-7.0, "Analysis of Potassium Perfluorooctanesulfonateor other Fluorochemicals in Liver Extracts Using HPLC-Electrospray/MassSpectrometry".
The analyses were performed by monitoring one or more product ions selected from a single primary ion characteristic of a particular fluorochemical using HPLC-ES/MS/MS. For example, molecular ion 499, selected as the primary ion for PFOS (C8FI7SO3-)analysis, was fragmented further to produce ion 99 (FS03-). The characteristic product ion 99 was monitored for quantitative analysis.
ANAL YTICAL EQUIPMENT
The actual analytical equipment settings used in the present analytical phase of this study varied slightly during actual data collection. The following is representative of the settings used during the analytical phase of this study.
Liquid Chromatograph: Hewlett-Packard@Series 1100 Liquid Chromatograph system Analytical column: Keystone@BetasilTMCIS2x50 mm (5 pm) Column temperature: Ambient Mobile phase components:
Component A: 2mM ammonium acetate Component B: methanol Flow rate: 300 pUmin
Injection volume: 10 p L
Solvent Gradient: 13.5 minutes
Time (minutes)
%B
0.0
40%
8.5
90%
11.0
90%
12.0
40%
13.5
0%
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Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
Mass Spectrometer: Micromass@APVMass Spectrometer Quattro llrM Triple Quadrupole system Software: Mass LynxrM2.3,3.1,3.2,3.3,3.4 Cone Voltage: 30-60 V Collision Gas Energy: 25-45 eV Mode: Electrospray Negative Source Block Temperature: 150C ~ 1 0 C Electrode: Z-spray Analysis Type: Multiple Reaction Monitoring (MRM)
Table 4. Target Ions Monitored in 3M LaboratoryAnalyses
I Target Analge I~~ Primary Ion (AMU) I P r o d u x o ( A M U ) l
I PFOS I
499
I 80,99,130 I
PFOSA
498
78
I PFOSAA 1
584
I
83,169 I
EtFOSE-OH
630
59
PFOSEA
526
65
M556
556
65,78,831,69
THPFOS
427
80
Data Quality Objectives and Data Integrity
The following data quality objectives were indicated in the method performance section of ETS-
8-5.1, Analysis of Potassium Perfluorooctanesulfonateor Other Fluorochemicals in Serum
Extracts Using HPLC-Electrospray/MassSpectrometry and ETS-8-7.0, Analysis of Potassium Perfluorooctanesulfonateor Other Fluorochemicals in Liver Extracts Using HPLC-Electrospray/Mass Spectrometry:
0 Linearity: The coefficient of determination (r2) equal to or greater than 0.980.
0 Limits of Quantitation (LOQ): The LOQ is equal to the lowest acceptable standard in the calibration cuwe.
0 Acceptable Precision: Precision is better than 30% for the method.
0 Acceptable Spike Recoveries: 70-1 30%
Data Summary, Analyses, and Results
Data quality objectives for the analytical phase of this study outlined in the 3M Environmental Laboratory protocol for FACT TOX-001 (see Appendix B) were met with the exceptions noted in this report. See Appendix B for deviations.
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Analytical Report: FACT-TOX-001 LRN-U2103
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Analytical Report: FACT TOX-001 LRN-U2103
Summary of Quality Control Analyses Results for PFOS, PFOSA, PFOSAA, M556, EtFOSE-OHand PFOSEA
Linearity: The coefficient of determination (r2)of the standard curve was 20.980.
Calibration Standards: Quantitation of the target analytes was based on linear regression analysis weighted l / x of a single, opening or two bracketing extracted matrix curves for each group of samples. Rat and rabbit sera were used for matrix curves for sera analyses, while rabbit liver was used for matrix curves for liver analyses. High or low points on the curve may have been deactivated to provide a better linear fit over the curve range most appropriate to the data. Low curve points with peak areas less than two times that of the extraction blanks were deactivated to disqualify a data range that may have been significantly affected by background levels of the analyte. Occasionally, a single mid-range curve point that was an obvious outlier may have been deactivated. Quantitation of each analyte was based on the response of one or more specific product ion@)using the multiple reaction monitoring mode of the instrument (see Appendix C, Analytical Methods). Calibration standards were prepared to run, undiluted, approximately within the linear range of the instrument (approximately 51000 ng/g).
Limits of Quantitation (LOQ): The LOQ is equal to the lowest acceptable standard in the calibration curve (defined as a standard within *30% of the theoretical value), and is at least two times the analyte peak area detected in the surrogate matrix blanks. (see Appendix D).
Blanks: All blanks were below the limit of quantitation for the compounds of interest, except
PFOSA Week 8 H 2 0+ liver Blk-2 (0.0663 pg/g and 0.0414 pg/g) and PFOS Week 105 liver-
Blk-2 (0.0163). To simplify analyses that were complicated by endogenous levels of fluorochemicals in unexposed rat sera and liver, rabbit sera and liver were selected as suitable surrogate matrices.
Precision, Instrumental: Instrumental precision was determined by replicate injections of a single serum extract. Instrumental precision was determined for PFOS, PFOSAA, and M556;
variation was less than 7.0 Yofor all targeted analytes.
Matrix Spikes: Sera-Matrix spike samples were prepared from control rat sera along with
each batch of sera samples. Samples were spiked between approximately 75-250 ng/mL,
levels that approximate the levels detected in the Group l-Group 5 samples, depending upon the analyte. All spikes were prepared to run, undiluted, within a ten-fold limit of the linear range of the calibration curve. For some analytes, samples for some high dose animals may be much higher than the range of these prepared spikes. Sera matrix spike recoveries are presented in tabular form in Table 5.
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Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
1 I 1 Table 5. Matrix Spikes-Sera # of Spikes
* Averagespike
Recovery SD
PFOS 1 PFOSA
1 28 I 9 5 i 2 5 % 1
28
103 2 20%
PFOSAA
28
111 i 2 4 %
EtFOSE-OH
22
39 i 29%
M556* PFOSEA
22
126 i 22%
22
63 * 14%
Range
65183% 72-1 43% 57-1 86% 18-1 27%
86-1 53%
3747%
# of Spikes Deviating
> &o% and < *50%
1
3
I
4
3
0
8
8
II 1 1
0 1 20 3 6
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Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001
LRN-U2103
PFOS
# of Spikes
24
Average Spike Recovery f SD
90 * 61%
Range
0-1 96%
# of Spikes Deviating > *30% and < *50%
4
# of Spikes Deviating > &50%
9
PFOS, revised (')
18
119 * 38% 6&196%
4
3
PFOSA
18
94 f 27%
26-128%
0
2
1
I
I
I
I
I
PFOSA, revised (')
16
102 * 17% 71-128Yo
0
0
PFOSAA
20
86 f 44%
0-1 47%
1
4
1 1 PFOSAA,
revised (')
105*19% 174147%
1
0
MFOSE-OH
16
133 f 166% 25567%
1
8
EtFOSE,
revised ('I
14
148 173% 26-567%
1
6
M556*
12
102 * 15% 85141%
1
0
PFOSEA
10
97 * 12% 80-117%
0
0
Surrogates: The surrogate (THPFOS) was added to all samples and standards. THPFOS was not used for quantitation, but was used to monitor for gross instrument failure. After 11/04/99, the surrogate response of each analytical run was verified to determine that it did
not vary more than &50% from the mean within each analytical run. Deviations of greater
than f 50% are noted in the results table.
Statement of Data Quality
It is not possible to verify true recovery of endogenous analyte from tissues without radio-labeled reference material. The only measurement of accuracy available at this time, matrix spike studies, indicate that the sera and liver data can be considered accurate to within one standard deviation of the average fortified samples recovery. For example, in liver, PFOS data is accurate to 119 f 38%. Please see bolded values in Tables 4 and 5 for specific values relating to data quality.
The results of quality control analyses (curve fit, CCVs, and MS/MSDs) for EtFOSE-OH and PFOSEA were inconsistent and indicate that data presentedfor these two analytes should be
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considered to be qualitative only. Values for these two analytes are presented in data tables in the spirit of full disclosure, but should not be used in any quantitative assessment of the data.
Summary of Sample Results
Some PFOS results (those obtained using lot 171) have been corrected for purity of the analytical reference material. Uncorrected results are noted in the data tables.
0 Samples from Control Animals: The target analytes were often detected in the sera and liver samples from the control animals. These levels were usually lower than those found in the low dose test animals.
0 Samples from Dosed Animals: In general, levels of the target analytes present in the sera and liver samples from the test animals increased with dose group, with the exception of Group 6, which was taken off the compound after 53 weeks. Detailed sample data tables are presented in Appendices D and E.
Statistical Methods and Calculations
Statistical methods were limited to the calculation of means and standard deviations. See Appendix F for example calculations used to generate the liver and serum sample data in FACT TOX-001,
Statement of Conclusion
Under the conditions of the present study, PFOS, PFOSA, PFOSAA, EtFOSE-OH, M556, and PFOSEA were observed in the sera and liver of rats dosed with N-Ethyl Perfluoroctanesulfonamido Ethanol during the in-life phase of the study.
References
Covance Study No.: 6329-212, 104-Week Dietary Carcinogenicity Study with Narrow Range (98.1%) N-Ethyl PerfluoroctanesulfonamidoEthanol in Rats
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Appendix A: Chemical Characterization and Control Matrices
Table 7. Characterization of the Control Matrices Used for Sera Analyses in Study FACT TOX-001
Control Matrix I RatSerum 1 Rat Serum 1 Rabbitserum 1
~
Source
Sigma
Sigma
Sigma
Expiration Date
201 0
2010
2010
Storage Conditions
-20C k10"C
-20C *I 0C
-20C *I 0C
Chemical Lot #
17H9306
19H89291
47H4641
Physical Description
I
NR-nd recorded
Rat Serum
I
I
Rat Serum
Rabbit Serum
I
I
Control Matrix
Rabbit Liver
Rabbit Liver
Rabbit Liver
Rabbit Liver Rabbit Liver
Source
Covance Laboratories,
Inc.*
Covance Laboratories,
Inc.'
Covance Laboratories,
Inc.'
Covance Laboratories,
Inc.'
Unknown
Expiration Date
2010
201 0
12/99
2010
12/01/99
Storage Conditions
-20C *1O"C
-20C *I 0C
-20C *I 0C
-20C *I 0C
-20C *lO"C
Chemical Lot #
FOOOI 4
F00008
F00007
FOOOI 6
NR (TCR-99062-22)
Physical Description
Rabbit Liver
Rabbit Liver
I
Rabbit Liver
1
Rabbit Liver
Rabbit Liver
I
NR-not recorded
T h e controlsource is listedas CHW (Coming HazeltonWisconsin) in the rawdata This is the former name of C m c e
Laboratories. Inc.
Table 9. Characterization of Test Article in Study FACT TOX-001
Chemical Name
Source Expiration Date Storage Conditions
I Chemical Lot #
Physical Description Purity
Et FOSE-OH N-Ethyl Perfluorooctanesulfonamido ethanol
3M
1 1/26/01
Ambient temperature
I
30035,30037,30039
1
Waxy solid
97.4%'
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~
Appendix B: Protocol, Amendments and Deviations
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c o v m THE DWELOPYLNTSERVICESC W M
Analytical Report: FACT-TOX-001 LRN-U2103
3M
St. Paul, Minnesota
PROTOCOL
Study 'ICtle:
104-Wezk Dietary CarcinogenicityStudy with Narrow Range (98.1%) N-Ethyl PerfluorooctanesulfonamidoEthanol in Rats
Date: January 21,1998
Performing Laboratory:
Covance Laboratories Inc.
3301 Kiusman Boulevard Madison, Wisconsin 53704
Laboratory Study Identification: Proposal No. 6777 C O V ~63~29C-2~12
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C O V ~ ~6N32X9-212 Page 2
Study
104-Week Dietary Carcinogenicity Study with Narrow Range (98.1%) N-Ethyl
Perfluorooctanesulfonamido Ethanol in Rats
Purpose To assess the carcinogenicity of the test material when administered in the diet to rats for at least 104 weeks
Sponsor 3M Toxicology Services Building 220-2E-O2,3M Center St. Paul, Minnesota 55144-1000
Study Monitor Andrew M. Seacat, PhD 3M Telephone No.: 612.575.3161 Facsimile No.: 612.733.1773
Study Location Covance Laboratories Inc.
3301 Kinsman Boulevard Madison, Wisconsin 53704
Mailing Address: PO Box 7545 Madison, Wisconsin 53707
Study Director Peter J. Thomford, PhD Covance Laboratories Inc. Telephone No.: 608.241.7207 Facsimile No.: 608.242.2736
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Toxicologist
Thomas E. Ryan,BS
Covance Laboratories Inc.
Covance 6329-212 Page 3
Proposed Study Timetable In-Life Start Date: January 26, 1998 In-Life End Date: January 31,2000
Regulatory Compliance
This study will be conducted in compliance with the Food and Drug Administration Good Laboratory Practice Regulations as set forth in Title 21 of the US Code of Federal
Regulations, Part 58, issued December 22, 1978 (effective June 20, 1979), and with any applicable amendments.
Animal Care and Use Statement
All procedures in this protocol are in compliance with the Animal Welfare Act Regulations, 9 CFR 1-4. In the opinion of the Sponsor and study director, the study does
not unnecessarily duplicate any previous work.
Quality Assurance The protocol, study conduct, and final report will be audited by the Covance Qu&ty
Assurance Unit (QAU). The proliferation cell nuclear antigen evaluation, data, and report
will be audited by the QAU of Pathology Associates InternationaL
Test Material
Identification T-6316 (Narrow Range N-Ethyl PeffluorooctanesulfonamidoEthanol, NEtFOSE)
Lot Numbers The lot numbers will be maintained in the raw data.
Purity 98.1% NEtFOSE (w/w)
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Stability Responsibilityof the Sponsor
Storage Conditions At room temperature
Characteristics Information on synthesis methods, composition, or other characteristicsthat define the test material is on file with the Sponsor.
Reserve (Archive) Samples A reserve sample (approximately5 g) will be taken and stored at room temperature. This sample will be transferred to the Sponsor after completion of the in-lifephase to be retained in accordance with 21 CFR 58.195.
Disposition of Test Material After authorization from the Sponsor, any remaining test material will be returned to:
Andrew M. Seacat, PhD
3M Toxicology Services Building 220-2B-O2,3M Center St. Paul, Minnesota 55144-1000
Telephone No.: 612.575.3 161 Facsimile No.: 612.733.1733
Animals
species Rat
Strain . Crl:CD@(SD)BR
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Source Charles River Laboratories, Inc., Raleigh, North Carolina
Covance 6329-2 12 Page 5
Age at Initiation of Treatment Preferably 6 weeks of age, but not more than 8 weeks of age
Weight at Initiation of Treatment 100to 300 g
Number and Sex 410 males and 4 10females
Identification Implantable microchip identification device
Husbandry
Housing Individual (may be group-housed during acclimation)
Diet
Certified Rodent Diet #5002 (PMJ? Feeds, Inc.) ad libitum, unless otherwise
specified. The diet is routinely analyzed by the manufacturer for nutritional
components and environmental contaminants. Specified nutrient and contaminant analyses are on file at Covance-Madison.
Water Ad libitum. Samples of the water are routinely analyzed for specified microorganisms and environmental contaminants. The results are on file at Covance-Madison.
Contaminants There are no known contaminants in the diet or water at levels that might interfere with this study.
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Environment Environmental controls for the animal room will be set to maintain 18 to 26"C, a relative humidity of 30 to 70%, a 12-hour IightllZhour dark cycle, and minimum of 10 room air changeshour. The lighvdark cycle may be interrupted to accommodate study-related activities.
Acclimation At least 1 week
Randomization Selection of animals for the study will be based on body weights, c h c a l observations, and other data as appropriate. Animals wjll be assigned to treatment groups using a computerized blocking procedure designed to achieve body weight balance with respect to treatment groups. At the time of randomization,the weight variation of the animalsof each sex used will not exceed & standard deviations of the mean weight, and the mean body weight for each group of each sex will not be statisticallydifferent at the 5.0% probability level.
Justification Rats historically have been used in safety evaluation studies and are recommended by appropriate regulatory agencies.
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Group Designations and Dietary Levels
Covance 6329-2 12 Page 7
Number of Animals
Dietary Levels
Group
Male
Female
(ppm NEtFOSE)"
1 (ControI)b-c*d
70
70
0
2 (Low)"
60
60
3
3 (Mid)c
60
60
30
4 (Mid-HighYd
70
70
100
5 (HighYd
70
70
300
6 (Mid-High Recovery)"
40
40
100
7 (High Recovery)"
40
40
300
a T-6316 is 98.1% n-ethyl perfluorooctanesulfonamido ethanol (NEtFOSE); dose
levels are expressed as ppm of NEtFOSE.
b The control animalswill receive the basal diet only.
c Five animals/sex m Groups 1 through 5 will be sacrificed during Weeks 3 and 14 for hepatocellular proliferationrate measurements and biochemical analyses
(palmitoyl-CoA oxidation).
d Ten animals/sex in Groups 1,4, and 5 will be designated as interim sacrifice animals
and will be sacrificed after at least 78 weeks of treatment.
e Animals in Groups 6 and 7 will be treated for at least 78 weeks,then treatment will
be discontinued, and the animalswill be observed for reversibility, persistence, or
delayed occurrence of toxic effects for at least 26 weeks posttreatment. During
recovery, the animalswill receive basaldiet only.
Dosing Procedures
Method ofAdministration Dietary. Animals in Groups 1 through 5 willreceive test diet for at least 104 weeks. Animals in Groups 6 and 7 will receive test diet for 78 weeks only.
Reason for Dosing Route The potential human exposure is by the oral route.
Dose Preparation Before initiation of treatment, alldose preparations will be mixed once, and low- and
high-dose preparations will be mixed four times for determination of homogeneity and
stability.
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During treatment, all dose preparations will be mixed at least once every 4 weeks according to the study-specificmixing procedure developed by Covance. Dose concentrations will be based on the NEtFOSE content as supplied; the Sponsor has
stated the T-6316 is 98.1% NEtFOSE (w/w) as supplied. All dose preparations will
be stored at room temperature.
Retention Samples Samples (approximately 100g) will be taken from each dose preparation during the in-life phase and stored at room temperature. Unless used for analyses, these samples will be discarded at least 1 month after completion of the in-life phase.
Dose Analyses By Covance using a method supplied by the Sponsorand validated by Covance
Homogeneity
Homogeneity will be determinedfor all dose level preparations once pretest and for the preparations for Weeks 1 through 3; for two additional pretest high-dose level
preparations; and for four additional pretest low-dose level preparations. One sample (approximately 100 g) each from the top, middle, and bottom of the dose preparations mixed for homogeneity analyses will be collected, divided into three subsamplesfor extraction and analysis, and analyzed for test material content. All samples will be
stored at room temperature until analyzed within 7 days of mixing. Homogeneity
analysis will be repeated if batch size changes by more than 30%.
Stability Four sets of samples (approximately 100g each) will be taken from the low- and high-dose level concentrations of diet preparations mixed pretest to establish stability. One set will be analyzed on the day of mixing. One set will be stored at room temperature for at least 19 days, then analyzed. The third set will be stored at room temperature after at least 32 days, then analyzed. The remaining set will be stored in a freezer set to maintain -10 to -30C for 8 weeks, then analyzed.
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In addition, samples (approximately 100 g each) wjll be taken from the low- and high-dose level concentrations of diet preparations mixed pretest. The samples will be stored at room temperature for 5 days, then for 7 days under animal room conditions (room temperature in a feeding container), then analyzed.
Dose Cofirmation Samples (approximately 100 g each) will be collected from all dose preparations and analyzed in duplicate. Homogeneity samples collected from the middle of the dose preparations for Weeks 1 through 3 will be used for dose confirmation results. All samples will be stored at room temperature until analyzed.
Observation of Animals
Clinical Observations Each animal will be observed twice daily (a.m. and p . a ) for mortality and moribundity, recording findings as they are observed.
Once prior to treatment and weekly thereafter, each animal will be removed from its cage and examined; abnormal findings or an indication of normal will be recorded. The following information on each grossly visible or palpable mass will be recorded.
time of onset
location
size (smallor large) appearance progression
Body Weights Prior to treatment (at randomization), weekly for Weeks 1 through 17, once every 4 weeks thereafter, and at Week 105
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Food Consumption Weekly for Weeks 1 through 16 and once every 4 weeks thereafter
Covance 6329-212 Page 10
Clinical Pathology
Frequency and Number of Animals
Unscheduled Collection
When possible, a blood film will be made and held for possible future examination from animalssacrificed at unscheduled intervals.
Scheduled Collections Hematology, clinical chemistry, urinalysis, urine chemistry, and serum sampling will be done on 10 animals/sex/group in Groups 1 through 5 during Weeks 14,27, and 53.
A blood Nm wiU be made and held for possible future examinationfor animals at
scheduled sacrifices after at least 78 and 104 weeks of treatment.
Method of Collection
Hematology, Clinical Chemistry, Urinalyses, Urine Chemistry, Serum
SampIf5
Animals will be fasted overnight;blood will be collected from a jugular vein. The anticoagulant will be potassiumEDTA for hematologytests. Samples for clinical chemistry and serum samples will be collected without anticoagulant. Urine will be collected chilled overnight (approximately 16 hours).
Blood Films Blood films will be taken as part of the necropsy procedure.
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Tests
Hematology
red blood cell (erythrocyte)count hemoglobin hematocrit mean corpuscular volume mean corpuscular hemoglobin mean corpuscular hemoglobin concentration
platelet count
white blood cell (leukocyte) count differential blood cell count
blood cell morphology reticulocyte smear (made, but not
examined)
glucose urea nitrogen creatinine total protein albumin globulin cholesterol total bilirubin
Clinical Chemistry
alanine aminotransferase gamma glutamyltransferase aspartate aminotransferase calcium inorganic phosphorus sodium potassium chloride
appearance volume specific gravity
PH
protein urobilinogen
sodium potassium
Urinalysis
glucose ketones bilirubin blood microscopic examination of sediment
Urine Chemistry
16 hour excretion of: sodium potassium
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Serum Samples Serum not used for clinical chemistry will be stored in a freezer set to maintain -60 to -80C.Samples will be packed on dry ice and shipped to:
Kris J. Hansen, PhD 3M Environmental Technology and Safety Services 935 Bush Avenue Building 2-3E-09 St. Paul, Minnesota 55133-3331 Telephone No. : 612.778.60 18 Facsimile No.: 612.778.6176
Samples will be retained by the Sponsor for possible future analysis.
Hepatocellular Proliferation and Biochemical Analyses
Frequency and Number of Animals Five animals/sex in Groups 1 through 5 during Weeks 3 and 14
Cell Proliferation Tissue Collection and Immunohistochemical Evaluation At each interval, animalswill be fasted overnight, anesthetized with sodium pentobarbital, weighed, and exsanguinated. The abdominal cavity of each animal will be opened, and the liver will be removed, weighed, and representative samples of left lateral, right median, and right lateral lobes of the liver and any macroscopic lesions of the liver will be collected and preserved in zinc formalin.
After fixation, each sample of liver will be embedded in paraffin, and the paraffin blocks will be shipped to:
Sandra R. Eldridge, PhD
Pathology Associates International 15 Woman's Mill Court, Suite I Frederick, Maryland 21701 Telephone No.: 301.663.1644, ext. 2201 Facsimile No: 301.663.8994
Proliferation cell nuclear antigen (PCNA) evaluation will be done on the samples. Results will be provided for inclusion in the final report.
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Palmitoyl-CoA Oxidase Tissue Collection and Analyses A sample (approximately500 mg) of the right lateral lobe of the liver will also be collected from each animal and flash-frozen in liquid nitrogen. The liver tissue will be stored in a freezer set to maintain -60 to -80C until analyzed by Covance for palmitoyl-CoA oxidase activity.
Animal Disposition Animals will be discarded after liver collection.
Termination
Unscheduled Sacrifices and Deaths Necropsies will be done. Animals to be sacrificed will be anesthetized with sodium pentobarbital, weighed, and exsanguinated. A blood film will be taken as part of the necropsy procedure for sacrificed animals.
Scheduled Sacrifices
Interim Sacrifice After at least 78 weeks of treatment, 10 animals/sex from Groups 1,4, and 5 will be fasted overnight, anesthetized with sodium pentobarbital, weighed, exsanjpinated, and necropsied. A blood film will be taken as part of the necropsy
procedure.
Terminal Sacrifice After at least 104weeks of treatment, the remaining animals in Groups 1 through 5 will be fasted overnight, then anesthetized with sodium pentobarbital, weighed, exsanguinated, and necropsied. A blood film will be taken as part of the necropsy procedure.
Recovery Sacrifice After at least 78 weeks of treatment and 26 weeks without treatment, the remaining animalsin Groups 6 and 7 Wiu be fasted overnight, then anesthetized with sodium pentobarbital, weighed, exsanguinated, and necropsied. A blood film will be taken as part of the necropsy procedure.
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Pos@nortem Procedures
Covance 6329-212 Page 14
Necropsy The necropsy will include an examination of the external features of the carcass; all external body orifices; the abdominal, thoracic, and cranial cavities; organs; and tissues.
Organ Weights
At the scheduled sacrifices, the following organs (when present) will be weighed; paired organs will be weighed separately:
adrenal (2) brain kidney (2) liver
lung
ovary (2) spleen testes
thyroid (2) with parathyroid uterus with cervix
Organ-to-body weight percentages and organ-to-brain weight ratios will be calculated.
Bone Marrow Smear
From the femur of each animal at scheduled sacrifices only; made but not examined
Tissue Preservation The following tissues (when present) fiom each animal will be preserved in 10%neutral-buffered formalin:
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adrenal (2)
pancreas
brain
pituitary
cecum
prostate
cervix
rectum
colon
sahvary gland [mandibular (2)]
duodenum
sciatic nerve
epididymis (2)
seminal vesicle (2)
esophagus
skeletal muscle (thigh)
eye (2) femur with bone marrow (articular surface
Skin
spinal cord (cervical, thoracic, and
of the distal end)
lumbar)
Harderian gland
spleen
heart
sternum with bone marrow
ileum
stomach
jejunum
testis (2)
kidney (2)
thymus
lesions
thyroid (2) with parathyroid
liver
trachea
.
lung with mainstem bronchi lymph node (mesenteric)
mammary gland (females only)
urinary bladder uterus vagina
ovary (2)
Histopathology Tissues (as appropriate) from each animal in Groups 1,5, and 7 and from each animal that dies or is sacrificed at an unscheduled interval will be embedded in paraffin,
sectioned, stained with hematoxylin and eosin, and examined microscopically.
Macroscopic lesions will also be examined microscopicallyfrom each animal in Groups 2,3,4, and 6.
Reports One copy of each draft report will be sent to the Sponsor. The report will include the following information:
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Experimental Design and Methods
Covance 6329-212 Page 16
Results dose analyses mortality clinical observations body weights body weight changes food consumption test material consumption clinical pathology results palmitoy1CoA oxidase activities macroscopic observations microscopic observations cell proliferation assessments (provided by the Sponsor's designee)
Statistical Evaluation body weights body weight changes food consumption survival rates clinical pathology values palmitoyl CoA oxidase activities neoplastic and nonneoplastic lesions
Statistical methods will be those presented in Attachments Nos. 1 and 2. For each sex, Groups 2 through 7 win be compared to Group 1 (Control).
At the end of 1 year after issuance of the audited draft report, if no requested revisions or instructions to finalize have been communicated by the Sponsor, then the audited draft report will be considered 'final'and issued as the final report, signed by the study director, and submitted to the Sponsor.
Any modifications or changes to the audited draft report requested 1 year after issuance will be performed at additionalcost to the Sponsor.
Two copies of the signed final report (one unbound and one bound) will be sent to the Sponsor.
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Covance 6329-212
Record Retention
AU raw data, documentation, records, protocol, specimens, and final report generated as a
result of this study, including those items listed below, will be archived in the storage facilities of Covance-Madisonfor a period of 1 year following submission of the find report to the Sponsor. All raw data stored on magnetic media, the protocol and protocol amendments, study correspondence, and the original report will be retained by Covance. One year after submission of the final report, all of the aforementioned materials will be sent to the Sponsor, and a return fee will be charged. The Sponsor may elect to have the materials retained in the Covance archives for an additionalperiod of time, and Covance will charge a storage fee. If the Sponsor chooses to have Covance dispose of the materials, a disposal fee will be charged.
protocol and protocol amendments dose preparation records in-life records
animal receipt acclimation animal room maintenance randomizations dose administration clinical observations body weights food consumption sample collection
clinical pathology records
anatomical pathology records statistical analyses study correspondence tissue specimens (wet and in paraffin) blood, bone marrow,and tissue slides final report (original signed copy)
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The following supporting records will be retained at Covance-Madison but will not be
archived with the study data.
feed analysis records water analysis records animal room environment records refrigerator and freezer temperature records room temperature records for test material storage instrument calibration and maintenance records
PCNA evaluation data and paraffin blocks and tissue slides for PCNA will be retained by Pathology Associates International.
Serum samples sent to the Sponsor will be retained by the Sponsor
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PROTOCOL APPROVAL
Covance 6329-212 PaRe 19
W
Andrew M. Seacat, PhD
Study Monitor 3M
Department of Toxicology Covance Laboratories Inc.
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Attachment No. 1
Covance 6329-212 Page 20
Statistical Analyses
The statisticalmethods that will be used are described below. Only data collected on or after the first day of treatment will be analyzed statistically.
One-way analysis of variance [ANOVA (Winer, 1971)) will be used (if applicable) to analyze body weights; body weight changes; food consumption; clinical chemistry and hematology values (except blood cell morphology); urine specific gravity, pH, and volume; urine chemistry values; palmitoy1CoA oxidase activities; organ weights; organ-to-body weight percentages; and organ-to-brain weight ratios..
Levene's test (Levene, 1960) will be done to test for variance homogeneity. In the case of heterogeneity of variance at p 5 0.05, transformationswill be used to stabilize the variance. ANOVA will be done on the homogeneous or transformed data. If the ANOVA is significant,Dunnett's t-test (Dunnett, 1964) will be used for pairwise comparisons between treated and control groups.
If the ANOVA shows significancefor body weights at Week 1, one-way analysis of
covariance [ANCOVA(Winer, 1971)) Win be used to a n a l p body weights, with initial
body weights as the covariate, using untransformed data. If the ANCOVA is significant, least squares means t-test (Winer, 1971) Win be used for pairwise comparisons between treated and control groups.
Group comparisons will be evaluated at the 5.096, two-tailed probability level.
References
Dunnett, C. W., "New Tables for Multiple Comparisons with a Control," Biometrics,
-20:482-491 (1964).
Levene, H., "Robust Tests for Equality of Variances," Contributions to Probability and Statistics, (eds.) I. OXkin et al., Ch. 25, pp. 278-292, Stanford University Press: Stanford, California (1960).
Winer, B. J., Statistical Principles in Exuerimental Design, Second Ed., McGraw-Hill:
New York, New York (1971b).
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Attachment No. 2
Adjusted survival data are analyzed by the National Cancer Institute (NCI) Metable package (Thomas, 1977). The tests include: Graphical (Kaplan-Meier product-limit estimation curves), Cox-Tarone binary regression methods for trend and heterogeneity, and Gehan-Breslow nonparametric methods for trend and heterogeneity.
Non-neoplastic lesions. Non-neoplastic lesions are analyzed by the Cochran-Armitage test for trend and the Fisher-Irwin exact test for heterogeneity (Thakur, 1985).
Neoplastic lesions. Incidental tumors are analyzed by Dinse-Lagakos logistic prevalence methods (Dime, 1983) for trend and heterogeneity. Rapidly lethal and palpable tumors are analyzed in the same manner as survival.
In the cases where the study pathologist can assign particular occult neoplastic lesions as the cause of death in the animals,such information will be taken into appropriate analysis
as in the IARC document (Peto et al, 1980).
References
Thomas, D. G., Breslow, N., and Gart,J. J., "Trend and Homogeneity Analyses of Proportions and Life Table Data," Comput. Biomed. Res., u:373-381(1977).
Thakur, A IC,Berry, K J., and MieIke, Jr., P.W.,"AFORTRAN Program for Testing Trend and Homogeneity mProportions," Comput. Progr. Biomed., B:229-233 (1985).
Dinse, G. E., and Lagakos, S . W.,"Regression Analysis of Tumor Prevalence Data,"
J. Rov. Stat. SOC.Series C (ApDL Stat.L =:236-248 (1983).
Peto, R., Pike, M. C., Day, N. E., Gray, R. G., Lee, P. N., Parish, S., Peto, J., Richards, S., and Wahrendorf, J., "Guidelines for Simple Sensitive Significance Tests for Carcinogenic EffectshLong-term Animal Experiments, in Long-term and Short-term Screening Assays for Carcinogens: A Critical Appraisal," Lyon: International Anencv for Cancer Research, pp. 311-426 (1980).
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THE DRIELOPYENT SERWCES COUPANY
PROTOCOL AMENDMENT NO. 1 Covance 6329-212
104-Week Dietary Carcinogenicity Study with Narrow Range (98.1%)N-Ethyl Peffluorooctanesulfonamido Ethanol in Rats
Sponsor: Study Monitor: Testing Facility: Study Director:
3M, St. Paul, Minnesota Andrew M. Seacat, PhD Covance Laboratories Inc., Madison, Wisconsin Peter J. Thomford, PhD
This amendment modifies the followingportions of the protocol:
Effective January 21,1998 1 . Page 4, Animals, Strain. To correct the strain of the animals used in this study,
delete the text in this section and replace with the following: CrlCD@(SD)IGSBR
Effective February 6,1998
2. Page 7, Group Designations and Dietary Levels, Footnote C. To reflect the decision to delay the Week 3 collection, delete the text in this section and replace with the following:
C Five animals/sex/group in Groups 1through 5 will be sacrificed during Weeks 4 and 14 for hepatocellularproliferation rate measurements and biochemical analyses (palmitoyl-CoAoxidation).
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Page 2
3. Page 12, Hepatocellular Proliferation and Biochemical Analyses, Frequency and Number of Animals. To reflect the decision to delay the Week 3 collection, delete the text in this section and replace with the following:
Five animals/sedgroup in Groups 1 through 5 during Weeks 4 and 14 -
4. Page 13,
Effective February 17,1998
5. Page 12. To reflect the decision to collect serum samples for possible future analysis, add the following section after "ClinicalPathology".
Serum Analyses
Frequency and Number of Animals Five animals/sex/group in Groups 1 through 5 during Weeks 4 and 14 (animals selected for hepatocellular proliferation and biochemical analyses); five animals/sedgroup from Groups 1,4, and 5 (from animalsselected for interim sacrifice) after at least 78 weeks of treatment; and five animalslsedgroup from Groups 1through 5 at the terminal sacrifice
Method of Collection Animals will be fasted overnight; blood (approximately2 mL) will be collected from a jugular vein. Samples will be collected without anticoagulant.
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Page 3
Sample Handling Blood samples will be allowed to clot at room temperature and centrifuged. Serum samples will be harvested and stored in a freezer set to maintain -60 to -80C. Samples will be packed on dry ice and shipped to Kris J.
Hansen, PhD,3M Environmental Technology and Safety Services.
Samples will be retained by the Sponsor for possible future analysis.
6. Page 13, Hepatocellular Proliferation and Biochemical Analyses. To reflect the decision to collect liver samples for possible future analyses, add the following section after "Palmitoyl-CoA Oxidase Tissue Collection and Analyses":
Additional Liver Sample Collection At the collections during Weeks 4 and 14, the remaining liver will be stored in a freezer set to maintain -60 to -80C. Samples will be packed on dry ice and
shipped to Kris J. Hansen, PhD,3M Environmental Technology and Safety
Services. Samples will be retained by the Sponsor for possible future analysis.
7. Page 14, Postmortem Procedures. To reflect the decision to collect liver samples for possible future analyses, add the following section after "Bone Marrow Smear":
Additional Liver Sample Collection A portion of the liver will be collected from five animals/sex/group from Groups 1, 4, and 5 at the interim sacrifice and from five animals/sex/group from Groups 1 through 5 at the terminal sacrifice and stored in a freezer set to maintain
-60 to -80C. Samples will be packed on dry ice and shipped to Kris J. Hansen,
PhD, 3M Environmental Technology and Safety Services. Samples will be retained by the Sponsor for possible future analysis.
8. Page 17, Record Retention, Paragraph 4. To indicate that frozen liver samples sent to the Sponsor will be retained by the Sponsor, delete this paragraph and replace with the following:
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Page 4
Frozen liver samples and serum samples sent to the Sponsor will be retained by the Sponsor.
Effective March 13,1998
9. Page 7, Group Designations and Dietary Levels. To reflect the decision to sacrificefive animaldsexlgroup from Groups 1 and 5 and to terminate the remaining animalsin Group 5 and 7 during Week 8, delete the text in this section
and replace with the following:
Number of Animals
Dietary Levels
Group
Male
Female
(ppm NEtFOSE)'
1 (Control)b*c-d*e
70
70
0
2 (Low)c
60
60
3
3 (Mid)"
60
60
30
4 (Mid-High)"."
70
70
100
5 (HighPd
70
70
300
6 (Mid-High Recovery)f
40
40
100
7 (High Recovery)d
40
40
300
a T-6316 is 98.1% n-ethyl peffluorooctanesulfonamido ethanol (NEtFOSE); dose levels are expressed as ppm of NEtFOSE.
b The control animals will receive the basal diet only. c Five animals/sex/groupin Groups 1 through 5 will be sacrificed during Week 4
and five animals/sex/group in Groups 1 through 4 will be sacrificed during Week 14for hepatocellularproliferationrate measurementsand biochemical analyses (palmitoyl-CoAoxidation). d Five animalskexlgroup in Groups 1 and 5 will be sacrificed during Week 8; the remaining animals in Groups 5 and 7 will be sacrificed and discarded during Week 8.
e Ten animalslsexlgroup in Groups 1 and 4 will be designated as interim sacrifice animals and will be sacrificed after at least 78 weeks of treatment.
f Animals in Group 6 will be treated for at least 78 weeks, then treatment will be discontinued, and the animalswill be observed for reversibihty, persistence, or delayed occurrence of toxic effects for at least 26 weeks posttreatment. During
recovery, the animals will receive basal diet only.
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Protocol Amendment No.1
Page 5
10. Page 7, Dosing Procedures, Method of Administration. To reflect the decision to terminate Groups 5 and 7 during Week 8, delete the text in this section and replace with the following:
Dietary. Animals in Groups 1 through 4 will receive test diet for at least 104 weeks. Animals in Group 6 will receive test diet for 78 weeks only. Animals
in Groups 5 and 7 will receive test diet for at least 7 weeks.
11. Page 9, Observation of Animals,Body Weights. To reflect.the decision to record body weights before sacrificeduring Week 8, add the following to this section:
Body weights will also be recorded for all animalsin Groups 5 and 7 before
sacrifice during Week 8.
12. Page 10, Clinical Pathology, Frequency and Number of Animals, Scheduled Collections. To reflect the decision to collect clinicalpathology samplesfrom animals in Groups 1 and 5 during Week 8 and to terminate Groups 5 and 7 during Week 8, delete the text in this section and replace with the following:
Hematology, clinical chemistry, urinalysis, and urine chemistry will be done on five ammals/sex/groupfrom Groups 1 and 5 during Week 8. Hematology, clinical chemistry, urinalysis, urine chemistry, and serum sampling will be done on 10 animals/sex/group in Groups 1 through 4 during Weeks 14,27, and 53.
A blood film will be made and held for possible future examinationfor animalsat scheduled sacrifices after at least 78 and 104 weeks of treatment.
13. Page 12, Serum Analyses, Frequency and Number of Animals. To reflect the decision to collect serum samples from animalsin Groups 1 and 5 during Week 8
and to terminate Groups 5 and 7 during Week 8, delete the text in this section and
replace with the following:
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Five animals/sex/group in Groups 1 through 5 during Week 4 (animalsselected for
hepatocellular proliferation and biochemical analyses); five animals/sex/group in Groups 1 and 5 during Week 8; five animals/sex/group in Groups 1 through 4 during Week 14 (animals selected for hepatocellular proliferation and biochemical analyses); five animalshedgroup from Groups 1 and 4 (from animals selected for interim sacrifice) after at least 78 weeks of treatment; and five animals/sex/group from Groups 1 through 4 at the terminal sacrifke
14. Page 12, Hepatocellular Proliferation and Biochemical Analyses, Frequency and Number of Animals. To reflect the decision to perform analyses on livers from animalsin Groups 1 and 5 during Week 8 and to terminate Groups 5 and 7 during Week 8, delete the text in this section and replace with the following:
Five animals/sex/group in Groups 1 through 5 during Week 4; five animals/sex/group in Groups 1 and 5 during Week 8; and five animals/sex/group in Groups 1 through 4 during Week 14
15. Page 13, HepatocellularProliferation and Biochemical Analyses, Additional Liver Sample Collection. To reflect the decision to collect livers from animalsin Groups 1 and 5 during Week 8, delete the text in this section and replace with the following:
At the collections during Weeks 4,8, and 14, a portion of the remaining liver will be stored in a freezer set to maintain -60 to -80C. Samples will be packed on dry ice and shipped to Kris J. Hansen, PhD,3M EnvironmentalTechnology and Safety
Services. Samples will be retained by the Sponsor for possible future analysis.
16. Page 12, Hepatocellular Proliferation and Biochemical Analyses, Cell Proliferation Tissue Collection and Immunohistochemical Evaluation, Paragraph 1. To reflect the decision to collect only the left lateral lobe of the liver at the Week 8 and 14 collections, delete the text in this paragraph and replace with the following:
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Page 7
At each interval, animalswill be fasted overnight, anesthetized with sodium
pentobarbital, weighed, and exsanguinated. The abdominalcavity of each animal will be opened, and the liver will be removed and weighed. At the Week 4 collection, representative samples of left lateral, right median, and right lateral lobes of the liver and any macroscopic lesions of the liver will be collected and preserved in zinc formalin. At the Week 8 and 14 collections, representative samples of the left lateral lobe of the liver and any macroscopic lesions of the liver will be collected and preserved in zinc formalin.
17. Page 13, Termination, Scheduled Sacrifices. To reflect the decision to sacrifice five animals/sex/group from Groups 1 and 5,to terminate the remaining animalsin Groups 5 and 7 during Week 8, and to sacrifice five animals/sex/group from Groups 1 through 4, delete the text in this section and replace with the following:
Interim Sacrifices During Week 8, five animals/sex/groupfrom Groups 1 and 5 will be fasted overnight, bled for clinical pathology and serum analyses, anesthetized with sodium pentobarbital, weighed, exsanguinated, and necropsied. Liver samples will be collected for palimitoyl CoA, PCNA, and frozen samples for possible analysis. The remaining animalsin Groups 5 and 7 will be euthanatized with carbon dioxide and discarded without necropsy.
During Week 14, five animals/sex/group from Groups 1 through 4 will be fasted overnight, bled for clinical pathology and serum analyses, anesthetized with carbon dioxide, weighed, exsanguinated, and necropsied. Liver samples will be collected for palimitoyl CoA, PCNA, and frozen samples for possible analysis.
After at least 78 weeks of treatment, five animals/sex/groupfrom Group 1 and 10 animals/sex from Group 4 will be fasted overnight, anesthetized with carbon dioxide, weighed, exsanguinated, and necropsied. A blood film will be taken as part of the necropsy procedure.
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Page 8
.Terminal Sacrifice After at least 104 weeks of treatment, the remaining animalsin Groups 1through 4 will be fasted overnight, then anesthetized with carbon dioxide, weighed, exsanguinated, and necropsied. A blood film will be taken as part of the necropsy procedure.
Recovery Sacrifice After at least 78 weeks of treatment and 26 weeks without treatment, the
remaining animalsin Group 6 will be fasted overnight, then anesthetized with carbon dioxide, weighed, exsanguinated, and necropsied. A blood film will be taken as part of the necropsy procedure.
18. Page 14, Postmortem Procedures, Additional Liver Sample Collection. To reflect the decision to sacrifice five animals/sex/group from Groups 1and 5 and to terminate the remaining animalsin Group 5 and 7 during Week 8, delete the text in this section and replace with the following:
A portion of the liver will be collected from five animals/sex/group from Groups 1 and 4 at the Week 79 sacrifice and from five animals/sex/group from Groups 1 through 4 at the terminal sacrifice and stored in a freezer set to maintain -60 to -80C. Samples will be packed on dry ice and shipped to Kris J. Hansen,
PhD,3M Environmental Technology and Safety Services. Samples will be
retained by the Sponsor for possible future analysis.
19. Page 15, Postmortem Procedures, Histopathology. To reflect the decision to terminate Groups 5 and 7 early, to examine tissues from animalssacrificed during Weeks 8 and 14, and to examine tissues from Groups 4 and 6, delete the text in this section and replace with the following:
Tissues (as appropriate) from each animal in Groups 1,4, and 6 sacrificed at the Week 79 interim sacrifice and terminal sacrifice and from each animal that dies or is sacrificed at an unscheduled interval will be embedded in paraffin, sectioned, stained with hematoxylin and eosin, and examined microscopically. Adrenals, brain, eyes, kidneys, liver, mesenteric lymph node, pancreas, spleen, testes, and
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Page 9
,ovariesfrom the animals necropsied at Weeks 8 and 14 interim sacrifice will also be embedded in paraffin, sectioned, stained with hematoxylin and eosin, and examined microscopically.
Macroscopic lesions will also be examined microscopically from each animalin
Groups 2 and 3 sacrificed at terminal necropsy.
20. Page 16, Reports, Results. To reflect the decision to include results from Covance 6329-228 as an appendix to this report, add the following:
The study report for Covance 6329-228 will be included as an appendix to this report.
Effective March 30,1998
21. Page 12, Hepatocellular Proliferation and Biochemical Analyses, Cell Proliferation Tissue Collection and Immunohistochemical Evaluation, Paragraph 3. To include the microscopic examinations of liver sections stained with hematoxylin and eosin and to indicate that evaluations will be done on the left lateral lobe of the liver only, delete the text in this section and replace with the following:
Proliferation cell nuclear antigen (PCNA) evaluation will be done on the samples (left lateral lobe only). In addition, sections of the left lateral lobe of the liver will be stained with hematoxylin and eosin and examined microscopically. Results will be provided for inclusion in the final report.
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AMENDMENT APPROVAL
Covance 6329-212 Protocol Amendment No. 1
Page 10
Study Monitor 3M
Covance Laboratories Inc.
Date
,
~
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c o v m TMEDEVELOPMENTSERYlCESWYPANY
PROTOCOL AMENDMENT NO.2
Covance 6329-212
104Week Dietary Carcinogenicity Study with Narrow Range (98.1%) N-Ethyl Perfluorooctanesulfonamido Ethanol in Rats
Sponsor: Study Monitor: Testing Facility: Studv Director:
3M, St. Paul, Minnesota Andrew M. Seacat, PhD Covance Laboratories Inc., Madison, Wisconsin
Peter J. Thomford, PhD
This amendment modifies the following portions of the protocol:
Effective April 23,1998
1. Page 13, Termination, Unscheduled Sacrificesand Deaths. To reflect the decision to anesthetize animals with carbon dioxide for unscheduled sacrifices, delete the text in this section and replace with the following:
Necropsies will be done. Animals to be sacrificed will be anesthetized, weighed, and exsanguinated. Animals sacrificed before Week 13 will be anesthetized with sodium pentobarbital, animals sacrificed during or after Week 13 will be anesthetized with carbon dioxide. A blood film will be taken as part of the necropsy procedure for sacrificed animals.
Effective April 28,1998
2. Page 2, Alternate Study Monitor. To include alternate study monitor in the protocol, add the following after "Study Monitor:"
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.3M Medical Department Study: T6316.1
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Alternate Study Monitor
Marvin T. Case, DVM, PhD
3M Toxicology Services Telephone No. : 612.733.5 180 Facsimile No.: 612.733.1773
Covance 6329-212 Protocol Amendment No. 2
Page 2
3. Page 7, Group Designations and Dietary Levels. To reflect the decision to begin recovery after 52 weeks of treatment and to change the Week 79 interim sacrificeto Week 53, delete the text in this section and replace with the following:
Group
Number of Animals
Male
Female
Dietary Levels (ppm NEtFOSE)"
1 (Control)b*c*4e
70
2 (Low>"
60
3 (Mid)"
60
4 (Mid-High)"."
70
5 (HighYd
70
6 (Mid-High Recovery)'
40
7 Wgh Recovery)d
40
70
0
60
3
60
30
70
100
70
--3w
40
100
40
- 300
a T-6316 is 98.1% n-ethyl perfluorooctanesulfonamido ethanol (NEtFOSE); dose levels are expressed as ppm of NEtFOSE.
b The control animalswill receive the basal diet only. c Five animalslsexlgroupin Groups 1through 5 will be sacrificed during Week 4,
and five animals/sex/groupin Groups 1 through 4 will be sacrificed during Week 14 for hepatocellularproliferation rate measurements and biochemical analyses (palmitoyl-CoAoxidation). d Five animals/sex/group in Groups 1 and 5 will be sacrificed during Week 8; the remaining animalsin Groups 5 and 7 will be sacrificed and discarded during Week 8. e Ten animals/sex/group in Groups 1 and 4 will be designated as interim sacrifice animals and will be sacrificed after at least 52 weeks of treatment. f Animals in Group 6 will be treated for at least 52 weeks, then treatment will be discontinued, and the animalswill be observed for reversibility, persistence, or delayed occurrence of toxic effects for at least 52 weeks posttreatment. During recovery, the animals will receive basal diet only.
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4. Page 7, Dosing Procedures, Method of Administration. To reflect the decision to beg& recovery after 52 weeks of treatment, delete the text in this section and replace with the following:
Dietary. Animalsin Groups 1 through 4 wdl receive test diet for at least 104weeks. Animals in Group 6 will receive test diet for 52 weeks only. Animals in Groups 5 and 7 will receive test diet for at least 7 weeks.
5. Page 10, Clinical Pathology, Frequency and Number of Animals,Scheduled Collections, Paragraph 2. The Week 79 interim sacrifice will be moved to Week 53, therefore blood films will be prepared from animalssacrificed after 52 weeks of treatment. To reflect this decision, delete the text in this paragraph and replace with the following:
A blood film will be made and held for possible future examinationfor animals at scheduled sacrifces after at least 52 and 104 weeks of treatment.
6. Page 12, Serum Analyses, Frequency and Number of Animals. The Week 79 interim sacrifice will be moved to Week 53, therefore serum samples will be collected from animals sacrificed after 52 weeks of treatment. To reflect this decision, delete the text in this section and replace with the following:
Five animals/sex/groupin Groups 1 through 5 during Week 4 (animalsselected for hepatocellular proliferation and biochemical analyses); five animals/sex/group in Groups 1 and 5 during Week 8; five animals/sex/group in Groups 1 through 4 during Week 14 (animalsselected for hepatocellular proliferation and biochemical analyses); five animals/sex/group from Groups 1 and 4 (from animals selected for interim sacrifice) after at least 52 weeks of treatment; and five anjmals/sex/group from Groups 1 through 4 at the terminal sacrifice.
7. Page 13, Termination, Scheduled Sacrifices. To reflect the decision to move the Week 79 interim sacrifice to Week 53 and to begin recovery after 52 weeks of treatment, delete the text in this section and replace with the following:
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Covance 6329-212 Protocol Amendment No.2
Interim Sacrifices During Week 8, five animalshedgroup from Groups 1 and 5 will be fasted overnight,bled for clinicalpathology and serum analyses, anesthetized with sodium pentobarbital, weighed, exsanguinated,and necropsied. Liver samples will be collected for palimitoyl CoA analysis and PCNA evaluation; additional liver
samples will be frozen for possible analysis. The remaining animals in Groups 5
and 7 will be euthanatized with carbon dioxide and discarded without necropsy.
During Week 14, five animaldsedgroup from Groups 1through 4 will be fasted overnight, bled for clinicalpathology and serum analyses, anesthetized with carbon dioxide, weighed, exsanguinated,and necropsied. Liver samples will be collected for palimitoyl CoA analysis and PCNA evaluation; additional liver samples will be frozen for possible analysis for possible analysis.
After at least 52 weeks of treatment, five animals/sedgroup from Group 1 and 10 animals/sex from Group 4 will be fasted overnight, anesthetized with carbon dioxide, weighed, exsanguinated, and necropsied.
Terminal Sacrifice After at least 104 weeks of treatment,the remaining animalsin Groups 1 through 4 will be fasted overnight, then anesthetizedwith carbon dioxide, weighed, exsanguinated,and necropsied. A blood film will be taken as part ofthe necropsy procedure.
Recovery Sacrifice M e r at least 52 weeks of treatment and 52 weeks without treatment, the remaining animalsin Group 6 will be fasted overnight, then anesthetized with carbon dioxide, weighed, exsanguinated, and necropsied. A blood film will be taken as part of the necropsy procedure.
8. Page 14, Postmortem Procedures, Organ Weights. To reflect the decision to record organ weights at the Week 8, 14, and 53 interim sacrifices only, delete the text in thrs section and replace with the following:
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Covance 6329-212 Protocol Amendment No. 2
At the Week 8, 14, and 53 interim sacrifices, the following organs (when present) will be weighed; paired organs will be weighed separately:
adrenal (2) brain kidney (2) liver
lung
ovary (2) spleen testis (2) thyroid (2) with parathyroid uterus with cervjx
Organ-to-body weight percentages and organ-to-brainweight ratios will be calculated.
9. Page 14, Postmortem Procedures, Additional Liver Sample Collection. The Week 79 interim sacrifice will be moved to Week 53,therefore liver samples will be collected from animals sacrificed after 52 weeks of treatment. To reflect this decision, delete the text in this section and replace with the following:
A portion of the liver will be collected from five animals/sex/group from Groups 1 and 4 at the Week 53 sacrifice and from five animals/sex/group from Groups 1 through 4 at the terminal sacrifice and stored in a freezer set to maintain -60 to -80C. Samples will be packed on dry ice and shipped to Kris J. Hansen,
PhD, 3M Environmental Technology and Safety Services. Samples will be
retained by the Sponsor for possible future analysis.
10. Page 15, Postmortem Procedures, Histopathology, Paragraph 1. The Week 79 interim sacrifice will be moved to Week 53, therefore histopathology will be done for animals sacrificed after 52 weeks of treatment. To reflect this decision, delete the text in this section and replace with the following:
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.
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Covance 6329-212
Protocol Amendment No.2
Tissues (as appropriate) from each animal in Groups 1,4, and 6 sacrificed at the Week 53 interim sacrifice and terminal sacrifice and from each animal that dies or is sacrificed at an unscheduled interval will be embedded in parain, sectioned, stained with hematoxylin and eosin, and examined microscopically. Adrenals, brain, eyes, kidneys, liver, mesenteric lymph node, pancreas, spleen, testes, and ovaries from the animalsnecropsied at the Week 8 and 14 interim sacrifices will also be embedded in paraffin, sectioned, stained with hematoxylin and eosin, and examined microscopically.
11. Page 15, Reports, Paragraph 1. To reflect the decision to provide unaudited summary reports after the Week 14 and 53 interim sacrifices, delete the text inthis paragraph and replace with the following:
After the Week 14 and 53 interim sacrifices, unaudited summary reports will be sent to the Sponsor. The summary reports will include a brief description of methods and results and summary tables of in-life data, clinical pathology data, and anatomical pathology data. After completion of the study, one copy of the draft report will be sent to the Sponsor. The draft report will include the following information:
Effective May 15,1998
12. Page 12, Serum Analyses, Method of Collection. To reflect the decision to increase the volume collected for serum analyses at the Week 53 and 105 sacrifices, delete the text in this section and replace with following:
Animals will be fasted overnight; blood (approximately2 mL at the Week 4, 8 and 14 sacrifices, approximately 3 mL at the Week 53 and 105 sacrifices) will be collected from a jugular vein. Samples wdl be collected without anticoagulant.
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AMENDMENT APPROVAL
C O V ~ I6I C32~9-212
Protocol Amendment No.2
Page 7
Andrew M. Seacat, PhD Study Monitor 3M
Covhce Laboratories Inc.
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covm
PROTOCOL AMENDMENT NO. 3
Covance 6329-212
1WWeek Dietary CarcinogenicityStudy with Narrow Range (98.1%) N-Ethyl PeduorooctanesulfonamidoEthanol m Rats
sponsor: Study Monitor:
Testing Facility:
Study Director:
3M,St. Paul, Minnesota Andrew M. Seacat, PhD Covance LaboratoriesInc., Madison, Wisconsin Peter J. Thomford, PhD
This amendment modifies the following portions of the protocol:
Effective January 21,1998
1. Page 4. To include the vehicle used to dissolve the test material before mixing with the diet, add the following section.
Vehicle
Identification Acetone
Lot Numbers The lot numbers will be maintained in the raw data.
MtY On file with the manufacturer Stability
On file with the manufacturer Storage Conditions At room temperature
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characteristics
Information on synthesismethods, composition, or other characteristics that define the vehicle is on file with the manufacturer.
2. Page 16, Reports, Results. To include organ weights as a result to be reported, add "organ weights" to this section.
3. Page 16, Reports, Statistical Evaluation. To include statistical evaluation of organs weights, add "organ weights (Weeks 8, 14, and 53 interim sacrifices only)"
Effective April 28,1998
4. Page 7, Group Designationsand Dietary Levels, Footnote e. To correct the number of Group 1animalsto be sacrificed at the Week 53 interim sacrifice, delete thissentence and replace with the foIIowing:
e Five aninddsex in Group 1 and 10 animals/sex m Group 4 will be designated as interim sacrifice animals and will be s a c s c e d after at least 52 weeks of treatment.
Effective June 30,1998
5. Page 8, Dosing Procedure, Retention Samples. To reflect the decision to send retention samples of control diet to the Sponsor, delete the text m this section and replace with the following:
Samples (approximately 100 g) Win be taken from each dose preparation during the in-life phase and stored at room temperature. Unless used for analyses, retention samples from the treated groups Win be discarded at least 1 month after completion of the in-life phase. Samples from control diets prepared for Weeks 24 and before will be shipped to:
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Covance 6329212 Protocol Amendment No.3
Kris J. Hartsen, PhD 3M EnvironmentalTechnology and Safety Services 935Bush Avenue Building 2-3E-09 St. Paul, Minnesota 55133-3331
Telephone No.: 651.778.6018 Facsimile No.: 651.778.6176
Efkctive July 20,1998
6. Page 2, Study Monitor and Alternate Study Monitor. To indicate the change in the area code, delete the text in these sections and replace with the following:
Study Monitor Andrew M.Seacat, PhD 3M Telephone No.: 651.575.3161 Facsimile No.: 651,733,1773
Alternate Study Monitor Marvin T. Case, DVM,PhD 3M Toxicology Services Telephone No.: 651.733.5180
Facsimile No.: 651.733.1773
7. Page 4, Disposition of Test Material. To indicate the change m the area code, delete the text m these section and replace with the following:
After authorization fiom the Sponsor, any remaining test material will be returned to:
Andrew M. Seacat, PhD 3M
Toxicology Services Building 220-2E-O2,3MCenter St. Paul, Minnesota 55144-1000
Telephone No.: 651-575.3161 Facsimile No.: 651.733.1733
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Covance 6329212 Protocol Amendment No. 3
8. Page 12, Clinical Pathology, Serum Samples. To indicate the change in the area code, delete the text m these section and replace with the following:
Serum not used for clinical chemistry will be stored in a freezer set to maintain -60 to -80C. Samples will be packed on dry ice and shipped to:
Kris J. Hamen, PhD 3M Environmental Technology and Safety Services 935 Bush Avenue Building 2-3E-09
St. Paul, Minnesota 55133-3331
Telephone No.: 651.778.6018
Facsimile No.: 651.778.6176
Samples will be retained by the Sponsor for possible future analysis.
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A M E N D ~ N TAPPROVAL
Covance 6329212 Protocol Amendmemt No. 3
Andrew M. Seacat, PhD Study Monitor 3M
Study Direztor Covance Laboratories Inc.
Date '
3M Environmental Laboratory
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c o v m TnEDEVELOPYEN7SERVKIS COYPANV
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PROTOCOL AMENDMENT NO.4
Covance 6329-212
104-Week Dietary CarcinogenicityStudy with Narrow Range (98.1%)N-Ethyl Perfluorooctanesulfonamido Ethanol in Rats
Sponsor: Study Monitor: Testing Facility: Study Director:
3M,St.Paul, Minnesota Andrew M. Seacat, PhD Covance LaboratoriesInc., Madison, Wisconsin Peter J. Thomford, PhD
This amendment modifies the following portion of the protocol.
Effective January 13,2000
1. Page 14, Postmortem Procedures, Tissue Preservation. The Sponsor has requested that a subset of tissuesbe collected for possible electron microscopy. Therefore, add the following to thissection
At the terminalsacrifice, sections of the heart and liver will be collected from
10 animals/sex/group m Groups 1,3,4, and 6 and preserved m 2.0% paraformaldehyde/2.5% glutaraldehyde in 0.1 M phosphate buffer. These tissues win be processed and embedded in epoxy blocks for possible future
examination by electron microscopy.
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AMENDMEN" APPROVAL
Covance 6329-2 12 Protocol Amendment No.4
Page 2
&&?if
Andrew M.Seacat, PhD
Study Monitor
3M
~ovanceLaboratories ~nc:
3M Environmental Laboratory
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?
c o v m WE DEVELOPMENTSERYKXS COMPANY
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PROTOCOL AMENDMENT NO.5
Covance 6329-212
104-Week Dietary Carcinogenicity Study with Narrow Range (98.1%) N-Et,.yl Perfluorooctanesulfonamido Ethanol in Rats
Sponsor: Study Monitor: Testing Facility: Study Director:
3M, St. Paul, Minnesota Andrew M. Seacat, PhD Covance Laboratories Inc., Madison, Wisconsin. Peter J. Thomford, PhD
This amendment modifies the following portion of the protocol.
EffectiveJanuary 21,2000
1. Page 10, Clinical Pathology, Frequency and Number of Animals,Scheduled Collections. The Sponsor has requested that specific clinical chemistry parameters be determined for animals at terminaland recovery sacrifice. To & e c t this decision, add the following to thissection
In addition, samples for clinicalchemistryparameters (cholesteroland
triglycerides) will be collected from all remaining animals at terminal and recovery sacrifice.
2. Page 12, Serum Analyses, Frequency and Number of Animals. The Sponsor has requested that serum be collected from all animalsat terminal and recovery
sacrifice. To reflect this decision, delete the text in this section and replace with the following.
Five animals/sex/group in Groups I through 5 during Week 4 (animalsselected for hepatocellular proliferation and biochemical analyses); five animals/sex/group in Groups 1 and 5 during Week 8; five animals/sex/group in Groups 1through 4 during Week 14 (animalsselected for hepatocellular proliferation and biochemical analyses); five anirnals/sex/groupfrom Groups 1 and 4 (from animals selected for interim sacrifice) after at least 52 weeks of treatment; and all remaining animals at terminal and recovery sacrifice.
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Covance 6329-212 Protocol Amendment No.5
3. Page 14, Postmortem Procedures,Additional Liver Sample Collection. The Sponsor has requested that frozen liver samples be collected from all animalsat terminal and recovery sacrifice. Therefore, delete the text in this section and replace with the following.
A portion of the liver will be collected from five animals/sex/group from Groups 1
and 4 at theWeek 53 sacrifice and from all remaining animalsat the terminal and recovery sacrifice and stored in a freezer set to maintain -60 to -80C. Samples will be packed on dry ice and shipped to Kris J. Hansen, PhD, 3M Environmental
Technology and Safety Services. Samples will be retained by the Sponsor for possible future analysis.
EffectiveJanuary 26,2000
4 Page 15, Postmortem Procedures, Histopathology. The Sponsor has requested
that all tissues from animalsin Groups 1and 4 at terminal sacrifice and selected tissues from animals in Groups 2,3, and 6 at the terminal and recovery sacrifice be examined microscopically. To reflect this decision, delete the text in thissection and replace with the following.
Tissues (as appropriate) from each animalin Groups 1and 4 sacrificed at the
terminal sacrifice and from each animalthat dies or is sacrificed at an unscheduled interval wiIl be embedded in paraffin,sectioned, stained with hematoxylin and eosin, and examined microscopically.
Tissues (as appropriate) fiom each animal in Groups 1,4, and 6 sacrificed at the
Week 53 interim sacrifice will be embedded in paraffin, sectioned, stained with
hematoxylin and eosin, and examined microscopically.
Lesions, liver, lungs, kidneys, pancreas, thyroid, testes, and mammary glands (females) from each animalin Groups 2,3, and 6 sacrificed at the terminal and recovery sacrifice wiU be embedded in paraffin, sectioned, stained with hematoxylin and eosin, and examined microscopically. Parathyroids will be processed with the thyroids, but will not be examined.
Adrenals, brain, eyes, kidneys, liver, mesenteric lymph node, pancreas, spleen,
testes, and ovaries fromthe animalsnecropsied at the Week 8 and 14 interim sacrifices will also be embedded in paraffin, sectioned, stained with hematoxylin and eosin, and examined microscopically.
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AMENDMENT APPROVAL
Covance 6329-212 Protocol Amendment No.5
Page 3
- Andrew M. Seacat, PhD
Study Monitor 3M
3M Environmental Laboratory
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3M Environmental Laboratory
Protocol - Analytical Study Phase
104-Week Dietary Carcinogenicity Study with Narrow Range N-Ethyl PerfluorooctanesulfonamidoEthanol in Rats
In-Vivo Study Reference Number: Covance # 6329-212
Study Number: AMDT-092597.1 Test Material: T-6316
Name and Address of Sponsor:
3M Toxicology Services Building 220-2E-O2,3M Center St. Paul, MN 55144-1000
Name and Address of Testing Facility:
3M Environmental Technology and Services 935 Bush Avenue St. Paul, MN 55106
Proposed Initiation Date: April 7,1998
Proposed Completion Date: October, 31,1998
Method Numbers and Revisions FACT-M-1.0, Extraction of Perfluorooctanesulfonate from Liver for Analysis
using HPLC-ElectrosprayNass Spectrometry FACT-M-2.0, Analysis of Liver Extracts for Fluorochemicals using HPLC-
ElectrosprayMass Spectrometry
FACT-M-3.0, Extraction ofPerfluorooctanesulfonatefrom Sera for Analysis
using HPLC-ElectrosprayNas Spectrometry FACT-M-4.0, Analysis of Sera Extracts for Fluorochemicals using HPLC-
ElectrosprayMass Spectrometry
Author: Lisa Clemen
Kris J. Handen, PhD Study Director
II ?[ f t Date
Dale Bacon
Date
Study Director Management
Andrew M. Seacat, PG
Dhe
Sponsor Representative
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1.0 PURPOSE
1.1 According to this analytical protocol, the 3M Environmental Laboratory will analyze the tissue and fluid samples fiom the Covance study number 6329-212, "104-Week Dietary Carcinogenicity with Narrow Range N-Ethyl Perfluorooctanesulfonamido Ethanol in Rats." The collected data will be given to the sponsor for their use in the assessment of toxicological effects of the test material when administered in the diets of rats for at least 104 weeks.
1.2 Data collected in the Environmental Laboratory will be considered non-quantitative screening data until future studies have been conducted to determine absolute recoveries of specific or general fluorochemical compounds.
2.0 REGULATORY COMPLIANCE
2.1 This analytical phase of the study will be conducted in accordance with the FDA Good Laboratory Practices Regulations 21 CFR 58, with the following exceptions:
2.1.1 The analytical phase is being conducted as a separate study and therefore has a separate Study Director, protocol, and f m d report, from those listed in the Covance protocol 6329-212.
2.1.2 The characterization of the reference material, including purity, identity, and stability, are the responsibility of the sponsor.
2.1.3 Sample storage stability will not be determined.
3.0 TEST MATERIALS
3.1 Control, and reference Materials and Matrices
3.1.1 Analytical Reference Material: T-6316, from 3M ICPRCP Division
3.1.2 Analytical Reference Matrix: Rat liver, from Covance and rat serum, from Sigma Chemical Company.
3.1.3 Analytical Control Material: None.
3.1.4 Analytical Control Matrix: Rat liver, fiom Covance and rat serum, fkom Sigma
Chemical Company.
3.2 Number of Test and Control Samples: Liver and serum fiom 680 test animals and 140 control animals will be made available; samples will be analyzed as requested by the sponsor or the study director. Other biological tissues (kidney, bile, dermal application site, and cellular fraction) will be available for analysis if deemed appropriate.
3.3 Identification of Test and Control Samples: The samples will be identified using the Covance animal identification number which consists of a letter and five digit number, plus the tissue identity and day identity (serum).
3.4 Purity and Identity of Reference Material: To be determined by Sponsor.
3.5 Stability of Reference Material: To be determined by Sponsor.
3.6 Storage Conditions for Reference Materials: Reference materials will be stored at room temperature (3.1.l), and samples will be stored at -20 f 10C (3.1.2,3.1.4). Test and Control samples will be received according to AMDT-S-10-0.
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3.7 Disposition of Specimens: Biological tissues and fluids will be retained per GLP Regulation for the time period required for studies longer than 28 days.
3.8 Safety Precautions: Refer to appropriate MSDS. Wear appropriate laboratory attire. Use caution when handling knives for cutting tissue samples.
4.0 EXPERIMENTAL - Overview
4.1 The tissues from animals dosed as described (Covance# 6329-212), will be available for analysis for fluorine-containingcompounds. At the discretionof the Study Director, a series of analytical tests can be performed. All high dose and control sera and livers will be analyzed initially using HPLC-electrospray mass spectrometry to identify fluorine-containing compounds of interest present in the sera and liver (if any). The screening for fluoride in liver via combustion may be performed to present definitive data for fluorine in the liver. Based on the findings from these analyses, additional samples, tissues, or fluids may be analyzed at the discretion of the Study Director to determine the presence of fluorochemicals in these matrices.
5.0 EXPENMENTAL - Methods
5.1 Methods (attached): 5.1.1 FACT-M-1.0, "Extraction of Perfluorooctanesulfonatefrom Liver for Analysis using HPLC-ElectrosprayMass Spectrometry'' 5.1.2 FACT-M-2.0, "Analysis of Liver Extracts for Fluorochemicals using HPLCElectrosprayMass Spectrometry'' 5.1.3 FACT-M-3.0, "Extraction of Perfluorooctanesulfonate from Serum for Analysis using HPLC-ElectrosprayM a s s Spectrometry" 5.1.4 FACT-M-4.0, "Analysis of Serum Extracts for Fluorochemicals using HPLCElectrosprayMass Spectrometry''
6.0 DATA ANALYSIS
6.1 Quality Control: Matrix spikes will be extracted and analyzed to determine accuracy of the method. Also, continuing calibration checks will be analyzed to determine response bias.
6.2 Transformations: Any transformationsperformed on data collected during the analytical phase of the study will be documented in the final report.
6.3 Statistics: At the discretion of the Study Director, statistics used may include regression
analysis of serum concentrationswith time, averages, and standard deviationsof
concentrationsfor the different dose groups. If necessary, simple tests such as the Student's t-test may be applied to determine statistical difference. Any statistical analysis performed will be documented in the final report.
6.4 Data Reporting: A final data package will be submitted to 3M Toxicology Services. The data package will include the following with additional data included as deemed appropriate.
6.4.1 A summary of individual sample results, reported as a concentration (weightlweight, weightlvolume) of fluoride per tissue or fluid, or as the mass of a specific fluorochemical (HPLC-electrospray mass spectrometry) per unit of tissue or fluid.
6.4.2 A summary of quality control results (continuing calibration checks, method blanks, instrument blanks, matrix spikes, and matrix spike duplicates).
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6.4.3 Certified copies or originals of the written validated methods.
6.4.4 Certified copies or originals of sample identification sheets sent from Covance.
6.4.5 Certified copies or originals of study specific raw data.
6.4.6 A summary of key personnel involved with the analytical phase of the study.
6.4.7 A signed QAU statement listing the dates of inspections and reports of findings to management and Study Director.
7.0 MAINTENANCE OF RAW DATA AND RECORDS
7.1 The following raw data and records (or certified copies thereof) will be maintained in the study folder in the archives according to appropriate SOPs.
7.1.1 7.1.2 7.1.3 7.1.4 7.1.5 7.1.6 7.1.7
Approved protocol Approved methods Data summaries Study correspondence Shipping records Raw data Electronic copies of data
7.2 Supporting records to be retained separately from the study folder in the archives according to 3M ET & S S SOPs, will include, but not necessarily be limited to the following:
7.2.1 7.2.2 7.2.3 7.2.4 7.2.5 7.2.6
Approved validation reports Training records Calibration records Instrument maintenance logs Standard operating procedures, equipment procedures, and methods Appropriate specimens
8.0 REFERENCES
8.1 AMDT-S-1, "Chemical Tracking" 8.2 AMDT-S-2, "Solutions and Standards Making" 8.3 AMDT-S-3, "Training" 8.4 AMDT-S-4, "General Lab Documentation Systems" 8.5 AMDT-S-5, "GLP-related Documentation Systems" 8.6 AMDT-S-6, "General Lab Records" 8.7 AMDT-S-7, "GLP-Related Records" 8.8 AMDT-S-8, "Archives" 8.9 AMDT-S-9, "GLP Program and Responsibilities" 8.10 AMDT-S-10, "Sample Tracking System"
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8.11 AMDT-S-12, "Analytical Method Validation" 8.12 AMDT-S-13, "Equipment Installation" 8.13 AMDT-S-14, "Quality Assurance Unit" 8.14 AMDT-S-15, "Laboratory Practices and Data Management" 8.15 AMDT-S-17, "Analytical Equipment Systems Documentation" 8.16 AMDT-S-18, "Routine Calibration Checks of Balances"
8.17 AMDT-S-20, "Daily Calibration Check of Automatic Pipettors"
8.18 AMDT-S-21, "Annual Calibration Checks of Automatic Pipettors"
8.19 AMDT-S-25, "Labeling, Storage, and Use of Test, Control, and Reference Substances"
8.20 AMDT-S-30, "Project Control and Data Review in the AMDT"
9.0 ATTACHMENTS 9.1 FACT-M-1.0, Extraction of Perfluorooctanesulfonate fiom Liver for Analysis using HPLC-
ElectrosprayMass Spectrometry 9.2 FACT-M-2.0, Analysis of Liver Extracts for Fluorochemicals using HPLC-
ElectrosprayMass Spectrometry 9.3 FACT-M-3.0, Extraction of Perfluorooctanesulfonate from Serum for Analysis using HPLC-
ElectrosprayMass Spectrometry 9.4 FACT-M-4.0, Analysis of Serum Extracts for Fluorochemicals using HPLC-
ElectrosprayMass Spectrometry
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Study Title 104-Week Dietary Carcinogenicity Study with Narrow Range N-Ethyl
PerfluorooctanesulfonamidoEthanol in Rats
PROTOCOL AMENDMENT NO. 1
Amendment Date: 20 January 2000
Performing Laboratory 3M Environmental Technology & Safety Services
3M Environmental Laboratory
935 Bush Avenue St. Paul, MN 55106
Laboratory Project Identification ET&SS LRN-U2103 FACT TOX-001
Covance Study: 6329-212 3M Medical Department Study: T-63 16.1
3M Environmental Laboratory
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Protocol LRN-U2103 Amendment Number 1
This amendment modifies the following portion(s) of the protocol:
1. PROTOCORLEADS: The following methods will be used:
FACT-M-1.O,Extraction of Perfluorooctanesulfonatefrom Liver for Analysis using
HPLC-Electrospray/Mass Spectrometry FACT-M-2.0, Analysis of Liver Extracts for Fluorochemicals using HPLCElectrospray/Mass Spectrometry FACT-M-3.0, Extraction of Perfluorooctanesulfonatefrom Sera for Analysis using HPLC-Electrospray/Mass Spectrometry FACT-M-4.0, Analysis of Sera Extracts for Fluorochemicals using HPLCElectrospray/Mass Spectrometry
AMENDTO READ: The following methods will be used: ETS-8-4.1, Extraction of Potassium Perfluorooctanesulfonateor Other Fluorochemical compounds from Serum for Analysis Using HPLCElectrospray/Mass Spectrometry
ETS-8-5.1, Analysis of Potassium Perfluorooctanesulfonateor Other
Fluorochemicals in Serum Extracts Using HPLC-Electrospray/Mass Spectrometry ETS-8-6.0, Extraction of Potassium Perfluorooctanesulfonate or other Fluorochemical Compounds from Liver for Analysis using HPLC-ElectrospraylMass Spectrometry ETS-8-7.0, Analysis of Potassium Perfluorooctanesulfonate or Other Fluorochemicals in Liver Extracts Using HPLC-Electrospray/Mass Spectrometry
REASON: The methods originally listed were superseded during the course of the study.
2. PROTOCORLEADS: There is no independent section of the protocol that addresses sample retention. AMENDTO READ: Specimens will be maintained in the 3M Environmental Laboratory specimen archives. Any specimens sent to sub-contract laboratories will be returned to the 3M Environmental Laboratory upon completion of analysis and submission of the subcontract laboratory(s) final report. Specimens analyzed at sub-contract laboratories will be returned with the following documentation: the signed original chain of custody and records of storage conditions while at the sub-contract facility. REAsON: To define in detail the appropriate disposition of specimens analyzed at subcontract laboratories.
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LRN-U2103
Protocol LRN-U2103 Amendment Number I
3. PROTOCORLEADS:
Section 7 states that the following raw data and records will be retained in the study folder in the archives according to AMDT-S-8: Approved protocol and amendments; approved methods; data summaries; study correspondence; shipping records; raw data; and electronic copies of data. Additionally, Section 7 states that supporting records to be retained separately from the study folder in the archives according to AMDT-S-8 will include at least the following: Approved validation reports; training records; calibration records; instrument maintenance logs; Standard Operating Procedures, Equipment Procedures, and Methods; and appropriate specimens. AMENDTO READ: Section 7 states: "The original data, or copies thereof, will be available at the 3M Environmental Laboratory to facilitate audits of the study during its progress and before acceptance of the final report. When the final report is completed, all original paper data, including: approved protocol and amendments, study correspondence, shipping records, raw data, approved final report, and electronic copies of data will be retained in the archives of the 3M Environmental Laboratory. All corresponding training records, calibration records, instrument maintenance logs, standard operating procedures, equipment procedures, and methods will be retained in the archives of the facility performing each analysis." REASON: To direct subcontract laboratories in the disposition of the items listed above.
4. PROTOCOL READS: The study director for the present study was identified in the protocol as Kristen J. Hansen, Ph.D. AMENDTO READ: The role of study director for the present study was reassigned to John L. Butenhoff, Ph.D., as of 20 January 2000. The previous study director, Kristen Hansen, has been reassigned to the role of Principle Analytical Investigator.
REASON:
The role of study director was reassigned in an effort to ensure compliance with Good Laboratory Practice Standards that outline study personnel requirements (refer to 21 CFR Part 58).
5. PROTOCOL READS: The sponsor for the present study was identified as Andrew M. Seacat, Ph.D. AMENDTO READ: The role of sponsor for the present study was reassigned to Marvin T. Case, D.V.M., Ph.D., as of 20 January 2000. REASON: The change was made at the request of the sponsor.
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Amendment Approval
Analytical Report: FACT-TOX-001
LRN-U2103 Protocol LRN-U2I03 Amendment Number I
Andrew M Seacat, Ph.D., Outgoing Sponsor Representative
k l L 6 Kristen J. Hansen, Ph.D., Outgoing Study Director
5!I/Lb/zoaa
date
/ / - F C b -POO Date
/ b hLL 5L-04
Marvin T.Case, D. K M , Ph.D., Incoming Sponsor Representative
Date
John L. ButenhoJfjCPh.D., Incoming Study Director
F& 2 w y $ l o /
Date
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Study Title 104-Week Dietary Carcinogenicity Study with Narrow Range N-Ethyl
PerfluorooctanesulfonamidoEthanol in Rats
PROTOCOL AMENDMENT NO. 2
Amendment Date: January 8,2001
Performing Laboratory 3M Environmental Technology & Safety Services
3M Environmental Laboratory 935 Bush Avenue
St. Paul, MN 55106
Laboratory Project Identification ET&SS LRN-U2103 FACT TOX-001 Covance 6329-212
3M Medical Department Study:T-6316.1
3M Environmental Laboratory 3M Environmental Laboratory
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LRN-U2103 Protocol FACT TOX-001
Amendment No. 2
This amendment modifies the following portion(s) of the protocol:
1. PROTOCOL READS: 1.2 Data collected in the Environmental Laboratory will be considered non-quantitative screening data until future studies have been conducted to determine absolute recoveries of specific or general fluorochemical compounds.
AMENDTO READ: 1.2 If matrix spike studies provide accurate representation of recovery of endogenous levels of PFOS, PFOSA, PFOSAA, PFOSEA,M556,and EtFOSE-OH, the 3M EnvironmentalLaboratory will provide semi-quantitative data for sera and liver samples collected from test animals.
REASON: Due to improved analytical methods, the decision was made to change the purpose of the study results from non-quantitative to semi-quantitative.
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Amendment Approval
#
Analytical Report: FACT-TOX-001
LRN-U2103 Protocol FACT TOX-001
Amendment No. 2
Marvin T. Case, D.V.M., Ph.D., Sponsor Representative
/d 9-l */
Date
c
John L. Butenhog Ph.D., Study Direcior
pH JWzaar
Date
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Study Title 104-Week Dietary Carcinogenicity Study with Narrow Range N-Ethyl
Perfluorooctanesulfonamido Ethanol in Rats
PROTOCOL AMENDMENT NO. 3
Amendment Date: February 15,2001
Performing Laboratory 3M Environmental Technology & Safety Services
3M Environmental Laboratory 935 Bush Avenue
St. Paul, MN 55 106
Laboratory Project Identification ET&SS LRN-U2 103 FACT TOX-001 Covance 6329-212
3M Medical Department Study: T-6316.1
3M Environmental Laboratory
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Protocol FACT TOX-001 Amendment No. 3
This amendment modifies the following portion@) of the protocol:
1. PROTOCOL READS: Specimens will be maintained in the Environmental Laboratory specimen archives. Any specimen sent to sub-contract laboratories will be returned to the 3M Environmental Laboratory upon completion of analysis and submission of the sub-contracted laboratory(s) final report. Specimens analyzed at sub-contracted laboratories will be returned with the following documentation: the signed original chain of custody and records of storage conditions while at the sub-contracted facility.
AMENDTO READ: Specimens will be maintained in the Environmental Laboratory specimen archives. Specimens sent to sub-contract laboratories for analysis of PFOS will be returned to the 3M Environmental Laboratory upon completion of analysis and submission of the sub-contracted laboratory(s) final report. Specimens sent to sub-contract laboratories for analysis of compounds other than PFOS will not be returned. Specimens returned by sub-contracted laboratories will be returned with the following documentation: the signed original chain of custody and records of storage conditions while at the sub-contracted facility.
REASON: Some specimens sent to sub-contract laboratories will not be returned. Portions of these specimens have been retained at the 3M Environmental Laboratory.
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Amendment Approval
Analytical Report: FACT-TOX-001 LRN-U2103
Protocol FACT TOX-001 Amendment No. 3
Marvin T. Case, D.V.M., Ph.D., Sponsor Representative
Date
John L. Butenhog, Ph.D., Study Director
Date
3M Environmental Laboratory 3M Environmental Laboratory
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Study Title 104-Week Dietary CarcinogenicityStudy with Narrow Range N-Ethyl
Perfluorooctanesulfonamido Ethanol in Rats
PROTOCOL AMENDMENT NO. 4
Amendment Date: April 2,2001
Performing Laboratory 3M Environmental Technology & Safety Services
3M Environmental Laboratory
935 Bush Avenue St. Paul, MN 55106
Laboratory Project Identification ET&SS FACT TOX-001
3M Laboratory Request No. U2103
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LRN-U2103 Protocol FACT TOX-001
Amendment #4
This amendment modifies the following portion(s) of the protocol:
1. THEAMENDED PROTOCOL READS: (Amendment #1) The following methods will be used: ETS-8-4.I , "Extraction of Potassium Perfluorooctanesulfonate or Other Fluorochemical Compounds from Serum for Analysis Using HPLC-ElectrosprayMass Spectrometry" ETS-8-5.I , "Analysis of Potassium Peffluorooctanesulfonateor Other Fluorochemicals in Serum Extracts Using HPLC-ElectrosprayMassSpectrometry" ETS-8-6.0, "Extraction of Potassium Perfluorooctanesulfonate or Other Fluorochemical Compounds from Liver for Analysis Using HPLC-ElectrosprayMass Spectrometry" ETS-8-7.0,"Analysis of Potassium Perfluorooctanesulfonateor Other Fluorochemicals in Liver Extracts Using HPLC-ElectrosprayMassSpectrometry"
AMENDTO READ: The following methods will be used: ETS-8-4.1, "Extraction of Potassium Perfluorooctanesulfonate or Other Fluorochemical Compounds from Serum for Analysis Using HPLC-ElectrosprayMass Spectrometry" ETS-8-5.I , "Analysis of Potassium Perfluorooctanesulfonate or Other Fluorochemicals in Serum Extracts Using HPLC-ElectrosprayMass Spectrometry"with thefollowing exception: (Section 14.5.1) "Matrix spike recoveries must be within -F 30% of the spiked concentration for all analytes except M556, which must be within 6 0 % . ETS-8-6.0, "Extraction of Potassium Perfluorooctanesulfonate or Other Huorochemical Compounds from Liver for Analysis Using HPLC-ElectrosprayMas Spectrometry" ETS-8-7.0, "Analysis of Potassium Perfluorooctanesulfonate or Other Fluorochemicals in Liver Extracts Using HPLC-ElectrosprayMass Spectrometry" with the following exception: (Section 14.5.1) "Matrix spike recoveries must be within +30% of the spiked concentration for all analytes except PFOS, which must be G O % .
REASON: The analytical method and resulting QC data support a 50%-150% acceptable
range for spike recoveries for these analytes and matrices.
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Protocol FACT TOX-001 Amendment #4
Amendment Approval
John L. Butenhoff, Ph.D., Study Director
Date
Marvin T. Case, D.KM., Ph.D., Sponsor Representative
Date
3M Environmental Laboratory
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Record of Deviation
1 Study / Project No.
1. FACT-TOX-001
Identification Covance 6329-212
Deviation Type (Check one)
0 SOP
X Method 0 Equipment Procedure
0 Protocol 0 Other:
_ _ _ _ I - ____ ___
Document N&ber(s):
Date(s) of occurrence:
FACT-M-2.0, FACT-M-4.0, ETS-8-5.0,
Entire Study
ETS-8-7.0
11. Description:
Required Procedure/process: These methods state: Typically the analytical batch run sequence begins and ends with a set of extracted matrix standards.
Actual Procedure/process:
In
ma-ny
analytical
r- uns,
only
the
initial
extra-c--ts-_matrix
curve -
was
use-d
to
evaluate
the
extracts.
"_I_ I
__I__ __l_l_--_
Either the second curve was not injected or the bracketing curve was deactiv.a"te- d.s-.inc_e_th- is
calibraton curve was divergent.
I Ill. Actions Taken: (such as amendment issued, SOP revision, etc.) This deviation was written and a few method modificationswere also written stating that the
second bracketing calibration curve may be deactivated if ins&ental drift affects the data.
The first curve and acceutable calibration checks shall then bracket usable data.
H Recorded Bv
Date
~ ~ & 5 //-5---- p IV. Impact on Study / Project
- .-
- No adverse impact on the outcome of this study shce data weresufficiently_ b_ r-a-cketed by
ca_l_i-bra_t_io- n c-h_ec-k-s.-- __
----_ - - -- -
-l_l-_--"_I I _ _ ___
_ I
_-
-
-
Authorized By (Study Director /Project Lead)
Date
4J L . 2 - &2&&4gf&//
3M Environmental Laboratory FOKWETS-4-8.0
3M Environmental Laboratory
Deviation No.
1
(assigned by Study Director or Project Lead at the end of study or project)
Page 88
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Record of Deviation
1. Identification
______ _ I- "
~
Study I Project No. FACT-TOX-001
Covance 6329-212
--__-_____---__
Deviation Type (Check one)
a SOP
DProtocol
x Method IJEquipment Procedure
iJ Other:
- ~
__
Document Number(s): FACT-M-3.0
Date(s) of occurrence:
04123198,04128198,05111198
11. Description:
R......equired F'rocedure/process:
...................
..........
........... ____
._
............ ................
asthe.s.amp1es, S...e....c....t..i...o....n.......1....1......1.2 s..t..a..t..e...s..: If the major..i...t..y of th.....e serum sample-s.__a_r_e-.._less than 1.O mL, ............................................... extra...c....t the standards ...........................
in the_S~.e.,v.o~u,m.e..
..........____ ~~
__ ..
__.__c
Actual Procedure/process:
_-___~__"-l___
.I..n...i.t..i.a...l...s..e...r..a...v.. olume.s for weeks ...... 4, 8, and 14.....w_er_ e below 1..O mL (0.6 0.5 mL, mL,........................... & 0.5 m_L_re.spectiv.e..l.y...). T. -h.e_c_u_r~vIe_s....prepared fo__r_t._h_e_-s_e samples were made using 1.O mL of serum. .___I____ I_ _ __ _ _--.
.................
....................
..___
__
.........................................................
~~
......................
Ill. Actions Taken:
(such as amendment issued, SOP.rev- ision, etc.)_.__-_ ___ _ _____-.
This-deviationwas G-tten. -- --
-- _ - -
. -_
__
3M Environmental Laboratory Form ETS-4-8.0
3M Environmental Laboratory
Deviation No.
a
(assigned by Study Directoror ProjectLead at the end of study or project)
Page 89
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Record of Deviation
1. Identification
-
-
-
-
~
-
~
I
_
- _
_
S m P s c x F A C T - T O X - 0 01 Covance 6329-212
Deviation Type (Check one)
a SOP
DProtocol
x Method Cl Equipment Procedure
a Other:
Document Number(s): ETS-8-5.1
. Date(s) of occurrence: 05/05/98
I/* Description:
Required Procedure/process: ........
-_____ ___._
__ .
....................................... _.
Actual Procedure/process: -
_"
_____-I_______
~
____I
4/2-8-/-98) analyzed on 05/05/9-8--wa-s ab-o_ve_th_e_ra_n_ge-of-th-e calibration curve.
.... ........................
. - - .........
......... ............... .- ........... ....... .- ............... ...
.-.......
.................... - ............................ -....
111. Actions Taken:
(such as amendment issued, SOP revision, etc.)
I__
-- ~-
___
This deviation was yitten.-
-
- -~
__
IV. Impact on Study / Project .Th~e s_ am_pleIre_sult will be
I -
_ll.___l_ll _
_
I
"
~
~~~
"^l
-- --
Authorized By (Study Director /Project Lead)
.I
I Date
i
.- ~ .-. -
3M Environmental Laboratory Form ETS-4-8.0
3M Environmental Laboratory
Deviation No.
3
(assignedby Study Director or Project Lead at the end of study or project)
Page 90
3M Medical Department Study: T6316.1
Record of Deviation
Analytical Report: FACT-TOX-001 LRN-U2103
1. Identification
Study / Project No.
a SOP X Method TOXOO1 (LIMS #U2103)
~
l__ll____
Deviation type
~ _ _ _ I I _ _ _.____
(Check one)
___~_
--
0 Equipment Procedure
-
_- ---
OProtocol Cl Other:
_ I -
- I _ - - _ _
Document number FACT-M-4.0 and ETS-8-5.1
Date(s) of occurrence
I 05/05/98,4/20/00,4/21/00, 5/02/00, 5/24/00,
j 5/30/00, 8/23/00,02/28/00, 03/15/00,
i 02/27/00,04/17/00,04/18/00,04/19/00,
05/31/00,06/19/00, 06/20/00,06/2 1/00,
08/02/00,04/06/00
11. Description
Required procedure/process:
Section 10.1.2: Analyze a method blank and a matrix blank prior to each calibration curve.
~
1
1
Actual
I
procedure/process:
~-
l _ - - _ _ l -
-On- se-ve-ral~occasions, the blanks were either a) analyzed after the calibration curves orb) not
analyzed at all for a particular MS run.
~_-~_
_lll_--_-_l____ll_l---_
~
_
-
I
111. Actions Taken (such as amendment issued, SOP revision, etc.)
Deviation written.
-I_~_l_l___-I_
Recorded by
~
l
_
l
_
_
_
IV. Impact on Study / Project
(completedby StudyDirector or Project Lead)
............................
- __
~
......
All blanks were analyzed at least once during the course of the study. When blanks were run
after the calibration curve, all control-of-bias practices were followed. In the instances where
blanks were not run at all, the samples being analyzed were usually well above the typical run
LOQ. In addition, the vast majority of samples run without blanks were high level dilutions.
The hnction of the blank is to determine if contaminationwas introduced during extraction;
any low-level contamination would be inconsequential to extracts requixjng dilution. This
deviation has no adverse affect on the study data.
...............................................
...........
............. .- ..... ............ .- ........
-
............................................................
................ - ...
4h Oe/l..O../O.I. ~ ._.......
.. ........
... ...................
. _
..
__ - .....
._ _ ............._
Authorized by
-.
.-
1 - --- --___
__
3M Environmental Laboratory
Page 91
3M Medical Department Study: T6316.1
Record of Deviation
Analytical Report: FACT-TOX-001 LRN-U2103
1. Identification
Study / Project No.
a X T..-O-.""Xl__O_"O_.l__.(_LI_-I.-MS #U2103) Covance 6329-212 "_ .-.---" --.-I_.
~~
~
Deviation type
SOP
Method
(Check one)
~
~
0 Equipment Procedure
-- _i
- - - I - - - - -
CJProtoc- ol
CI
Other:
I I _ ~~- ~ ~- l l - _ l _ - l - _
Document number: ETS-8-5.1 (Modified method) Date(s) of occurrence:
ETS-8-7.0 (Modified method)
05/05/98 (ETS-8-5.l), 02/18/99, 12/06/00
(ETS-8-7.0)
11. Description
Required procedure/process:
-_
Section 14.3.6: A valid calibration curve must contain at least 5 active Doints
~-
Actual procedure/process: -_--
l_ll_l~-_l_-l--l
A suitable calibration curve (i.e. with all points within 30% of theoretical and with an
r"2>0.980) could not be derived from 5 points; four points were used for the calibration curve
for PFOS and PFOSAA (5/5/98), for Et-FOSE-OH (2/18/99), and for PFOSAA (12/06/00).
Ill. Actions Taken (such as amendment issued, SOP revision, etc.)
- - _ -- ~ II
I_----Ix
ll_-
I I_--I1-__
___ __--_^-_-
_I_--_I
Deviation written. Data evaluated against 4 point curve is specificallymarked in the table of
final results.
IV. Impact on Study f Project
(completed by Study Director or Project Lead)
____
- __
The
data
quality
__
.of_s_amples
evaluated
against
- - --
the
f- o_z
_p o
i
n
t
curve
i-s
ad__v-e_r_s_e_ ly
affe_c_ted.
Authorized by
--
-
Date
3M EnvironAmtteanchtamleLntaAb:oRraectoorrdyof Deviation
ETS-4-8.0
Page 92
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Record of Deviation
1. Identification
-
Study / Project No. FACT-TOX-001 Cov&ce 6329-212
-- . __
IDeviation Type (Check one)
- - __ Document Number(s): FACT-TOX-001
0 SOP
0 Method 0 Equipment Procedure
XProtocol 0 Other:
.- -- -
Date(s) of occurrencei 05/06/98,05/13/98,05/14/98,05/15/98,. 05117/98,06/03/98, 06/05/98,06/12/98, 06/14/98,06/18/98,06/25/98,06/26/98, 07/06/98,07/09/98, 12/14/98, 12/29/98, 01/06/99,0 1/18/99,02/16/99,02/18/99 11. Description:
Required Procedurelprocess:
IThe protocol states: Methods FACT-M-2.0 and FACT-M-4.0 are to beused to analyze liver
and sera extracts.
-_
-
~
P
Actual Procedure/process: Methods were not documented
or
the
incorrect methodswere
listed
for-analyses
of
these
I
Ill, Actions Taken:
(such as amendmeIn-t_issu-ed,-_SO_P_ revisio_n_,_etc.) - -
- -- -
_I_I_
I
This deGation was written.
-
I ,..
,.. -. " -
RecordedBy
,
.
.
,
,
.
,I_ _ _ -
. ~-.-....-...~,"."__I___" __^.--.._I_
I_____._
_ I I
~
.... . . . li
"I
.
"~
.
. ,
: Date
dYA. L
IV. Impact on Study / Project
T.hese an-alyses were review-- ed an- d-th-_e.s_e-_da_ta
were ana@ed
accordingto -
m-e- thods
as
-li-sted
in
-_I
--__I-__
the protocol. No adverse impact on the outcome of this study.
_Authorized By (Study Director /Project Lead) -~
-
~ Date
s%, &hr DufChhoff
3M Environmental Laboratory Form ETS-4-8.0
3M Environmental Laboratory
1
, y ~ h s s v:M a u c h
GYL3@t9w
Deviation No.
(assigned by Study Director or Project Lead at the end of study or project)
Page 93
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Record of Deviation
I
1. Identification
Study / Project No. -FACT'-TOX-001 Covance 6329-212
Deviation Type (Check one)
__ - __
0 SOP
x
Method-
__ c1 Equipment
Procedure
OProtocol lJ Other:
__ Document Number(s)r ETS-8-5.1
_-
-
Date(s)-of occurrence:
I 05/14/98
11. Description:
.Require-d. Procedure/process:
.- __.-_-._____ .................................................
___ .
............................................
The continuing calibration verification (CCV) must be within +/- 30~ % o~ f thx e t_ heo- ret- ica- l _ .l_ ll_. - -
concentration.
....
.....................
....... ..._ . ...... __ .
.......:....... .
.........
......................................
IActual Procedure/process: .....
.......................................................................
..
-..
.
........
........... __ .........
PFOSAA The Week 8, Sera, PFOS and
....
..
MS,
.......
MSD,
H
2
0
Blank,
an.d..... S_ _e.r....a....
Blank .
data
..
were .................
entered even .............................................
though .......
CCVs ...
d_i_d_n....o.....t.....m........e.....e....t......c....r....i..t...e. ria. _.
..........
.....................
.............................................
The CCV analyzed prior to the PFOS data was within criteria and the curve immediately
........... ......
. ......
. .-.__ ..............................................
........
..
................... -. ......................................
following these data were within criteria. Three CCVs in a row, prior to the good CCV, failed
.-._I" "
.. I-----. .I -" lllll___l._----.--
...
--__1__1__
the 30% criteria.
_-- __
-- -
Two CCVs analyzed prior to the PFOSAA datawere within criieria and the Grve
........
....................
.
..
...........
.................................................
. -.....
..
. . . . .............. .......... ..........._.. .
immediately foliowing these data were within criteria.
...........
.
....
...............
...- ....
Two
CCVs prior to the .......... ......... .-
go_....o.. d
CCVs .........
........
~
failed the 30% criteria.
I....- .....
___ ....... . . .... _
... ............
.
Ill. Actions Taken:
-.
......
...................
(such as a- me.n....dment issued, SOP r_ev_isi-o. n, etc.) ~
- ~ ...
....
.....................................
This deviation was written and data will be flagged as tentative in the raw data.
......
Recorded By
&&A
___ ....................................
cQcrrL,L,
IV. Imroact on Studw / Proiect
: Date................. ..............................
3M Environmental Laboratory Form ETS-4-8.0
3M Environmental Laboratory
Deviation No.
3
(assigned by Study Director or Project Lead at the end of study or project)
Page 94
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Record of Deviation
1. Identification
Study / Project No. FACT-TOX-001 Covance 6329-212
Deviation Type (Check one)
17 SOP 13Protocol
x Method tJ Equipment Procedure
Cl Other:
Document Number(s): ETS-8-7.0
Date(s) of occurrence: 05/29/98,06/01/98 11. Description:
Required Procedurdprocess: ..........................
...........................................................
.
-.
A... five..p..o..i.nt cu.r.ve or
the ca..li.b--ra..t.i..o..n. curve. ._._.........
...
..................
......................................................................................
..............................
.
........
........
....
Actual Procedure/process:
--
A fourpoint curvewas used for plo&ng the EtFOSE calibrationcurvefor the Weekl4,
Liver curve, generated on 12/14/98.
............
.................
....
.............
Ill. Actions Taken:
(such as amendment issued, SOP revision, etc.)
These data were flagged in the raw data and this deviation was written.
....................................
.........................
...................
.............
-..
Recorded By
.............
Date
EtFOSE:OHda&s
IV. Impact on Study/ Project
-
flagged as qual%itive, so thisdata &ill not be adversely affected.
hh o ~ / / ~ / O /
Authorized By- (Study Director /Project G a d )
- .Date
3M Environmental Laboratory F o ET~S-4-8.0
3M Environmental Laboratory
Deviation NO.
8
(assignedby Study Director or ProwLead at the end of study or project)
Page 95
3M Medical Department Study: T6316.1
~~
~~
Analytical Report: FACT-TOX-001
LRN-U2103
Record of Deviation
I. Identification
Study / Project No. FACT-TOX-001 Covance 6329-212
Deviation Type (Check one)
D SOP
13 Protocol
x Method D Equipment Procedure
D Other:
Document Number(s): ETS-8-7.0
Date(s) of occurrence: 06/02/98,01/14/99,01/17/99 11. Description:
Required Procedure/process:
-
.
Section 14.4.1 states: matrix spikeDercent recoveriesmustbe within-&30%ofthe suiked
concentration. _ _
__
--
.-
Actual Procedure/process:
The week 14,liver matrix spike &d matrix spike duplicate samples prepared for PFOS apd PFOSAA analysis(exQacted 06/02/98) weren't within criteria. -me noncompliance-of the-PFOS and PFOSAA data on 06/02/98 can-be agributed to inappropriatepreparation: spikes were prepared at lOOng/g, a level not distinguishablefrom background levelspf the analytein the-controls. Spikes were reprepped at a higher level (250 ndg) on 01/14/99, but again, for PFOS analysis, the spikelevel was not distinguishable from background levels; PFOSAA was inadvertently omitted from analysis. Spikesfor the week 1_4liver sampleswere prepared a third time on-O1/17/99 at 750 ngg. Results-ofthe third analysis show@ an averagePFOS recovery of 132%;one of the two matrix spikes was recovered outside the stated 130%criteria (138%). Results of matrix spike recoveryfrom PFOSAA at the 750 ng/g level were acceptable.
Ill. Actions Taken:
(such as amendment issued, SOP revision, erc.)
This deviationwas &itten. A note will be added tothe week14 liver data stating that one PFOS MS was recovered at 132% and that week 14 PFOS analytical results may be biased high.
Recorded By
-_ .
__ -
Date
IV. lmpaa on Study/ Project PFOS results for week 14liver samples may be biased high.
Authorized By (Study Director /Project Lead)
$jb O Z / l 4 / 6 /
Date
3M Environmental Laboratory F o ET~S-4-8.0
3M Environmental Laboratory
Deviation NO.
9
(assigned by Study Director or Project Lead at the end of study or project)
Page 96
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Record of Deviation
1. Identification
Study / Project No. FACT-TOX-001 Covance 6329-212
Deviation Type (Check one)
a SOP
CJ Protocol
x Method 0 Equipment Procedure
Cl Other:
Document Number(s): ETS-8-7.0
Date@)of occurrence: 06/03/98 11. Description:
.R...e..q..u..i..r.e..d....P..rocedur.e../..p..r..o..c..e. ss: .......
................
...
...
.....
.S..e..c..t.i.o...n...1..4....4....1...states:. . .m. . a. .t.r.i.x. . .s.p. .i.k. .e. .p. .e.r. c. .e. .n. t. .r. e. .c. .o.v. .e. .r.i.e. .s. .m. .u. .s.t. .b. .e. . w. . .i.t.h. .i.n. .&. . 30% . . . . . . . .o. .f. .t.h. .e. .s. .p. i. k. .e. .d. . . . . . .
.c-o.n..c.e-n.t.r.a. t-io..n... -. ....- ...-.-. .... - ...-.- .... ..........
.... - .. .- .... - .. - .- ....- _ .... _...._ ... _ _.... - ......
Actual Procedure/process:
- _-
All week 4 liver MS recoveries are outside criteria, however, themat- rix . spike-and s&pie d a b
appeared to be mislabeled.
When the MS and sample labels are corrected, all recoveries are within critega-withthe
Exception of PFOS and EtFOSE. Average PFOS recoveries are 192% and average EtFOSE
Recoveries are 133%.
-. . . . . . . . . . . - .
................
_. .
....
.....
....... ~
Ill. Actions Taken:
(suchas amendment issued, SOP revision, etc.)
The MS and sample data labels were corrected in the raw data, the PFOS data were flagged in
the spreadsheet, sample results are noted to have a potential high bias, &d 6 s deviation
was written.
-
_.-
Recorded By
Date
IV, Impact on Study / Project PFOS data in week 4 liver samples is noted to be potentially biased high. EtFOSE-OH data
3;i Are already d e s i p a t e as qualitative only and is not fu-&er-affected by the deviantrecoveries. o=./M/01
.-.
Authorized By (Study Director /Project Gad)
-
Date
3M Environmental Laboratory F o ET~S-4-8.0
3M Environmental Laboratory
Deviation No. lo
(assigned by Study Director or Project Lead at the end of study or project)
Page 97
3M Medical Department Study: T6316.1
Record of Deviation
Analytical Report: FACT-TOX-001 LRN-U2103
Study / Project No. FACT-TOX-001
- __ Covance 6329-212
IDocument Number(s):
a Protocol ETS-8-7.0
II.
X Method
o Other:
Equipment Procedure
Date(s) of occurrence: 12/29/98 Description:
Required Procedurelprocess:
Section 14.5.1states:Continuing calibrationvenficationpercknt recoveries mustbe
within +/-30% of the soiked concentrationl -
_-
__
__ __
I .. -
.
.. -
-
.
.
. __ - ._.. -~....
.
.
. -. . - . .
_.
Actual Procedure/process:
The continuingcalibrationverification s6plesfor PFOS; PFOSA,A d PFOSAA analyzed on 12129-98 .had percent recove-es greater- ~ a1q30.%of-expected. ___ ___
. _- - - _ _ - -
_- I __ -
.- __ - - ._ __ __ -
- -- _-
__ - -
- __
__
__
-. __
-_
Ill. Actions Taken: (such as amendment issued, SOP revision, etc,)
This deviation was written; affected data is noted in the data tables
- -. . . - .~ ~. ... . .-. . __ . . .- . ..~..
Recorded By
n
IV. Impact on Study / Project Affected data may be biased high. -
_c,'b. bz((3IbI
-~
.... . -. . ._.. . ... . -
Date
2. '3-0(
-I_._
3M Environmental Laboratory Form ETS-4-8.0
3M Environmental Laboratory
Deviation No. 11
(assigned by Study Director or Project Lead at the end of study or project)
Page 98
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Record of Deviation
1. Identification
Study / Project No. FACT-TOX-001 Covance 6329-212
Deviation Type (Check one)
a SOP
Protocol
x Method b Equipment Procedure
0 Other:
Document Number(s): ETS-8-7.0
Date(s) of occurrence: 01/18/99 11. Description:
Required Procedure/process:
--
Section_ 1_ 4.5_ .1 s.ta- tes: Continuing calibration verification percent recoveries must be within ~
Actual Procedurdprocess: The-Week 14, liver samples C91281F, C91288F, d91293F, C91299F, and C91304F were bracketed by a-continuingcalibration verification that did not meet the +/- 30% criteria. (-31%)
Ill. Actions Taken:
(such as amendment issued, SOP revision, etc.)
These data were flagged in the raw data as having a potential low bias and this deviation
was written.
Recorded By
dih b LIV. lmpact on -Study/ Project
Resuits for these analyses may be-biased low.
- . . .. .. .. .. . .. .. . - .. .
.. - . . . . . . ..- .. .
.. . . . .-.- ~ . . . .~ . . . . . . ... .
Date
.. .
Authorized By (StudyDirector /Project Lead)
Date
3M Environmental Laboratory Fomt ETS-4-8.0
3M Environmental Laboratory
I'
Deviation No. la
(assigned by Study Director or Project Lmd at the end of study or project)
Page 99
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Record of Deviation
1. Identification
Study / Project No. FACT-TOX-001 Covance 6329-212
Deviation Type (Check one)
Docum&t-Nu&&( s ) I
FACT-TOX-001
0 SOP
0 Method 0Equipment Procedure
XProtocol 0 Other:
- -_
-- __ -
Date@)of occurrence:
02/07/00,02/08/00,02/09/00
11. Description:
Required Procedure/process:
... .ll._l I ....._I_____"
_. _ I .
,..
_ _ _ I . ........
~.......~~..._._....I" ."
......-..."I .
The lxotocol states: Method FACT-M-3.0 is to be used when extracting the serum
samples.
-. ...
Actual Procedure/process: Method ETS-8-4.1 was used to extract these serum samples.
- I
"
".I
. .
. .. .
..
~
,
. ".
...... "_
Ill. Actions Taken:
(such as amendment issued, SOP revision, etc.)
This deviation w& written,'-
Recorded By __ - .__
IV. Impact on Study / Project
4 No adverse impact on the outcome of this study. Sera method ETS-8-4.1 is an improvement
over sera meth-o_ _d FAC_ T_ -M- --3~.O..
;S b 5/W/Q)
Authorized By (Study Director /Project Lead)
Date
5$+
1
3M Environmental Laboratory Form ETS-4-8.0
3M Environmental Laboratory
Deviation No.
13
(assigned by Study Director or Project Lead at the end of study or project) .
Page 100
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Record of Deviation
1. Identification
Study / Project No. FACT-TOX-001 Covance 6329-212 LIMS U2103
Deviation Type (Check one)
0SOP 0Protocol
x Method 0Equipment Procedure
0 Other:
Document Number(s): ETS-8-7.0
Date(s) of occurrence: 02/22/00,04/24/00, 04/26/00,04/28/00, 05/24/00,07/28/00, 08/01/00,08/14/00,08/15/00, 08/21/00, 08/23/00,03/22/01 11. Description:
Required Procedure/process:
_--
_I^____II---
- ^_x____ - -I___----I.-
- ___I I _ .I_--_^__
_ _ _ __I__^_I__
Section 10.1.2 states: Analyze a method blank and a matrix blank prior to each calibration curve. -
- . .. .. -. .- . ..- . ....... . - .
. .. .. .- - -. - .... .
I"..- ..
. ... .. . . . .- . - ,. .
_ _ ,,
Actual Procedure/process:
On several occasions,the bla& were eithe.r a).ana-ly.z.ed.af.t.er the calibration curves or b) n-o.t analy.ze.dAt all for a particular MSanalysis.
111. Actions Taken:
(such as amendment issued, SOP revision, etc.)
This deviation was written.
1 RecordedBy
Date
IV. Impact on Study/ Project
1 All blanks were analyzed at least once during the c o k e of the study. When blanks were analyzed
. . after the calibrationcurve. allcontrol-of-biasDracticeswere followed. In the instanceswhere blanks
- Iwere not analvzed at all. the samdes being aialvzed were usuallv well above the mica1run LOO. Y -.- 4 In addition, tce vast majoritfof gamples analyzed without blank; were high 1
function of the blank is to determine if contaminationwas introduced during extraction; any low-level
contamination would be inconsequential to extracts requiring dilutions. This deviation has no adverse
affect on these study data.
- 4 h OY//4lO/
IAuthorized By (Study Director /Project Lead)
Date
3M EnvironmentalLaboratoiy Form ETS-4-8.0
3M Environmental Laboratory
Deviation No.
1y
'
(assigned by Study Director or Project Lead at the end of study or project)
Page 101
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Record of Deviation
"
1. Identification
- ..............
.........
.....
.
Study / Project No.
: ala -t4..k-t-SoX-..oo.!..
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a a Deviation Type
SOP
El Method Eq-ui-pment Procedure
a (Check one) -
Protocol t i Other:
..
........
Document Number
ETS- 8 -5. I
............ .-
................................
11.
....
~ ._
i Date(s) of occurrence
i
i
OLl2llDO
Description:
Required Procedure/process:
d
....Ganm+rQ..kbn ..........
I .......
I
.
__..___
Actual Procedure/txocess:
_ I _
Recorded By
I -_____.______ Date
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IK Impact on Study/ Project
- _ I _ I
-
Authorized By (Stud' D
F o ET~S-4-8.0
3M Environmental Laboratory
---___I-.----
w S p t W . R-p: b d CaLC
: Date
(assigned by Study Director or Project Lead at the end of study or project)
Page 102
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Record of Deviation
1. Identification
""
Study / Project No. FACT-TOX-001 Covance 6329-212
Deviation Type (Check one)
- 0 SOP
[IMethod [IEquipment Procedure
XProtocol 0 Other:
FACT-TOX-001
07/28/00,08/01/00,08/14/00,08/15/00,
08/2 1/00,08/23/00,08/28/00,08/29/00 11. Description:
IRequired Procedure/process: Theprotoco_l _states: Metho_d- -ET-S-8-7.0
is
to
be
used
to
analyze
liv--er
extr_%_cts.
IActual Procedure/process_: _
Method ETS-8-6.0was incorrectly listed as the method used to analyze these liver extracts. '
I ....
. -.......~
......................
................................................
.....
.............. ..............
Ill. Actions Taken:
-(such as amen--dment issu-ed-, SO-P rev~bio-n--,_etc- .)
-_1__---
_I
- I _ __ I_
This deviation was written.
- - - I_
I RecordedBy
-.
Date .
IV. Impact on Study / Project
ET-S_~-8-6-.0-__is__t_h_e--extractionmethod, ETS-8-7.0 is the analytical method-hese analyses--were
-__--I_-_I
~
I _ - _ _ _ I ~
-____^I_-
_ _ -him y o f reviewed
and data were analyzed acc_o-rd-i-n-_g to ETS-8-7.0.
No
adverse impact o-n the outcome
_
-
I
-
_
_
_
I
_I____----
this of study. _- - I
I___I__
-
- I_
_- I
I
I --
_-_
I Authorized By (Study Director /Project Lead)
-.
Date
I'
S p :&hn
BMfLllhofl
3M Environmental Laboratory Form ETS-4-8.0
3M Environmental Laboratory
(assigned by Study Director or Project Lead at the end of study or project)
Page 103
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Record of Deviation
1. Identification
Study / Project NO.
.--
.
..
Deviation Type (Check one)
__
#SOP OProtocol
PMethod Cl Equipment Procedure iJ Other:
-..
--
--
Document Number
p- -7 0
I Date(.s,) of occurrence
i
,3-3!?2&3/
II. Description:
m !.-mJ&A Req...u.._ir_ed Procedure/process:
.
.....
.
...........
lL.L%4uq ......
..............................
.A... ctual Procedure/process: ......
..............
............
......................................................................................
......
-
_
-
~
_
^
.................
.......
_I^
Ill. Actions Taken: (such as amendment issued, SOP revision, etc.)
................................. .................................
__.-._^--I
.....
Authorized By (StudyDirector 1Project Lead)
................
-7- ..h 4.3L2 \ Date
.- _-
.-......
3M Environmental Laboratory
F o ET~S-4-8.0
Sbd8 ~ ; ~ ) o -,.-. &ob, 3M Environsm~~e~n~t~a~lRLeapb-\ocrhae:tory
&AJC
Mtxivin Cade
k-rL
Deviation NO.
17
Director or Project Lead at the end of study or project)
27btd%,
Page 104
3M Medical Department Study: T6316.1
3M Medical Department Study: T-6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
Appendix C: Extraction and Analytical Methods
This appendix includes the following methods:
Preparatory Methods
FACT-M-1.O. Extraction of Potassium Perfluorooctanesulfonateor Other Anionic Fluorochemical Surfactants from Liver for Analysis Using HPLC-Electrospray/Mass Spectrometry, (8 pages)
FACT-M9.0, Extraction of Potassium Perfluorooctanesulfonateor Other Anionic Fluorochemical Surfactants from Serum for Analysis using HPLC-Electrospray/Mass Spectrometry, (8 pages)
ETS-8-4.1, Extraction of Potassium Perfluorooctanesulfonate or other Fluorochemical Compounds from Serum for Analysis using HPLC-Electrospray/MassSpectrometry, (14 pages)
ETS-8-6.0, Extraction of Potassium Perfluorooctanesulfonateor other Fluorochemical Compounds from Liver for Analysis using HPLC-Electrospray/MassSpectrometry, (14 pages)
AnalyticaI Methods
FACT-M-2.0, Analysis of Liver Extracts for Fluorochemicals Using HPLCElectrospray/Mass Spectrometry, (8 pages)
FACT-M-4.0, Analysis of Fluorochemicals in Serum Extracts Using HPLCElectrospray/Mass Spectrometry, (8 pages)
ETS-8-5.1, Analysis of Potassium Perfluorooctanesulfonateor other Fluorochemicals in
Serum Extracts Using HPLC-Electrospray/Mass Spectrometry, (9 pages)
ETS-8-7.0, Analysis of Potassium Perfluorooctanesulfonateor other Fluorochemicals in Liver Extracts Using HPLC-Electrospray/Mass Spectrometry, (10 pages)
3M Environmental Laboratory
Page 105
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
3M ENVIRONMENTLAALBORATORY
METHOD
EXTRACTIOONF POTASSIUM PERFLUOROOCTANESULBONATEOR OTHER ANIONIC FLUOROCHEMICASULRFACTANTS FROM LIVERFOR ANALYSIS USING H P L C - E L E C T R O S P R A YSP~EC~TSRSOMETRY
Method Number: -FACT-M-1.0
1
Author: Lisa Clemen Approved By:
81%- 1 % -
Laboratory Manager
Group Leader
TGhnical Reviewer
Adoption Date: 5 / J L / 9 ,f Revision Date: M)A
Date
3/2l, / q f
Date
5123)4P
Date
fa l
1.0 SCOPE AND APPLICATION
1.IScope: This method is for the extraction of Potassium Perfluorooctanesulfonate (PFOS) or
other fluorochemical surfactants fiom liver.
1.2 Applicable Compounds: Fluorochemical surfactants or other fluorinated compounds.
F k i c r o s o f t 7.0.1/95
- 3M Environmental Laboratory
FACT-M- 1.O Extraction of PFOS from Liver
Page 1 of 8 Page 106
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
2.0 SUMMARY OF METHOD
2.1 This method describes how to extract potassium perfluorooctanesulfonate (PFOS) or other fluorochemical surfactants from liver using ion pairing reagent and 5.0 mLs of ethyl acetate. An ion pairing reagent is added to each sample and partitioned into ethyl acetate. Four mLs of extract is removed to a centrifuge tube and put onto a nitrogen evaporator
- until dry. Each extract is reconstituted in 1.O mL methanol then filtered through a 3 cc
plastic syringe attached to a 0.2 pm filter into glass autovials.
4.1.1 Use universal precautions when handling animal livers, they may contain pathogens.
,
5.0 INTERFERENCES 5.1 There are no known interferences at this time.
6.0 EQUIPMENT
6.1 The following equipment is used while carrying out this method. Equivalent equipment is acceptable.
6.1.1 6.1.2 6.1.3 6.1.4 6.1.5 6.1.6
Ultra-Tmax T25 Grinder for grinding liver samples Vortex mixer, VWR, Vortex Genie 2 Centrifuge, Mistral 1000 or IEC Shaker, Eberbach or VWR Nitrogen Evaporator, Organomation Balance
7.0 SUPPLIES AND MATEIUALS 7.1 Gloves 7.2 Dissecting scalpels 7.3 Eppendorf or disposable pipettes 7.4 Nalgene bottles, capable of holding 250 mL and 1 L 7.5 Glass, type A, volumetric flasks 7.6 40 mL glass I-CHEM vials 7.7 Plastic sampule vials, Wheaton, 6 mL 7.8 Polypropylene centrifuge tubes, 15 mL 7.9 Labels
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Analytical Report: FACT-TOX-001 LRN-U2103
7.10 Syringes, capable of measuring 10 pL to 50 pL 7.11 Glass, type A, volumetric pipettes 7.12 Graduated pipettes 7.13 Electronic pipettor, Eppendorf or equivalent 7.14 Timer 7.15 Disposable plastic 3 cc syringes 7.16 Filters, nylon syringe filters, 0.2 pm, 25 mm 7.17 Crimp cap autovials Note: Prior to using glassware and bottles, rinse 3 times with methanol and 3 times with Milli-
Q" water. Rinse syringes a minimum of 9 times with methanol, 3 rinses from 3 separate vials.
8.0 REAGENTS AND S~~ANDARDS
8.1 Reagents
8.1.1 Sodium Hydroxide (J.T Baker or equivalent), (NaOH) 1ON: weigh approximately ' 200 grams NaOH. Pour into a 1000 mL beaker containing 500 liters (L) Milli-Qm water, mix until all solids are dissolved. Store in a 1 L nalgene bottle.
8.1.2 Sodium Hydroxide (J.T Baker or equivalent), (NaOH) 1N. Dilute 10N 1:lO. Measure 10 mL of the 1ON NaOH solution into a 100 mL volumetric flask and dilute to volume using Milli-QTMwater. Store in a 125 mL nalgene bottle.
8.1.3 Tetrabutylammoniumhydrogen sulfate (Kodak or equivalent), (TBA) 0.5M:Weigh approximately 169 grams of TBA into a 1 L volumetric containing 500 L Milli-QTM water. Adjust to pH 10 using approximately 64 mL 1ON NaOH and dilute to volume with Milli-Qm water. Add NaOH slowly while adding the last 1 mL of NaOH because the pH changes abruptly. Store in a 1 L nalgene bottle.
8.1.3.1 TBA requires a check prior to each use to ensure pH = 10. Adjust as needed using 1N NaOH solution.
8.1.4 Sodium carbonate/Sodium Bicarbonate Buffer (J.T. Baker or equivalent), (NqCO,/NaHCO,) 0.25M: Weigh approximately 26.5 g of sodium carbonate (Na,,CO,) and 21 .O g of sodium bicarbonate (NaHCO,) into a 1 L volumetric flask and dilute to volume with Milli-QTMwater. Store in a 1 L nalgene bottle.
8.1.5 PFOS (3M Specialty Chemical Division), molecular weight = 538.
8.1.6 Ethyl Acetate, Omnisolv, glass distilled or HPLC grade.
8.1.7 Methanol, Omnisolv, glass distilled or HPLC grade.
8.1.8 Liver and control liver, received frozen from testing laboratory.
- 8.1.9 Milli-QTMwater, all water used in this method should be Milli-QTMwater and may be provided by a Milli-Q TOC Plus system.
8.2 Standards
8.2.1 Prepare PFOS standards for the standard curve.
3M Environmental Laboratory
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Analytical Report: FACT-TOX-001 LRN-U2103
8.2.2 8.2.3 8.2.4 8.2.5 8.2.6
Weigh approximately 100 mg of PFOS into a 100 mL volumetric flask and record the actual weight.
Bring to volume with methanol for a stock standard of approximately 1000 ppm (CLdmL).
Dilute the stock solution with methanol for a working standard 1 solution of
approxi.mately 50 ppm.
Dilute the stock solution with methanol for a working standard 2 solution of approx. 5.0 ppm.
Dilute the stock solution with methanol for a working standard 3 solution of approx. 0.50 ppm.
9.0 SAMPLEHANDLING 9.1 All livers are received frozen and must be kept frozen until the extraction is performed.
10.0 QUALITYCONTROL 10.1 Matrix Spikes
10.1.1 Prepare and analyze matrix spike and matrix spike duplicate samples to determine the accuracy of the extraction.
10.1.2 Prepare each spike using liver chosen by the analyst, usually a control liver.
10.1.3 Expected concentrations will fall in the mid-range of the initial calibration curve.
10.2 Continuing Calibration Checks
10.2.1 Prepare and analyze continuing calibration check samples to determine the continued linearity of the initial calibration curve.
10.2.2 One check is prepared per group of ten samples. For example, if a sample set = 34, four checks are prepared and extracted.
10.2.3 Prepare each continuing calibration check fiom the same liver homogenate used to prep the initial curve.
10.2.4 The expected concentration will fall within the mid-range of the initial calibration curve.
11.0 CALIBRATIOANND STANDARDIZATION 11.1 Prepare Liver Homogenate to Use for Standards
11.1.1 Weigh approximately 40 g of liver into a 250 mL Nalgene bottle containing 200 mLs Milli-QTMwater. Grind to a homogeneous solution.
11.1.2 If 40 g is not available, use appropriate amounts of liver and water in keeping with a 1:5 ratio.
11.1.3 See section 13.0 to calculate the actual density of liver.
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3M Medical Department Study: T6316.1
Y
Analytical Report: FACT-TOX-001 LRN-U2103
11.1.4 Add 1 mL of homogeneous solution to a 15 mL centrihge tube. Re-suspend homogeneous solution by shaking between aliquots while preparing a total of sixteen 1 mL aliquots of homogeneous solution in 15 mL centrifuge tubes.
11.1.5 Two 1 mL aliquots serve as matrix blanks. Use the standard concentrations and spiking amounts listed in table 1 to spike, in duplicate, two standard curves for a total of fourteen samples.
Approximate Spiking Amounts for Calibration Standards
(Approx. Conc.)
-
0.50 ppm .
0.50 ppm
0.50 DDm
1
11
5.0 ppm
5.0 ppm
5.0 ppm
50 uDm
-
4 20 40
10 .
20 30 4
PFOS in liver Blank
0.010 ppm 0.050 ppm 0.100 uum
I-
0.250 ppm 0.500 ppm 0.750 ppm
1.OOO ppm
11.1.1 See section 13.0 to calculate actual concentrationsof PFOS in calibration standards.
11.2 Extract spiked liver homogenates following 12.14-12.24 of this method. Use these standards to establish each initial curve on the mass spectrometer.
12.0 PROCEDURES 12.1 Obtain frozen liver samples. In spent tissue, note that the liver has not been packaged with
other tissues. 12.2 Cut approximately 1 g of liver using a dissecting scalpel. 12.3 Weigh the sample directly into a tared plastic sampule vial. 12.4 Record the liver weight in the study notebook. 12.5 Label the sampule vial with the study number, weight, liver ID, date and analyst initials. 12.6 Add 2.5 m L s of water to sampule vial. 12.7 Grind the sample. Put the grinder probe in the sample and grind for about 2 minutes, or
until the sample is homogeneous. 12.8 Rinse the probe into the sample with 2.5 m L s water using a pipette. 12.9 Take the grinder apart and clean it with methanol after each sample. Follow AMDT-EP-22. 12.10 Cap the sample and vortex for 15 seconds.
3M Environmental Laboratory
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12.11 Pipette 1 mL homogenate into a 15 mL polypropylene centrifuge tube. Label the centrifuge tube with the identical information as the sampule vial. (See Worksheet for documenting the remaining steps.)
12.12 Spike liver homogenates with the appropriate amount of PFOS standard as described in section 11.1 or Table 1.
12.13Pipette two 1 mL aliquots of Milli-Qm water to centrifuge tubes. These will serve as instrument blanks.
12.14Add 1 mL 0.5 M TBA and 2 mL of the 0.25 M sodium carbonatekodium bicarbonate buffer.
12.15Using a volumetric pipette, add 5 m L s ethyl acetate.
12.16 Cap each sample and put on the shaker for 20 minutes.
12.17 Centrifuge for 26 to 25 minutes, until layers are well separated. Set power on the centrifuge to approximately 3500 rpm.
12.18Remove 4 d s of organic layer, using a 5 mL graduated glass pipette, to a clean 15 mL centrifuge tube. Label this fresh tube with the same information as in 12.5.
12.19Put each sample on the analytical nitrogen evaporator until dry, approximately 2 to 3 hours.
12.20Add 1.OmL of methanol to each centrihge tube using a graduated pipette.
12.21 Vortex mix for 30 seconds.
12.22Attach a 0.2 pm nylon mesh filter to a 3 cc syringe and transfer the sample to this syringe. Filter into a 1.5 mL glass autovial.
12.23Label the autovial with the study number, animal number and gender, sample timepoint, matrix, final solvent, extraction date, and analyst(s) who performed the extraction.
12.24Cap and hold for electrospray mass spectrometry analysis. 12.25 Complete the worksheet and tape to page of study notebook.
13.0 DATAANALYSISAND CALCULATIONS 13.1 Calculations:
13.1.1 Calculate the density of liver (mg) in 1.OmL homogenate using the following
equation:
g of Liver x Average weight of ten 1 mL aliquots (mg)
(g of Liver + g of Water)
3M Environmental Laboratory
FACT-M- 1.O Extraction of PFOS from Liver
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Analytical Report: FACT-TOX-001 LRN-U2103
13.1.2 Calculate actual concentrations of PFOS in calibration standards using the following equation:
pL of Standard x Concentration (pg /mL) = Final Concentration (pg/g or mgkg)
mg Liver'/ 1 mL homogenate
of PFOS in Liver
*Avefage weight of liver in solution as determined in 13.1.1, by weighing ten 1 mL homogenates of approximately 40 mg liver in 200 mL of Milli-Q water.
14.0 METHODPERFORMANCE
14.1 The method detection limit is equal to half the lowest standard in the calibration curve.
- 15.0 POLLUTION PREVENTION AND WASTE MANAGEMENT
15.1 Sample waste is disposed in biohazard containers, flammable solvent waste is disposed in
high BTU containers, and used glass pipette waste is disposed in broken glass containers
located in the laboratory.
16.0 RECORDS 16.1 Complete the extraction worksheet and tape into the study notebook.
17.0 TABLESD, IAGRAMSF,LOWCHARTASN,D VALIDATION DATA 17.1 The validation report associated with this method is FACT-M-1.0 & 2.0-V-1,
18.0 REFERENCES 18.1 AMDT-EP-22, "Routine Maintenance of Ultra-Turrax T-25"
19.0 AFFECTEDOCUMENTS
19.1 FACT-M-2, "Analysis of Liver Extracts for Fluorochemicalsusing HPLC-Electrospray Mass Spectrometry"
20.0 REVISIONS
Revision Number.
Reason For Revision
Revision Date
3M Environmental Laboratory
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3M Medical Department Study: T6316.1
#
Extraction Worksheet for FACT-M- 1
Analytical Report: FACT-TOX-001 LRN-U2103
Study #
Sample Number
Date and approx. 0.5 ppm approx. 5 ppm approx. 50 ppm Initials
Liver Blank
Remove a 4 mL aliquot of organic layer
Put on Nitrogen Evaporator to dryness Evaporator
Temperature
Add 1.OmL of Methanol
TN-A-
Vortex 30 sec.
Filter using a 3cc B-D syringe with a 0.2bm SRI filter into a 1.5 mL autosample vial
MS/MSD/- Cont. Checks: Spiked
uL of a
ppm std (
) for a final concentration of
ppm. MS/MSD used sample
. Cont. Checks used same homogenate as for std curve.
3M Environmental Laboratory
FACT-M- 1.O Extraction of PFOS from Liver
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3M ENVIRONMENTLAALBORATORY
METHOD
EXTRACTIOONF POTASSIUM PERFLUOROOCTANESULFONATEOR OTHER ANIONIC FLUOROCHEMICASULRFACTANTSFROM SERUM FOR ANALYSIS USING HPLC-ELECTROSPRAYLMSAPSESCTROMETRY
Method Number: FACT-M-3 -0 Author: Lisa Clemen
Adoption Date: y txl q 8
Revision Date: NiA
, Group Leader .
Lk c.
&#J
Technical Reviewer
Date
Y/zz/93
Date
zp
E" ,a
1.0 SCOPEANDAPPLICATION
1.1 Scope: Thismethod is for the extraction of potassiumperfluorooctanesulfonate (PFOS)or
other fluorochernical surfactants fiom serum.
1.2 Applicable Compounds: Fluorochemical surfactants or other fluorinated compounds.
-1 + 3 1.3 Matrices: Rabbit, rat, and bovine serum or other sera as designated in the validation report.
-.01.
cha -J Microsoft 7.0.1/95
p>
FACT-M-3.O Extraction of PFOS fiom Serum
Page 1 of 8
3M Environmental Laboratory
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Analytical Report: FACT-TOX-001 LRN-U2103
2.0 SUMMAROYFMETHOD
2.1 This method describeshow to extract potassium peffluorooctanesulfonate(PFOS) or other anionic fluorochemical suffactants from serum using an ion pairing reagent and 5 .O mL of ethyl acetate. An ion pairing reagent is added to the sample and the analyte ion pair is partitioned into ethyl acetate. Four mL of extract are removed and put onto a nitrogen evaporatoruntil dry. Each extract is reconstituted in 1.O mL of methanol, then filtered through a 3 cc plastic syringe attached to a 0.2 pm nylon filter into glass autovials.
3.0 DEHNITIONS 3.1 None.
4.0 WARNINGASND CAUTIONS 4.1 Health and Safety Warnings:
4.1.1 Use universal precautions, especially laboratory coats, goggles, and gloves when handling animal serum, it may contah pathogens.
5.0 INTERFEE~ENCES 5.1 There are no known interferences at this time.
6.0 EQUIPMENT
6.1 The following equipment is used while carrying out this method. Equivalent equipment is
acceptable.
6.1.1 Vortex mixer, VWR, Vortex Genie 2
6.1.2 Centrifige, Mistral 1000 or E C
6.1.3 Shaker, Eberbach or VWR
6.1.4 Nitrogen evaporator, Organomation
6.1.5 Balance, (It 0.100 gm)
7.0 SUPPLIES AND MATERIAIS 7.1 Gloves 7.2 Eppendorf or disposable pipettes 7.3 Nalgene bottles, capable of holding 250 mL and 1 L 7.4 Glass, type A, volumetric flasks 7.5 40 mL glass I-CHEM vials 7.6 Polypropylene centrifuge tubes, 15 mL 7.7 Labels 7.8 Syringes, capable of measuring 10 pL to 50 pL 7.9 Glass, type A, volumetric pipettes 7.10 Graduated pipettes
3M Environmental Laboratory
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7.11 Electronic pipettor, Eppendorf or equivalent 7.12 Timer 7.13 Disposable plastic 3 cc syringes 7.14 Filters, nylon syringe filters, 0.2 pm, 25 mm 7.15 Crimp cap autovials
Note: Prior to using glassware and bottles, rinse 3 times with methanol and 3 times with MilliQm water. Rinse syringes a minimum of 9 times with methanol, 3 rinses from 3 separate
Vials.
8.0 REAGENTS AND STANDARDS
8.1 Reagents
8.1.1 Sodium hydroxide (J.TBaker or equivalent),(NaOH) 1ON: weigh approximately 200 grams NaOH. Pour into a 1000 mL beaker containing 500 liters (L) Milli-Qm water, mix until all solids are dissolved. Store in a 1 L Nalgene bottle.
8.1.2 Sodium hydroxide (J.TBaker or equivalent),(NaOH) 1N. Dilute 1ON 1:lO.
Measure 10 mL of ION NaOH solutioninto a 100mL volumetric flask and dilute ' to volume using Milli-QTMwater. Storein a 125 mL Nalgene bottle.
8.13 Tetrabutylammonhmhydrogen sulfate (Kodak or equivalent), (TBA) OSM: Weigh approximately 169 grams ofTBA into a 1L volumetriccontaining 500 L Milli-Qm
water. Adjust to pH 10using approximately 64mL of 1ON NaOH and dilute to
volume with Milli-QTMwater. Add NaOH slowly while adding the last mL of NaOH because the pH changes abruptly. Store in a 1L Nalgene bottle.
8.1.3.1 TBA requires a check prior to each use to ensure pH = 10. Adjust as needed using 1N NaOH solution.
8.1.4 Sodium carbonate/sodium bicarbonate buffer (J.T. Baker or equivalent), (Na&03/NaHC03)0.25M:Weigh approximately26.5 g of sodium carbonate (NqCO,) and 21.O g of sodium bicarbonate (NaHCO,) into a 1L volumetric flask and bring to volume with Milli-Q"" water. Store in a 1 L nalgene bottle.
8.1.5 PFOS (3MSpecialty Chemical Division), molecular weight = 538.
8.1.6 Other fluorochemicals, as appropriate.
8.1.7 Ethyl Acetate, Omnisolv, glass distilled or HPLC grade.
8.1.8 Methanol, Omnisolv, glass distilled or HPLC grade.
811.9 Serum, frozen liquid from Sigma.
8.1.10 Control serum received with each sample set.
8.1.11 Milli-Qm water, all water used in this method should be Milli-Qm water and may be provided by a Milli-Q TOC Plus system.
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8.2 Standards
8.2.1 Prepare PFOS standards for the standard curve.
8.2.2 Prepare other fluorochemical standards, as appropriate.
8.2.3 Weigh approximately 100 mg of PFOS into a 100 mL volumetric flask and record the actual weight.
8.2.4 Bring to volume with methanol for a stock standard of approximately 1000 ppm (I.Lg/mL)-
8.2.5 Dilute the stock solution with methanol for a working standard 1solution of approximately 50 ppm.
8.2.6 Dilute the stock solution with methanol for a working standard 2 solution of approx. 5.0 ppm.
8.2.7 Dilute the stock solution with methanol for a working standard 3 solution of approx. 0.50 ppm.
9.0 SAMPLJE~ANDLING 9.1 All sera are received frozen and must be kept frozen until the extractionis performed.
10.0 OUALITCYONTROL 10.1 Matrix Blanks and Method Blanks
10.1.1 Two 1.O mL aliquots of the serum are extracted following thisprocedure and used as matrix blanks. See section 11.1.2.
10.1.2 Two 1.0 mL aliquots of Milli-Qm water are extracted following this procedure and used as method blanks.
10.2 Matrix Spikes
10.2.1 Prepare and analyze matrix spike and matrix spike duplicate samples to determine the accuracy of the extraction.
10.2.2 Prepare each spike using serum chosen by the analyst, usually control serum
received with each sample set.
10.2.3 Expected concentrationswill fall in the mid-range of the initial calibration curve. Additional spikes may be included and may fall in the low-range of the initial calibration curve.
10.3 Continuing Calibration Checks
10.3.1 Prepare and analyze continuing calibration check samples to determine the continued linearity of the initial calibration curve.
10.3.2 One check is prepared per group of ten samples. For example, if a sample set = 34, four checks are prepared and extracted.
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10.3.3 Prepare each continuing calibration check fiom the same serum used to prep the initial curve.
10.3.4 The expected concentration will fall withinthe mid-range of the initial calibration
curve.
11.0 CALIBRATION AND STANDARDIZATION 11.1 Prepare Serum Standards
11.1.1 Transfer 1 mL of serum to a 15 mL centrifuge tube.
11.1.2 If the majority of serum sample volumes are less than 1.O mL, extract standards using serum volumes inthe standards equal to the serum volumes in samples. Do not extract below 0.50 mL of serum. Record the serum volume on the extraction sheet.
11.1.3 Mix or shake between aliquots while preparing a total of sixteen aliquots of serum in 15 mL centrifugetubes. .
11.1.4 Two 1 mL or appropriate aliquots serve as matrix blanks. Typically use the standard concentrations and spiking amounts listed in table 1to spike, in duplicate, two standard curves for a total of fourteen samples.
11.1.5 Refer to the validation report FACT-M-3.0-V-1 and FACT-M-4.0-V-1 which lists the working ranges for calibration curves.
Working Standard
- (Approx. Conc.)
0.500 ppm 5.00 ppm 5.00 ppm 5.00 ppm 50.0 ppm 50.0 m m
PL
Approx. final conc. of
- PFOS in serum B- -lank
20
0.0 10ppm
5
0.025 ppm
10
0.050 ppm
20
0.100 ppm
5
0.250 ppm -
10
0.500 vpm
11.1.4 See section 13.0 to calculate actual concentrations of PFOS in calibration standards.
11.2 Extract spiked serum standards following 12.6-12.16 of this method. Use these standards to establish each initial curve on the mass spectrometer.
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12.0 PROCEDURES .
12.1 Obtain frozen serum samples and allow to thaw.
12.2 Vortex mix for 15 seconds then remove 1.OmL, or appropriate volume to a 15 mL
polypropylene centrifuge tube.
1 2 3 Return serum samplesto freezer after extraction amount has been removed.
12.4 Record the serum volume on the extraction worksheet. The final methanol volume will equal the initial serum volume.
12.5 Label the tube with the study number, serum ID, date and analyst initials. See attached worksheet for documenting the remaining steps.
12.6 Spike serum with the appropriate amount of PFOS standard as described in section 11.1 or Table I for the calibration curve standards. Also spike matrix spikes and continuing calibration standards.
12.7 Vortex mix the standard curve samples, matrix spike samples, and continuing calibration samples for 15 seconds.
12.8 Add 1 mL 0.5 M TBA and 2 mL of the 0.25 M sodium carbonatdsodium bicarbonate buffer.
12.9 Using a volumetric pipette, add 5 mL ethyl acetate.
12.10 Cap each sample and put on the shaker for 20 minutes.
12.11 Centrifugefor 20 to 25 minutes,until layers are well separated. Set power on the centrifuge to approximately 3500 rpm.
12.12 Transfer 4 mL of organic layer, using a 5 mL, graduated glass pipette, to a clean 15 mL
centrifugetube: Label this freshtube with the same information as in 12.5.
12.13 Put each sampleon the analytical nitrogen evaporatoruntil dry,approximately 2 to 3
hours.
12.14 Add 1.OmL or appropriate volume of methanol to each centrifugetube using a graduated pipette. (This volume equals the initial volume of serum used for the extraction.)
12.15Vortex mix for 30 seconds.
12.16 Attach a 0.2 pmnylon mesh filterto a 3 cc syringe and transfer the sampleto this syringe.
Filter into a 1.5 mL glass autovial.
12.17Label the autovial with the study number, animal number and gender, sampletimepoint, matrix, final solvent, extraction date, and analyst(s) who performed the extraction.
12.18Cap and hold for HPLC-electrospray/massspectrometryanalysis. Extracts may be stored at 4" C until analysis.
12.19 Complete the extraction worksheet, attached to this document, and tape to page of study notebook.
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13.0 DATAANALYSIASND CALCULATIONS
13.1 Calculations:
13.1.1 Calculate actual concentrationsof PFOS, or other appropriate fluorochemical,in
calibration standards using the following equation: mL of Standard x Concentration(UE /mL) = Final Concentration (pg/mL)
m L of Standard +Initial Serum Volume (a)of PFOS in Serum
14.0 METHOD PERFORMANCE
14.1 The-methoddetection limit is equal to halfthe lowest standard in the calibration curve.
15.0 POLLUTIOPNREVENTIONAND WASTE MANAGEMENT 15.1 Samplewaste is disposed inbiohazard containers, flammablesolvent waste is disposed in
high BTU containers, and used glass pipette waste is disposed in broken glass containers
located in the laboratory.
16.0 RECORDS 16.1 Complete the extraction wwksheet attached to this method, and tape into the study
notebook.
17.0 TABLESD,IAGRAMFSL. OWCHARTANSD. VALIDATION DATA 17.1 The validation report associated with this method is FACT-M-3.0 & 4.0-V-1.
18.0 REFERENCES 18.1 None
19.0 AFFECTEDDOCUMENTS
19.1 FACT-M-4, "Analysis of Serum E2dract.s for Fluorochemicals using HPLC-Electrospray Mass Spectrometry"
20.0 REVISIONS
Revision Number.
Reason For Revision
Revision
- Date
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Extraction of PFOS from Serum
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ExtractionWorksheet for FACT-M-3
Study #
-
Sample Number
set # H20Blank
Serum Blank
PFOS approx. 0.5 ppm actual ppm
#W
PFOS
approx. 5 ppm actual ppm #W
-
PFOS approx. 50 ppm actual ppm
#W -
Date and Initials for
Std. or Comments
I
I
-
ppm. MSNSD used sample
. Cont. Checks used same serum as for std curve.
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3M ENVIRONMENTALLABORATORY
METHOD
EXTRACTION OF POTASSIUM~RFLUOROOCTANESULFONATEOR OTHER
FLUoRoCREMICAL COMPOUNDS FROM SERUM FOR ANALYSIS USINGHPLCELECTROSPRAYMSAPESCSTROMETRY
Method Number: ETS-8-4.1
Adoption Date: 03/01/99
Author: Lisa Clemen,Glenn Langenburg
Revision Date: Lc/a7@?
Approved By:
Laboratory Manag&
Date
Technical Reviewer
olllaL/4 9
Date
1.0 SCOPEANDAPPLICATION
Scope: This method is for the extraction of potassium perfluorooctanesulfonate (PFOS)
0
or other fluorochemical compounds fiom senun.
Applicable compounds: Fluorochemical surfactants or other fluorinated compounds.
Matrices: Rabbit, rat, bovine, monkey, and human serum or other fluids as designated in the validation report.
Word 6/95
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2.0 SUMMARY OF METHOD 2.1 This method describes the procedure for extracting potassium perfluorooctanesulfonate
(PFOS)or other fluorochemical surfactants fromserum, or otherfluids, using an ion pairing reagent and methyl-fert-butyl ether (AWE). In this method, seven fluorochemicalswere extracted: PFOS, PFOSA, PFOSAA, EtFOSE-OH, PFOSEA, M556, and surrogate standard (see 3.0 Definitions). An ion pairing reagent is added to the sample and the analyte ion pair is partitioned into MtBE. The MtBE extract is removed and put onto a nitrogen evaporatoruntil dry. Each extract is reconstituted in 1.O mL of methanol, then filtered through a 3 cc plastic syringe attached to a 0.2 p m nylon
filter into glass autovials. 2.2 These sample extracts are analyzed following method ETS-8-5.1 or other appropriate
methods.
3.0 DEFINITIONS 3.1 PFOS:perfluorooctanesulfonate(anion of potassium salt) C,F,,SO,'
3.2 PFOSA.perfluorooctanesulfonylamideC,F,,SO,NH,
3.3 PFOSM. peffluorooctanesulfonylamido(ethy1)acetate C8F,,S0,N(CH2CH3)CH2CO;
3.4 EtFOSE-OH: 2(N-ethylperfluorooctane sulfonamide)-ethyl alcohol
C~F,,S02N(CH,CH3)CH2CH20H
3.5 PFOSEA: perfluorooctane sulfonyl ethylamide C,F,,SO,N(CH,CH,)H
3.6 M556:C8F,,SO,N(H)(CH,COOH)
3.7 Surrogate standard: lH-lH-2H-2H perfluorooctane sulfonicacid
4.0 WARNINGS AND CAUTIONS
4.1 Health and safety warnings
4.1.1 Use Universalprecautions,especiallylaboratory coats, goggles, and gloves when handling animal tissue, which may contain pathogens.
5.0 INTERFERENCES 5.1 There are no intexfkences known at this time.
6.0 EQUIPMENT 6.1 The following equipment is used while performing this method. Equivalent equipment is
acceptable. 6.1.1 Vortex mixer, VWR, Vortex Genie 2 6.1.2 Centrifbge,Mistral 1000or IEC 6.1.3 Shaker, Eberbach or VWR
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6.1.4 Nitrogen evaporator, Organomation 6.1.5 Balance (zk 0.100 g)
7.0 SUPPLIES AND MATERIALS 7.1 Gloves 7.2 Eppendorf or disposable pipettes 7.3 Nalgene bottles, capable of holding 250 mL and 1L 7.4 Volumetric flasks, glass, type A 7.5 I-CHEM Vials, glass, 40 mL glass 7.6 Centrifbge tubes, polypropylene, 15 mL 7.7 Labels 7.8 Oxford Dispenser- 3.0 to 10.0mL 7.9 Syringes,capableofmeasuring 5 pL to 50 pL 7.10 Graduated pipettes 7.11 Syringes, disposable plastic, 3 cc 7.12 Syringe filters, nylon, 0.2 p,25 mm 7.13 Timer 7.14 Crimp cap autovials and caps 7.15 Crimpers Note: Prior to using glassware and bottles, rinse 3 times with methanol and 3 times with
Milli-Q"" water. Rinse syringes a minimum of 9 times with methanol, 3 rinses h m 3
separate vials.
8.0 REAGENTS AND STANDARDS
8.1 Type I reagent grade water, Milli-Qm or equivalent; all water used in this method should be Milli-QWwater and may be provided by a Milli-Q TOC PlusTMsystem
8.2 Sodiumhydroxide (NaOH), J.T Baker or equivalent 8.3 Tetrabutylammonium hydrogen suifate(TBA), Kodak or equivalent 8.4 Sodium carbonate (N%CO,), J.T.Baker or equivalent 8.5 Sodiumbicarbonate (NaHCO,), J.T. Baker or equivalent 8.6 Methyl-T-Butyl Ether, Omnisolv, glass distilled or HPLC grade 8.7 Methanol, Omnisolv, glass distilled or HPLC grade 8.8 Serum or blood, frozen fiom supplier 8.9 Fluorochemical standards
8.9.1 PFOS (3M Specialty Chemical Division), molecular weight = 538 8.9.2 PFOSA (3M Specialty Chemical Division), molecular weight = 499
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8.9.3 PFOSAA (3M SpecialtyChemical Division), molecularweight = 585
8.9.4 EtFOSE-OH(3MSpecialty Chemical Division), molecular weight = 570
8.9.5 PFOSEA (3M Specialty Chemical Division), molecular weight = 527
8.9.6 M556 (3M SpecialtyChemicalDivision), molecular weight =557
8.9.7 Surrogate standard:4-H, perfluorooctane: sulfonic acid (1-H,l-H, 2-H,2-H CBF,3S0,Hm) olecular weight =428
8.9.8 Other fluorochemicals, as appropriate
8.10 Reagent preparation
NOTE: When preparing larger volumes thanlisted in reagent, standard,or surrogate
preparation, adjust accordingly.
8.10.1 10N sodium hydroxide (NaOH): Weigh approximately200 g NaOH. Pour into a
1000 mL beaker containing 500 mL MillS-Qw water, mix until all solids are
dissolved. Store in a 1L Nalgene bottle.
8.10.2 1N sodium hydroxide (NaOH): Dilute IO N NaOH 1:lO. Measure 10mI,of 10 N NaOH solution into a 100mLvolumetric flask and dilute to volume using
Milli-QTMwater. Store in a 125 mL Nalgene bottle.
8.10.3
'
0.5M tetrabutylammoniumhydrogen sulfate (TBA): Weigh approximately 169g of TBA into a 1L volumetriccontaining 500 dMilli-Qm water. Adjust to pH 10using approximately44to 54 mLof 1~0N NaOH (While adding the last mL of
NaOH, add slowly because the pH changes abruptly). Dilute to volume with
Milli-Qm water. Store in a 1L Nalgene bottle.
8.10.3.1 TBA requires a checkprior to each use to ensure pH = 10. Adjust as needed using 1N NaOH solution.
8.10.4 0.25M sodium carbonatelsodium bicarbonate buffer (Na$0,/N&C03): Weigh approximately 26.5 g of sodium carbonate (NqCO,) and 21.Og of sodium bicarbonate (NaHCO,) into a 1L volumetric flask and bring to volume with Mlli-
Qm water. Store in a 1L Nalgenebottle:.
8.11 Standards preparation
8.11.1 Prepare PFOS standards for the standard curve.
8.1 1.2 Prepare other fluorochemkal standards, as appropriate. Multicomponent fluorochemicalstandardsare acceptable(for example, one working standard solution containing 1.00 ppm PFOS, 1.02 ppm PFOSA, 0.987 ppm PFOSAA, and 1-10ppm EtFOSE-OH.)
8.11.3 Weigh approximately 100 mg of PFOS into a 100 mL volumetric flask and record the actual weight.
8.11.4 Bring to volume with methanol for a stock standard of approximately 1000ppm
(Cldd).
8.11.5 Dilute the stock solutionWith methanol for a working standard 1solutionof approximately 50 ppm.
8.11.6 Dilute working standard 1 with methanol for a working st&dard 2 solution of approx. 5.0 ppm.
mS-8-4.1 Extraction of PFOS f'rorn Serum
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8.11.7 Dilute working standard 1 with methanol for a working standard 3 solution of approx. 0.50 ppm.
8.12 Surrogate stock standard preparation
8.12.1 Weigh approximately 50-60 mg of surrogate standard 1-H,l-H2,-H,2-H,
C$,,SO,H into a 50 mLvolumetric flask and record the actual weight.
8.12.2 Bring to volume with methanol for a surrogate stock of approximately 1000-1200 PPm*
8.12.3 Prepare a m g a t e working standard. Transfer approximately 1 mL of surrogate stock to a 10 mL volumetric flask and biing to volume with methanol for a working standard of 100ppm. Record tlhe actual volume transferred.
9.0 SAMPLEHANDLING
9.1 All samples are received fiozen and must be kept h z e n until the extraction is performed. 9.2 Allow samples to thaw to room temperature prior to extraction.
10.0 OUALITCYONTROL
10.1 Solvent Blanks, Method blanks and matrix blanks
10.1.1 An aliquot of 1.0 mL methanol is used as a solvent blank.
10.1.2 Extract two 1.0 mL aliquots of Milli-QTdwater following thisprocedure and use as method blanks.
10.1.3 Extract two 1.0 mL aliquots of the s e m i followingthisprocedure and use as matrix blanks. See 11.1.4.
10.2 Matrix spikes 10.2.1 Prepare and analyze matrix spike and mlatrixspike duplicate samples to determine the accuracy of the extraction.
10.2.2 Prepare each spike using a sample chosen by the analyst, usually the control
matrix received with each sample set.
10.2.3 Expected concentrationswill fall in the ]mid-rangeof the initial calibrationcurve. Additional spikes may be included and may fall in the low-range of the initial calibration curve.
10.2.4 Prepare one matrix spike and matrix spike duplicate per 40 samples, with a
minimum of 2 matrix spikes per batch.
10.3 Continuing calibration checks
10.3.1 Prepare continuing calibration check samples to ensure the accuracy of the initial calibration curve.
10.3.2 Prepare, at a minimum, one continuing check per group of 10 samples. For example, if a sample set = 34,four checks are prepared and extracted.
10.3.3 Prepare each continuing calibration check from the same matrix used to prepare the initial curve.
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10.3.4
The expected concentrations will fall within the mid-range of the initial
calibration curve. Additional spikes mait be included that fall in the low-range of the initial calibration curve. This is necessary if the analyst must quantitate using
only the low end of the calibrationcurve (for example, 5 ppb - 100ppb, rather
than
5 ppb - 1000 ppb).
11.o CALIBRATION AND STANDARDIZATION
11.1 Prepare matrix calibration standards
11.1.1 Transfer 1 mL of serum to a 15mL centrifuge tube.
11.1.2 Ifmost sample volumes are less than 1.01 mL, extract standardswithmatrix
volumes equal to the sample volumes. Do not extract less than 0.50 mL of matrix. Record each sample volume on the extraction sheet.
11.1.3 While preparing a total of twenty aliquolsin 15mL centrifuge tubes, mix or shake between aliquots.
11.1.4 Two 1 mL aliquots, or othex appropriatevolume, serve as matrix blanks. Typically use the standard concentrations and spiking amounts listed in Table 1, at the end of this section,to spike, in duplicate, two standard curves, for a total of eighteen standards, two matrix blanks, and two method blanks.
11.1.5 Refer to validation report ETS-8-4.0 & IETS-8-5.0-V-1,which lists the working ranges and the Linear CalibrationRange (LCR) for calibrationcurves.
11.1.6 Use Attachment D as an aid hcalculating the concentrations of the working standards. See Section 13.0 to calculate actual concentrations of PFOS in calibration standards.
11.2 To each standard, blank, or continuing check, add appropriate amount of swrogate
working standard for the concentrationto fall within the calibration curve range 5 ppb -
1000 ppb.
113 Extract spiked matrix standardsfollowing 12.6-12.16 of this method. Use these standards
to establish each initial curve on the mass spectrometer.
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Table 1 Approximate spiking amounts for standards and spikes
Using 1.0 mL of maitrix .
Working standard
PL
Approx. final conc. of
(approx. conc.)
analyte in matrix
-
Blank
0.500 ppm
10
0.005 ppm
0.500 ppm
20
0.010 ppm
5.00 ppm
5
0.025 ppm
5.00 ppm
10
0.050 ppm
5.00 ppm
20
0.100 ppm
50.0 ppm
5
0.250 ppm
50.0 ppm
10
0.500 ppm
50.0 ppm
-
50.0 ppm
15
0.750 ppm
20
1.OOppm
12.0 PROCEDURE
12.1 Obtain fiozen samples and allow to thaw at room temperature or in a lukewarm waterbath.
12.2 Vortex mix for 15 seconds,then transfer 1.0 mL,or other appropriatevolume to a 15mL polypropylene centrifige tube.
12.3 Return unused samples to fieezer after extraction amounts have been removed,
12.4 Record the initial volume on the extractionworksheet.
12.5 Label the tube with the study number, sample E),date and analyst initials. See attached
worksheet for documenting the remaining steps.
12.6 Spike all samples,includingblanks and standartis, ready for extraction with surrogate standard as described in 11.2.
12.7 Spike each matrix with the appropriateamount of standard as described in 11.1, or Table
1 in that section, for the calibration curve standards. Also prepare matrix spikes and
continuing calibration standards.
I
12.8 Vortex mix the standard curve samples, matrix spike samples, and continuing calibration samples for 15 seconds.
12.9 Check to ensure the 0.5 M TBA reagent is at pH[ 10. If not, adjust accordingly.
12.10 To each sample, add 1mL 0.5 M TBA and 2 rn12of 0.25M sodium carbonatdsodium bicarbonate buffer.
12.11 Using an Oxford Dispenser, add 5 mL methyl-twt-butyl ether.
12.12 Cap each sample and put on the shaker at a setting of 300 rpm,for 20 minutes.
12.13 Centrifuge for 20 to 25 minutes at a setting of 3500 rpm,or until layers are well separated.
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12.14 Label a fiesh 15 mL centrifuge tube with the same information as in 12.5.
12.15 Remove 4.0mL of the organic layer to this clean 15mL centrihge tube.
12.16 Put each sample on the analytical nitrogen evaporator until dry, approximately i to 2 hours.
12.17 Add 1.O mL of methanol to each centrifugetuba using a graduatedpipette.
12.18 Vortex mix for 30 seconds.
12.19 Attach a 0.2 pm nylon mesh filterto a 3 cc syringe and transfer the sampleto this syringe. Filter into a 1.5 mL glass autovial or low-volume autovial when necessary.
12.20 Label the autovial with the study number, animal number and gender, sample timepoint,
matrix, final solvent, extraction date, and analyst@)performing the extraction.
12.21 Cap and store extracts at room temperature or at approximately4 "C until analysis.
12.22 Complete the extractionworksheet, attached to this document, and tape in the study notebook or include in study binder, as appropriate.
13.0 DATA ANALYSIASN D CALCULATIONS
13.1 Calculations
13.1.1 Calculate actual concentrationsof PFOS,or other applicable fluomchemical, in
calibration standards using the following equation:
mL of standard x concentrationof standard lug /mU
-
. mL of standard +mL of surrogate standard +initialmatrix volume (d)
Final Concentration (pg/mL,) of PFOS in matrix
14.0 METHODPERFORMANCE
14.1 The method detection limit (MDL) is analyte and matrix specific. Refer to MDL report for specificMDL and limit of quantitation (LOQ) values (see AttachmentsB and C).
14.2 The following quality control samples are extracted with each batch of samples to
evaluate the quality of the extraction and analysis.
14.2.1 Method blanks and matrix blanks.
14.2.2 Matrix spike and matrix spike duplicate samples to determine accuracy and precision of the extraction.
14.2.3 Continuing calibration check samples to determine the continued accuracy of the initial calibrationcurve.
14.3 Refer to section 14 of ETS-8-5.1 for method performance criteria.
15.0 POLLUTION PREVENTION AND WASTE MANAGEMENT
15.1 Sample waste is disposed in biohazard containers, flammable solvent waste is disposed in high BTU containers, and used glass pipette waste is disposed in broken glass containers
located in the laboratory.
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16.0 RECORDS
16.1 Complete the extraction worksheet attached to this method, and tape in the study notebook or include in the 3-ring study binder, as appropriate.
17.0 ATTACHMENTS 17.1 Attachment A., Extraction worksheet 17.2 Attachment B, MDL/LOQ values and summary 17.3 Attachment C, Calibration standard concentration worksheet
18.0 REFERENCES
18.1 The validation report associated with this method is ETS-8-4.0& 5.0-V-1.
18.2 FACT-M-3.1,"Analysis ofSerum or Other Fluid Extracts for Fluorochemicals using
HPLC-Electrospray Mass Spectrometry"
19.0 AFFECTED DOCUMENTS
19.1 ETS-8-5.1, "Analysis of Serum or Other Fluid Extracts for Fluorochemicals using HPLC-Electrospray Mass Spectrometry"
20.0 IREVISIONS .
Revision Number
1
Reason For Revision
Section 12.21 Changedto include sample storage at room temperatwe. Section 12.13 Added the shaker speed. Section 12.17 Final volume is 1.0 mL; not adjusted for initial volumes less than 1.0 mL.
Revision
- Date
04/02/99
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Extraction Worksheet ETS-8-4.I
I
1 Shake 20 min.
Shaker speed:
Cont. Cal. Verificationsused same matrix as for std m e .
Attachment A
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Compound
PFOS PFOSA PFOSAA EtFOSE-OH M556 PFOSEA
MDL (ppb)
1.74 1.51 3.46 11.4 6.03 5.71
LOQ (ppb)
5.55 4.79 20.5 36.2 19.2 18.2
Linear Calibration Range (LCR)
Approximate concentrations to be used for preparing the Standard Calibration Curve
5 ppb - 1000 ppb
- 5 ppb 1000 ppb
- 5 ppb 1000ppb
5 ppb - 1000 ppb
- 5 ppb 1000ppb - 5 ppb 1000ppb
Attachment B: MDWLOQ Summary
3M Environmental Laboratory
ETS-8-4.1 ExtractionofPFOS from Serum
Page 11 of 14 Page 132
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Prepared range LCR from %
1 1 ,I 11i- Rabbit Serum ofstandards bPb) (ng/mL)
Full Range
I
[lCke
0.995 - 978
4.94-248
curve
(Kpb)
(ndmL)
24.8 - 978
4.94-248
83-108
4.67-1 1.0
I
I
W;;; 5.34-12.0
High curve
97.8 - 9713
0.995 - 978
97.8 - 978
4.94 - 978
85-106
4.849.80 4.60-10.5
Rabbit Serum
Prepared range of standards
(PPb) WmL)
FullRange . 0.993 -976
LCB from
CurYe
(PPb)
(ndmL)
- 4.93 976
Low h e
I I Highcurve
I 1 l/x
4.93 - 97.6
24.8-976 0.993-976
4.93 - 97.6
1 24.8-978
I 4.93-976
% Recovery Range
88-103 87-105
I I 93-102
I 1 94-103
RSD Range
5.1 0-14.7 9.85-14.7
I 5.08-13.9
I 5.10-14.5
Rabbit Serum Full Range
Prepared range of standards
(PPb) (nl4m.L)
- 0.991 974
LCR from
curve
0
(ndmL)
24.7 - 974
YORecovery Range
81-111
RSD Range
4.18-10.6
Low Curve
4.92 - 247
9.74 - 247
97-107
6.38-2 1.8
High curve
49.2 - 974
97.4 - 974
85- 108
4.33-12.5
1/X I
- - 0.991 974
9.74 974
95-1 15
4.1 1-23.2
I
I
I
I
I
Attachment B: MDLnOQ Summary 3M Environmental Laboratory
ETS-8-4.1
Extraction of PFOS from Serum
1 Page 12 of 14
Page 133
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Rabbit Serum
Full Range Low Curve High curve
1/X
Prepared range of standards (Ppb) (ng/mL)
0.993 - 976
4.93 - 97.6
49.3 - 976 0.993 - 493
LCR from
curve (PPb)
(ng/mL)
49.3 - 976
9.76 - 97.6
97.6 - 976
9.76 - 976
% Recovery Range
77-110 97-107 90-109 86-111
RSD Range
11.2-25.5 14.1-21.3 11.5-1 9.6 11.1-21.2
Rabbit Serum
Prepared range of standards
(PPW (ng/mL)
Full Range Low Curve High curve
1/X
0.993 - 976
4.93 - 248
49.3 - 976
0.993 - 976
LCR fiom
curve
0
(ndrnL)
2 4 8 - 976
9.76 - 248
49.3 - 976
9.76 - 976
% Recovery
Range
96-106 91-110 86-106 95-1 17
RSD
Range
~
10.1- 16.2 11.8-19.5 10.2-18.2 10.1-19.1
Prepared range LCR fim YORecovery
RSD
Rabbit Serum of standards
curve
Range
Range
(PPb) ( n d d ) (PPb)
(ng/mL)
Full Range
0.993 - 976
24.8 - 976
88-106
4.82-17.9
Low Curve 1 4.93 ..97.6 1 9.76-97.6 1 100-105 1 5.95-18.2 I
Highcurve I 97.6-976
1/X
I 0.993-976
I 97.6-976 I I 9.76-976 I
81-111 97-110
I 5.11-9.74 1 I 4.77-19.5 I
Attachment B:MDL/LOQ Summary 3M Environmental Laboratory
ETS-8-4.1 ExtractionofPFOS from Serum
Page 13 of 14 Page 134
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Analytical Report: FACT-TOX-001 LRN-U2103
Ion Pair Standard Curves - Fluids
Prep date(@:
Standard number:
Analyte(s):
Equipment number:
Sample matrix:
Final solvent and TN:
Blank fluiaidentifier:
Method/revision:
Target analyte(s):
FC mix std approx. 0.500ppm:
FC mix std approx. 5.00 ppm:
FC mix std approx. 50.0ppm:
Surrogate std approx 100 ppm:
Actual concentrations of standards in the FC mix
493
500
524
494
501
513
735
746
782
737
749
766
976
989
1038
978
993
1017
Sernm Rabbit
I PFOS
5.00-1000
PFOSA
PFOSAA EtFOSE-OH PFOSEA
M556
5.00-1000 I 5.00-1000 I 5.00-1000 I 5.00-1000 1 5.00-1000
Bovine
Estimates only. Use values for rabbit.
Rat
Estimates only. Use values for rabbit.
Monkey & Plasma Estimates only. Use values for rabbit.
Human
Estimates only. Use values for rabbit.
Attachment C:Ion Pair StandardCurves
ETS-8-4.1
Extraction of PFOS from Serum
3M Environmental Laboratory
Page 14 of 14
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3M ENVIRONMENTLAALBORATORY
METHOD
EXTRACTIOONF POTASSIUM PERFLUOROOCTANESULFONATEOR OTHER FLUOROCHEMICCAOMLPOUNDS FROM LIVERFOR ANALYSIS USING HPLC-
ELECTROSPRAY/MASPSESCTROMETRY
Method Number: ETS-8-6.0 Author: Lisa Clemen, Robert Wynne
Adoption Date: 03J 2 I"y
Revision Date: $k
Group Leader
FWlg3
Date
,
$- @ Technical Reviewer
0 . 4 ,CI /as
Date
+ 1.0 SCOPE AND APPLICATION
1.1 Scope: This method is for the extraction of potassium perfluorooctanesulfonate (PFOS) or
TJ other fluorochemical compounds from liver.
Y
0 1.2 Applicable Compounds: Fluorochemical surfactants or other fluorinated compounds.
-+a
0 1.3 Matrices: Rabbit, rat, bovine, and monkey livers or other tissues as designated in the
2. validation report.
-0 e.
a
Word 6.0195
ETS-8-6.0
Page 1 of 14
3M Environmental Laboratory
Extraction of PFOS from Liver
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Analytical Report: FACT-TOX-001 LRN-U2103
2.0 SUMMARY OF METHOD
2.1 This method describes the procedure for extracting potassium perfluorooctanesulfonate (PFOS) or other fluorochemical surfactants from liver, or other tissues, using an ion pairing reagent and methyl-tert-butyl ether (MtBE). In this method, seven fluorochemicalscan be extracted: PFOS, PFOSA, PFOSAA, EtFOSE-OH,PFOSEA, M556, and surrogate standard. An ion pairing reagent is added to the sample and the analyte ion pair is partitioned into MBE. The MtBE extract is transferred to a centrifugetube and put onto a
nitrogen evaporator until dry. Each extract is reconstituted in 1.O mL methanol then
filtered through a 3 cc plastic syringe attached to a 0.2 pm nylon filter into glass autovials.
2.2 These sample extracts are analyzed following method ETS-8-7.0 or other appropriate methods.
3.0 DEFINITIONS 3.1 PFOS: perfluorooctanesulfonate (anion of potassium salt) C,FI7SO, 3.2 PFOSA: perfluorooctane sulfonylamide C,F,,SO,NH,
3.3 PFOSAA: perfluorooctane sulfonylamido (ethy1)acetate C,F,,SO,N(CH,CH,)CH,CO, 3.4 EtFOSE-OH: 2(N-ethylperfluorooctane su1fonamido)-ethyl alcohol
C,F,,S0,N(CH,CH,)CH,CH20H
3.5 PFOSEA: perfluorooctane sulfonyl ethylamide C,F,,SO,N(CH,CH,)H 3.6 M556: C,F,,SO,N(H)(CH,COOH) 3.7 Surrogate standard: lH-lH-2H-2H perfluorooctane sulfonic acid
4.0 WARNINGS AND CAUTIONS
4.1 Health and Safety Warnings:
4.1.1 Use universal precautions, especially laboratory coats, goggles, and gloves when handling animal tissue, which may contain pathogens.
5.0 INTERFERENCES 5.1 There are no interferences known at this time.
6.0 EQUIPMENT 6.1 The following equipment is used while performing this method. Equivalent equipment is
acceptable.
6.1.1 Ultra-Turrax T25 Grinder for grinding liver samples 6.1.2 Vortex mixer, VWR, Vortex Genie 2 6.1.3 Centrifuge, Mistral 1000 or IEC 6.1.4 Shaker, Eberbach or VWR
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6.1.5 Nitrogen Evaporator, Organomation 6.1.6 Balance (sensitivity to 0.100 g)
7.0 SUPPLIES AND MATERIALS 7.1 Gloves 7.2 Dissecting scalpels 7.3 Eppendorf or disposable pipettes 7.4 Nalgene bottles, capable of holding 250 mL and 1 L 7.5 Volumetric flasks, glass, type A 7.6 I-CHEM vials, 40 mL glass 7.7 Plastic sampule vials, Wheaton, 6 mL (or appropriate size) 7.8 Centrifuge tubes, polypropylene, 15 mL 7.9 Labels 7.10 Oxford Dispensor - 3.0 to 10.0 ml 7.11 Syringes, capable of measuring 5 pL to 50 pL 7.12 Graduated pipettes 7.13 Syringes, disposable plastic, 3 cc 7.14 Syringe filters, nylon, 0.2 pm, 25 mm 7.15 Timer 7.16 Crimp cap autovials and caps 7.17 Crimpers Note: Prior to using glassware and bottles, rinse 3 times with methanol and 3 times with Milli-
Q" water. Rinse syringes a minimum of 9 times with methanol, 3 rinses from 3 separate vials.
8.0 REAGENTASND STANDARDS
8.1 Type I reagent grade water, Milli-QTMor equivalent; all water used in this method should
be Milli-QTMwater and be provided by a Milli-Q TOC PlusTMsystem 8.2 Sodium hydroxide (NaOH), J.T Baker or equivalent 8.3 Tetrabutylammoniumhydrogen sulfate(TBA),Kodak or equivalent 8.4 Sodium carbonate (Na.$O,), J.T. Baker or equivalent 8.5 Sodium bicarbonate (NaHCO,), J.T. Baker or equivalent 8.6 Methyl-tert-butyl ether, Omnisolv, glass distilled or HPLC grade 8.7 Methanol, Omnisolv, glass distilled or HPLC grade 8.8 Liver, frozen from supplier
8.9 Dry ice from supplier
8.10 Fluorochemical standards 8.10.1 PFOS (3M Specialty Chemical Division), molecular weight = 538
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8.10.2 PFOSA (3M Specialty Chemical Division), molecular weight = 499
8.10.3 PFOSAA (3M Specialty Chemical Division), molecular weight = 585
8.10.4 EtFOSE-OH (3M Specialty Chemical Division), molecular weight = 570
8.10.5 PFOSEA (3M Specialty Chemical Division), molecular weight = 527
8.10.6 M556 (3M Specialty Chemical Division), molecular weight = 557
8.10.7 Surrogate standard: 4-H, perfluorooctanesulfonic acid (1-H,1-H, 2-H, 2-H C,F,,SO,H) molecular weight = 428
8.10.8 Other fluorochemicals,as appropriate
8.11 Reagent preparation
NOTE: When preparing larger volumes than listed in reagent, standard, or surrogate preparation, adjust accordingly.
8.11.1 10N sodium hydroxide (NaOH): Weigh approximately200 g NaOH. Pour into a 1000 mL beaker containing 500 mL Milli-Q'" water, mix until all solids are dissolved. Store in a 1L Nalgene bottle.
8.11.2 1 N sodium hydroxide (NaOH): Dilute 10N NaOH 1:10. Measure 10mL of 10N NaOH solution into a 100mL volumetric flask and dilute to volume using Milli-QTMwater. Store in a 125mL Nalgene bottle.
8.11.3 0.5 M tetrabutylammoniumhydrogen sulfate (TBA): Weigh approximately 169 g of TBA into a 1 L volumetric containing 500 mL Milli-QTMwater. Adjust to pH 10 using approximately44 to 54 mL of 10N NaOH (While adding the last mL of NaOH, add slowly because the pH changes abruptly). Dilute to volume with Milli-QTMwater. Store in a 1L Nalgene bottle.
8.11.3.1 TBA requires a check prior to each use to ensure pH = 10. Adjust as needed using 1N NaOH solution.
8.11.4 0.25 M sodium carbonatehodium bicarbonate buffer (Na$O,/NaHCO,): Weigh approximately 26.5 g of sodium carbonate (N%COJ and 21.Og of sodium
bicarbonate (NaHCO,) into a 1 L volumetric flask and bring to volume with Milli-
QTMwater. Store in a 1 L Nalgene bottle.
8.12 Standards preparation
8.12.1 Prepare PFOS standards for the standard curve.
8.12.2 Prepare other fluorochemical standards, as appropriate. Multicomponent fluorochemical standards are acceptable (for example, one working standard solution containing 1.OO ppm PFOS, 1.02ppm PFOSA, 0.987 ppm PFOSAA, and 1.10 ppm EtFOSE-OH.)
8.12.3 Weigh approximately 100mg of PFOS into a 100mL volumetric flask and record the actual weight.
8.12.4 Bring to volume with methanol for a stock standard of approximately 1000ppm WmL).
8.12.5 Dilute the stock solution with methanol for a working standard 1 solution of approximately 50 ppm.
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8.12.6 Dilute the stock solution with methanol for a working standard 2 solution of approx. 5.0 pprn.
8.12.7 Dilute the stock solution with methanol for a working standard 3 solution of approx. 0.50 ppm.
8.13 Surrogate stock standard preparation 8.13.1 Weigh approximately 50-60 mg of surrogate standard 1-H,l-H, 2-H, 2-H, C,F,,SO,H into a 50 ml volumetric flask and record the actual weight.
8.13.2 Bring to volume with methanol for a surrogate stock of approximately 1000-1200 PPm-
8.13.3 Prepare a surrogate working standard. Transfer approximately 1.O ml of surrogate stock to a 10 ml volumetric flask and bring to volurne with methanol for a working standard of 10-20 ppm. Record the actual volume transferred.
9.0 SAMPLHEANDLING 9.1 All samples are received fkozen and must be kept frozen until the extraction is performed.
10.0 QUALITY CONTROL 10.1 Matrix blanks and method blanks
10.1.1 An aliquot of 1.0 mL methanol is used as a solvent blank. 10.1.2 Extract two 1.O mL aliquots of Milli-Q"" water following this procedure and use
as method blanks. 10.1.3 Extract two 1.0 mL aliquots of liver homogenate following this procedure and use
as matrix blanks. Refer to 11.1.6.
10.2 Matrix spikes
10.2.1 Prepare and analyze matrix spike and matrix spike duplicate samples to determine
the accuracy of the extraction.
10.2.2 Prepare each spike using a sample chosen by the analyst, usually a control liver received with each sample set.
10.2.3 Expected concentrationswill fall in the mid-range of the initial calibration curve. Additional spikes may be included and may fall in the low-range of the initial calibration curve.
10.2.4 Prepare one matrix spike and matrix spike duplicate per 40 samples, with a minimum of 2 matrix spikes per batch.
10.3 Continuing calibration verifications
10.3.1 Prepare continuing calibration verification samples to ensure the accuracy of the initial calibration curve.
10.3.2 Prepare, at a minimum, one continuing calibration verification sample per group of 10 samples. For example, if a sample set = 34, four verifications are prepared
and extracted.
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10.3.3 Prepare each continuing calibration verification from the same matrix used to prepare the initial curve.
10.3.4 The expected concentrationswill fall within the mid-range of the initial calibration curve. Additional spikes may be included that fall in the low-range of the initial calibration curve. This is necessary if the analyst must quantitate using
only the low end of the calibration curve (for example, 5 ppb - 100 ppb, rather than 5 ppb - 1000 ppb).
11.0 CALIBRATION AND STANDARDIZATION
11.1 Prepare matrix calibration standards
11.1.1 Weigh approximately40 g of liver into a 250 mL Nalgene bottle containing 200 m L s Milli-QTMwater. Grind to a homogeneous solution,
11.1.2 If 40 g is not available, use appropriate amounts of liver and water to ensure a 1:5 ratio.
11.1.3 Refer to 13.0 to calculate the actual density of liver homogenate and the concentration of solid liver tissue dispersed in 1.0 mL of homogenate solution.
11.1.5 Add 1 mL of homogenate to a 15 mL centrihge tube. Re-suspend solution by shaking between aliquots while preparing a total of eighteen 1 mL aliquots of homogeneous solution in 15 mL centrifuge tubes.
11.1.6 Two 1mL aliquots, or other appropriate volume, serve as matrix blanks.
11.1.7 Typically use the standard concentrations and spiking amounts listed in Table 1, at the end of this section, to spike, in duplicate, two standard curves, for a total of eighteen samples, two matrix blanks, and two method blanks.
11.1.8 Refer to validation reports ETS-8-6.0 and ETS-8-7.0-V-1 or Attachment By
which lists the working ranges and the Linear CalibrationRange (LCR) for calibration curves.
11.1.9 Use Attachment C as an aid in calculating the concentrations of the working standards. Refer to 13.0 to calculate actual concentrations of PFOS in calibration standards.
11.2 To each working standard, blank, or continuing verification, add appropriate amount of surrogate working standard for the concentration to fall within the calibration curve range 5 ppb - 1000ppb.
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11.3 Extract spiked liver homogenates following 12.14-12.25 of this method. Use these standards to establish each initial curve on the mass spectrometer,
Table 1 Approximate Spiking Amounts for Calibration Standards
Working Standard
1.11
(Approx. Conc.)
-
-
I
0.50 ppm
I
0.50 ppm
I
0.50 ppm
I I 0.50 ppm
I 2
I 4
I
10
I 20
I
0.50 ppm
I 40
I
5.0 ppm
I
10
I
5.0 ppm
I 20
5.0 ppm
30
50 PPm
4
Approx. final conc. of
PFOS in liver
*-
0.500 ppm
12.0 PROCEDURE 12.1 Obtain frozen liver samples. 12.2 Cut approximately 1 g of liver using a dissecting scalpel. This part of the procedure is best
performed quickly, not allowing the liver to thaw.
12.3 Weigh the sample directly into a tared plastic sampule vial.
12.4 Record the liver weight in'the study notebook.
12.5 Return unused liver portions to fieezer.
12.6 Add 2.5 mLs of water to sampule vial.
12.7 Grind the sample. Put the grinder probe in the sample and grind for about 2 minutes, or until the sample is homogeneous.
12.8 Rinse the probe into the sample with 2.5 mLs water using a pipette.
12.9 Take the grinder apart and clean it with methanol after each sample. Refer to AMDT-EP-
22.
12.10 Cap the sample and vortex for 15 seconds. Label the sampule vial with the study number, weight, liver ID, date and analyst initials.
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12.11 Pipette 1.0 mL, or other appropriate volume, of homogenate into a 15 mL polypropylene centrifuge tube. Label the centrifuge tube with the identical information as the sampule vial. Refer to attached worksheet for documenting the remaining steps.
12.12 Pipette two 1 mL aliquots of Milli-QTMwater to centrihge tubes. These will serve as method blanks.
12.13 Spike all samples, including blanks and standards ready for extraction with surrogate standard as described in section 11.2.
12.14 Spike each matim with the appropriate amount of standard as described in 11.1, or Table 1 of that section, for the calibration curve standards. Also prepare matrix spikes and continuing calibration standards.
12.15 Vortex mix the standard curve samples, matrix spike samples, and continuing calibration samples for 15 seconds.
12.16 Check to ensure 0.5 M TBA reagent is at pH 10. If not, adjust accordingly.
12.17 To each sample, add 1 mL 0.5 M TBA and 2 mL of the 0.25 M sodium carbonate/sodium bicarbonate buffer.
12.18 Using an Oxford Dispenser, add 5 mL methyl-tert-butyl ether.
12.19 Cap each sample and put on the shaker at a setting of 300 rpm, for 20 minutes.
12.20 Centrifuge for 20 to 25 minutes at a setting of 3500 rpm, or until layers are well separated.
12.21 Label a fiesh 15 mL centrifuge tube with the same information as in 12.10.
12.22 Remove 4.0mL of the organic layer to the fresh 15 mL centrifuge tube.
12.23 Put each sample on the analytical nitrogen evaporatoruntil dry, approximately 1to 2 hours.
12.24 Add 1.O mL to each centrifuge tube using a graduated pipette.
12.25 Vortex mix for 30 seconds.
12.26 Attach a 0.2 pm nylon mesh filter to a 3 cc syringe and transfer the sample to this syringe. Filter into a 1.5 niL glass autovial or low-volume autovial when necessary.
12.27 Label the autovial with the study number, animal number and gender, sample timepoint, matrix, final solvent, extraction date, and analyst(s) performing the extraction.
12.28 Cap and store extracts at room temperature or at approximately4 "C until analysis.
12.29 Complete the extraction worksheet, attached to this document, and tape in study notebook or include in study binder, as appropriate.
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13.0 DATAANALYSIASND CALCULATIONS 13.1 Calculations:
13.1.1 Calculate the average density of the liver homogenate by recording each mass of
ten separate 1.O mL aliquots of homogenate.
Average density (mg/mL) = Average mass (mg) of the aliauots
1.OmL aliquot
13.1.2 Calculate the amount of liver (mg) per 1.0 mL homogenate (or concentration of dispersed solid tissue per mL of homogenate suspension) using the following equation:
g of Liver x Average density* of homopenate (mdmL)
(g of Liver + g of Water) * refer to 13.1.1 for details.
13.1.3 Calculate actual concentrations of PFOS and other fluorochemicals in calibration standards using the following equation:
pL of Standard x Concentration (LE /mL] = Final Concentration (&g or mg/kg)
mg Liver / 1 mL homogenate*
of PFOS in Liver
*refer to 13.1.2 for details.
14.0 METHODPERFORMANCE 14.1 The method detection limit (MDL) is analyte and matrix specific. Refer to MDL report for
specific MDL and limit of quantitation (LOQ) values (refer to Attachments B and C).
14.2 The following quality control samples are extractedwith each batch of samples to evaluate
the quality of the extraction and analysis.
14.2.1 Method blanks and matrix blanks.
14.2.2 Matrix spike and matrix spike duplicate samples to determine accuracy and . precision of the extraction.
14.2.3 Continuing calibration verification samples to determine the continued accuracy of the initial calibration curve.
14.3 Refer to section 14 of ETS-8-7.0 for method performance criteria.
15.0 POLLUTION PREVENTION AND WASTE MANAGEMENT
15.1 Sample waste is disposed in biohazard containers, flammable solvent waste is disposed in high BTU containers, and used glass pipette waste is disposed in broken glass containers
located in the laboratory.
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16.0 RECORDS
16.1 Complete the extraction worksheet attached to this method, and tape in the study notebook or include in the 3-ring study binder, as appropriate.
17.0 TABLEDS,IAGRAMFSL, OWCHARTASN.D VALIDATION DATA 17.1 Attachment A, Extraction worksheet 17.2 Attachment B, MDWLOQ values and sumniary 17.3 Attachment C, Calibration standard calculation and concentrationworksheet
18.0 REFERENCES 18.1 The validation report associated with this method is ETS-8-6.0 & 7.0-V-1. 18.2 AMDT-EP-22, "Routine Maintenance of Ultra-Turrax T-25" 18.3 FACT-M-1.1, "Extraction of PFOS or Other Anionic Fluorochemical Surfactantsfiom
'
Liver for Analysis Using HPLC-ElectrospraylMassSpectrometry"
19.0 AFFECTEDOCUMENTS
19.1 ETS-8-7.0, "Analysis of Liver Extracts for Fluorochemicalsusing HPLC-Electrospray Mass Spectrometry"
20.0 REVISIONS
Revision Number.
Reason For Revision
Revision
- Date
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Analytical Report: FACT-TOX-001 LRN-U2103
Study # Matrix Box #
way Date Sr>iked/Analvst
. I
ccv
MS ~~ MSD
Surrogate Std approx. pprn actual ppm #
FC Mix Std
FC Mix Std approx. 50 ppm actual ppm #
Comments
I
I
I
I
I
I
I
I
I
I
I
-
I
I
-
- I
-
I
I I
I
I
I
Cont. Cal. Verifications used the same matrix as for the standard curve.
Attachment B: MDL/LOQ Values
3M Environmental Laboratory
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Extraction of PFOS from Liver
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3M Medical Department Study: T6316.1
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Compound
PFOS PFOSA PFOSAA EtF'OSE-OH M556 PFOSEA
MDL (ppb)
8.45 3.50 24.6 108
82.3 33.9
LOQ (ppb)
26.9 11.1 78.3 345 262 108
Linear Calibration Range (LCR)
Approximate concentrations to be used for preparing the Standard Calibration Curve
30 ppb - 1200 ppb
12 ppb - 1200ppb 30 ppb - 1200 ppb
60ppb-900ppb"
60 ppb - 1200 ppb
30 ppb- 1200ppb
MDWLOQ values in rat, bovine, and monkey liver were not statisticallydetermined. Two curves in each of these matrices were extracted and analyzed with the rabbit liver curves to determine equivalence. Responses in the rat, bovine, and monkey liver curves were equivalent to the rabbit responses, therefore, their MDL and LOQ will be assumed to be equivalent to those values as determined for the rabbit liver.
Refer to LOQ Summary and MDL study in ETS-8-6.0 & 7.0-V-1for further information
* EtFOSE-OH estimates only for MDL and LOQ. Did not meet criteria for validation.
Compound: PFOS
ComDound: PFOSA
Rabbit
12- 1200 12- 1200. 12- 300 12- 300 60 - 1200 60 - 1200
Liver matrix
Rabbit
Prepared ' Range of
range of
average
standards
curve
(ppb) (ng/mL) (ppb) (ng/mL)
6.16 - 1232 12 - 1200
L
LCR from ave curve
( P P ~ )(ndmL)
30 - 1200
Range of low std curve
( P P ~ )(ng/mL)
30 - 900
LCR from low std curve
(ppb) W m L )
60 - 900
Range of high std
curve
(ppb) (ndmL)
N/A
LCR from high std
curve
(ppb) (ndmL)
N/A
Attachment B: MDL/LOQ Values 3M Environmental Laboratory
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Page 12 of 16
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Liver matrix
Rabbit
Prepared range of standards
(ppb) (ng/mL)
6.17- 1235
Range of average curve
(ppb) (ng/mL)
31 -900
LCR from ave curve
(Ppb) (ndml-1
31 - 900
Range of low std curve
( P P ~ )(ng/mL)
NIA
LCR from low std curve
( P P ~ ()ng/mL)
NIA
Range of high std
curve
(ppb) (ndmL)
NIA
LCR from high std
curve
(ppb) (ng/mL)
NIA
Liver matrix
Rabbit
Prepared ' Range of
range of
average
standards
curve
(ppb) W m L ) (ppb) (ng/mL)
6.17 - 1235 31 - 1200
LCR from ave curve
(PPW (ng/mL)
31 - 1200
Range of low std CUNe
(PPb) (ng/mL)
N/A
LCR from low std
curve
( P P ~ )W m L )
NIA
Range of high std
curve
(ppb) (ng/mL)
NIA
LCR from high std
curve -
(ppb) (ndmJ-1
NIA
Compound: M556
Attachment C: Standard Calculations
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Ion Pair Standard Curves - Tissue
Prep date(s): Analytets): Sample matrix:
Methodhevision: Target analyte(s): FC mix std approx. 0.500 ppm: FC mix std approx. 5.00 ppm: FC mix std approx. 50.0ppm: Surrogate std approx. 100 ppm:
Standard number: Equipment number: Final solvent and TN: Blank livedidentifier:
Actual concentrations of standards in the FC mix
PFOS PFOSA PFOSAA EtFOSE PFOSEA
Final
Final Final conc Final
Final
I I I I conc
conc
ndg
conc
conc
c onc
I n g k
np/g
ngk
+'* 5- ..9-9. I 5.99 I 5.99 I 5.99 I . n5g.9/9g
5.99
1
12.0 I
-
12.0
I I
12.0
I
1
12.0 1I
12.0 I 12.0 II
29.9
29.9
29.9
29.9
29.9
2!9.9
59.9
59.9
59.9
59.9
59.9
59.9
120
120
120
120
120
120
299
299
299
299
299
299
599
599
599
599
599
599
1 I 1 I I 1 8-9.8- I 898 I 898 9 898
1198
1198
1198
1198
898 1198
898 1198
Surrogate Std conc ng/mL
100
Surrogate Final conc
ng/mL 0.500
All Am't spiked
mL
0.005
Attaclment C: Standard Calculations
3M Environmental Laboratory
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3M ENVIRONMENTALLABORATORY
METHOD
ANALYSIS OF FLUOROCHEMICAINLLSIVER-EXTRACUTSSING
HPLC-ELECTROSPRAYAMSAPSESCTROMETRY
Method Number: FACT-M-2.0
-
Author: Lisa Clemen
Approved By:
Qql'$%- Laboratory Manager
Adoption Date: s / J b198 Revision Date: / d / A
Date
& & A CQMhLk
Technical Reviewer
d 27198
Date
SCOPE AND APPLICATION
13 Scope: This method is for the analysis of extracts of liver or other tissues for fluorochemical
*surfactants using HPLC-electrospray/mass spectrometry.
0
Q Applicable Compounds: Potassium perfluorooctanesulfonate, anionic fluorochemical
a surfactants, or other ionizable compounds. Matrices: Rabbit, rat, bovine, and monkey livers or other livers as designated in the
0validation report.
2.
32
&rd 7.0.1/95
FACT-M-2.0
Page 1 of 8
Analysis of Liver Extract Using ES/MS
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2.0 SUMMARY OF METHOD
2.1 This method describes the analysis of fluorochemicalsurfactants extracted from liver using HPLC-electrospray/mass spectrometry.The analysis is performed by monitoring a single ion characteristic of a particular fluorochemical, such as the potassium perfluorooctanesulfonate(PFOS) anion, M/Z= 499. Samples may also be screened to veri@ compound identification.
3.0 DEFINITIONS 3.1 None.
4.0 WARNINGS AND CAUTIONS 4.1 Health and Safety Warnings:
4.1.1 Use caution with the voltage cable for the probe. When the voltage cable is plugged into the probe DO NOT TOUCH THE PROE$E,there is risk of electrical shock.
4.2 Cautions:
4.2.1 Do not run solvent pumps above capacity of ,400bar (5800 psi). If pressure goes over 400 bar, the HP1100will initiate autom;3ticshutdown.
4.2.2 Do not run solvent pumps to dryness.
5.0 INTERFERENCES
5.1 Teflon should not be used for sample storage or any part of instrumentation that comes in contact with the sample or extract.
6.0 EQUIPMENT 6.1 Equipment listed below may be changed in order to optimize the system.
6.1.1 Micromass Electrospray Mass Spectrometer 6.1.2 HP1100 low pulse solvent pumping system and autosampler.
7.0 SUPPLIES AND MATERIALS 7.1 Supplies
7.1.1 Nitrogen gas, refrigerated liquid, regulated to approximately 100 psi. 7.1.2 HPLC column, specifics to be determined by the analyst. 7.1.3 Capped autovials or capped 15 mL, centrifuge tubes.
8.0 REAGENTSAND STANDARDS 8.1 Reagents
8.1.1 Methanol, HPLC grade or equivalent.
Word 7.0.1/95 3M Environmental Laboratory
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8.1.2 Milli-QTMwater, all water used in this method should be Milli-QTMwater and may be provided by a Milli-Q TOC Plus system.
8.1.3 Ammonium acetate, HPLC grade or equivalrmt.
8.2 Standards
8.2.1 Typically one H,O blank, one liver blank, and seven liver standards are prepared
during the extraction procedure. See FACT-M-1. -
9.0 SAMPLHEANDLING 9.1 Fresh liver standards are prepared with each analysis. Extracted standards and samples are
stored in capped autovials or capped 15 mL centrifuge tubes until analysis.
9.2 If analysis will be delayed, extracted standards and samples may be refrigerated until analysis can be p'erformed.
10.0 QUALITYCONTROL 10.1 Matrix Blanks and Method Blanks
10.1.1 Analyze a method blank and matrix blank prior to each calibration curve.
10.2 Matrix Spikes 10.2.1 Analyze a matrix spike and matrix spike duplicate with each analysis.
10.2.2 Expected concentrationswill fall in the mid-range of the initial calibration curve. Additional spike concentrations may fall in the low-range of the initial calibration curve.
10.2.3 See section 13 to calculate percent recovery. 10.3 Continuing Calibration Checks
10.3.1 Analyze a mid-range calibration standard afber every tenth sample. If a significant change (*30%) in peak area occurs, relative to the initial standard curve, stop the
run.Only those samples analyzed before the last acceptable calibration standard
will be used. The remaining samples must be reanalyzed.
10.3.2 See section 13 to calculate percent difference.
10.4 System Suitability
10.4.1 System suitability (e.g. peak area, retention time and peak shape, etc.) will be assessed for each run.
11.o CALIBRATION AND STANDARDIZATION
11.1 Analyze the extracted liver standards prior to and following each set of extracts. The mean of two standard values, at each standard concentration, will be plotted by linear regression for the calibration curve using MassLynx or other suitable software.
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11.2 The 8value for the data should be 0.98 or greater. Lower values may be acceptable at the
discretion of the analyst.
11.3 If the curve does not meet requirements, perfom routine maintenance or reextract the standard curve (if necessary) and reanalyze.
12.0 PROCEDURES 12.1 Acquisition Sd up
12.1.1 Click on start button in the Acquisition Comrol Panel. Set up a sample list. Assign a filename using letter-MO-DAY-last digit of year-sample number, assign a method (MS) for acquiring, and type in sample descriptions.
12.1.2 To create a method click on scan button in the Acquisition control panel and select SIR. SetJonization Mode as appropriate anti mass to 499 or other appropriate masses. A scan is usually collected along with the SIRS. Save method.
12.1.3 Typically the sample list begins with the first set of liver standards and ends with
the second set of standards.
,
12.1.4 Samples are analyzed with a continuing calibration check injected after every tenth sample. Solvent blanks should be analyzed ]periodicallyto monitor possible analyte
carryover and are not considered samples but may be included as such.
12.2 Using the Autosampler
12.2.1 Set up sample tray according to the sample 1ist prepared in section 12.1.1,
12.2.2 Set-up the HP11OO/autosampler at the followingconditions or at conditions the analyst considers appropriate for optimal response. Record actual conditions in the instrument logbook:
12.2.2.1 Sample size = 10 pL injection with a sample wash
12.2.2.2 Inject/sample = 1
12.2.2.3 Cycle time = 15 minutes
12.2.2.4 Solvent ramp =
Time
2.0 mM
Ammonium acetate
0.00 min.
45%
7.5 min.
90%
10%
11.O min.
90%
11.5 min.
45%
Note: In this instrument configuration, the run must be set up on the electrospray software with a "Waiting for inlet start" message before the "Start" button is pressed on the HP Workstation.
12.2.2.5 Press the "Start" button.
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12.3 Instrument Sep-up
12.3.1 Refer to AMDT-EP-31 for more details.
12.3.2 Check the solvent level in reservoirs and refill1 if necessary.
12.3.3 Check the stainless steel capillary at the end of the probe. Use an eye piece to check the tip. The tip should be flat with no jagged edges. If the tip is found to be unsatishctory, disassemble the probe and replace the stainless steel capillary.
12.3.4 Set HPLC pump to "On". Set the flow to 10 .-500 uL/min or as appropriate. Observe droplets coming out of the tip of the probe. Allow to equilibrate for approximately 10 minutes.
12.3.5 Turn on the nitrogen. A fine mist should be expelled with no nitrogen leaking around the tip of the probe.
12.3.6 The instrknent uses these parameters at the following settings. These settings may change in order to optimize the response:
12.3.6.1 Drying gas 250-400 litershour ' 12.3.6.2 ESI nebulizing gas 10-15 liters/how
12.3.6.3 LC constant flow mode flow rate 10- 500 uL/min 12.3.6.4 Pressure <400 bar (This parameter is not set, it is a guide to ensure the
instrument is operating correctly.)
12.3.7 Carefully guide the probe into the opening. Insert probe until it will not go any M e r . Connect the voltage cables to the probe.
12.3.8 Record tune parameters in the instrument log.
12.3.9 Using the cross-flow counter electrode in the ESMS source is recommended for the analysis of biological matrices.
12.3.10 Click on start button in the Acquisition Control Panel. Press the start button at top of sample list. Ensure start and end sample number includes all samples to be analyzed.
13.0 DATAANALYSIASND CALCULATIONS 13.1 Calculations:
13.1.1 Calculate matrix spike percent recoveries using the following equation:
% Recovery =
Observed Result - Background Result x 100
Expected Result
13.1.2 Calculate percent difference using the following equation:
% Difference = Expected Conc. - Calculated Co- nc. x 100
Expected Conc.
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13.1.3 Calculate actual concentration of PFOS anion in total liver (mg):
ug PFOS anion calc. fiom std curve g of liver used for analysis lo00 ug/ 1 mg
x `Total mass of liver (g)
14.0 METHODPEWORMANCE 14.1 The method detection limit is equal to at least three limes the baseline noise in the matrix
blank.
14.2 The practical quantitation limit is equal to the lowest standard in the calibration curve.
15.0 POLLUTION PREYENTION AND WASTE MANAGEMENT 15.1 Sample waste is disposed in biohazard containers, flammable solvent waste is disposed in
high BTU containers, and glass pipette waste is disposed in broken glass containers. All containers are located in the laboratory.
,
16.0 RECORDS 16.1 Store chromatograms in the study folder. Each chromatogram should have the following
information included either in the header or hand written on the chromatogram: study number, sample name, extraction date, and dilution factor (if applicable).
16.2 Plot calibration curve by linear regression and store in the study folder.
16.3 Print sample list from MassLynx and tape into the instrument runlog.
16.4 Print data integration summary fiom MassLynx and tape into the instrument runlog.
16.5 Copy instrument runlog pages, including instrument parameters and sample results, and tape into appropriate study notebook.
16.6 Summarize data using suitable software and store in the study folder.
16.7 Back up electronic data to appropriate media. Record in study notebook the file name and location of backup electronic data.
17.0 TABLESD,IAGRAMSF,LOWCHARTASN,D VALIDAT1ON DATA 17.1 Attachment A: FACT-M-2 Data reporting spreadsheet 17.2 The validation report associated with this method is FACT-M-1.O& 2.0-V-1.
18.0 REFERENCES 18.1 AMDT-EP-31, "Operation of VG Platform Electrospray Mass Spectrometer"
3M Environmental Laboratory
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19.0 AFFECTEDOCUMENTS
19.1 FACT-M- 1 .O, "Extraction of Potassium Perfluorooctanesulfonate from Liver for Analysis Using HPLC-ElectrosprayNass Spectrometry"
20.0 REVISIONS
Revision Number.
Reason For Revision-
Revision Date
3M Environmental Laboratory
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L
Analytical Report: FACT-TOX-001 LRN-U2103
Laboratory Study #
Study: Test Material:
. MatridFinal Solvent:
MethodRevision: Analytical Equipment System Number: Instrument SoftwareNersion: Filename: R-Squared Value: Slope: Y Intercept: Date of Extractiodhalyst; Date of Analysis/Analyst:
Group Dose
Sample# ,
Concentration ug/mL
- Initial Vol. mL
Dilution Factor
Final Conc. ug/mL
Slope: Taken from linear regression equation.
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3M ENVIRONMENTLAALBORATORY
I
METHOD
ANALYSISOF F'LUOROCHEMICALS IN SERUM EXTFUCTSUSING
HPLC-ELECTROSPRAY/MA!?S SPECTROMETRY
Method Number: FACT-M-4.0 Author: Lisa Clemen
Adoption Date: 91 q 8
Revision Date: NlA
v i App-r.oved
By:
x
-
-
-
_
!d.
Laboratory ManGer
"
Group Leader
dk C L
Technical Reviewer
Date
i Date
Y/l4/98
Date
m
X
f
D
a
I 0, 1.1 Scope: Thismethod is for the analysis of extractsof serum or tissue for fluorochemical
0 surfactantsusing HPLC-electrospray/massspectrometry.
h U
73 1.2 Applicable Compounds: Potassium perfluorooctanedowte, anionicfluorochemical
0 surfactants, or other ionizable compounds. 1.3 Matrices: Rabbit, rat, and bovine serum or other sem as designated in the validation report.
- 3 Word 7.0.1/95 3M Environmental Laboratory
FACT-M-4.0 Analysis of Serum Extract Using ESMS
Page 1 of 8
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Analytical Report: FACT-TOX-001 LRN-U2103
2.0 SUMMARY OF METHOD 2.1 This method describes the analysis of fluorochemical surfactants extracted from serum
using HPLC-electrospray/massspectrometry. The (analysisis performed by monitoring a single ion characteristic of a particular fluorochemiical, such as the potassium perfluorooctanesulfonate (PFOS) anion, M/Z= 499. Samples may also be screened to verifl compound identification.
3.0 DEFINITIONS 3.1 None.
4.0 WARNINGSAND CAUTIONS 4.1 Health and Safety Warnings:
4.1.1 Use caution with the voltage cable for the probe. When the voltage cable is plugged
into the probe DO NOT TOUCH THE PROBE, there is risk of electrical shock.
4.2 Cautions: 4.2.1 Do not run solventpumps above capacity o:F400 bar (5800 psi). If pressure goes over 400 bar, the HP1100 will initiate autornatic shutdown. 4.2.2 Do not run solvent pumps to dryness.
5.0 INTERFERENCES 5.1 Teflon should not be used for sample storage or any part of instrumentation that comes in
contact with the sample or extract.
6.0 EQUIPMENT
6.1 Quipment listed below may be changed in order tcl optimize the system. 6.1.1 Micromass Electrospray Mass Spectrometer 6.1.2 HP1100 low pulse solvent pumping system and autosampler.
7.0 SUPPLIES AND MATERIALS 7.1 Supplies
7.1.1 Nitrogen gas, refiigerated liquid, regulated to approximately 100 psi. 7.1.2 HPLC column, specifics to be determined by the analyst. 7.1.3 Capped autovialsor capped 15mL centrifugetubes.
8.0 REAGENTS AND STANDARDS 8.1 Reagents
8.1.1 Methanol, HPLC grade or equivalent.
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8.1.2 Milli-Qm water, all water used in this method should be Milli-Qm water and may be provided by a Milli-Q TOC Plus system.
8.1.3 Ammonium acetate, HPLC grade or equivsilent.
8.2 Standards
8.2.1 Typically one H20 blank, one serum blank, and seven serum standards are prepared
during the extraction procedure. See FACT-M-3.
9.0 SAMPLEHANDLING
9.1 Fresh serum standards are prepared with each anal;ysis. Extracted standards and samples
are stored in capped autovials or capped 15 mL, centrifuge tubes until analysis.
9.2 If analysis will be delayed, extracted standardsand samplesmay be refrigerated at 4 O C mtil analysis can be performed.
10.0 QUALITY CONTROL 10.1 Matrix Blanks and Method Blanks
10.1.1 Analyze a method blank and a matrix blank prior to each calibration curve.
10.2 Matrixspikes
10.2.1 Analyze a matrix spike and matrix spike dyplicate with each analysis. 10.2.2 Expected concentrations will fall in the mid-range of the initial calibration curve.
Additional spike concentrationsmay fall in the low-range of the initial calibration curve.
10.2.3 See section 13 to calculatepercent recovery.
10.3 Continuing Calibration Checks
(* 10.3.1 Analyze a mid-range calibration standard after every tenth sample. If a significant
change 30%) in peak area occurs, relative to the initial standard curve, stop the
run.Only those samples analyzed before the: last acceptable calibrationstandard will be used. The remaining samples must be reanalyzed.
10.3.2 See section 13 to calculate percent difference.
10.4 System Suitability 10.4.1 System suitability (e.g., peak area, retention time, peak shape, etc.) will be assessed for each run.
11.0 CALIBRATION AND STANDARDIZATION 11.1 Analyze the extracted serum standards prior to and allowing each set of extracts. The
mean of two standard values, at each standard concentration,will be plotted by linear regression for the calibration curve using MassLp: or other suitablesoftware.
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11.2 The 3 value for the data should be 0.98 or greater. Lower values may be acceptable at the discretion of the analyst.
11.3 If the curve does not meet requirements, perform routine maintenance or reextract the standard curve (if necessary) and reanalyze.
12.0 PROCEDURES
12.1 Acquisition Set up
12.1.1 Click on start button in the Acquisition Coritrol Panel. Set up a sample list. Assign a filename using letter-MO-DAY-last digit of year-sample number, assign a method (MS) for acquiring, and type in sample descriptions.
12.1.2 To create a method click on scan button in ithe Acquisition control panel and select SIR (Single Ion Recording). Set Ionization Mode as appropriate and mass to 499 or other appropriate masses. A scan is usually collected along with the SIRS. Save method.
12.1.3 Typically the sample list begins with the first set of serum standards and ends with the second set of standards.
12.1.4 Samples are analyzed with a continuing calibration check injected after every tenth
sample. Solvent blanks should be analyzed periodically to monitor possible and* carryover and are not considered samples biut may be included as such.
12.2 Using the Autosampler
12.2.1 Set up sample tray according to the sample list prepared in section 12.1.1.
12.2.2 Set-up the HPl lOO/autosampler at the followingconditions or at conditionsthe analyst considersappropriatefor optimal response. Record actual conditions in the instrument logbook
12.2.2.1 Sample size = 10 pL injection with a sample wash
12.2.2.2 Inject/sample = 1
12.2.2.3 Cycle time = 15 minutes
12.2.2.4 Solvent ramp =
Z - 7 1 El 11.Omin. I
Ammonium acetate
I
11.5min. I 45% I
55?h
Note: In this instrument configuration, the nm must be set up on the electrospray software with a "Waiting for inlet start7' mesmge before the "Start7' button is pressed on the HP Workstation.
12.2.2.5 Press the "Start" button.
FACT-M-4.0 Analysis of Serum Extract Using ESMS
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12.3 Instrument Set-up
12.3.1 Refer to AMDT-EP-3 1 for more details.
12.3.2 Check the solvent level in reservoirs and refill if necessary.
12.3.3 12.3.4
Check the stainless steel capillary at the end of the probe. Use an eye piece to
check the tip. The tip should be flat with no jagged edges. If the tip is found to be
unsatisfactory, disassemble the probe and replace the stainless steel capillary.
Set HPLC pump to "On". Set the flow to 10 - 500 ul/min or as appropriate.
Observe droplets coming out of the tip of the probe. Allow to equilibrate for approximately 10 minutes.
12.3.5 Turn on the nitrogen. A fine mist should bt: expelled with no nitrogen leaking
around the tip of the probe.
12.3.6 The instrument uses these parameters at the following settings. These settings may change in order to optimizethe response:
12.3.6.1 Drying gas 250-400 literdhour
12.3.6.2 ESI nebulizing gas 10-15 literdhoirr
12.3.63 HPLC constant flow mode flow rate 10 - 500 pL/min
12.3.6.4 Pressure <400 bar (This parameter is not set, it is a guide to ensure the
HPLC is operating correctly.)
12.3.7 Carefully guide the probe into the opening. Insert probe until it will not go any further.Connect the voltage cablesto the probe.
12.3.8 Record tune parameters in the instrument log.
12.3.9 Using the cross-flowcounter electrode in the ESMS source is recommended for the analysis of biological matrices.
12.3.1OClick on start button in the Acquisition Control Panel. Press the start button at top of sample list. Ensure start and end sample number includes all samples to be
analyzed.
13.0 DATAANALYSIASND CALCULATIONS
13.1 Calculations:
13.1.4 Calculate matrix spike percent recoveries using the following equation:
% Recovery = - Observed Result Background Result x 100
Expected Result
13.1.5 Calculate percent difference using the following equation:
YODifference = Emected Conc. - Calcul!atedConc. K 100
Expected Cclnc.
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13.1.6 Calculate actual concentration of PFOS, or other fluorochemical, anion in serum (IZg/mL): pg of PFO calc. from std. Curve x Dilution Factor x Final Volume (mL) Initial Volume of serum (d)
14.0 METHODPERFORMANCE 14.1 The method detection limit is equal to half the lowlest standard in the calibration curve. 14.2 The practical quantitation limit is equal to the lowest standard in the calibration curve.
15.0 POLLUTION PREVENTION AND WASTE MANAGEMENT
15.1 Sample extract waste and flammable solvent is disposed in high BTU containers, and glass
pipette waste is disposed in broken glass container:; located in the laboratory.
16.0 RECORDS 16.1 Store chromatograms in the study folder. Each chromatogram must have the following
information included either in the header or hand unitten on the chromatogram: study number, sample name, extraction date, and dilution factor (if applicable). 16.2 Plot calibration curve by linear regression and ston: in the study folder. 16.3 Print sample list fiom MassLynx and tape into the instrument runlog. 16.4 Print data integration summary fiom MassLynx and tape into the instrument runlog. 16.5 Copy instrument runlog pages, including instrument parameters and sample results, and tape into appropriate study notebook. 16.6 Summarize data using suitable software and store in the study folder. 16.7 Back up electronic data to appropriate medium. Record in study notebook the file name and location of backup electronic data.
17.0 TABLESD,IAGRAMSF,LOWCHARTANSD. VALIDATION DATA 17.1 Attachment A: FACT-M-4 Data reporting spreadsheet 17.2 The validation report associated With this method is FACT-M3.O & 4.0-V-1.
18.0 REFERENCES 18.1 AMDT-EP-3 1 "Operation of VG Platform Electrospray Mass Spectrometer"
19.0 AFFECTEDDOCUMENTS 19.1 FACT-M-3.0, "Extraction of Fluorochemicd Anions from Senun for Analysis Using
HPLC-ElectrosprayMasss Spectrometry"
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20.0 F&ViSIONS
Revision Number.
Reason For Revision
Revision
- Date
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Laboratory Study #
Study: Test Material: Matriflinal Solvent: MethodlRevision: Analytical Equipment System Number: Instrument SoftwareNersion: Filename: R-Squared Value: Slope: Y Intercept: Date of Extraction/Analyst: Date of AnalysidAnalyst:
Group/Dose: Taken from the study folder. Sample#: Taken from the study folder. Concentration (ug/rnL): Taken from the MassLynx integration summary. Initial Volume (rnL): Taken fiom the study folder. Dilution Factor: Taken from the study folder. Final Cone (ug/rnL): Calculated by dividing the initial volume from the concentration
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3M ENVIRONMENTLAALBORATORY
METHOD
ANALYSIS OF POTASSIUM PERFLUOR0OC"ESULFONATE OR OTHER
FLUOROCHEMICAINLSSERUM[EXTRACTUSING HPLC-ELECTROSPRAY/MAS!~ SPECTROMETRY
Method Number: ETS-8-5.1
Author: Lisa Clemen, Robert Wynne Approved By:
Adoption Date: 03/01/99 Revision Date:
~
Laboratory Manager
~~
Date
Group Leader
Date
$flc Technical Reviewer .o SCOPE AND APPLICATION
09/2 h i 7 1
Date
.l Scope: This method describes the analysis of s e m i extracts for fluorochemical surfactants
vD using HPLC-electrospray/mass spectrometry.
21.2 Applicable Compounds:Fluorochernical surfactants or other fluorinated compounds, or
other ionizable compounds.
0
2.1.3 Matrices: Rabbit, rat, bovine, monkey, and human serum, or other fluids as designated in
'2. the validation report.
3
P,
Word 6/95
ETS-8-5.1
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2.0 SUMMARY OF METHOD
2.1 This method describes the analysis of fluorochemical surfactants extracted from serum or other fluids, using HPLC-electrospray/massspectrometry, or similar system as appropriate. The analysis is performed by monitoring a single ion characteristic of a particular fluorochemical, such as the perfluorooctanesulfonate (PFOS) anion, m/z= 499. Additionally, samples may be analyzed using a taridem mass spectrometer to further verify the identity of a compound by detecting daughter ions of the parent ion.
3.0 DEFINITIONS
3.1 Atmospheric Pressure Ionization (API): The Micromass Quattro I1 triple quadrupole
systems allow for various methods of ionization by utilizing various sources, probes, and interfaces. These include but are not limited to: Electrospray Ionization (ESI), Atmospheric Pressure chemical Ionization (APcI), Thermospray, etc. The ionization process in these techniques occurs at atmosphericpressure (i.e., not under a vacuum).
3.2 Electrospray Ionization (ES,ESI): a method of ionizationperformed at atmospheric
pressure, whereby ions in solution are transferred to the gas phase via tiny charged droplets. These charged droplets are produced by the applicatj.onof a strong,electricalfield.
3.3 Mass Spectrometry, Mass Spectrometer (MS), Tandem Mass Spectrometer ( M S / M S ) : The API Quattro 11triple quadrupole systems are equipped with quadrupolemass selective detectors. Ions are selectively discriminatedby mass to charge ratio ( d z ) and subsequently detected. A single MS may be employed for ion detection or a series ( M S M S ) for more specific fi-agmentationinformation.
3.4 Conventional vs. Z-spray probe interface: The latest models of Micromass Quattro II
triple quadrupole systems (post 1998) utilize a "Z-spray" conformation. The spray emitted from a probe is orthogonalto the cone aperture. In the conventionalconformationit is aimed directly at the cone aperture, after passing through a tortuous pathway in the counter . electrode. Though the configurationis different,the methods of operation, cleaning, and maintenance are the same. However, Z-spray components and conventional components are not compatiblewith one another, but only with similar systems (Le., Z-spray components are compatiblewith some other Z-spray systems, etc.)
3.5 Mass Lynx Software: System software designed fclr the specific operation of these Quattro I1triple quadrupole systems. CurrentlyMassLynx has Windows 95 and WindowsNT 4.0 versions. All versions are similar. For more details see the manual specific to the instrument (Micromass Quattro I1 triple quadrupole MassLynx or MassLynx NT User's Guide).
4.0 WARNINGS AND CAUTIONS 4.1 Health and Safety Warnings:
4.1.1 Use caution with the voltage cables for the probe. When engaged, the probe employs a voltage of approximately5000 'Volts.
4.1.2 When handling samples or solventswear appropriateprotective gloves, eyewear, and clothing.
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4.2 Cautions: 4.2.1 Do not operate solvent pumps above capacity of 400 bar (5800 psi) back pressure. If the back pressure exceeds 400 bar, the HP1100 will initiate automatic shutdown,
4.2.2 Do not run solvent pumps to dryness.
5.0 INTERFERENCES 5.1 To minimize interferenceswhen analyzing samplles, teflon should not be used for sample
storage or any part of instrumentationthat comes in contact with the sample or extract.
6.0 EQUIPMENT 6.1 Equipment listed below may be modified in order.to optimize the system. Document any
modifications in the raw data as method deviations.
6.1.1 Micromass Quattro 11triple quadrupole Mass Spectrometerequipped with an
electrospray ionization source
6.1.2 HP 1100 low pulse solvent pumping system, solvent degasser, column
compartment, and autosampler
7.0 SUPPLIES AND MATERIALS 7.1 Supplies
7.1.1 High purity grade nitrogen gas regulated tlo approximately 100psi (House air system)
7.1.2 HPLC analytical column, specificsto be determined by the analyst and documented in the raw data.
7.1.3 Capped autovials or capped 15 mL centrifuge tubes
8.0 REAGENTS AND STANDARDS
8.1 Reagents
8.1.1 Methanol, HPLC grade or equivalent 8.1.2 Milli-QTMwater, all water used in this method should be Milli-QWwater or
equivalent, and may be provided by a Mil1.i-QTOC Plus system or other vendor
8.1.3 Ammonium acetate, reagent grade or equivalent
8.2 Standards 8.2.1 Typically two method blanks, two matrix blanks, and eighteen matrix standards are prepared during the extraction procedure. See ETS-8-4.1.
9.0 SAMPLEHANDLING 9.1 Fresh matrix standards are prepared with each analysis. Extracted standards and samples
are stored in capped autovials or capped 15 mL cmtrifuge tubes until analysis.
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9.2 If analysis will be delayed, extracted standards and samples can be refrigerated at . approximately 4" C, or at room temperature, until analysis can be performed.
10.0 QUALITY CONTROL
10.1 Solvent Blanks, Method Blanks and Matrix Blranks
10.1.1 Solvent blanks, method blanks and matrix blanks are prepared and analyzed with each batch to determine contamination or carryover.
10.1.2 Analyze a method blank and a matrix blank prior to each calibration curve.
10.2 Matrix Spikes
10.2.1 Matrix spikes are prepared and analyzed to determine the matrix effect on the recovery efficiency.
10.2.2 Matrix spike duplicates are prepared and analyzed to measure the precision and the recovery for each analyte.
10.2.3 Analyze a matrix spike and matrix spike duplicate per forty samples, with a minimum of 2 spikes per batch.
10.2.4 Matrix spike and matrix spike duplicate concentrationswill fall in the mid-range of the initial calibration curve. Additional spike concentrationsmay fall in the lowrange of the initial calibration curve.
10.3 Continuing Calibration Verifications
10.3.1 Continuing calibration verifications are analyzed to veri@ the continued accuracy of the calibration curve.
10.3.2 Analyze a mid-range calibration standard after every tenth sample, with a minimum of one per batch.
11.0 CALIBRATION AND STANDARDIZATION
11.1 Analyze the extracted matrix standards prior to and following each set of extracts. The
average of two standard curves will be plotted by linear regression (y = my + b), weighted
l/x, not forced through zero, using MassLynx or other suitable software.
11.2 If the curve does not meet requirements, perform routine maintenance or reextract the standard curve (if necessary) and reanalyze.
11.3 For purposes of accuracy when quantitating low levels of analyte, it may be necessary to use the low end of the calibration curve rather than the full range of the standard curve. Example: when attempting to quantitate approximately 10 ppb of analyte, generate a calibration curve consisting of the standards from 5 ppb to 100 ppb rather than the full range of the curve (5 ppb to 1000ppb). This will reduce inaccuracy attributed to linear regression weighting of high concentrationstandards.
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12.0 PROCEDURES
12.1 Acquisition Set up
12.1.1 Click on start button in the Acquisition Control Panel. Set up a sample list, Assign a filename using MO-DAY-last digit of year-sample number, assign a method (MS) for acquiring, and type in sample descriptions.
12.1.2 To create a method click on scan button in the Acquisition control panel and select SIR (Single Ion Recording) or MRM. Set Ionization Mode as appropriate and mass to 499 or other appropriatemasses. A full scan is usually collected along with the SIRS. Save acquisition method. If MSMS instruments are employed, additional product ion fiagmentation information ma.1 be collected. See Micromass
MassLynx GUIDE TO DATA ACQUISITION for additional information and
MRM (Multiple Reaction Monitoring).
Time
0.00 min. 8.50 min.
11.Omin.
12.0 min.
Ammonium acetate
60%
90%
10%
90%
10%
40%
60%
12.2.2.5 Press the "Start" button. 12.3 Instrument Set-up
12.3.1 Refer to ETS-9-24.0 for more details. 12.3.2 Check the solvent level in reservoirs and refill if necessary.
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12.3.3 Check the stainless steel capillary at the end of the probe. Use an eyepiece to check the tip. The tip should be flat with no jagged edges. If the tip is found to be unsatisfactory, disassemble the probe and replace the stainless steel capillary.
12.3.4 Set HPLC pump to "On". Set the flowto :LO - 500 uL/min or as appropriate.
Observe droplets coming out of the tip of the probe. Allow to equilibrate for approximately 10 minutes.
12.3.5 Turn on the nitrogen. A fine mist should he expelled with no nitrogen leaking
around the tip of the probe. Readjust the tip of the probe if no mist is observed.
12.3.6 The instrument uses these parameters at thie following settings. These settings may change in order to optimize the response:
12.3.6.1 Drying gas 250-400 litershour 12.3.6.2 ESI nebulizing gas 10-15 litershur
12.3.6.3 HPLC constant flow mode, flow rate 10- 500 pL/min
12.3.6.4 Pressure <400 bar (This parameter is not set, it is a guide to ensure the HPLC is operating correctly.)
12.3.7 Carefully guide the probe into the opening. Insert probe until it will not go any further. Connect the voltage cables to the probe.
12.3.8 Print the tune page, with its parameters, arid store it in the study binder with a copy taped into the instrument log.
12.3.9 Using the cross-flow counter electrodein the ESMS source is recommended for the analysis of biological matrices.
12.3.10Click on start button in the Acquisition Control Panel (this may vary among MassLynx versions, see appropriate MasslLynx USER`S GUIDE). Press the start button. Ensure start and end sample number includes all samples to be analyzed.
13.0 DATAANALYSIASND CALCULATIONS 13.1 Calculations:
13.1.4 Calculate matrix spike percent recoveries using the following equation:
% Recovery =
Observed Result - Backaound Result x 100
Expected Result
13.1.5 Calculate percent difference using the following equation:
% Difference = ExDected Conc. - Calculated Conc. x 100
Expected Conc.
13.1.6
Calculate actual concentration of PFOS, or other fluorochemical,in matrix (pg/mL):
Inn of PFOS calc. from std. Curve x Dilution Factor) x 1 c1q (Initial Volume of matrix (mL) + mL of Surrogate Standard) 1000 ng
Final Volume (mL)
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14.0 METHODPERFORMANCE 14.1 Method Detection Limit (MDL) and Limit of Quantitation (LOQ) are method, analyte, and
matrix specific. Please see ETS-8-4.1, Attachment B, for a listing of current validated MDL and LOQ values.
14.2 Solvent Blanks, Method Blanks, and Matrix Bkanks
14.2.1 Solvent blanks, method blanks, and matrix blanks values are must be below the lowest standard in the calibration curve
14.3 Calibration Curves
14.3.1 The I? value for the calibration curve must be 0.980 or better.
14.4 Matrix Spikes
14.4.1 Matrix spike percent recoveries are must be within k 30% of the spiked concentration.
14.5 Continuing Calibration Verifications
14.5.1 Continuing calibration verification percent recoveries must be k 30% of the spiked concentration.
14.6 If criteria listed in this method performance section isn't met, maintenance may be performed on the system and samples reanalyzed or other actions as determined by the analyst. Document all actions in the appropriate logbook.
14.7 If data are to be reported when performance criteria have not been met, the data must be footnoted on tables and discussed in the text of the report.
15.0 POLLUTION PREVENTION AND WASTE MANAGEMENT 15.1 Sample extract waste and flammable solvent is disposed in high BTU containers, and glass
pipette waste is disposed in broken glass containers located in the laboratory.
16.0 RECORDS
16.1 Each page generated for a study must have the following information included either in the header or hand written on the page: study or project number, acquisitionmethod, integrationmethod, sample name, extraction date, dilution factor (if applicable), and analyst.
16.2 Print the tune page, sample list, and acquisition method from MassLynx to include in the appropriate study folder. Copy these pages and tape into the instrument runlog.
16.3 Plot the calibration curve by linear regression, weighted l/x, ihen print these graphs and store in the study folder.
16.4 Print data integration summary, integration method, and chromatograms, from MassLynx, and store in the study folder.
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16.5 Summarize data using suitable software (Excel 5.0) and store in the study folder, see Attachment A for an example of a summary spreadsheet.
16.6 Back up electronic data to appropriate medium. Record in study notebook the file name and location of backup electronic data.
17.0 TABLESD,IAGRAMSF,LOWCHARTASN,D VALIDATION DATA 17.1 Attachment A: ETS-8-5.1 Data summary spreadsheet.
18.0 REFERENCES
18.1 FACT-M-4.1,"Extraction of Potassium Perfluoroloctanesulfonateor Other Fluorochemical
compounds from Serum for Analysis Using HPLC-ElectrospraylhlassSpectrometry
18.2 ETS-9-24.0, "Operation and Maintenance of the Micromass Atmospheric Pressure Ionization/Mass Spectrometer Quattro I1 triple q~iidrupoleSystems"
18.3 The validation report associated with this method is ETS-8-4.0 & 5.0-V-1.
19.0 AFFECTEDOCUMENTS
19.1 ETS-8-4.1,"Extraction of Potassium Perfluorooctatnesulfonate or Other Fluorochemical
Compounds from Serum for Analysis Using HPLC-ElectrosprayMass Spectrometry"
20.0 REVISIONS
Revision Number.
1
Reason For Revision
Section 6.1.2 Clarification of HP1100 system components. Section 11.1 Average of two curves, not standard values, are used for plotting linear regression and added the l/x weighting of the curve. Section 12.2.2.4 Clarification of solvent ramp. Section 17.1 Changed from attachment B to A.
Revision 04/02/99
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Laboratory Study #
Study: Test Material: Matriflinal Solvent: MethodRevision: Analytical EquipmentSystemNumber: Instrument SoftwareNersion: Filename: R-Squared Value: Slope:
Y Intercept:
Date of ExtractiodAnalyst: Date of Analysis/Analyst:
Group Dose
Sample#
Concentration ug/d
Initial Vol. mL
Dilution Factor
Final Conc. ug/mL
Slope: Taken from linear regression equation.
Attachment A: Summary Spreadsheet
ETS-8-5.1
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3M ENVIRONMENTLAALBORATORY
METHOD
ANALYSIS OF POTASSIUM PERF'LUOROOCTANESU14FONATEOR OTHER
FLUOROCHEMICINALLISVER EXTRACTUSSING HPLC-ELECTROSPRAYMSAPSESCTROMETRY
Method Number: ETS-8-7.0 Author: Lisa Clemen, Glenn Langenburg
Adoption Date: 0?/2.zl T f
Revision Date: Nfi
Approved By:
Group Leader
C\-PPNR LA.
Technical Reviewer
I
Date
3 / 14/33
Date
Date
I
3oL J
1.1
Scope: This method is for the analysis of mLC-electrospray/mass spectrometry.
liver
extracts
for
fluorochemical
surfactants
using
Applicable Compounds:Fluorochemical surfactants or other fluorinated compounds, or
other ionizable compounds.
Matrices: Rabbit, rat, bovine, monkey liver, or other tissues as designated in the validation report.
Word 6/95
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2.0 SUMMAROYF METHOD
2.1 This method describes the analysis of fluorochemicalsurfactants extracted from liver using HPLC-electrospray/massspectrometry, or similar system as appropriate. The analysis is performed by monitoring a single ion characteristic of a particular fluorochemical, such as the perfluorooctanesulfonate(PFOS) anion, m/z =: 499. Additionally, samples may be analyzed using a tandem mass spectrometer to further verify the identity of a compound by detecting daughter ions of the selected parent ion.
3.0 DEFINITIONS
3.1 Atmospheric Pressure Ionization (MI): The Micromass Quattro IItriple quadrupole
systems allow for various methods of ionization by utilizing various sources, probes, and interfaces. These include but are not limited to: Electrospray Ionization (ESI), Atmospheric Pressure chemical Ionization (APcI), Thermospray, etc. The ionization process in these techniques occurs at atmosphericpressure (Le. not under a vacuum).
3.2 Electrospray Ionization (ES, ESI): a method of ioilization performed at atmospheric pressure, whereby ions in solution are transferred to the gas phase via tiny charged droplets. These charged droplets are produced by the application of a strong electrical field.
3.3 Mass Spectrometry,Mass Spectrometer (MS), Tandem Mass Spectrometer (MSMS): The MI Quattro I1triple quadrupolemass spectrometer is equipped with two quadrupole mass selective detectors and a collision cell. Ions are selectively discriminated by mass to charge ratio ( d z ) and subsequentlydetected. A single MS may be employed for ion detection or an ion may be selected in the first quadrupole, fragmented in the collision cell, and these fragments may be analyzed in the second quadrupole.
3.4 Conventional vs. Z-spray probe interface: The latest models of Micromass Quattro I1 triple quadrupole (post 1998)utilize a "Z-spray" conformation. The spray emitted from a probe is orthogonal to the cone aperture. In the conventionalconformationit is aimed directly at the cone aperture, after passing through a tortuous pathway in the counter electrode. Though the configuration is different, the methods of operation, cleaning, and maintenance are the same. However, Z-spray Components and conventional components are not compatible with one another, but only with similar systems (Le. Z-spray components are compatible with other Z-spray systems, etc.)
3.5 Mass Lynx Software: System software designed for the specific operation of these Quattro 11triple quadrupole systems. Currently MassLynx has Windows 95 and WindowsNT 4.0 versions. All versions are similar. For more details refer to the manual specific to the instrument (Micromass Quattro I1 triple quadrupole MassLynx or MassLynx NT User's Guide).
4.0 WARNINGS AND CAUTIONS 4.1 Health and Safety Warnings:
4.1.1 Use caution with the voltage cables for the probe. When engaged, the probe employs a voltage of approximately 5000 `Volts.
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4.1.2 When handling samples or solvents wear appropriate protective gloves, eyewear, and clothing.
4.2 Cautions:
4.2.1 Operate the solvent pumps below a back pressure of 400 bar (5800 psi). If the back pressure exceeds 400 bar, the HPllOO will initiate automatic shutdown.
4.2.2 Do not run solvent pumps to dryness.
5.0 INTERFERENCES
5.1 To minimize interferences when analyzing samp1cs, Teflon shall not be used for sample storage or any part of instrumentationthat comes in contact with the sample or extract.
6.0 EOUIPMENT
6.1 Equipment listed below may be modified in order to optimize the system. Document any modifications in the raw data as method deviations.
6.1.1 Micromass Quattro II triple quadrupole Mass Spectrometer equipped with an
electrospray ionization source.
6.1.2 HP1100 low pulse solvent pumping systern, solvent degasser, column compartment, and autosampler
7.0 SUPPLIES AND MATERIALS
7.1 Supplies 7.1.1 High purity grade air regulated to approximately 100psi (house air system) 7.1.2 HPLC analytical column, specifics to be determined by the analyst and documented in the raw data
7.1.3 Capped autovials or capped 15 ml centrifuge tubes
8.0 REAGENTASND STANDARDS 8.1 Reagents
8.1.1 Methanol, HPLC grade or equivalent
8.1.2 Milli-QTMwater (ASTM type I), all water used in this method should be ATSM type I, or equivalent, and be provided by it Milli-Q TOC Plus system or other
vendor
8.1.3 Ammonium acetate, reagent grade or equivalent
8.1.3.1 When preparing different amounts than those listed, adjust accordingly.
8.1.3.2
2.0 mM ammonium acetate solutjon: Weigh approximately 0.300 g ammonium acetate. Pour into a 2000 mL volumetric container containing 2000 mL Milli-QTMwater, mix until all solids are dissolved. Store at room temperature.
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8.2 Standards
8.2.1 Typically two method blanks, two matrix blanks, and eighteen matrix standards are prepared during the extraction procedure. Refer to ETS-8-6.0.
9.0 SAMPLHEANDLING 9.1 Fresh matrix standards are prepared with each analysis. Extracted standards and samples
are stored in capped autovials or capped 15 ml centrifuge tubes until analysis.
9.2 If analysis will be delayed, extracted standards arid samples may be stored at room temperature, or refiigerated at approximately4' C, until analysis can be performed.
10.0 OUALITYCONTROL
10.1 Method Blanks and Matrix Blanks
10.1.1 Solvent blanks, method blanks, and matrix blanks are prepared and analyzed with each batch to determine contamination or carryover.
10.1.2 Analyze a method blank and a matrix blank prior to each calibration curve.
10.2 Matrix Spikes
10.2.1 Matrix spikes are prepared and analyzed to determine the matrix effect on the recovery efficiency.
10.2.2 Matrix spike duplicates are prepared and analyzed to measure the precision and the recovery for each analyte.
10.2.3 Analyze a matrix spike and matrix spike d!uplicateper forty samplep. With a minimum of 2 spikes per batch.
10.2.4 Matrix spike and matrix spike duplicate concentrationswill fall in the mid-range of the initial calibration curve. Additional spike concentrations may fall in the low-
range of the initial calibration curve.
10.3 Continuing Calibration Checks
10.3.1 Continuing calibration verifications are analyzed to veri@ the continued accuracy of the calibration curve.
10.3.2 Analyze a mid-range calibration standard every tenth sample, with a minimum of one per batch.
11.0 CALIBRATION AND STANDARDIZATION 11.1 Analyze the extracted matrix standards prior to arid following each set of sample extracts.
The average of two standard curves will be plotted by linear regression (y = mx -t- b), weighted l/x, not forced through the origin, using MassLynx or other suitable software.
11.2 If the curve does not meet requirements perform routine maintenance or reextract the standard curve (if necessary) and reanalyze.
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11.3 For purposes of accuracy when quantitating low kvels of analyte, it may be necessary to use the low end of the calibration curve rather than the full range of the standard curve. Example: when attempting to quantitate approxirnately 10 ppb of analyte, generate a calibration curve consisting of the standards from 5 ppb to 100ppb rather than the full range of the curve (5 ppb to 1000ppb). This will reduce inaccuracy attributedto linear regression weighting of high concentration standards.
12.0 PROCEDURES
12.1 Acquisition Set up
12.1.1 Set up the sample list.
12.1.1.1 Assign a sample list filename using MO-DAY-last digit of year-increasing letter of the alphabet starting with a
12.1.1.2 Assign a method ( M S file) for acquiring 12.1.1.3 Assign an HPLC program (Inlet iile) 12.1.1.4 Type in sample descriptions and vial position numbers
12.1.2 To create a method click on method in the Acquisition control panel then mass spectrometer headings and select SIR (Single Ion Recording) or MRM (Multiple Reaction Monitoring). Set Ionization Mode as appropriate and mass to 499 or other appropriate masses. A full scan is usually collected along with the SIRS. Save acquisition method. If MSMS instruments are employed, additional product ion fragmentation information may be collected. Refer to Micromass MassLynx GUIDE TO DATA ACQUISITION for additional information and MFW.
12.1.3 Typically the analytical batch run sequencle begins and ends with a set of extracted matrix standards.
12.1.4 Samples are analyzed with a continuing calibration verification injected standard after every tenth sample. Solvent blanks should be analyzed periodically to monitor possible analyte carryover and are not considered samples but may be included as such.
12.2 Using the Autosampler
12.2.1 Set up sample tray according to the sample: list prepared in Section 12.1.1.
12.2.2 Set-up the HPllOO/autosampler at the following conditions or at conditions the analyst considers appropriate for optimal response. Record actual conditions in the instrument logbook:
12.2.2.1 Sample size = 10 pL injection
12.2.2.2 InjecVsample = 1
12.2.2.3 Cycle time = 9 minutes
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12.2.2.4 Solvent ramp conditions
I
0.00min. I 40%
1.0 min. I 40% I
4.5min. I 95%
7.0 min.
40%
9.0 mi.
40%
I Ammoniumacetate I
1
60Yn
1
1 I
60%
1
I
I
5%
60%
12.2.2.5 Press the "Start" button.
12.3 Instrument Set-up
12.3.1 Refer to ETS-9-24.0, "Operation and Maintenance of the Micromass Quattro I1 Triple Quadrupole Mass SpectrometerFitted with an Atmospheric Pressure Ionization Source," for more details.
12.3.2 Check the solvent level in reservoirs and rafill if necessary.
12.3.3 Check the stainless steel capillary at the end of the probe. Use an eyepiece to check the tip. The tip should be flat with no jagged edges. If the tip is found to be unsatisfactory, disassemble the probe and replace the stainless steel capillary.
12.3.4 Turn on the nitrogen.
12.3.5 Open the tune page. Clicks on operate to initiate source block and desolvation heaters.
12.3.6 Open the Inlet Editor.
12.3.6.1 Set HPLC pump to "On"
12.3.6.2 Set the flow to 10 - 500 uL/min or as appropriate
12.3.6.3 Observe droplets coming out of the tip of the probe. A fine mist should be expelled with no nitrogen leaking around the tip of the probe. Readjust the tip of the probe if no mist is o`bserved
12.3.6.4 Allow to equilibrate for approximately 10 minutes.
12.3.7 The instrument uses these parameters at the following settings. These settings may change in order to optimize the response:
12.3.7.1 Drying gas 250-400 litershour 12.3.7.2 ESI nebulizing gas 10-15 litershour 12.3.7.3 HPLC constant flow mode flow rate 10- 500 pL/min 12.3.7.4 Pressure <400 bar (This parameter is not set, it is a guide to ensure the
HPLC is operating correctly.)
12.3.7.5 Source block temperature 150'
12.3.7.6 Desolvation temperature 250"
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12.3.8 Print the tune page, with its parameters, and store it in the study binder with a copy taped into the instrument log.
12.3.9 Click on start button in the Acquisition Control Panel (this may vary among MassLynx versions, refer to appropriate RlassLynx User's Guide). Ensure start and end sample number includes all samples to be analyzed.
13.0 DATAANALYSIASND CALCULATIONS 13.1 Calculations:
13.1.4 Calculate matrix spike percent recoveries using the following equation:
% Recovery =
Observed Result - Backmourtd Result x 100
Expected Result
13.1.5 Calculate percent difference using the following equation:
% Difference = Expected Conc. - Calculated Conc. x 100
Expected Conc.
13.1.6 Calculate actual concentrations in matrix (pg/g):
(ncz of PFOS calc. from std. Curve x Dilution Factor) (Initial Weight of'Liver (a) Final Volume (mL)
x 1 up,
1000 ng
14.0 METHODPERFORMANCE 14.1 Method Detection Limit (MDL) and Limit of Quatntitation (LOQ) are method, analyte, and
matrix specific. Refer to ETS-8-6.0, Attachment B for a listing of current validated MDL and LOQ values.
. 14.2 Solvent Blanks, Method Blanks and Matrix Blanks
14.2.1 Solvent blanks, method blanks, and matrix blanks must be below the lowest standard in the calibration curve.
14.3 Calibration Curves
14.3.1 The 3 value for the calibration must be 0.980 or better.
14.4 Matrix Spikes
14.4.1 Matrix spike percent recoveries must be within rt 30% of the spiked concentration.
14.5 Continuing Calibration Verification
14.5.1 Continuing calibration verificationpercent recoveries must be within 1- 30% of the spiked concentration.
14.6 If criteria listed in the method performance section are not met, maintenance may be performed on the system and samples reanalyzed or other actions as determined by the analyst. Document all actions in the appropriate logbook.
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14.7 If data are to be reported when performance criteria have not been met, the data must be footnoted on tables and discussed in the text of the report.
15.0 POLLUTION PREVENTION AND WASTE MANAGEMENT 15.1 Sample extract waste and flammable solvent is disposed in high BTU containers, and glass
pipette waste is disposed in broken glass containers located in the laboratory.
16.0 RECORDS 16.1 Each page generated for a study must have the following information included either in the
header or hand Written on the page: study or project number, acquisition method, integration method, sample name, extraction date, dilution factor (if applicable), and analyst. 16.2 Print the tune page, sample list, and acquisition method from MassLynx to include in the appropriate study folder. Copy these pages and tape into the instrument runlog.
16.3 Plot the calibration curve by linear regression, weighted l/x, then print these graphs and store in the study folder.
16.4 Print data integration summary, integration method, and chromatograms from MassLynx and store in the study folder.
16.5 Summarize data using suitable s o h a r e (Excel 5.0+) and store in the study folder, refer to Attachment A for an example of a summary spreadsheet.
16.6 Back up electronic data to appropriatemedium. Fkecord in study notebook the file name and location of backup electronic data.
17.0 TABLESD, IAGRAMFS,LOWCHARATNSD, VALIDATION DATA 17.1 Attachment A: ETS-8-7.0 Data summary spreadsheet
18.0.REFERENCES 18.1 FACT-M-2.1, "Extraction of Potassium Perfluorooctanesulfonateor Other Fluorochemical
Compounds from Liver for Analysis Using HPLC!-Electrospr;iy/Mass Spectrometry"
18.2 ETS-9-24.0, "Operation and Maintenance of the Micromass Atmospheric Pressure IonizationMass SpectrometerQuattro I1triple quadrupole Systems"
18.3 The validation report associated with this method is ETS-8-6.0 & 7.0-V-1
19.0 AFFECTED DOCUMENTS 19.1 ETS-8-6.0, "Extraction of Potassium Perfluorooctanesulfonateor Other Fluorochemical
Compounds from Liver or Fluid for Analysis Using HPLC-Electrosprayblass Spectrometry"
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20.0 REVISIONS Revision Number
Analytical Report: FACT-TOX-001 LRN-U2103
Reason For Revi!;ion
Revision
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Laboratory Study #
Study: Test Material: Matrix/Final Solvent: MethodIRevisi on: Analytical Equipment System Number: Instrument SoftwareNersion: Filename: R-Squared Value: Slope:
Y Intercept:
Date of ExtractiodAnalyst: ' Date of AnalysislAnalyst:
Group Dose
Sample#
Concentration Wg
lnitiai wt.
g
Uilution Factor
Final Conc.
wk
Attachment A: Sunlmary Spreadsheet
ETS-8-7.0
3M Environmental Laboratory
Analysis of Liver Extract Using ES/MS
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Appendix D: Data Summary Tables
Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
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..
h
d
0
E
LL
b
3
3
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1
A
Analytical Report: FACT-TOX-001 LRN-U2103
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Table 12. FACT TOX-001 Data Summary of PFOSAA Concentration-Serum (pg/mL)
Analytical Report: FACT-TOX-001 LRN-U2103
b L W m i tof Quantitation= 0.0248p@mL ' L W m i t of Quantitation= 0.00493p@mL
dLOQ--Limit of Quantitatjon= 0.0097 *AnimalC91216Fsamplewas lost duringextraction.
NOTE: Results are expressed as grwp/genderaverages *the standaddeviation associatedwith that grcup/gender.
NOTE: The only measurementof accuracyawilableatthis time, matrixspike studies, indicatethatthe sera and liver data canbe consideredaccurateto within one standarddeviationof the average
fortifiedsamples recovery.The averagefortifiedsamplerecoverywas 109%with a standarddeviationof 23%.
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Analytical Report: FACT-TOX-001 LRN-U2103
Table 13. FACT TOX-001 Data Summary of EtFOSE-OHConcentration-Serum (pg/mL)
a Not correctedfor purityof the standardmaterial. bLOQ--Limitof Quantitation= 0.00977pgmL CLOC+Limit of Quantitation= 0.0248 pgmL dLO(tlimit of Quantitation= 0.00493ugmL `Animal C91216F sample was lost during extraction.
NOTE: Resultsare expressed as grouplgenderaveragesfthe standard dm'ationassociated with that group'gender.
NOTE: The resultsof qualiiycontrolanabes (curvefit, CCVs, and MSiMSDs) for EtFOSE-OHwere inconsistentand indicatethat datapresentedshouldbe consideredto be qualitativeonly. Values are presentedinthis data table inthe spiritof full disclosure,butshouldnotbe usedinanyquantitativeassessmentof the data.
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Table 14. FACT TOX-001 Data Summary of M556 Concentration-Serum (pg/mL)
Analytical Report: FACT-TOX-001 LRN-U2103
Male
I
I
I
I
I
I
Week 14a week 2 7
Male
Female I
Male (<nL=O1C0Ib)
II 1I Week53"
Male Female
Male
<LOCIC (n = 15)
<LOQC (n=15)
In = 14)
Female
<LOQC (n = 13)
0.680f 0.667 (n = 11)"
3.02 i 1.08 (n = 15)
5.06 f 1.39 (n = 19)
<LO@ (n = 12)
a Not correctedfor puntyof the standardmaterial. bLOQ--Limitof Quantitation= 0.0248 p g h L 'LOQ-Limit of Quantitation= 0.00494pglrnL 'Animal C91216F sample lost during extraction.
NOTE: Resultsare eqxessed as group/gender averages*the standarddeviation associatedv4th that group/gender. NOTE: The miy measurementof accuracyavailaMe at this time, matrixspike studies. indicatethat the sem and l i i r data can beconsideredaccumteto withinm e standardhiationof the aemge fortified samples m.The
a e m ~ f w t i f i e dsample~BCO\RTYwas 123%with a standarddeviationof 20%.
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Analytical Report: FACT TOX-001 LRN-U2103
Table 15. FACT TOX-001 Data Summary of PFOSEA Concentration-Serum , + g h
Analytical Report: FACT-TOX-001 LRN-U2103
b L W m i tof Quantitation= 0.0247 pg'mL "LOQ-4imit of Quantitation= 0.W92 pdmL d L W m i tof Quantitation= 0.00975ps/mL ' L O W m i t of Quantitation= 0.04% pg'mL 'Animal C91216F sample lost during exhaction.
NOTE: Resub areexpressedasgroupgenderaverages ithestandardd a t i o n associatedwith that group/gendet.
NOTE: The resultsof qualitycontrolanalyses(CUMfit, CCVs, and IVSMSDs) for PFOSEAwere inconsistentand indicatethat data presentedfor this anatyte shouldbe consideredto be qualitatie only. Values are presentedhereinthe spirit of full disclosure,but shouldnotbe usedinanyquantitativeassessmentof the data.
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Analytical Report: FACT TOX-001 LRN-U2103
Table 16. FACT TOX-001 Data Summary of PFOS Concentration-Liver (pg/g)
Analytical Report: FACT-TOX-001 LRN-U2103
Male Week 8"
2.13i0.668 (n = 5)
1067 f 197 (n = 5)
Week 27
I
Week53
Male Male
I
0.571 f 0.175
(n = 5)
Week 105
ivide Female
I 0.143io.133 I ?.56*7.!c! I 90.j *?C.3 1
(n = 18)
(n = 22)
(n = 22)
I
I
I
0.178f 0.111
38.5f 21.9
127 i 68.5
(n = 14)
(n = 13)
(n = 15)
695 f 189 (n = 5)
313 i 22G
I
(n = 17)
297 f 171 (n = 19)
I 2.05 f 3.36 (n = 10)
7.69f 7.62 (n = 12)
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Analytical Report: FACT TOX-001 LRN-U2103
Table 17. FACT TOX-001 Data Summary of PFOSA Concentration-Liver (pg/g)
Timepoint
Sex
Group 1 Control Average &D
Group 2 Low
Average t S D
Group 3 Mid
Average &D
Group 4 Mid-High Average &D
Analytical Report: FACT-TOX-001 LRN-U2103
Group 5 High
Average &D
Group 6 Mid-High Recovery
Average SD
Week 8"
Male
0.0313 i 0.00163
(n = 5)
0.0310i 0.00189
19.2 f 0.987' (n = 5)
I Female
(n = 5)
I 1 I 1.80*0.0831 (n = 5)
7.98k1.03 (n = 5)
14.6 f 1.52 (n = 5)
I
Male
week27
I
I
I
I
I
I
I
Week53" I
Male Female
0.0182 i u.0100
(n = 5)
(n = 5) I
28.2 i 8.44
(n = 5)
(n = 5)
I
bLOQ-Limitof Quantitatim= 0.0123 pg'g 'LOQ-Limit of Quantitation= 0.00614pg'g 'Animal C90748M sample lost during extraction. %CVs failed, data enteredas estimated.
NOTE Results are expressedas group/genderaveragesithe standard deviationassociated with that group/gender.
NOTE: The only measurementof accuracyavailableatthis time, matrixspike studies,indicatethat the sera andliver datacanbeconsideredaccurateto withinone standarddeviationof the average fortifiedsamples recovery.The averagefortifiedsamplerecoverywas 102%with a standarddeviationof 17%(revisedresults).
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Analytical Report: FACT TOX-001 LRN-U2103
Table 18. FACT TOX-001 Data Summary of PFOSAA Concentration-Liver (pg/g)
Analytical Report: FACT-TOX-001 LRN-U2103
C L O W m i tof Quantitation= 0 0123 p$g 'Animal C90748M lost during exlraction.
NOTE:Resultsare expressed as grWp/gender averagesfthe standarddeviationassociatedwiththat group/gender.
NOTE: The onb measurementof accuracyawilableat this time, rnatnxspke studies, indicatethat the sera and lwrdata can be msidered accurateto wlthinone standarddewation of the awragefottlfied samples m r y The awragefortdied sample remery was 105% wlth a standalddevlatim of 19%(msed resuks)
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Analytical Report: FACT TOX-001 LRN-U2103
Analytical Report: FACT-TOX-001 LRN-U2103
Table 19. FACT TOX-001 Data Summary of EtFOSE-OHConcentration-Liver (pglg)
1 1 1 1 Timepoint
Sex
Group 1 Control Average tSD
Group 2 Low
Average *SD
Group 3 Mid
Average +SD
Group 4 Mid-High
Average S D
II II week4"
Male Female
;Lmnb=5) (n = 5)
Group 5 High
Average A D
Group 6
* Mid-High Recovery Average SD
bLOQ--Limit of Quantitation = 0.0596 pg'g ' L W m i t of Quantitation= 0.119pg'g dLOQ-Limit of Quantitation = 0.0298 pg'g
'LOQ--Limit of Quantitation= 0.0614 pg'g
NA-Not applicable NR-Not reported 'Animal C91216F sample lost during earaction.
NOTE: Results areeqxessed as group/gender%rages *the standard deviationassociatedwith that grcup/gender.
NOTEThe resultsof qualitycontrol analyses (cumfit, CCVs, and fvWvtSDs)for EtFOSE-OHwere inconsistentand indicatethat data presentedfor this analyteshouldbe consideredto be qualitative only. Values are presentedhereinthe spiritof fulldisclosure, but should not be usedin anyquantitativeassessmentof the data.
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Analytical Report: FACT TOX-001 LRN-U2103
Table 20. FACT TOX-001 Data Summary of M556 Concentration-Liver (pg/g)
Analytical Report: FACT-TOX-001 LRN-U2103
Weeksa
I
week 10sa
Male Female Male Female
<LOQ~ (n =5)
<LOCIb
(n = 51
I
pt,Sb,e
i V . W 2 V.JI 0 I
9.5i f 3 . B I
(n = 18)
(n=22)
(n = 22)
<Lab$
(n = 14)
2.03f 2.74 (n = 13)
8.57f 3.33 (n = 15)
58.9f 17.0 (n = 5)
36.3 f 9.51 (n = 5)
27.1 f 9.41 (n = 17)
28.5f 8.86 (n = 19)
<LOQC,d
(n = 10)
<LO@* (n = 12)
a Not corrected for purityof the standard material. b L w C i r n i tnf ~uzr?!i~ti=wP! . P ~
cLOQ-Limit of Quantitation= 0.00615ps/s dLOQ-Lirnitof Quantitation= 0.123 pg'g 'LOQ-Lirnit of Quantitation= 0.0123 ps/s ' L W m i t of Quantitation= 0.0615 pg'g
NOTE Resultsare expressed as grouplgender ayerages f the standard deviation associatedwiththat group/gender.
NOTE: The mlymeasurementof accuracyavailableat his time, matrixspikestudies,indicatethat the sera and lmrdata canbe msideredaccurate to within m e standarddeviationof the awrap fortified samples recwry. The awragefortifiedsample recoverywas 102%with a standardMatim of 15%.
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Analytical Report: FACT TOX-001 LRN-U2103
Analytical Report: FACT-TOX-001 LRN-U2103
Timepoint
week4 Week8 Week 14
Group 1
Group 2
Group 3
Group 4
Group 5
Sex
Control
Low
Mid
Mid-High
High
Average &D Average tSD Average tSD
Average +SD
Average tSD
Male
I
I
I
I
I
Group 6
Mid-High Recovery Average t SD
Male
I
I
I
I
I
J
Male
I
I
I
1
a Not correctedfor purityof the standardmaterial
bLOQ--Limitof Quantitation= 0.0307ps/s
"LOQ-Limit of Quantitation= 0.0613 ps/s
NOTE: Results are expressed as grwp/aenderm m ~ ethe stmdzc!devk??sasswigedvv%iWit giiX@@iid~i. NOTE: The resultsof qualitycontrolanalyses(curvefit,CCVs, andlvWMSDs)for PFOSEAwere inconsistentandindicatethat data presentedforthis analyteshouldbe consideredto be qualitatieonly.
Values are presentedhereinthe spiritof full disclosure,butshouldnotbe used inanyquantitatk assessmentof the data.
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Appendix E: Data Spreadsheets
Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
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AMDT# 092597.1 Covance# 6329-212
St"@ product N w n k Q e r t Subslance)
Sample Data I'EEK4 RAT SER
Group Dose
REWORK Snmplr x
Group 2 Low Dore 3 0 mgng
Group 3 Mid Dose 30 0 mgnig
H20 Elk-! H 2 0 Elk-2 Rat Serum Blk-l Rat SenunBlk-2 MS 4/23/98 MSD 4123198 MS 4128198 MSD 4/28/98
C90719M C90732M C90725M C90753M C90775M C91135F CY1 143F C91165F CY1169F C91171F C90789M C90814M C90817M C90833M C90834M C91198F C91205F C91222F C9123OF C91237F C90846M C90853M C90866M
/.-"".., C90890M
b,"Y,III.
C91251F C91272F C91285F C91287F C91291F C9093SM C90939M
Group 5
C91333F C9134SF C91350F C90984M CYIWSM CYlOZ4M C91033.M C91037M C91423F C91427F C91430F C91443F
C.alld*F
104 Week Dietary Carcinogenicity Sludy with N m w Range (98 1%) N-E?h)lPerfluorwctanerulfonamldoEthanol m Rats
T-6316 (EIFOSEOH)
Rat Serum
FACTM-3 0 & FACT-MM4 0 reuorkrd u m g ETS-8-5 I
Filenames
Chick 080697 and Madelme 041098
PFOS
MassL- 2 3 & 3 I
BLS
13042780243 & 59-60
See llsllng 10 Ule "ghl See Attachments See Attachments See Attachments 04123198,041281Y0 RWW
04127198,04128198,04/30198,05105198
KIWHOJ
crpl crpz crp3 crp4
Grp 5
R04278 13-24 R05058 12-23 RO505826-37 R05058M-51 R0428813-24
09'01'W, 12101'W, 12/04'W, 12!05'W M M H W H
412311938 MS,MSD
R0427856-57
ErtTnctIon Val. mL
I I I I I I I I I I I I I I
- PFOS Std
- COWHtiO" FXIW
0 9275 0 9275
~
0 9275
0 9275
~
NA
- - NA NA NA
0 9275
0 9275 0 9275 0 9275
- 0 9275 0 9275
Lot215
PFOSPurity Comerdon
Fanor unknown Unknown unknown unknown
NA NA NA NA Unknown UnknOUn Unknown unknoxn unknown unknown
412811938 MS, MSD
PFOS Dilution Fsrtar
1 1 I 1 I I I I
1 1 I 1 1 1
PFOS Canr. nc,ImL
OW 0680 OW 248 240 233
161 457 263 325 263 80 I 534 120
rnk"mn
R0427802 R0427859 R0427803 R04278M u.n~427856 R0427857 RO505852 R0505853 R04278 I3 RIM27814 R0427815 R0427816 R0427817 R0427820
Cancmlmthln Of PFOS
ugh& or *h RH
<LoQ(0 0231 u g i d ) 4LoQ (00231 u g i d )
CLOQ (00231 u g l d ) <LOQ (00231 ug/mL)
96% 93% 65% 183%
0 0244 0 0302 0 0244 0 0743 0 0495 0 111
RO505852-53 MIS" PFOS U@mL CLOQ LoQ 95% 124%
0 OM5
1
0 9275
Unknown
I
114 R0427821
0 106
1
0 9275
Unknown
I
135 R0427822
- 1
0 9275
Unknown
1
133 R0427823
1
0 9275
UnknOWn
I
127 R0427824
I
0 9275
Unknown
50
3 2 5 R0505812
0 126 0 123 0117
I51
0.117
I
0 9275
Unknown
SO
18 5 R0505813
I 78
I
0 9275
Unknown
SO
4 1 3 RO505814
I91
I
0 9275
Unknown
SO
476 R0505815
221
- I
0 9275
I
0 9275
R0505816
I87
186
R0505819
3 01
I
0 9275
R0505820
3 63
I
0 9275
Unknowo
RO505821
2 65
I
0 9275
UnknOWIl
74 7 RO505822
3 47
1
0 9275
UnknoUn
76 4 R0505823
3 54
3 26
- I
0 9275
Unknown
250
8 4 0 R0505826
195
I
0 9275
unknown
250
102 R0505827
23 6
I
0 9275
unknown
250
9 9 5 R0505828
231
I
0 9275
Linknow
250
8 4 2 RO505829
195
- 1, 2 5227:
?.I'"III?
22 <
I
0 9275
ROSOS833
27 6
I
0 9275
R0505834
33 7
I
0 9275
R0505835
24 3
- 1
0 9275
1
0 9275
1
0 9275
I
0 9275
I
0 9275
I
0 9275
unknoun
- I
0 9275
I
0 9275
R0505836
31 9
R0505837
32 0
299
IR0505840
51 5
R0505841
65 4
R0505842
536
RO505843
R0505844
R0505847
I
0 9275
Unknaxn
R0505848
1
0 9275
LlnknOwn
R0505849
- 1
0 9275
Llnlowwn
500
200 ROSOSSSO
I
0 9275
Llnknoun
SW
ROSOS8Sl
I
0 9275
Unknown
SW
404 R0427827
I
0 9275
Unknown
1000
294 R0428814
273
I
0 9275
unknown
Iwo
293 R0428815
272
I I
0 9275
rnknown
500
R0427830
223
- I
0 9275
Unknown
5W
406 R042783I
188
1
0 9275
Unknown
IOW
330 R0428820
306
I
229
I
0 9275
UnlOlDwn
1WO
R0428821
270
I
0 9275
llnloloun
IWO
417 R0428822
387
I
I
- 0 9275 0 9275
Unknown L'nknonn
1000
451 R0428823
loo0
435 R0428824
419 403
357
Sample quantitaledoutoflinearrange olcune
Date Enleremy Dale VenBedlBy Punty EnteredlVenBed
12/061W KIH lZiM1W HOJ i0413O~Ol LAC
12127100 LAC
PFOS 04/27/98 Lot 215 04128198 Lot 215 05105198 Lo1 215
PFOSA R042780263, R043080344 R04278 13-24 R04308 14-25 RO430828-39 RO430842-53 RO42784147.52-53 R04278 150-51 R042785657 RO430856-57
RSD Sld DCV. MYMSD RPD
NA
NA
3%
96%
53 0 00215
7 10 0 W828
136 0 252
12 7 0415
PFOSA 04127198 Lo1 L-2353 04130198 Lot L-2353
PFOSAA R042780243BSYM R04278 13-24 R05058 12-23 RO505826-37 R0505840-51 RO427827-38
R042785657 RO505852-53
Lot L-2353 PFOSA Purity
Camrrlian FsnW UnknOW
unknown UnknOWn unknown
NA NA NA NA UnknoWl LlnknOwn unknown UnknOUn
L'nknOWn unknown unknown UnknOHn unknoxn unknown LhknOwn L'nknOWl UnknoWll unknown unknown 1lnknOwn unknown LlnknOWll UnknOWn Unknown UnknOUn Unknown unknown
PFOSAA 04/27/98 Lot 617 05105198 Lot 617
Dilull~ns 111, 11. Ill 111, 111, Ill 1150. 1/10, 1/50 11250, 1/50. I1250 IISW, IilW. IISW 1/1ooo, 115, 115W IISW Ill,111, I l l
111, Ill. I l l
PFOSA Dilution Fnomr
I 1 I I I I I 1 1 1 1 I I I I I I I IO 10 10 10 10 10 10
10 10 10 50 50 50
UnknOwn
50
UnknOUn
50
UnknOW
50
12 8
UnknOXn
50
3 84
UnknOWl
50
I : 1 1 ImnknOUll
100
UnknOUn
IW
ClnknOwn
unknown
Unknown
IW
cnkn0,m
IN
unlmown unknown
.
IW 100
unknown
IW
unknown
100
UnknOW
5
UnknOUn
5
I unknown
5
18 6
I
Unknoun
I
5
I
42 5
UnknOWll
5
unknown
5
Llnknoun
500
LlnknOwn
Sno
18 3
L1nkn"Wll
5
65 2
UnknOUn
5
PFOS = Pernuo-mesulfo~tonate
PFOSA = Pernuo-tanesulio-Ide
PFOSAA = P e r n u O m O C t a n e S u l f D n d ~ ~ ~ ~ t a l ~
Corrected PFOS LOQ (0 0249 uglmL) to include rtd comcllon Caclorr newLOQiroO23l ugimL LACO2119~01
Analytical Report: FACT-TOX-001 LRN-U2103
PFOSA COM. n@mL
0 00 0 W 0 W OW 243 228 295 283
0.W 006 000 059
0 31 0 35 0 83 0 64 0 37 021
255 268 297 389 3 39 5 39 656
732 526 657 140
Filmsme
R0427802 R0430803 R0427803 R0430804 R0427856 R0427857 R0430856 R0430857 R0427813 Rob27814 R0427815 ROC27816 R0427817 R0427820 R0427821 R0427822 R0427823 R0427824 R0430814 ~043n815 R0430816 R0430817 R0430818 R0430821 R0430822
ROO430823 R0430824 R0430825 R0430828
Conrrnbmtian of PFOSA
u@mLor Y. Rce <LoQ (0.00249 u g i d )
<LOQ <LoQ (0 W249 ugimL)
<Log 97%
91% 118% 113%
<LoQ (0.W249 ugimL) <LoQ(OW249uglmL) <LCQ(OW249ughL)
<LoQ(OW249ugimL)
cLOQ (OW249ug/mL) <LCQ (0 W249 u # d ) cLOQ (0 W249 ugimL) CLOQ (0 00249 u g i d ) <log(0 W249 ugimL) <LCQ (0 W249 ugimL)
0 0255
n 0268
0 0297 0 0389 0 03390 0 0539 0 0656
0 0732 0 0526 0 0657 0701 0 668 0611
::4 I 1 I 2sY
no430835
344
IC0430836
123
R0430837
270
R0430838
278
R0430839
192
R0430842
126
R0430843
R0430844
R0430845
I 29 I 72 0614 I35 I39 I 92
I26 I29 242
?I7
R0430846
2 17
234
R0430849
2 34
300
R0430850
3W
266
R0430851
266
223
Rob30852
2 23
218
R0430853
2 18
208
R0427841
I 04
266
R0427842
133
I I 208
R0427843
I 04
267
R0427844
I34
239
R0427845
I20
476
R0427849
2 38
6%
R0427835
3 48
126
R0427836
6 29
382
R0427852
I 91
233
R0427853
117
FSD S l d DLV. MYMSD RPD
NA NA 6% 4%
NA NA
NA NA
17 7 0 WS49
14 I 0 00874
I1 7
: "I!$
0 147
65 6 2W
3M EnEExTcvSe-l8i9-r57Ionmental Laboratory
Sen Week 4 Rework TOXM)I -sen-?12- I I AI XIS
Page 199
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
SMy.
104 Week DEW Cmmogemcay study wth N m w Range (98 1%) N-Ethyl P c r f l u o m l m e s u l f o n d ouhanal m &IS
Pmduct NumkrCTcst Substance)
1-6316 (MFOSEQH)
Rat Sem
FACT-M-3 0 & FACT-M-4 0 reworked usmg FTS-8-5 I
Chick080697and Madeline 041098
MarrLwZ3& 3 I
See listing to the nght
See Amchmenls
See Attafhmenlr
See Amchmenls
04/23198,04128198 RWW
04127198,04/28198,04/30/98,05105/98 KJHMOJ
09101~W.12iOliW, 12'041W. I2iO5/00 M M W H
Sample Data
WEEK4 RAT SERA
I GTOUI)
I
DOSC
REWORK
Ssmpbx
Lo1617
Correction Factor
unknown
NA NA
Dilution I
PFOSAA
C0"C.
n&Id OW OW OW OW 271 252 143 466 13 7
- Filename
- - R0427802
R0427803 Ro4278M)
- R0427856
- R0505852
R04278 13
ConrrnlrltlOn afPFOSM
u & I der % RIC :LoQ (0 W256 ugimL) :I@ (0 W256 nglmL) :LoQ (0 W256 uglmL) 'LOQ (0 00256 ugimL)
108% 101%
57% 186% 00137
- MI."
- P F O S M
UYd
<toQ
3
- 104%
- 122%
CO"!ml
C90732M
43 2
R0427814
0 0432
0 0 mgkg
C90725M
37 7
R0427815
0.0377
C90753M
unknown
82 4
R0427816
00824
- 78 7
R0427817
449
<04279820
00787 0 0449
- O O S l l
C91143F
85 7
<04279821
00857
C91165F
54 4
COO4279822
0 OS44
Group 2
C91169F C91171F C90789M
UnknoW
57.2
COO4279823
59 7
31 1
RO505812
0 0572 0 0597
I55
- 0 0604
C90814M
42 7
RO505813
2 13
3 0 m@g
C908IN
32 I
R0505814
I60
C90833M
109
RO505815
5 46
45 0
R0505816
2 25
I12
R0505819
5 61
- 2 6 0
C91205F
49 3
R0505820
2 47
C91222F
54 2
R0505821
2 71
C91230F CW846M
- 37 9
R0505822
190
53 9
R0505823
9 7r'
56 4
R0505826
- 3 07
45.8
R0505827
I1 4
45 3
R0505828
11 3
- 49 5
R0505829
12 4
57 2
?.%"%E
!f?
73 9
KO505833
I8 5
- !3 2
139
R0505834
34 9
C91285F
54 4
R0505835
13 6
C91287F
- 74 3
R0505836
I8 6
121
R0505837
30 2
446
RO505840
22 3
- 33 I
448
R0505841
22 4
39 0
R0505842
195
85 3
R0505843
42 6
- 55 5
RO505844
27 8
47 5
W505847
23 8
- 26 9
C913IR
604
R0505848
30 2
C91333F
640
R0505849
32 0
C91345F
- 115
R0505850
57 3
51 5
RO50585I
25 8
I23
R0427827
61 3
- 33 8
Rgh Dare
C91W5M
137
R0427828
68 4
3W m g k g
I C91024M C91033M
151
R0427829
75 6
126
R0427830
63 I
- 75 8
R0427831
37 9
175
R0427834
87 5
- 61 2
C91427F
168
R0427835
83 9
C91430F
1%
R0427836
978
C91443F C91448F
271 115
- R0427837
R0427838
136 57 6
- 92 5
* Sample quaniltaredout o f imar range of c u m
RSD Sld. Dlv. MYMSD RPD
NA NA 7% 106%
56 8 0 0291
25 2 00152
627 I 63
47 3
174 2 3:
38 7 8 95
34 5 9 28
401 13 6
23 2 14 2
30 6 % 1
Date Enternmy Dale VenfieediBy Punty EnterndNenfied
12106!wKJH 121061W HOJiOU30/01 LAC 12127100 LAC
Corrected PFOS LCQ (0 0249 ugimL) UJ lncludcstd cometion facton neu'LOQa00231 ugimL LAC02119101
3M EEEnTxScve-lSi9-7r5Ionmental Laboratory
Analytical Report: FACT-TOX-001 LRN-U2103
Page 200
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Slvdy Pmduct Numbeflest Substance) Mamx MeUlodiRe\alon Analylical Equipment System Numkr Instrument SoRWareNenK," Filename R-Sqquared Value Slope Y-intercept. D a m of E~mctloniAnalpt Dales of Analysis/Analyst Dale of Data Reductiodhlyst
Sample Data E E K 4 RAT S E R A R E W O R K
MethodBlk
Qc-250 ppb
Group 1 C0"UOl 0 0 mgng
Group 2 Low Dore 30m a g
Group 3 Mid Dose 30 0 mgkg
Group 4 Mid-High Dose
100 m a g
GrrJYP 5 High Dose 300 mgkg
Rat Serum Blk-2 MS 4/23/pJ MSD 4/23/98 MS 4/28/98 MSD 4/28/98
C90719M C90732M
C90725M C90753M C90775M C91135F C91143F C91165F C91169F C91171F C90789M CW814M C90817M C90833M C90834M C91198F C912OSF C91222F C9123OF C91237F
C90846M
1 C90853M C90866M C90890M CrnZ?!?.! C91251F C91272F C91285F C91287F C91291F
C90935M C90939M C90942M C90%1M
cm%m
I C91316F C91317F C91333F C91345F C91350F C90984M C91005M
I C91024M C91033M C91037M C91423F C91427F C91430F C91443F C91448F
104 Week D E W Can;mogcrucltyShldy with N m w Range (98 I,% N-Et)hyl P e r f l u o m m e s u l f o mE~thanol m Rats T-6316 (UFOSEOH) Rat S e m FACT'-M-3 0 & FACT-M4 0 reworked using mS-8-5I Chick080697and Madcline 041098 MarrLynr 2 3 & 3 I
See attachment^ See Attachments See Attachments See Attachments 04/23/98,04128198 RWW 04127i98,n41~8198,0413019085,105198 KJWHOI
n901100, iziniiw, I ~ W W1, 2 m t m MMWH
concrntntion Of PFOS
uYmL or *h Rcc
..
ctoQ (0 0231 u&L)
<LoQ
96%
93%
95%
65% 183%
* 124%
0 0244
0 0302
0 0244
0 0743
0 0495
0 123
0 117
I51
I78
I91
2 21
I87
3 01
3 63
2 65
3 47
3 54
19 5
1 i!236 23 I I9 5 22 < 27 6
65 4
53 6
72 8
I 58 4
I
58 6
' 797
I 972189
50 5
188
273
272
I
223
188
306
270
387
419
403
0117
I86
3 26
1 2! 5 299
604
I I 70 7
I
229
357
RSD Sld Div.
00215
n 252
- !
128 3 84 I4 5 88
CO"CC"trsti0"
of PFOSA
97% 91% 118%
~ L C Q(n 00249 ugimL)
cLOQ (000249 ugimL)
<LCQ(OW249ugimL) < L o p (0 00249 ugimL) <LOQ (0 00249 ugimL) <toQ(0 00249 ugimL)
CLOQ (0 00249 UgimL)
0 0255
0 0268 0 0297 0 0389
o 03390
0 0539
00656
0 0732 00526
o 0657
0 668
0611
1 K4 !
0 680 "132
I
I 29
I39
I92
I26
I 2 42 2 17 2 34
MIXll PFOSA
UYmL
RSD Sld Dtv. MYMSD RPD
'toQ
NA
<LOQ
NA
94%
6%
116%
4%
NA
<toQ
NA
NA
<LoQ
NA
00310
17.7 0 02549
0 0622
14 1 0 00874
15?$
I1 7
"$!$
31 7
I27
n 404
28 7
I81
0 520
13.8
2 48
0 344
I 04
18 6
I34
I2 3
42 5
I 20
119
0 147
2 38
3 48
6 29
I8 3
I91
65 6
65 2
I17
304
200
FOS = Perflu
Conrrntrntion af PFOSAA
vYmL or % Rce lIX2(0 00256 ugimL) LOQ (0 00256 ugimL)
(0 00256 ugiml.) LOQ (0 00256 ugimL)
108% 101%
57% 186YO
001372 n 0432 0 0377 0 0824 0 0787 0 0449 0 0857 0 0544 0 0572 0 0597
I55 2 13 IM 546 2 25 5 61 2 47 2 71 190 2 70 14 I 11 4 II 3 12 4 :SI I8 5 34 9 13 6 18 6 30 2
22.3 22 4 I9 5 42 6 27 8 23 8 30 2 ' 320 57 3 25 8
61 3 68 4 75 6 63 I 37 9 87 5 83 9 97 8 136 57 6
Analytical Report: FACT-TOX-001 LRN-U2103
- MIX" - PFOSAA
WmL
<LoQ
RSD MYSMldSDDIRVP. D
NA
CtOQ
NA
- I 04%
- I 22%
7,"
106%
- O O S l l
56 8 00291
- 0 0604
25 2 0.0152
62 7
- 2 M
I63
- 47 3
3 07
I45
- :3 3
- 23 I
38 7 90
34 5
- 26 9
93
- 33 8
401 13 6
23 2
- 61 2
I4 2
- 92 5
30 6 28 3
Dale EnInteredIBy Date VenfieUBy Punt) Entere&Venlied
12'06100 KJH l2ION00 HOJ! 04'30,Ol LAC 12127r00 LAC
Comcled PFOS LCQ (0 0249 ugjmL) Io include itd c ~ n e ~ t mfanston n e w ~ ~ e n o :u3g ~i m ~L A C O ~ ~ I ~ O I
3M EnEETxcvSe-l8i9-5r7Ionmental Laboratory
Sera Week 4 Reu'oh TOX-001 -rera-2 12-11AI XIS
533 liP2MaI ge 201
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Study Roduct Number(Ten Subrtancc) MauiX MethodiRnisioo Analytical Equipment System Number: h m c n t SaflwueNersion Filename R-Squarrd Value: slope. Y-Intercept: Date of ExuactioniAnalyst. Date of AnalyririAnalyrt Dale of Data R e d ~ c t i o n l h d y s t Sample Data
WEEK 8 RAT SERA REWORK
104Week Dietary Cueinageniciry Study with ~ a m Rwmgc (98 1%) T-6316 (ElFOSEqH)
Rat s m
FACT-MJ 0 & FACT-M-4 0 rcworked using ETS-8-5.1 Madeline 041098
M a r a L w 2 3 & 3. I See lining to the "&I See Atllchmmtr
See Attachmans See AtWchmenCI 05/11/98,05/14/98 RWWiOK 05/13/98, 05114198 HOJiKJWLAWJJ
04/10/W0.1/03/01 CSWMMH
N-Ethyl Pefluomoctmcmlfonamido
Ethanol in Rats
Lo1215
Filnumes
Bllu Grp 1 Grp 5
MS, MSD
pms
05114198 LO1215
PFOSA 05114198 Lot L-2353
Analytical Report: FACT-TOX-001
PFOSAA 05/14/98 Lo1617
LRN-U2103
PFOS RO5149802-03 & 8 6 8 7
RO5149812-23 RO5 149826-37
PFOSA R0514980263 & 8687
R05149812-23 R05149854-65
PFOSAA RO5149802-03 & 86-87
R05 149812-23 RO5 149840.5 I
Dilotianr
111. 111, Ill lISW0, 1/15. l/SW
ROS 149883-84
R05149883-84
RO5 149883-84
111. I l l . 111
Lot L-2353
Conrcntration of PFOSA
MIZll PFOSA
EL: I I i I 0.0mwkg ~~
C90717M C90718M C90737M
C90756M
I
C90769M
I
C91126F
I
C91140F
I
C91145F
I
C91162F
I
C91163F
I
croap 5
C90971M
I
_ _ High Dose
C90972M
I
3Wmgike.
C90988M
I
C90996M
I
C91017M
C91393F I
C91394F
I
I I
I
C914MF
I
C91415F
I
C91438F
I
Tentative results, CCVs did not meel criteria LAC 01/08/01
Date EnarcdiBy.
05/24/00. 01/08/01 CSWLAC
Date Verified/ By
12/28/00 HOJ / 01/08/01 KJH /04/30/01
Purity EnteredNcrified. 12127IW LAC
09275
i;::09275
0,9275 09275 09275 0.9275 09275 09275 09275 09275 09275 09275 09275 09275 09275 0.9275 09275 09275
LAC
Corrected PFOS LOQ (0.00976 ugimL) lo include n d correctionfactom new LOQ is 0 00905 ugimL LAC 02/19/01
I I Unlmown Uhwn Unknown
Unlmown Unknown Ubwn Unknown Unlmown
Unknown Unlmown Unlmown Unlmown Unknown
I Unlmown I
UnLnown Unlmown Unlmown Unlmown
i I :;: I I 369 R05149812
RO5 149813
R05149814
I
871 R05149815
I
495 R05149816
I
1% R05149819
I
183 R05149820
I
176 R05149821
I
225 R05149822
I
194
R05149823
5000
736 R05149826
5000
671 R05149827
5000
736 R05149828
5000
705 R05149829
5000
903 R05149830
5000 I 120 I R05149833 I
5000
I21 R05149834
5000
114 R05149835
5000
130 R05149836
5000
136 R05149837
0 0342 0.M82 OM95 0.0809 0 0459 0.182 0 170 0.163 0 209 0.180
341 311 341 327 419
557 559 530 603 63 I
103X
I I
I 1 unknown Unknown Unknown
I ::E I <LOQ (0.101069%78 UgimL)
110%
R05 L498L2
R05149813 <LOQ (0 00978 ugimL)
6.12
R05149814 <LOQ (0.00978 ugimL)
33 5
UnlmOWn
I
5.91
RO51498I5 <LOQ (000978 ugimL)
00518
0.0174
unknown
I
0.00
R05149816
UnlmOWlI
I
6.49
R05149819 <LOQ (0.W78 ugimL)
UhOW
I
6.47
R05149820 <LOQ (0.00978 UgimL)
UnloloWa
I
5.92
R05149821 <LOQ (0.00978 ug/mL)
9 60
UhW
I
6.W
R05149822 cLOQ (0 00978 ugimL)
0 181
0 0174
UDknOWn
1
6.12
R05149823
UhOW
15
76.7
R05149854
U"ln0Wa
I5
70.4
R05149855
UnlmOW
I5
41 8
R05149856
II 9
UlIkXlOWn
15
88 5
R05149857
348
41 5
LJ"knOw0
I5
88 4
R05149858
I
I
I
unlmown
I
I5
I
51 5
I R05149861
U"knOW0
I5
113
R05149862
0.773 I 69
UnlmOWn
I5
58.8
RO5149863
0.882
6.96
unlmown
I5
55 4
R05149864
0 830
576
40 I
unknown
I5
80.2
R05149865
1.20
PFOS = Peduomactanemlfonatc
PFOSA = Perfluorooctancsulfonamide PFOSAA = Perfluomoctanesulfonamidoacctate
ETS-8-5 I
3M EEnxcveli9r7 onmental Laboratory
S a a Week 8 Rework TOX-01-ren-212-1 IAI XIS
Page 202
3M Medical Department Study: T6316.1
RSD Std. De". MYMSD RPD
Study: Roduct Numba(Tcst Substance)
Matrix
McthodiRcvirion Analytical Equipment System Number I m m e n t SoRwveNcrrion Filename. R-Squared Value
Slope.
Y-lnl~epl: Date of E x u a e l i o d h l y a :
Date of Analysir/Andyst. Dale of Data ReducUodAoalyst-
Sample Data
WEEK 8 RAT SERA REWORK
ClOltp Dolt
Sample #
HZO Blk-1
AMDT# 092597.1 Covance# 6329-212
I04 Week Dietary Carcinogeoiciry SNdy with Narrow Range (98 1%) N-Ethyl PcrfluorwclmesulfonamidoEulvlol in Rats T4316 (EtFOSEaH) Rat Senun FACT-M-3 0 & FACT-M-4.0 reworkedusing ETS-8-5 I Madeline 041098 MassLynx 2 3 B 3. I See listing to thc right See Auaehments See Attachments See Anaehments 05111198.05/1498 RWWIOK 05/13/98, 05114198 HOJIKIWLADIJJ W10100,01103101 CSWMMH
Analytical Report: FACT-TOX-001 LRN-U2103
Lot 617
PFOSAA Pu"ty
PFOSAA
PFOSAA
Correction
Dilrlio.
Corn.
FldW Unh0wn
Fador
n#mL
I
I
I
Filensmr
Concentration of PFOSAA
m@mLor % R s
Meall PFOSAA
m6/nL
RSD
Std. DN.
MYMSD RPD I
NA
Rat Sown Blk-2
Unhown
I
000
R05149887 <LOQ(OOl00ug/mL) **
<LOQ
QC-75 ppb
MS 511 1198
NA
I
76 9
R05149883
103%
**
12%
MSD5111198
NA
1
78 3
R05149884
104'4
**
103%
CrooD 1
CW717M
Unlmown
I
186
R05149812
<
L
O
O.1,O
O
I
W
udm I
L) I
CanVOl
CW718M
Ullhwn
I
24 3
RO5149813
0.0243
0 0 mg/Lg
cw737M
Unloloun
I
17 9
R05149814 ELCQ (0.0100 u&L)
NA
C90756M
UIlhOWn
I
304
R05149815
0.0304
NA
C90769M
U"lm0W
I
24 2
R05149816 E L C Q (0.0100 u&L)
00169
C91126F
U"h0Wn
I
30 2
R05149819
0.0302
C91140F
U"h0W
I
55 2
R05149820
0.0552
C91145F
U"h0Wn
I
38.1
R05149821
0.0381
NA
C91162F
UllbOwn
I
43 4
R05149822
0 0434
NA
C91163F
U"h0W
I
49 5
R05149823
0.0495
0 0433
croup 5
C90971M
UnhoWU
500
I51
R05149840
75 3
High Dose
CW72M
U"hW
500
165
R05149841
82 3
300 mgikg
C90988M
U"bW
500
103
R05149842
51.6
26.2
C90996M
Unlm0Wn
500
126
R05149843
63 2
0 288
C91017M
U"bW
500
125
R05149844
62 3
67.0
C91393F
UllhOW
500
212
R05149847
106
C91194F
UnhlOW
500
130
R05149848
648
C91404F
U"h0W
500
157
R05149849
78.7
35 4
C91415F
UIIlmoW
500
158
R05149850
79 I
0381
C91438F
U"h0W
500
152
R05149851
75.9
80 9
** Tenlalive results,CCVr did not meet criteria LAC 01/08/01
NA 2%
57 5 0 00974
22.5 0.00973
17.9 12.0
18.8 15.3
ETS-8-5 I
3M EEnxcvel 9i7ronmental Laboratory
Sera Week 8 Rework TOX-WJI-sera-212-1IAl xlr
Page 5131/2001 203
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Study.
I 0 4 Week Dietary Clrcinogcnicily Study with Nmow Range (98 1%) N-Elhyl Pefluomlmerulfonunido Ethawl in Rals
Product Nwnbm(Test Substance)
T-6316 (ElFOSEaH)
Matrix. MethdRwision.
Rat Serum FACT-M-3 0 & F A C T - M ~0 reworked using ETS-8-5 I
Analy6ical Equipment System Number
Madeline 041098
l m m e n t SoRwvcNenion
MasrLynx 2 3 & 3. I
Filename.
See Auachmcnls
R-Squared Value
See Attachmenls
slope.
See Attachmenls
Y-htoccpt
See Atfachmenls
Date of ExtractiodAnalyrt
05111198.05114198 RWWIOK
Date of AnalysiriAnaly~.
05113198, 05114198 HOJIKIWLADIJJ
Date of Data ReductioniAnalyst:
04110100. 01103101 CSWMMH
Samole Data
iEEK 8 RAT SER
Gr0.p
DO%
tEwoRK Sample I
Method BIk M a k x Blk
H20 BIk-1 HZO BIk-2 Rat S- BIk-1 Rat Senun Blk-2
Concentration of PFOS
mdmL or % Rec <LOQ (0 m 5 ugiml)
4LCQ (0 00905 u mi) <LOQ (0 W905 ugiml)
<LOQ (0 m 5 u&l) **
cLOQ
RSD
I Coneratrntion I M a n I
Std. De,.
01 PFOSA
PFOSA
MYMSD RID
mI/mL o r % Rw
.I/nL
<LOQ ( 0 00978 ug m L j
UA
<LOQ1ocQ978ugmL1
cLOQ
cLOQtO 00978 u g m L )
NA
<LOQ (0 00978 UvmL)
<LOQ
RSD Sld D n MYMSD RPD
NA
NA
QC-75 ppb
MS 5111198 MSD5111198
104%
125%
'8
115%
18%
103%
Group 1
C90717M
0 0342
<LOQ (0101069%78 ugimL)
lI(p/o
12%
COnUOl 0 0 mflK
C90718M C90737M C90756M C90769M
0 0809
<LOQ (0 00978 ugimL)
<LOQ (0 00978 u d m L )
33 5
<LOQ (0 00978 u&L)
NA
00518
0 0174
<Log (0 00978 UgimL)
<LOQ
NA
1C91126F
C91140F C91145F C91162F C91163F
<LCQ (0 00978 u&L)
<LOQ (0 00978 ugimL)
9.60
<LOQ (0.00978 ugimL)
NA
IO181
0 0174
cLOQ (0.00978 ugimL)
<LOQ
NA
C90971M
1.15
C90972M
1.06
C90988M
0.63
11.9
I33
26.2
C91017M
41.5
1.33
110
0 288
C91393F
0 773
C91394F
1.69
C91404F
0.88
C91415F
6.96
0.83
35.4
C91438F
576
40 I
1.20
1 08
0 381
id not mcct criteria LAC 01108101
5124/00,01108101 CSWLAC
Date VerifiediBy-
12128100 HOJ I01108101 KJH I 04130101 LAC
Purity EntcrdVerified 12127100 LAC
I Concentratio. of PFOSAA
mdmL or % Ret < L O Q r O 0100 ug m L j ~ L O Q \ O O I W u y m L j*
<LOQ,ool00"amLI
<LOQ (0 os00 u&L) *' 103%
<LOQ (010140%0 ugimL) 0 0243
<LOO IO 0100 W m L ) 0 0304
<LOQ (0 0100 ugimL)
0 0552 0.0381 0.0434 0 0495
75.3 82 3 51.6 63 2 62 3 106 648 78.7 79 1 75 9
Analytical Report: FACT-TOX-001 LRN-U2103
MIS.
PFOSAA mI/mL
<LOQ
<LOQ
103%
mn
Std. D N . MyMSD RPD
NA
NA
2%
0.0169
57.53 0 00974
+ 00433
22.5 0.00973
18 8
80 9
15 3
Corrected PFOS LOQ (0 W976 ugimL) to include ndcorrection faclors new LOQ is 0 W905 ugimL LAC 02119101
ETS-8-5.1
3M EnExcveli9r7 onmental Laboratory
Sera Week 8 Rework TOX-001-rm-ZIZ-l IAl XIS
Page 5131/2WI 204
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Study
104 Week Dietary Caninogcnicily Study with Narrow Range (98 1%) N-Ethyl Poduomoclanesulfonamido Ethanol in Rats
Roduct Numbm(Ten Subnance)
T-6316 (ElFOSE-OH)
Matliix
Rat Serum
MethodiReviSiOll
FACT-MJ 0 & FACl-M-4 0 reworked using ETS-8-5.1
Analpical Equipment Synem Number.
Madeline 041098
I m m e n t SoftwarcNcnion
MasiLynx 2 3. 3 I, 3 2. 3.3
Filename
See listing to the right
R-Squared Value.
See Attachments
Slop:
See Attachments
Y-lntcrcep
see Attachments
Date of E x ~ a c t i o n i h a l y n .
OS11 1/98 RWW/OK
Date of AnalysidAndysI
05114198,051i5198.05/17/98.6105198 HOJIKJH
Date of Data RcductioniAnalyn.
I2/01/W, I2129IW, 01102101 MMWCSH
Smmple Data
1EEK 14 R A T S E R A REWORK
LolZl5
Grwp
Simple A
Extndion PFOS Std PFOS Purity PFOS PFOS Filename
Concentration
MIl"
DO%
VoI. Rplio
Corrcctioa FlClOr
Corrraion
Dilution Canc.
of PFOS mglmL or % RK
PFOS o%/mL
Mnhod BIk
HZO Blk-I H20 Blk-2
I
0.9275
I
0.9275
<LOQ (0.0230 ugimL) <LOQ (0.0230 UgimL)
<LOQ
Matrix BIk
Rat S m Blk-l
I
Rat Serum Blk-2
I
0.9275 0.9275
<LOQ (0.0230 ugimL) <LOQ (0 0230 ugimL)
<LOQ
QC-75 PF+
MS 5/11/98
i
NA
MSD 511 1/98
I
NA
104% 125%
115%
Group 1
C9073 IM
1
0.9275
0 0842
CiWvOI
C90746M
I
0 9275
0 0883
0 0 mg/lrg
C90748M C90768M
I
0.9275
1
0.9275
0 0753 0.0720
C90780M
I
0.9275
00779
C91129F
I
0.9275
0.148
C91155F
I
0.9275
C91160F
I
0.9275
60598029
0215
C91174F
I
0 9275
UhOW
60598030
0.223
C9llSlF
I
0.9275
UhOWn
0 168
Group 2
C90797M
I
0.9275
Low Dose
C90807M
I
0 9275
5 69
3 0 mgikg
C90818M
I
0.9275
7.14
C90831M
I
0 9275
6 53
C90836M
I
0.9275
5 85
C91192F
I
0 9275
51598054
11.5
C91223F C91233F
I
0 9275
1
0.9275
I 51598055
12 0
165
51598056
15.3
C91241F
I
0.9275
I1 8
croop 3
C91248F C90843M
1
0 9275
1
0 9275
I
0.9275
1
0 9275
I
0 9275
: I :::;:::: I 10.5
47 0
63.3
47 0
I53
51598033
71.0
I
0.9275
Unhoown
500
145
51598034
67 I
1
0.9275
U h o ~ 500
260
51598038
I20
I
0.9275
Unknoown
500
158 51598039
73 I
1
0.9275
U h o ~ 5W
248
51598040
I I5
I
0.9275
I
0.9275
104
I
0 9275
I
0 9275
I
0 9275
1
0 9275
1
0.9275
192
I
0 9275
I
0 9275
I
0 9275
I I
0 9275 0 9275
Unhoun I I 0 0 I 268 I 51598026 I
248
268
ne For all si ler and nani the initial volume is q u a l to the fmal volumefor an extraction volume ratio of 1.
Date EnteredIBy Date Verified, By
6/19/98 LAC, I2106/0C WH. OllO5ll 7/16/98 GML I 12107lW HOI I O M
LAC I KJH/O4/3OIOI LAC
PFOS = P e m u o r ~ m e ~ i f o n a t e PFOSA = Pduomoetanesulfonamide
Purity EnterWerified. IZl27lW LAC
PFOSAA = Pduomoctancsulfonamidaacctate
RSD Std.Dev. MyMSDRPD
NA NA 18%
10 1 OW791
0 0361
192
74 5 25 4
12 8 24 6
12 7 34 0
Filenames
Blks Grp 1 G v2 G v3 G v4
MS, MSD
PFOS 05/14/98 Lo1215 05/15/98 Lo1215 06/05/98 Lot 215
PFOS 51598004.5. 123.124 60598020-31 51598046-58 51598030.42 51598014-26
RO5149883-84
Lot L-2353
PFOSA Purity Correction Fador UnlmoW U"l0laWn
UhOW
U"h0WIl NA NA
U"lm0Wn
UhOW UllhOWn
UhOHm
UhOW
PFOSA DIInUan Fador
1 1 1 1 1 1 1 1 1 1
1 1
I1"h"un UhOWn
UhOW
U"h0Un UnLnOWn
UhOW UhOW
UhOW UhOW
UhOW UhOW UhOW
5
5
5
.
5
5
5
5
5
5
5
5
PFOSA 05/14/98 Lot L-2353 05117198 Lot L-2353 06/05/98 Lot L-2353
PFOSAA 05/14/98 Lo1617 05/15/98 Lot617 06/05/98 Lo1617
PFOSA 51798004-5.97.98 60598020-31 5 1798016-38 51798043-64 51798069-90
R05149883-84
PFOSAA 51598004-5, 123-124 60598020-31 51598103-116 51598084-97 51598065-78
Dilotiow lil, lil, 1/1 l / l , 1/1, I l l 1/1W.l/2, 1/25 11500, 1/5, l / l W 111o00, 115. li250
RO5149883-84
l / l , 111, 1/1
PFOSA C0"G
Filename
canerntraian of PFOSA
75 4 84 6 7 65 OW 0.00 744 7.30 OW OW 8.00 OW 7 13 37 0 25.8 29 8 23 4 33 4 46 5 54.0 78 5 53 0 42 6 6.50 124 74.5 128 101
168 117 189 160 142
274 408 397 285
R05149883
103%
R05149884
116%
60598020
<LOQ(0.0978 ug/mL)
60598021
cLOQ(0 0978 ugimL)
60598022
<LOQ(O 0978 ug/mL)
60598023
<LOQ(O 0978 ug/mL)
60598024
<LOQ(O 0978 ugimL)
60598027
<LOQ(O 0978 ug/mL)
60598028
<LOQ(O 0978 ugimL)
60598029
<LOQ(0.0978 ugimL)
60598030
<LOQ(0.0978 ug/mL)
60598031
<LOQ(0.0978 ugimL)
51798016
0.0740
51798018
0 0516
51798020
0 0597
51798022
0.0468
51798025
0.0667
51798030
0.0930
51798032
0 108
51798034
0.157
51798036
0.1059
51798038
0.0852
51798043
0 330
51798045
0621
51798047
0 372
51798049
0m1
I I 57198051
51798058
51798060
I 5!798%2
I
51798064
1 51798069 I
5 I79807I
0 505
:;;;
09945 0 799 0 708
51798073
51798075
57198077
0 753
5 I798082
137
51798084
204
51798086
199
51798088
I 42
57198090
2 59
Corrected PFOS LOQ (0.0248 u&L) to include nd Comation factors
new LOQ is 0 0230 ug/mL LAC 02119/01
** Tentative rmlts, CCVr did not m e t criteria LAC 011081Ol
Mean PFOSA a@mL <LOQ <LOQ
110%
<LOQ
<LOQ
0.0598
0. I10
RSD Sld. De". MyMSDRTD
NA NA 12%
NA NA
NA NA
18 4 00110
25.5 0 0280
ETS-8-5 1
3M EEnxcveli9r7 onmental Laboratory
Sera Week 14 Rework TOX-WI-sera-212-1 IAI xls
Page 513112WI 205
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Shldy. RoductNumber(Test Substance) Matrix MeIhcdlRevirion: halyiical Equipment System Number I m m e n t SoflwarclVmion. Filename. R - S q u d Value: slope. Y-laemcpt Date of Extractionihdyrc Date of h a l y s i d h d y n : Date ofDaIa Reductionihalyn.
Sample Data
I C 4 Week Dietary Carcinogenicity Study with Nmow Range (98 1%) N-Ethyl PerfluomaetanesulfonamidaELhaool in Rats T-6316 (EtFOSEaH) Rat S a m FACT-M-3 0 & FACT-M4 0 reworked using ETS-8-5 I Madelbe MI098 MassLyox 2.3, 3 I, 3.2, 3.3 See lining to the right See Allxchments see Auxhmenfs See AlUehments 05111198 RWWIOK 05114198,05115198, 05/17/98, 6105198 HOJIKJH IZlOllW. 121291W, 01102101 MMWCSH
Analytical Report: FACT-TOX-001 LRN-U2103
C91155F
U"h0W
I
38.0
60598028
0.0380
C9llMlF
U"lm0WlI
1
35.9
60598029
0.0359
C91174F
UlIlolOwn
1
46 9
60598030
0.0469
C91181F
UolmOWn
I
I8 4
60598031
<LGQ (0.0255 " g i m ~ )
Group 2
C90797M
UOlmoWll
25
65 4
51598103
I 63
L O W Dose
C90807M
UolmOUn
25
28.5
51598104
0.711
3.0 mgkg
C90818M
UilblOW
25
69 5
51598105
1.74
C90831M
UOlmOull
25
55 9
5 I598 106
1.40
C90836M
UOlnoUn
25
27.1
51598107
0.68
C91192F
UOlmOW
25
56 6
515981 12
I41
C91223F
UOlmOWn
25
1 08
5 I598 I I3
2.70
C91233F
UolmOUn
25
990
51598114
2.47
C91241F
U"lm0W
25
53 3
515981 I5
I33
C91248F
UllblOWn
25
57 6
51598116
1.44
Grollp 3
C90843M
U"lm0W
IW
80 5
SI598084
8 05
Mid Dose
C90852M
tinknown
IW
149
51598085
14.9
300mgikg
C90863M
U"h0W
IW
88 4
51598086
8 84
C90877M
Unlm.JWU
IW
246
51598087
24.6
C90880M
U"h0W
IW
126
51598088
12 6
C91281F
Unlm0.M
IW
106
51598093
106
C91288F
UllhOW
100
142
51598094
14 2
C91293F
UnlmOWU
IW
141
51598095
14.1
C91299F
U"h0W
100
309
51598096
30 9
C913MF
U"h0W
IW
I21
51598097
12.1
Groop 4 Mid-High Dose
100 mgks
C9090SM C90W7M C90917M C90921M
tinknown
hh0W U"kn0WU UllkllOW
250 250
.
57 7 99.1
51598065 51598066
14 4 24 8
250
87 7
51598067
21.9
250
97 8
51598068
24 4
C90960M
UIlhOW
250
73 5
51598069
18 4
C91329F
U"lm0Un
250
102
51598074
25 4
C91337F
U"lmO\w
250
153
51598075
38.1
C91355F
UDknOW
250
124
51598076
31.0
C9137OF
UDknOW
250
158
51598077
39 4
C91379F
UnlmOW
250
141
51598078
35.3
Extraction Volume Ratio = lnilial volumdfinal ~ol-e. For d l samples and nandards the initial volume is equal 10 Lhe final volume for an emaction volume ratio of I
0.0363 1.23 187 13 8 I6 4 20 8 33 8
20 9 0.00761
41.1 0 506
35 2 0 659
48.1 6 63
50 4 8.26
21 I 4.38
16 9 5.71
ETS-8-5 I
3M EEnxcvel i97ronmental Laboratory
SMa Week 14 Rework TOX-WI-raa-2I2-IIAl XIS
Page 513112WI 206
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Study
104Week Dietary Carcinogenicity Study with Narrow Range (98 I%) N-Ethyl Perfluorwclancsulfonaida EUlanol in Rats
Product Numbcr(Ter1Substance)
T-6316 (EtFOSE-OH)
M8ViX
Rat Serum
McthodiRevirion
FACT-M-3.0 & FACT-M-4 0 reworked using ETS-8-5.I
Analytical Equipment System Number
Madeline 041098
l m m e n t SoftwardVmian.
MassLynx 2.3. 3 I, 3 2.3 3
Filcname
See Alfachmenls
R-Squared Vduc. slow.
See Attachments See Anachments
Y-intercept.
See Attlchmenls
Dale of E ~ t r a ~ t i d h d y s t :
05/11/98 RWWiOK
Date of AnalyririAnalyn
05/14/98,05/15/98,05/17/98.6/05/98 HOJIKJH
Date of Data R e d ~ ~ t i ~ n i A n d y ~ t
12/01/00, 12/29/00, 01/02/01 MMWCSH
Sample Data
'EEK 14 RAT SERA REWORK
GKUIp
I Sample#
I Concentration
of PFOS
mg/mL or % Rec
I Meam 1
PFOS
RSD
1 Concentration
Std. DN.
of PFOSA
m#mL
MYMSDWD
u#mL or % Ree
I Meam I
PFOSA
RSD Std. DN.
v#mL
MYMSD RPD
McU~odfllk
HZO Elk-I
<LOQ (0 0230 UgimL)
<LOQ(O 0978 ugimL)
H20 Elk-2
cLOQ (0 0230 ug/mL)
<LOQ
NA
<LOQ(O 0978 ugimL)
<LOQ
NA
.. MaUix Elk
Rat Serum Blk-1 <LOQ (0 0230 UgimL)
<LOQ(O 0978 ugimL)
Rat Serum 811;-2 <LOQ (0 0230 ug/mL)
<LOQ
NA
cLOQ(00978 ugimL)
<LOQ
NA
QC-75 ppb
MS 511 1/98
104%
103%
MSD 5/11/98
125%
'*
115%
18%
116%
110%
12%
Group 1
C90731M
0 0842
<LOQ(O 0978 UgimL)
0 0 mgng
C90746M C90748M
0 0883 0 0753
< W ( O 0978 uglmL) <LOQ(O 0978 ugimL)
C90768M C90780M
0 0720
<LOQ(O 0978 ugimL)
NA
0 0779
0 00791
<LOQ(O 0978 ugimL)
<LOQ
NA
C91129F
<LOQ(O 0978 ugimL)
C91155F
cLoQ(00978 ugimL)
C9116OF
cLOQ(0 0978 ugimL)
C91174F
<LOQ(O 0978 ugimL)
NA
C91181F
0 168
0 196
0 0361
<LOQ(O0978 ugimL)
<LOQ
NA
Grovp 2
C90797M
5 48
I LOW Dose
C90807M
5 69
I C90818M I
7 I4
C90831M
6 53
I I 0 0740
00516
I
I
0 0597
II 2
0.0468
I 184
C90836M
5 85
I C~ 9119~2~ F
I1 5
C91223F
12 0
C91233F
I5 3
C9124 I F
II 8
6 14
I
I
0 688
I I4 9
0 0667 0 0930 0 108 0 157
0 106
0 0598
00110 25 5
Groq 3 Mid Dose 30 0 m a g
C91248F C90843M C90852M C90863M
0 0852 0 330 0621 0 372
0 110
0 0280
I I
C90877M
0 MI
28 5
C90880M
0 505
0 494
0 141
C91281F
0 677
C91288F
73.1
C91293F
C91299F
130
24 5
C91304F
80.5
1 CW505M 1
220
104
25 4
I
I
C90907M
0 755
C90917M
0 808
C90921M
0 864
7.78
C90960M
24.6
0 753
0 778
0 0605
C91329F
I37
C91337F
204
C91355F
199
I C9137OF
C91379F
248
12.7
I42
34 0
2 59
188
:traction Volume Ratio = Initial valumdfinal volume For all samples and s a n d a r k L e initial volume is q u a l to the fmal voIume for an exnaction volume ratio of 1
26 7 0 503
Date Enlercdifly.
6/19/98 LAC, 12/06/00 KJH. Ol/O5lOl LAC
PFOS = Pemuo-me~ifonate
Date Vcrificdi fly.
7/16/98 GML I 12/07/00 HOJ / 01108/01 KJH / 04130101 LAC
PFOSA = Pcrfluomctancsvlfonamide
Purity EntcrdNerificd 12127100 LAC
PFOSAA = Pcrflua-tancsulfonamidaacetate
I Concentration
I
of PFOSAA
w#mL or % Rec
<LOQ (0 0255 ugimL)
<LOOQQ (0 0255 u&gm/mLL) )
cLOQ (0 0255 udmL)
103%
*.
104%
**
0 0539
0 04%
<LOQ (0 0255 UgimL)
<LOQ (0 0255 ugimL) cLOQ (0 0255 ugimL)
0 0355
0 0380
0 0359
0 0469
<LOQ (0 0255 ugimL)
I I I63 0711
1.74
I 1.40
0.68 1.41
2.70 2.41 I33
I
:,I 1I 12 6 I 10 6 14 2 14 I
24 8 21 9 24.4 184
I 25 4
38 I 31 0 39 4 35 3
Corrected PFOS LOQ (0 0248 ug/mL) to include std correction facton
new LOQ is 0 0230 uglmL LAC 02/19/01
** Tentative resulls. CCVs did not meet criteria LAC OllO8/Ol
Mean PQOSAA
m#mL <LoQ <LoQ 103%
0 0360
0 0363
1.23
13 8
16.4
20 8
33.8
I
RSD
Std. DN.
MYMSD RPD
NA
NA
2%
40 2 0 0145
20 9
0 00761
I I 411
I
0.506
I 352
1I 663
4 38
I 169 5 71
ETS-8-5 I
3M EnExcveli9r7 onmental Laboratory
Sera Weck 14 Rework TOX-WI-ren-212-lIM xls
Page 5/31/2001 207
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covanceff 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Snpk x
C91211F C91214F C91221F C9I224F Cll235F C91243F C91244F ".""I'C
- PFOS Std
10,171 PFOS Purig
- c.rrrrU.n F.dW 0 9275
C.r=t*" F.U., 0 86.0
0 9275
~
09275
0 864"
am a
09271
~
09271
0 8640 (I 8640
09271
~
HA
0 8640 NA
NA
NA
NA
NA
NA
NA
~
NA
NA
NA
N*
NA
- NA
NA
NA
NA
NA
NA
NA
0 9275
U 8640
NA
(I 9275
U 8640
NA
0 9275
0 864"
NA
0 9275
0 86.0
NA
0 9275
0 8640
NA
0 9275
0 86.0
NA
0 9275
0 86.0
0 9275
0 86.0
0 9275
0 86.0
09275
~
NA
0 9275
0 86.0 0 8640
0 9275
0 86.0
NA
0 9215
0 86.0
NA
0 9215
0 86.0
0 9275
0 86.0
0 9275
0 86.0
0 9275
0 86.0
09275
0 8640
- 09275 0 9275 a 921s 0 9275
0 8610 0 8640 0 86.0 0 86.0
"9215
0 86.0
0 9275
0 86.0
09271
0 8640
0 9271
0 8640
0 9271
0 8640
"927'
0 116".
(I 9275
0 8640
09275
~
U 9275
0 8640 0 8640
0 9275
U 8640
0 927,
0 86.0
09275
0 86.0
09275
0 86.0
0 9171 0 9171 0 9275
0 8640
a 8640 o 8640
,- 09175 09271 W91. ugh
g'mL IAC
- 'FOS
Sa.
- OW
ow
II I
- OW
1.28
- ow
168 NA 216
- NA
166 I54
- I84
NA 37 2 49 2 44 6 40 0 68 5 72 6 55 9 576 50 3 42 2 IIJ llZ 120 997 79 4 98 I 88 I 87 9
- 68 3
92.
274 180 165 5WI 211 408 279 364 343
- 505
412 677 528 430 154 MXI 704 722 603
- 787
..C.m*",ntb. .~PFOS 4 h L % r(rr
LCQ (0 W194 UpimL)
LCQ (0 W781 " y d ) UT (0 W394 "&Id) UT (0 W781 " y d )
WQ(OW394udd)
LCQ(OW78lUyd)
109%
NA
88%
NA
67%
62%
2n
71%
NA
0 0198
0 0394
0 0357
0 0320
0 05*9
0 0582
OWI8
0 0462
0 0403 0 0338
U 0x88
0114 0-
0 0799
0 0636
0 0786 (I 0706 0 0701 00147 0 074"
2 19 305
I32
401
I69
127 2 2, 2 91 2 75
4 OS 3 54 5 42
4 23 3 44 144
481 5 64 5 7%
4 83 631
FSD Sld E%". MSrmSD RPD
NA N.4 NA 21% 10%
22 9
n MI I
21 7 00172
33 0 0 "16
I9 7 0954
UlllnOW"
NA NA NA NA NA NA NA NA
bobow. uotnorn tinknown Uobown Cnlnovn Uokmorn "akoown liatnorn unlnowo untnowo Unknown Unknown Unkmow ""known U&"Lnorn Unborn Unborn Uoknown Uokmaouo lhknown
Unknown Unknown Unkmwn Uuknowll
".k"OWO Uoknown
Uoknown L'obom Uoknom Unknown Uoknown U"k"0W" Umkmoxn Unknown lloknown Untnown unt*oom t'"k"..""
UObOW llnknom
- Sun-.#-
- vermd NA HA
~
NA NA
~
NA NA
~
NA NA NA NA NA NA
- NA NA
NA NA NA NA NA NA NA NA NA NA
~
NA NA NA NA NA NA NA NA
- NA NA
NA NA NA NA NA NA NA YA NA
_N_A _ NA NA NA NA NA NA NA vi(
- NA N*
- PFOSA
C.W.
Wid-
- OW
ow
- ow
OW
- ow
ow
- 259
NA 242
- NA
181
NA
- 202 NA
OM
om ow
OM
ow ow ow om
(100
- ow (100
(I I R I
ow ow ow
OW
ow ow
- ow OW
121
I74 5 53 20 4 126
145 IS 8 176
I, 9
- IS 5
31 0
35 I 37 9 21 4
29 0 29 8
35 8 IS 1
- 43 8 39 6
RSD Sld. Dn. MYMSD RPD
NA NA NA 7% 11%
NA NA
NA NA
I00116
3M
Environmental ETSI-1 I Excel 97
Laboratory
Page 208
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
- - - SW"8.k
P F O S U PFOSAA
VIIW
- NA
- N A
DUuth" F.d.1
- I
- I
- C.W.
ndd ow
~ ow
NA
NA
~
NA
NA
~
NA
I
I ~ I
I ~ I
(100
ow ow ~ ow
121
NA
NA
NA
NA
NA
NA
I
1M ROIIIWO21
122%
NA
NA
NA
NA
NA
~
~
~
NA
I
2.1
R0317WO22
97%
NA
NA
NA
NA
NA
RTSO2230-MS5.4
- NA NA NA NA
- I NA I I
- 285
R0327WO23
NA
ow
nw
115%
CW736M
NA
I
0 5"
CW738M CW739M
NA
I
n 28
NA
I
ow
CW717M
NA
I
2 10
C9075IM CW752M
NA
I
.49
NA
I
ow
CW75JM
NA
I
304
CW766M
~ NA NA
I ~ I
0 I7
~ ow
C91131F
NA
I
8 07
NA
I
ow
C91137F
NA
I
0 05
C9111kF
UOkmrn
NA
I
ow
C9II53F
Unborn
NA
I
ow
CPllSIF
I - - - C9115BF
Unkmxi
NA
UllbOW
NA
NA
NA
NA
I
ow
I
ow
I
ow
I
ow
I
170
NA
I
.5J
CWIO2M
NA
I
217
CW803M
NA
I
713
CWIOSM
NA
I
356
OWBMM
NA
I
,w
CW82.M
RA
I
410
CW821M
NA
I
6,6
CW83PM
NA
I
512
N*
~
NA
10
~
I
180
~
578
C91207F
Unborn
NA
I
64,
RO32 ?OW76
C91210F
Uoborn
NA
I
663
R0327W77
C91211F
Unknown
NA
I
699
C91214F
Unbown
NA
10
165
C91221F
Unknorn
NA
I
68.
I C91221F C9123JF
Unknown
NA
UllhOUil
NA
I
685
I
655
UllbDW"
- - - " NA
I
702
NA
I
766
o m r e d PFI
P ow74
T
NA NA NA
q
NA
NA NA
NA
NA
N*
NA
I
UObOW
NA
NA NA
'LoQ (0 w977 UgirnL) CLOQ (0 m 7 7 "gld) <LOO 10 w977 "drnL1
RSD Sld. Dn. M W S D RSD
NA NA NA 4.5% II%
NA NA
NA NA
1
3M Environmental Laboratory
Page 209
3M Medical Department Study: T6316.1
,IN81 13047-80
unknow.
RTS02210-MSS-3 RTS02230-MS34 RTSQ2230-MS54
CW72IM CW733M W736M C90718M CW7l9M C907.1M C90751M C90112M C9075SM C90766M 01127F C9II28F C91113F C91137F C91144F C9115IF C911SIF C91158F C91161F C91183F
CW795M CWIWM CW802M CW803M CW10SM CY"806M C90821M CW825M CW839M CW8.0M C91196F C9l2OiF C9121OF C91211F C91211F CPI22IF C91224F C'II23SF C9124lF C91244F
%EF& tintnow
- Msl6
- C.W. WhL
OM OM
~
ow ~ ow
ow
_o_w _ 375
272
371
262 323 222
- 350 211
159 OW OW
Om
OW
7 34 0.330
ow ow
OW
~
0 om OW
OM
ow ow
2 95 OW OW OW
- nw 218 229 202 273
214
211 315 2" 3c6
__3w _ 245 307 323 223
3"
352 2.3
187
- 389 363
& 0 W17. Y
AMDT# 092597.1 Covance# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
s"rn,.U vIrw
NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA N* NA NA NA NA NA NA NA NA N* I* HA
WoS
miv#
F.S
I I I
I I I I I I I I I I I
I I I I I I I I I 1 I I I I I I I I I I
I I I I I I
.
.
'LOQ (0 024%u p i d )
C W (0 0247 u p i d ) CLOQ (0 0248 " g i d )
67%
RO127OW21
107%
2a
sox
R0328OWI9
83%
2n
PI0
R0327OW22
37%
R0328OWIB
116
R0327OW23
141
R0328m02I
58%
20
A5.,7%%.
20
OW
R0327OW27 'LOQ (0 0247 UymL)
OW
R0327OW28 'Loo 10 0217 u p i d )
OW
R0327m029
OW
R03270W30
OW
R03270W31
OW
R0327W035
OW
R0321OW36
OW
R0321OW37
NA NA
NA
RSD Sld. DN. MsiMSD W D
NA NA NA 28% 24%
NA NA
NA NA
N* NA
NA SA
3M Environmental Laboratory
Page 210
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
ample Dala 'EEK 27 RAT SEI
Gnw
%no*#
CH1735M C94736M CW738M C90739M C9UIIIM C90751M CH1152M C9VISIM
C91117F C91144F C9113JF CPII54F C91158f
CW799M C90802M CW801M C908OlM CW8MM CW824M CWPZIM CW839M CW8IOM C91196F C91207F C91210F CII2IIP C91214F C91221F C91224F C9I235P C91243F
.* C912UF
#".nu&
C.rrC","lla"
.~PFOS "Z,rnL" x r(rr
'LcQ (0 Do394 UpirnL) . ~ c ~ ( o w 7 8~1 y d ) ' L o g (0 w194 W d ) . W ( O W 7 8 1 ug/mL)
:W(oW394Uyd)
- ~ o(gow781uwd)
109%
NA
88%
NA
67%
62%
2n,
7.K
NA
0 0298
0 0394
0 0337
0 0320
00549
0 0582
0 0448
0 0461
0 0103
00338 0 En%
0 111
0 097
0 0799
0 06M
00786
0 0706
00703
00547 00740
1 I9
3 05 I32
4 01
I69
3 27
2 23
2 91
2 75
6 05
3 54
5 42
4 23
3 44
4 44
LSl
5 64
518
4 83
RSD
Sld. on:
MSlMSDRID
C.rn"t"t*" of PFOSA
~id.rKRn
CLCq (0 w 9 3 u p i d )
'LCQ(Ow193 UyrnL)
'LCQ ( O W 9 3 WmL) . L C Q ( o w 9 3 rnL)
I 104% NA
21.7 0 0172
I~ W ( O w 1 9 3 & L ) C W (0 00493 UymL) 00115 00171
00351 00379 00234
00298 00358 0 0284
RSD sld Do. MyMSD RPD
NA NA NA
~
7% I I%
NA NA
NA NA
65. OOL16
180 Ow608
yIid.r x Rn .LCQ(00493 "ymL) <LW(00248 uumL) ILcQ(OO493 " Y d )
CLCQ (0 0248 u g l d ) rLoQ (0 0493 u g l d )
'Lcq (0 0248 uy,"l.)
129%
NA 122% NA 97% NA 115% NA
CLCQ (0 0248 u y d )
CLcQ(OO2.8 WmL) <LCQ(OO248 yBlmL) CLOQ (0 0248 u p i d ) CLCQ (0 0248 u g l d ) F L C Q (002.8 " g l d ) r L W ( 0 0218 u&L) r W ( Q U 2 4 8UymL) <LCQ(OO248 oglmL) c c q (002.8 "S'mL) j L a g ( 0 02.8 "pi*) .LCQ(oa2.8 U p i d ) 'LCQ(""2.8 "El"&) .LCq("Ol48 "pd) ClCQ(OO248 WmL) CLCQ (00248 U p i d ) cLCQ(OO248 upirnL) rW(00148 upid) ' L c q (0 02.8 " p i d ) CLCQ ( 0 02.8 Y g l m L )
0 270 0 455
"0 1 3 7 713 0356 0 369 0410 8646 0512 I80 0 578 0641 0 663 0 699 I65
068, 0 685 0 651 0 702 0 766
C."Ce",..l*"
SLOQ (0 w977 u p i d )
c w (n w977 ~ y d )
<W(0 00977 u p i d ) CLCQ (0 W977 'd)
50%
31%
q - q - 2 2 116%
31%
26%
32%
21
C W (0 w977 UglmL)
<Loo10 W977 " d d l
I<w(0 w977 u y d ) CLCQ (0 w977 " g i d ) <m10 00977 W d l
I E:0214 0299
~
0 399
NA NA
"0389 161
RSD Sld. E-. MYMSD R I D
NA NA N.4 I% 8%
NA NA
N* NA
"23.8 0611
24 6 0 0744
3M Environmental Laboratory
Page 211
3M Medical Department Study: T6316.1
AMDT# 092597.1 Cavane& 6329-212
104 Weck Dietar, C-mogenicify T-6316 (EGOSE-OH)
Rat sem
ETS-84 I & ETS-8-5 I h w y 070799& Ruby 100699 Masislynx 3 3 R 3 4 see Below See Anscbmrots
SFF AnaEhmenB See Anarhmenla
Study aifh ?+muRange (98 la)S-Elbyl PerflwmoFlancsulfo~doEthanol in Rats
Analytical Report: FACT-TOX-001 LRN-U2103
PFOSEA = Perruomactaor
Sample #
C90847M
C908JSM
I
C90858M
1
C90859M
C90864M
1
C90865M
C9087iM
1
~90872~
C90882M cm8m C91252F
_I _ I
C91254F
1
C91264F
I
C91267F
I
C91283F
1
C91286F
1
C91292F
1
C91295F
I
C91301F C91303F C90916M
- I 1 1
C90931M
C90937M
C90940M
C90944M
C90945M
1
C90954M
1
c9095m
1
C90957M
I
C90963M C91312F
1 ~ I
C91323F
1
C91328F
I
C91339F
I
C91340F
1
C91351F
1
C91354F
I
C91357F
1
C91369F C91371F
- I I imsled PFC
lanude
M W LCQS are
mamidoacetale
yl Perfluomoclancsulfonamidoethyl alcohol
2"2)
suifonyi ethyl-&
S"rr0g.b
- vIrinrd NA NA NA NA NA NA NA NA NA
_N_A _ NA NA NA NA NA NA NA NA
- NA NA NA NA NA NA NA NA NA NA NA
_N_A _ NA NA NA NA NA SA NA NA NA NA
p
139410W
- PFOS Sfi - C o r r a t i o
Factor
0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275
~
0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275
- 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275
__ 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275
- 0 9275 0 9275
0 W974 u
'gld u
lot 171
pmskity comtlon
Factor
0 8640 o 8640 0 8640 0 8640 0 8640 0 8640 0 8640 o 8640 0 8640 0 8640
0 8640 0 8640 0 8640 0 8640
o 8640
0 8640 0 8640
o 8640 0 8640 0 8640
0 8640 0 8640 0 8640 0 8640 0 8640 0 8640 0 8640 o 8640 0 8640 0 8640 o 8640 0 8640 0 8640 0 8640 0 86411 o 8640 0 8640 0 8640 o 8640 o 8640
lo i m i d e std E 19/01
Date EntcrdRy Dale Yenfiedl By Punlv EnledNsrificd
0411IIW, 04/Iz/W, 04/171W,06iO3C?, 06/07/W, 0711IIW, 08ilSiW.09/OL/W CSHLAC OY22101 KIH/O4130101 LAC OY19101 LAC
- nos - Dilutioa
LUW
IW IW
IW
IW IW
IW
IW IW IW
_IW_ IW
IW
IW IW IW
IW IW
IW IW
- IW
m
2m
m
IW
m m
103
IW
?ow
IW
~
1wo
- m m m m m m m m 1wo E mrGt
PFOS
CON.
mdmL
183 269 268 305 268 271 281 235 243 213 629 536 391 506 419 587 481 552 520 329 637 429 509 836 523 509 874 624 633 875 122 145 848 88s 736
Fikosme
ormos
VymL or Y. Rm
~os19wo19
R0519wo20
21.6
R051900021
21 4
ROSi9wo22
R0519wo23
RO51900028 ~os19woz9
R051900030
RO519wo31
R051900032
RO519wo37
50 4
ROSl900038
42 9
R0519wo39
31 4
RO51900040
40 5
RO519wo4l
33 5
R051900046
47 0
R0519wo47
38 s
R051900048
44 2
R05190049
41 7
RO5I'X)IMJO
26 3
RO519wo55
973
R051HX)1156
68 7
R051900057
81 6
R0328MM27
67 0
R051900058
83 9
ROSI'XKXI59
81 5
~0328~032
70 0
~03.?8~~33
SO 0
A0817MM23
101
R032800035
70 I
Do403MM20
I96
W40300021
232
EO40300022
136
LN~O~WZ~
142
w40300024
0040300029 146
RSD Std. Ikv. MSMSO RPD
lot L-I5709 FTOSA hurily
C0,reCliOO
Surrog.~ vcriri
- PFOSA - Dilution
F.Cto7 I I
- PFOSA - COOr.
WmL 215 302
I4 0
20 3
2 85
I 1 I I I 1 I
1
~
1 I I
193 239 236 228 204 247 233
- 163 441 446 433
A062600019 A062600020 A062600024 A062600025 A062600026 A062600027 A062600028 A062600032 A062600033 A062600034
18 6
39 7
7 39
197
77 2
IS 2
I 1 I I I
- 1 1
1 I I I I I I I I I
~
I I I I t
516 631 490 557 706
- 491 365 424 524 382 476 410 269 442 292 554
- 402 779 863 606 954 % ,
A062600035 A062600036 A062600040 A062600041 A062600042 A062600043 A062600044
A062600048 A062600049 A062600050 A062600051 A062600052 A062600056 A062Mw57 A062600058 A062Mw59 A062600060 A062600064 A062600065 A062600066 A062Mw67
4"6,'rn6.P
i
963
I
896
22 6
170
38 3
I
- I IO
558
- 627 174
A062600075 W719wo17
0 239 0 236
o 228
0 204 0 247 0 233 0 163 0 441 0 446 0 433 0516 0631 0 490 0 557 0.706 0491 0 365
0 424 0 524 0 382 0 476 0410 0 269 0 442 0 292 0 554 0 402 0 779 0 863 0 606 0 954
MI.. FTOSA "diUL
RSD Std. Ikv. MWMSD RPD
0 226
163 0 0368
o son
199 0 IO1
0418
21 6 0 0903
o 875
38 6 0 338
ETS-8-5 I
3M Eonlccvl9i7ronmental Laboratory
sera wee* 27 (2) TOXaOl-~ra-2Il-IIXAII.
Page 212
3M Medical Department Study: T6316.1
AMDT# 092597.1 Cnvanee# 6329-212
104 Week Dietary CamlnogeolcilyStvdy M b N m w Range (98 1%) N-Ethyl PerIIuomactanesulfo-amido Ethanol in Rats T4316 (EtFOSE-OH) Rat serum ETS-8-4 I & ETS-8-5 I Davey070799 E Ruby 100699 Marslynx 3 3 E 3 4
see Below Sse AttachmPnIs SFCAffaehmcnts See A l t a c h n l s 02/23/W, 03/28mO SAI 03/07/00,03/27iW, 03/28/W, 04103/W, 04i05lW. 04/06/w,05II9IW. 06'261W. 07/19iW, 08/17/00 IAS!HOI!UMWCSH 03/09'W, 04/03/W,04104/W,04iVSiW. 01/07/00,04i10i00,05123iW. 06/27w), 07/25/W, 08/18/00 IASMOIMMH
WEEK 27 RAT SEF
*UP Dole omup 3 Mid Dose 30 0 mgkg
omup 4 MDd-Htgh Dosc
100 mgkg
s.mpr x
C90847M C90855M C90858M C90859M C90864M C90865M C90871M C90872M C90882M C90886M C91252F C91254F C91264F C91267F C91283F C91286F C91292F C91295F C91301F C91303F C90916M C9093lM C90937M C90940M C90944M C9094JM CW954M C90956M C90957M C90963M C91312F C91323F C91328F CY1339F C91340F C91351F C91354F C91357F C91369F C91371F
81s
- surrq.1.
- Filrmme
veriw
- NA
NA
444
;: I NA
204
NA
- R0328K080
R0328W081 R0328wO82 R0328W83
NA
R0328wO84
NA
R032800087
NA
R0328wO88
NA
R0328K089
NA
188
R0328wOH)
~ NA NA
139
R032800391
1 39
~
378
R032Bwo94
3 78
NA
R0328wO95
3 05
NA
R0328WO%
2 84
NA
R0328wO97
3 26
NA
R0328wO98
2 78
NA
M6
R0328WIVI
6 06
NA
293
R0328WIO2
2 93
NA
424
R0328WIO3
4 24
- NA
280
R0328W104
2 80
NA
286
2 86
NA
IW
991
9 91
NA
IW
705
7 OS
NA
IW
750
7 so
NA
IW
856
8 56
NA
IW
671
6 71
NA
460
4M
NA
10
503
5 03
NA
10
342
3 42
NA
10
480
4 80
NA
1w
819
R0328wO35
8 19
~
~
NA
100
964
w403wO34
964
NA
IW
977
w403wo35
9 77
NA
100
630
Do403wO36
6 30
NA
IW
865
W403wO37
8 65
NA
100
535
Do403wO38
5 35
SA
Do40lwo41
8 26
NA
W401wo42
113
NA
W40W3
NA
W40lwo44
IW
980
~40lwo45
-0Qd(0w492 & 0 w974 /mL)laloclu
m394 E 0 w781 u g i ~ c 0Yl9'0l
la1 uolnown/swI3
M S M S D RPD
Faclor
NA NA NA
2 27
NA
NA NA
3 46
NA
NA
NA
6 58
NA
NA
NA
NA
NA
I NA
NA NA
Fmrlor
Analytical Report: FACT-TOX-001 LRN-U2103
COOC.
"ghL 0 490 1.00 OW 000 000 0 490 04W I 46 2 41 0 560 000 000
ow
000 4 10 000 5 02 0 930 0 330 000 6 69 6 19 590 6 38 9 47 4 20 4 52 6 76 I7 4 8 79 8 05 14 7 599 134 IL 119
25 6 11 6 3 93 9 06 18 2
Fiknmr
Coorcohalloo
orEIFOSE-OH
A062600020 UCQ(0 0248 u p i d )
A062600024 <CQ (0 0248 u p i d )
A0626W025 UCQ (0 0248 u p i d )
A062600026 aCQ (0 0248 u p i d )
A062600027 cLCQ(0 0248 u p i d )
A062600028 <LCQ (0 0248 u p i d )
A062600032 UoQ(00248 ug/mL)
A062600033 <LCQ(VV248U d d )
A062600034 <LCQ(00248 ug/mL)
A062600035 <LOp(V 9248 Y d d )
A062600036 <LCQ(OV248u p i d )
A062600040 <LO? (0 0248 u g / d )
A062600041 <LCQ (0 0248 u p i d )
A062600042 <LCQ (0 0248 u g i d )
A062600043 A062600044
CCQ(0.0248 u p i d ) <LO? (00248 Y g l d )
A062600048 <LCQ (0 0248 u g / d )
A062600049 <LoQ (0 0248 U d d )
A062600050 <LCQ (0 0248 u@nL)
A0626WoSI UW (0 0248 u p i d )
A0626000SZ CoQ(0 0248 ug/mL)
A062600056 UCQ (00248 u u d )
A062600057 <CQ (0 0248 u d d )
aw A062600058 <LoQ (0 0248 u p i d )
~0626~059
(o 0248 ~ g / d )
AV62MWM Uw) (0 0248 u d d )
A062600064 UCQ(0 0248 u d d )
A0626W065 <CQ (0 0248 U U m L )
A062600066 <LOP (0 0248 u p i d )
A062600067 A"67-m
<" UCQ (00248
tl M "?**
ug/mL) "&.M)
A062600072
0 0156
RSD Std. Dcv. MSIMSDRTO
NA NA
NA NA
NA NA
ETS-8-5 1
3M EnEav4i9r7 onmental Laboratory
sera week 27 ( 2 ) TOXM)I-ncm-2l2-l IAI XIS
Page 213
3M Medical Department Study: T6316.1
AMDT# 09259'7.1 Covancdl6329-212
imple Data 'EEK 27 RAT SEI
hUP Dose
S.mplcY
Chup 3 Mid Dose 30 0 rn&E
C90847M C90855M C90858M C90859M C90864M C9086JM C90871M C9087zM C90882M C90886M C91252F C91254F C91264F C91267F C91183F C91286F C91292F C91295F C91301F C91303F CW16u CW93IM C90937M CW940M C90944M C90945M C90954M C90956M C93957M C90%3M C91312F C91323F C91328F C91339F CY134OF C91351F C91354F c91357F C91369F C91371F
,ate
,"amide
104 Week Vmtary Csrcmo~en~cislytudy w t h Narrow Range (98 1%) S-Ethyl Perfluomoclaocnulfo-& Elbanolin Rats T-6316 (EIFOSE-OH) Rat Spm ETS-84 1 81 ETS-8-J I Davey 07079981 Ruby 100699 Maslynx 3 381 3 4 see Below See Aftachmols %e Allschnxnts See Affachnxota UU231W.03128/W SAL 03/07/W. 03/27/W, 03128/W,04/03/W, 04/05iW, 04!06/00, 05,19/W. 06/Z&W.071191W,08/17/W IASHOJIMMWCSH 03/09/W, 04/03/W, 04I04'W. 04/0J/W, 04107lW. 04/101W,01/2?/W.06/27'W. 07125/W,08I18lW IASHOIMMH
new L a M
M556 Dilutiion Fmrlor
10 10 10 10 10 10 10 I0 10 10 10 IO 10 10 10 10 I0 10 10 10 1W 100 1W IW 100 1W IW 1W IW 1W 100 1W IW IW IW IW IW IW IW IW
CQS (0 w492 & I 0194 & Ow781 u
M556
C0"C.
Oe/mL 207 20s 21 I 186 182 251 167 301 I49 168 385 340 331 480 398 298 550 432 428 314 71 8 84 7 81 7 61 8 69 8 566 73 8 58 4 61 4 40 9 41 3 640 44 I 88 4 51 4 74 0 77 2 43 6 49 6
RUJ1900083 F.051900084 RUJ1900085 RU5 I 900086 RU51900091 A0817ooO24 RU51900093 A0817wO25 RUS190009J RUJI'XXIIW A0817wO26 R0519W102 R051900103 ROS I SWIM R0519WIO5 R05IHx)I 10 R0519WIII R0519W112 R0519W113 R051SW118 RU51900065 R0519wo66 RU51900061 R05Ipwo68 R05 I900073 RU5 I900074 RUJI W 7 5 RU51900076 R05 I900077 RUJ19wo82 w403wo34 00403wo35 W403KM36 W4U3wO37 0040300038 WI030W41 w403wo42 0040300043
Coocenll.fio. of M5M
U g h L or x nee
2 07 2 05 2 I1 186 182 2 51 1 67 3 01 I49 I 68 3 85 340 3 31 4 80 3 98 2 98 5 50 4 32 4 28 3 I4
7 18 8 47 8 17 6 I8 6 98 566 7 38 5 84 6 I4 4 09 4 13 640 4 41 8 n4 5 I4 7 40 7 72 4 36 4% 10 2
blOIS
RSD Std. Der. MSrmSD RPD
- 2 03
22 2 0 449
- 20 1
3%
0 7%
197
6 61
I30
~
- 33 2
6 36
2 I1
Analytical Report: FACT-TOX-001 LRN-U2103
- SW0g.f.
- V l l i f i d NA NA NA NA NA NA NA NA NA
- NA NA NA NA NA NA NA NA NA
- NA NA
NA NA NA NA NA NA NA NA NA NA
~
NA NA NA NA NA SA NA NA
- NA NA
PFOSEA miution F.CfW
1 I 1 I I I I I I I I
I I
PPOSEA
C0"C.
"ghL OW 0 IS0 OW 0 140 OW OW OW OW 000 OW OW OW OW OW 0 620 OW OW OW OW OW 0 510 OW (100 OW 0 170 OW OW UW OW OW OW 0 350 OW 0 490 "M
Ow) I 65 0 380 00lW OW
FUro.mr
A062600016 A062600017 A062600018 A062600019 A061600020 A062600024 AU6ZMW25 A062600026 AD62600027 A062600028 A062600032 A062MW33 A062600034 A062MW35 A062600036 A062MW40 A062600041 A062600042 A062MW43 AU62MW44 A062600048 A062600049 A061600050 A062600051 A062600052 A062600056 A062600057 A062600058 A062600059 A0626000M A062MWM A062600065 A062600066 A062600067
A"h'rn6,ll
A062MM072 A062600073 A062MW74 A062600075 A062600076
- M""
- PFOSEA
mdmL
RSD Sld. De-. MSIMSD RPD
NA
5ZL
NA
NA
Nn
NA NA
NA
ETS-8-5 I
3M EnExvceil 9r7 onmental Laboratory
sera week 27 ( 2 )
TOXM)I-sera-211-l IAI XIS
Page 214
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
104 Week D e w Carcinogenicity Sludy with N-u Range (98 1%) N-Elhyl Perfluomoftrncsulfom~amidoPhanol in Rats T-6316 (ElFOSEQH) Rat Serum ETS-84 I &ETS-BJ 1 Darey070799bRuby 100699 Masrlynx33B3 4 Ses AffachmroS Sce A l t a c h l s Sa Altacbnls See Allrchmrnts 02/?3/00,03/28/00 S A L 03/07'00,03/?7/W, 03128/00,04/03/00, 04/01/00, 04/06/W, 05i19IW. 06/26/00, 07/19/00.08~17/W IASMOJMMWCSH 03/09/W, 04/03/00, 04104100,04/0S/00,04/07/00. 04110/00.05/23/00, 06/21/00, 07/25/00, 08/18/00 IASMOJMMH
Analytical Report: FACT-TOX-001 LRN-U2103
cmvp Done
croup 3 Mid D o s 30 0 mekg
Smmpk X
C90847M C908SSM C908S8M C90859M C908MM C9086SM C90871M C9087zM C90882M C90886M C91252F C912S4F C912MF C91267F C91283F C91286F C91292F C9129SF C91301F C91303F c90916M C90931M C90937M C90940M C90944M C9094SM C90954M C90956M C90957M C90963M C913 I ZF C91323F C91328F CY1339F C91340F C91351F C91354F C91357F C91369F C91371F tc
I :::24 4
42 9 31 4 405 33 5 47 0 38 5 442 41 7
RSD Std. I k v . MSlMSD RPD
14 0 2 8s
I8 6 7 39
197 IS 2
169
22 6
146
I70
38 3
'mL) to include I
c 02/19/01
/" . . ~ ,~.",". .II. .'<. ~* >?.., ~
~3h#,,C,"., 111""
L "I ,I"_.
PFOSEh = Perfuomoclancsulfonyl e t h y l m d s
Date Entersmy Date Verified! By Purify EntcdNenIied
04/11/00, 04/12/00. 0 4 / 1 7 / ~0, 6/02/00,06107/00. 07/11/00, 08/15:00. 09/01/00 C S m C 02/22/01 KJH i 04130/01 LAC 02/19/01 LAC
coorontr.tioo 01PFOSA
eymL or K It0 21s 0 302 0 193 0 239 0 236 0 228 0 204 0 247 0 233 0 163 0 441 0 446 0 433 0516 0631 0 490 0 557 0 706 0 491 0 365 0 424 0 524 0 382 0 476 0 410 0 269 0 442 0 292 0 554 0 402 0 779 0 863 0 M6 0 954 0 7S8 0 963 0 8%
0 5S8 0 627 I74
lXCLlO" faefom
FSD Std. De". MSMSD RPD
I6 3 0.0368
19 9 0 101
21 6 fl 0903
"38 6 111
C0llCllIf"'b~
of PFOSAA UymL or K llec
2 30 4 44 2 04 2 S6 2 47 2.12 I 94 1 s3 I88 139 3 78
3 os
2 84 3 26 2 78 6 06 2 93 4 24 2 80 2 86 9 91 7 05
7 so
8 56 671 460 S 03 3 42 4 80 8 19 964 9 77 6 30 8 65 5 15
8 26 I1 3 5 SS 5 80 9 80
u#mL
MSlMSDRPD
31.3
6 58
2 06
I
8041
51':
ETS-8-5 1
3M EEnxcevl 9i7ronmental Laboratory
sna WCCk 27 ( 2 ) TOXM)I-wra-2l2-llAXIIS
Page 215
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Gm"p Dow
Smmpk X
Omup 3
CW847M
Mid Dose
C908SSM
30 0 mgkg
CW858M
C90859M
CW8MM
CW865M CW871M
CW871M
CW882M C90886M
C91251F
C91254F
C912MF
C91267F
C91283F C91286F
C9129S
C9129JF C91301F
C91303F
C90916M
CW931M
C90937M
CW940M
CW944M CW945M
C90954M
CW956M CW957M
C90963M
C91312F
C91323F
C91328F C91339F
C91340F
C91351F C91354F
C91357F
C91369F
C91371F
,mate
fonamide
'OSAA = Psrn"omaetanFsvlfonarmdo.Ectab
... .,.", il"l.l(.l ,L.._cyy, EIFOSE = N m r Range N-Elhyl Perflvomoclanesulfonamideothyl ilcahol l.~.,l..l,,ll.,.ll~,.,~. i ~C " Y . .
PFOSEA = Perfuomocfancsulfonyl ethylarm&
M"0 EtFOSWH
udmL
<LCQ
UCQ
'Lop
UCQ rected PFOS new LOQS a n 0.1
RSD Std. Der. MSMSD RPD
NA NA
NA NA
NA NA
;; 1
Eonerolr.tioo dM5%
ugimL or K llre 2 47 2.05 2 11 I86 I82 251 I 67 3 01 I49 I 68 3 85 340 3 31 4 80 3 98 2 98 5 50 4.32 4 28 3 I4 7 18 8.47 8 17 6 I8 6 98 566 7 38 5 84 6 I4 4 09 4 13 6 40 4 41 8 84 5 14
!%
Mcm M556 u#mL
2 03
3%
6 61
1 636
i (0W492 E 0 W974 u p i d ) to mcludc std wmclim fact
Date Enleredmy Date VcnfieU By PunlyEntere&Ve~&d
0411IIW, 04/12/W.04117 Do. OhiOXw, 06107lW.0711 IIW, 081151W,09101lW CSHAAC OMY01 KJtI104130/01 LAC 02/19/01 LAC
RSD Std. De".
CoOe..t,.tio. olPMSEA
UCQ( 000975 ugiml) noq( 0 00975 u p i d )
RSD Sld. Dev. MSlMSD RPD
NA NA
NA N*
NA NA
NA NA
ETS-8-5 I
3M EEnxcevl9i7ronmental Laboratory
sera weer 17 (I) TOXaOl-rrs-ll2-IIAI XIS
Page 216
3M Medical Department Study: T6316.1
AMDTX 092597.1 CovrneeX 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
'OS = RrnuomocUocl
- PFOS S t l
- 101171
PFOS ?wl
- PFOS
- 'arrrrtho F.UW 0 9115
C..nrt*,
- me1.r 0 8640
- muclan
F.UW I
0 9275
0 86.0
I
09275
_ _ 0 9175 0 9275
0 8640
__ 0 %MO 0 8640
I
- I
I
0 9175
0 8MO
I
0 9275
_ _ 0 9275 0 9275
0 8640
_ _ 0 8640 0 8MO
I
_I _ I
0 9275
0 8640
I
0 9275
_ _ 0 9271 NA
0 8640
_ _ 0 8640 NA
I
- I
I
NA
NA
~
NA
NA NA
~
NA
- I I NA
NA
NA
NA
- N A
NA
1
~
~
NA
NA
NA
I
NA
NA
NA
I
N A ~ N.4
NA
NA
NA
- I
HA
NA
- " - - NA
NA
NA
NA
NA
NA
NA
NA
NA
9275
0 8640
I
NA
0 9175
0 8MO
I
0 9275
0 8640
I
NA
0 9275
0 86.0
I
NA
0 9275
0 8MO
I
09275
0 8640
I
0 9175
0 1164
I
0 9275
0 8640
I
0 9275
0 86.0
I
NA
0 9275
0 8640
I
09275
0 8640
I
0 9275
0 86.0
I
0 927s
0 8MO
I
0 9215
0 8640
L
0 9275
~
0 9215
0 8640
~
0 8640
- I
I
I
Confimrd High
"9275
0 8640
I
I
C o a f i m d High
0 9275
. I ...~. ".., ".,.^ ,
"_".......1_.I1~.
n
0864
I
" "-"
" " I
CmfimdHigh
9275
8M"
I
I I
NA NA
"0 9215 9275
0 8640 0 86.0
I 1
I
ConfimdHigh
0 9275
0 8MO
I
I
ConfimrdHigh
0.9215
0 86.0
I
0 11.
I
ConfimdHtgh
0 9275
01MO
I
00301
I
ConfimrdHirh
0 9275
0 86&0
I
I
ConfimdHigh
'I9275
0 8MO
I
i - - - I
NA
0 9275
I
ConfimrdHigh
0 9275
I
P."..".c..-.1....." ....."I "?,1
I
NA
'I9275
0 86&0
I
0 8640
I
"649
0 8640
IO
I
,
Y.4
c 92'5
e 8640
IO
0 9175
0 8640
I
0 9275
0 8640
10
I23
"0 9275 9275
0 "
8640 8640
10 10
223 291
__ + 0 '1275
0 8640
I
0 9275
0 1640
I
0 9275
0 8MO
10
0 9275
~
0 8640
- 10
153
09275
0 8640
IO
18,
j I ;;NA
I I NA
0 9275 09275 "9275 0 9275 0 9275
0 8MLl
IO
0 8640
IO
0 8640
10
0 8640
IO
0 86.0
in
09275
0 8640
IO
197
R05020W35
4 93
3 68
2 1.
5 84
6%
- - - 09271
0 11640
IO
2 91
0 9275
0 8640
IO
6 so
0 9275
0 8640
IO
5 72
3M
Environmental ETS8.J I Exai 97
Laboratory
- - PFOSA PFOSA
- OU",*O
F.tC. 1 I
- C.n.
WmL
ow om
I
- I
I I
- I I I
- 0.00 OM
ow
0.w ow
ow ow
I
OW
Unknown
- I
0.w
I
- 0.w
I
206
- I
216
NA
- I I , ,
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
I
132
I
- I
NA
253
- 275
NA
- - NA
NA
NA
NA
I
I49
I
I79
I
I45
Unborn
I
I19
untaorn
I
I31
Unknorn
I
I49
I
153
I
I36
I
ow
I
149
I
OW
I
ow0
Unknown
I
0 870
- I
ow
- I
I (I.
NA
I
0 880
I
I 0.
I
Uakmrn
Cmfimd L%h
I
,: 0 830 1
I010
Unborn
NA
I
0 950
Unborn
NA
I
0 970
Unknorn
Confimd High
I
I IO
UaXoorn
Confi-dLgb
I
118
Unhown
C o n f i m d Higb
I
Ow0
Uokmrn
ConfimdHigh
1
I18
Umhorn U"h0W
U,~n.k,.m...r n
Coofimdlgb
NA
.ll.. Coofimd High
-.e.
I I
- I I
OW
ow
- I 0, 1 io
12 8
1
16 I
I
I2 3
I
12 8
I
I3 3
I
I5 2
I
I3 3
I
118
I
- I
I
13 8
- 23 6
28 6
I
34 5
I
32 1
I
I92
I
159
I
27 4
I
26 I
I
27 4
Lhknarn
- I I
- 34 5 30 8
Rso Sld. k. .WSDrn
NA NA NA 3% 1% NA NA 8% 9% NA NA
NA NA
NA h*
NA NA
NA NA
Page 217
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covmce# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Dow Mdhd BIk hhmr Blt hhmx Rlk
C90727M C90730M C90751M C90752M C90754M C90755M C90758M C90759M CM761M C90766M C90767M C90771M C91121F C91122F C9IIIIF C?!!I!P C'IIIISF CPIIJIF C91112F
Confimrd High Conhmrd H i d
NA NA
t183%
5%
C91227F C9121PF CPI23IF C91244F C9125OF
Unborn
Conhmrd High
I
Unbow
2ndAndysisOK
I
Unknown
VA
I
1 "k".,rn
VA
I
Laknowo
VA
I
177 I R0524WO24
809 Do421m18
870 680
I
0012loM59 M.1700084
I
I77 0809 0870 0680
- 0 597
83 2 0 697
~
- 0 5 5 6
- 35 7 0 199
NA NA NA HA NA
NA NA
NA
NA
NA
NA
I
NA
I
NA
I
NA
I
NA
I
N*
I
NA
I
C o n f i d High
I
NA
I
ConhmrdHigh
I
Confimrd Htgh
I
C o n f i d High
I
NA
I
2nd AnslyssOK
2ndAnul.lymrOK
I
NA
I
NA
I
C o n h m d High
I
2nd Amlyns OK
I
Conhmrd High
I
2ndAndynsOK
I
Conhmrd High
I
q ... ....N A
I
2nd
:.. AnalvnaOK ^"
I
I
NA
Comfimrd Htgh C o n f i d High Confimrd Htgb
NA
NA
NA
I
NA
I
NA
I I
etFOSEOH
Corn.
2@!L 2 89
0 8M
- "oww
2 57
ow
_ooww_
ow ow ow ~ ow
78 2
98 3
~ 95 1
69.5
78 1
~ 64.9
91 6
115
~ 114
87 2
- 70 6 91 2 ow
OW
ow
ow
OW
ow ow ow
OW
ow ow ow ow ow ~ ow ow ow ow
"I",
ow ow ow ow ow ow
"00
ow ow
- ow"" n Y YY ow
GW
OW
ow ow
0 880
ow ow
OW
~ ow
4 27
4 49
4 35
2 17
3 29
111
4 78
3 64
- 399 5 *'I
c.lu.ntntlon of EIFOSEOH "gid.,Jbll..
'LDQ (0w977u y d ) CLOQ (0 00977 u y d ) <LCQ (0 w977 u y d ) 'LDQ (0 w 9 7 1 u y d ) t L W (0 02977 u y d ) .Loll (0 w977 u y d ) <Looio w977 U J d I ' L G (0 w971&"Lj
rLoQ(Ow977uymL)
CLCQ I :E
CLDQ I
3M Environmental Laboratory
Page 218
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
5mpk#
CW761M C9077.M C91121F
C91111F C911J2F C9llSlF C91156F C9llJlF C91178F CIlllOF r?!!$?F C90781M CW791M C90793M C'X1798M C90799M C908WM C90812M C90822M C'X1829M CW832M C9119.F C91197F C91159F CI12WF C91206F C91227F C91229F CPI23IF C912b.F C91250F
- .8
Sur",.* verlfkd
NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA N.4 NA NA Conhmrd High NA CoohmrdHigb C o n f i m d Hi%b Conhmrd High NA NA NA
_..... r o n s m dWgh
....... Conhmrd High
"_.-"=-~, " ~1 L"
Conhmrd High NA NA
CoohmrdHigb CoohmdHigb Confimrd High Conhmrd High Conhmrd High
NA C o n h m d Hi%h C-35-d H+ Canhmrd High
Y* NA NA Conhmrd High 2nd *".ly.l.OY Cmh-d High Canhmrd High Confimd High Conhmrd High Confimrd High C o n f i m d High Comfimrd Htgb C o n h m d Hlgb Coofimrd High Cmofimrd High Conhmrd High NA NA NA
- M Y
come.
om
0 01
OW
_ow_ OW
ow
ow ow ~ ow ow
MSUIw02I
OW
__ O M 116
282
336
NA
NA
305
~
107
308
329
N*
N*
- 125 I36
Oil0
OM
om
OM
0 340
0 450
0 380
ow ow
0 33
ow0
ow ow ow
~
I78
" 82"
0 320
. .".r
0 00
I01
000
0 260
OW
000
I55
0220
ow
- 0 J10 !364 344
3'6
189
294
424
429
141
286
416
~ re,
UI
691
521
403
167
418
408
- 476 501' 356
0.03 0 167 0.18 0 408
n 476
0 504 0 156
NA NA NA 9% 11% NA NA 1% 55 NA NA
NA NA
NA I.'.
29 5 Oil0
30 1 0 134
Sump* \'"nkd
NA NA
i F.U.,
NA
NA
NA
NA
NA
NA
NA
<LOQ(0 w192 whL)
NA
< W ( O W492 ug/mL)
NA
<LOQ(Ow492upid)
NA
< L o p (0 W492 u p i d )
NA
70%
NA
64%
NA
.6%
NA
NA
NA
NA
51%
2nd
NA
31%
2nd
NA
63%
NA
76%
NA
78%
NA
63%
2nd
NA
NA
NA
NA
NA
NA
NA
NA
NA
1
OM
NA
1
ow
NA
I
ow
<LOQ(0 w492 U y d )
NA NA NA NA NA C o n h m d Hish NA confimrd High CmhmdHigh Confimrd High NA
I
OW
I
ow
I
ow
I
ow
I I
ow
ow
ow
ow
ow
:::
NA
NA
2nd AndgnsOK 2ndAndyniOX ;,,;A,,.lya,,ci 2nd AndynsOK
NA NA Coofimrd L%h 2nd AnalynsOK CoafimdHigh 2nd Analyni OK CoofimdHtgh NA
2.._"o>d"A~* s^m._"l,.v-.d...,sO*n.K".""
oca
I ;; ow ow ow ow ow ow ow ow ow
2ndAnalynsOK
XA
NA NA Caofimrd High 2ndAndvaiOK Confimnl L % h Coofimrd L g h
I
OW
:ow
Confimrd High
CoDfimd High
C o n f i m d High
CoofimrdHigh
Comfimrd High
C o n f i m d Hn%h
Confimd H i ~ h
Coofinxed H-gb
HA
NA
NA
NA
CLUO
N* NA NA 21% 13% 31% I,*% 11% 8% NA NA
NA NA
N* i*a
NA NA
NA NA
3M Environmental Laboratory
Page 5312001 219
3M Medical Department Study: T6316.1
AhlDT# 092597.1 CovrnceU 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
D.w Melbod Blt Mamr 811 Mamr 811 w.250 .g/mL
C9125OF 3.k
Corromlhn .~PFOS
qi.L or 96 h
Lcq (0 w394 UglrnL)
LOQ (0 00394 ug,rnL)
Wa (0 WJ94 WmL) L o g (0 w391UglrnL)
Lcq( 0 w394 u p i d ) LOQ (0 w394 UgimL) Lcq(" w394 "grid) Lcq(0 MI94 upimL) LOQ(OOa39,upid) Lcq(0 w394 u p i d ) Lcq(0 w394 WbL) Lcq(0 w394 "e',"L)
75% 76% 68% N* NA 78% 97% IWX 112% NA NA NA nolo, 0 0288 00121 LOQ (0 w394 ugrrnL) 0 w70 0 W88 0 n477 0 0325 O"116 OOlW "03"i 00193 0001.8 00393 0 101 0 138
.". 0 0590
"
0% "0788 00251 0 123 0 13, 00301 0 0160 0 0w . 00614 0 0537 0x9
I65 3 03 0 367 I21 2 23 2PI 0674 0 565 2 11 3 53 281 .17 4 93 3 68 2 31 584 666 2 97 6 80 512
RSD Std. Der. MSiMSDW D
N* NA NA 6% 4% NA HA 7% 8% HA NA
70 3 ""134
19 9 ""316
60 6 I128
31 9 I63
3M Environmental Laboratory
RSD Sed Do. MSlMSD WD
NA NA NA 3% 2% NA NA 8% 9% NA NA
NA NA
NA
.L.II..
NA
&CQ (0 w977 y/d)
'Lcq (0 w977 u p i d ) 'Lcq(Ow977 W d )
C L c q (0 ow77 "@*)
NA
C w (0 w977 u p i d )
(Lcq (0 w977 WmL) <LCQ (n w977 u p i d )
(Lcq (0 w977 u p i d )
NA
C L c q (0 w977 u p i d )
32%
5%
40%
5%
38%
28%
20
NA
32%
Zn
NA
26%
In
35%
1%
46%
5%
16%
35%
2n
NA
28%
2n
NA
37%
2.
<LCQ(0 ow77 u p i d )
-LOG (0 w977 upirnL) QoV(Ow977 W d ) .Lcq(ow977 "ghL)
'LOQ(OW977 UyrnL)
<LOQ(owI77 UyrnL)
.Lcq(ow9?7 "g/"L)
rLOQ(Ow977 u p i d )
(LOQ(0 w977 "&L)
CLcq (0 w917 UglrnL)
CLcq (" w977 "@d)
CLcq ( 0 w917 "gl"L) r ~ c (qn w977 u g l ~ )
NA
<LOQ(0 w977 uglmq
NA
CLOQ (0 W917 uglrnL)
.LOQ (e w113 W'mL)
.Lcq (0 w193 "g/"L)
4 cq (n on493 u y m ~ )
.LZ <G xi:: "8 ,ti,
CLcq (0 w493 upirnL)
.LOQ (" w493 "&'d)
< L c q (0 w493 "gh"L)
0 462
NA
NA
n 597
om
0 870
0 680
0 322
0 365
0 629
0 582
NA
0 5pv
NA
0 375
0 556
RSD Std. k.
C.ln.W.I*.
0 376 0 189 0 294 042,
I
0 694
E:
RSD slb I**. MYMSD RID
NA
NA
NA 9% 11% NA NA 4% 5% NA N.4
78%
63%
2n,
N.4
RSD Std. Dm, MSrMSDWD
NA
NA
NA 21% 13% 34% I,% 11% 8% NA NA
NA
NA
~ NA
NA
NA
NA
kfi
NA
29 5
NA
o 110
NA
30 4
NA
0 I34
NA
Page 220
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covancdl6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Sample D a l l 'EEK 53 RAT SEE
G"W Do.= G""p3 Mid h.r 30 0 my*%
C91372F C91171F .Y !".rn"J.
- - Extnrtb. *....ruS
- - \'.L
\'wIlw
nL
I
NA
P4
I
HA
I
NA
I
NA
I
HA
I
HA
I
NA
I
NA
I ~ I
NA
~
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
- - I
NA
I
NA
I
N*
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I ~ I
N*
~
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
- - I
NA
I
NA
ReCWCV E
lrnC*d PF
- PFOS Std - C a r m l b n
F.UW
0 9275 "02'1
0 9275 09275 09275 0 9275 0 9275 0 9275 0 9275 0 9275
~
0 9275 0 9275 0 9275 0 9275 0 9215 0 9275 09215 0 9215
- 0 9275 0 9275
0 9275 0 1275
n 9275
0 9275 0 9275 0 9211 0 9211 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 09275 0 9275
~
0 9275 0 9175 0 9275
n 9275
0 9273 09275 0 9275 0 9275 0 9275 0 9275 0 9175 0 9275 0 9275
- 0 9275 0 9275 E d h,ph win
win o n w
- PFOS
C.W.
* 208
' 156
2"
330
26 4
179
14.3
222
17.8
306
24 5
341
27 3
45
3 58
151
12 I
214
172
701
56 2
312
27.4
368
29 5
491
39 3
142
I,,
442
I5 4
475
38 I
363
29 I
- 480
38 5
392
314
880
70 5
697
55 8
680
5. 5
837
67 I
717
62 3
613
49 I
751
60 2
464
37 2
640
51 I
761
649
I50
60 I
330
164
274
220
614
49 2
n 911
73
~
218
175
917
73 5
274
220
I8k
148
824
66 0
167
131
195
317
195
317
164
132
174
119
154
123
154
284
228
183
- 698
55 9
95 I
76 2
RSD Sld. k. MSlMSD R I D
39 8 7 I8
31 8 I1k
80 I 660
53 6 81 2
SW..,.k VIlW
NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA N.4 NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA HA NA NA KA NA
- PFOSA
- Dl1ulbo
F.U.. 1 3 I I I I I I
- I I I I I I I I I I
I I
I
- I 10 I" I I
10 10 10
10
- PFOSA - Cam.
WmL 201 201 338 293 181 211 252 125
- I 80 165 393 268 324 (89 (85 101 279 283
- k15 323 615 275 382 642 305 123 363 2.7 311 270 23 I k74 343 203
- 430
105 120
30s 517 7M 577 112 109 203 637 103 159 224 IC4
- 125
0 305 0 223 0363
I59 224 106 I25
RSD SU. I*". MYMSD RPD
31 6 00751
22 5 00824
18 7 0 118
48 9 0 536
3M Environmental Laboratory
Page 5312WI 221
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
C9U85.M C9085SM C9085f.M W859M C9U873M C90819M C9Q881M C90896M CPl25JF C91258F C91264F C91269F CP1270F C912l.F C91289F C91294F
C91323F C91326F CV133.F C91317F C91352F CPl356F C91359F C91363F C91367F C91371F C91372F
.Y
U"h0-
U"h*W"
unlnown
UDhWW
Uokmow unlmown Uohova
limbown
Unknown
Unknown
UOknOW
Unknown
Unknown
Unknown
Unknown
~
unknown
Unknown Unknown Unknown
Unknown Unkmow
Unknown
Unknown Unknown Unknown
SW"l.1. vernkd
NA N4 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA keOV0.y coofim mrkd PFOS I I
- C.mrrnt"t
- d P F O S *
W I d .r % .I1
* .323 7.49 6M 3 21 4 I9 621 I7 I35 6 82 ~ 6 78
3M
A042100070
3 17
508
A042100071
5 0%
157
AO42IWU7Z
157
a" A012L00076
4 30
310
A042IWO77
3 10
341
A042lw078
3 47
- 4 35
431
227
M82100023
21 7
5 18
591
I5 2
74
5 03
596
4 68
5 32
5 12
4 92
22 0
118
3%
9 9,
~
8 37
7 U2
20 I
6 47
6 55
6 72
I5 2
21 5
22.3
8 25
8 I8
23 0
19 7
9 18
9 58
~
UOhOW UllhOW
Surmale vermd
NA H.6 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA N* NA N* NA NA NA
NA NA
NA NA NA
ElFOSEaH Dlhlk" F..tar I I I I I I I I I I I I I I I I I I I I I I I I I I I I I 1 I I I I I I I I I I
1
- IfFOSU - C.X.
Wid
om om 0000 om om om om om
0.m am
~
24 I
ow
26 6
ow
22 9 23 7 23.1 24 5
- 22 0 32 8
31 8 27 1
31 2 23 5 210 21 7 29 U 28 I 316 25 6 3 71
146 10 I 7 15 6 1"
~
18 I 22 7 24 0 I25 20 8
157
28 3
21 6
39 6
I4 4 38,
36 9
10 7
- 156 I5 7
00283
I
0 0216
00144 0018. 0 0369 0 0107
3M EEEnTxaSvl89-57iIronmental Laboratory
Page 222
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
C9OB.IM CPOBSOM C9Q854M CW855M CW856M CW859M CW873M CW879M C90881M CW8%M C9I25JF C9I258F
SWW.1. V"W
NA HA
NA
NA
NA
NA NA
NA
NA
NA
NA NA
NA
NA
NA
NA NA NA
NA NA
NA NA
NA
NA
SA NA
NA
NA
NA NA
NA
NA N*
NA
NA
NA
N4
1"
NA
IW
NA
1"
NA NA
N*
NA
NA
NA NA
SA
NA
NA N4
Pucovrrvronfim
ComrYd PFOS WQ (0W492 u d l !a11
-M Y
- C.W. 517 356 529 346 .I7 528 357 141 381 324 1n7 261 391 515 .68 19d 321 425
- 430 451
124 761 877 2'91 604 5199 POI 78, 6246 762 3327 I19 164 665 7 116 691
761 198 57, 927 668 147 178 258
708 815 116 251
- 901 '23 1% LACWi
colrmmtmt .f#%
",imLor%r(l 5 17 356 5 29 146
4 17 5 28 3 57 2 12 181 3 24 107 2 64 3 91 5 15 168 3% 321 4 25 430 151
22 4 76 88 20 1 6 0 5 80 9.0 79 6 25 76 J 33 I. 9 164 6 46
~1 1- 6 6 97 '61 19 8 5 74 9 I7 6 .a I47 178 25 8 7 08 8 35 176 25 I 901 7 23
Analytical Report: FACT-TOX-001 LRN-U2103
S".W.,. verw
NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA N* NA NA NA NA NA NA NA NA NA HA NA NA NA A :
PFOSEA DUutho F.U.I
I
I I
I
I I
- PFOSEA
C.M.
llyd.
ow ow ow ow ow ow ow ow ow
_o_w _
ow ow ow ow ow ow ow ow
- ow 17.8
ow ow
I1 I
OW
OW
ow
OM
ow ow
150
ow ow ow ow
_0_00 _
ow c 30 ow ow ow ow ow
2 52
ow
0 00
ow
5 60
OW
- OM Gw
IUD Sld. Dn. W DWD
NA NA
NA NA
NA NA
NA NA
3M EEEnTlSv4I-957iLronmental Laboratory
Page 223
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Sample Dah EEK 53 RAT SER G"up Drr
Crnupl Msd Dox 30 0 mg>kg
C91255F
C91258P
C9126.F
C91269F
C91270F
C91274F
C91289F
C912PlF
C91297F
311 J
C91305F
CM2M
70 I
I C91347F
317
CP1352F
117
C91356F
132
C91163F
123
C91367F
284
CPl37lF
CPI372F
"1373F
16 2
n.rm&
RSD Sld. Do. M-SD RPD
19 8 7 I8
0 489
".E5
0 .a4
0 179
0 283
33 8
0415
111
(I 323
0.615
I ) 275
0 382
0 662
"0 305 221
0 363 a 247
0331
0 270
0231
0.71
0343
BO I
0 2"1
660
0 430
~
I as
I20
51 6
323
I 6W 321 .I9
I :::621
31.6 00751
-115I , a225 0082, 22 7 5 28 5 91 I52 7, 5 03 596 4 68 5 31
6 72
8.25
23 0
.8 9 0536
,
9 78 1.51
FSD Sed Dn. M W S D RTD
35 9
I72
-LDQ(o w9n " g h L )
rLDQ (0 0248 u d d )
C W (0 0248 u g i d )
0.0266
C W (0 0248 UgimL)
W X (0 0248 u g i d ) .W (0 0248 UglmL) iW (0.0148 UgimL)
rW(00148ugimL)
27 0
cLOQ(O.0218U y d )
I I.
0.0328
a0318
0 0274
00312
CLOQ (0 024%udrnL) 'Loo (0 02.8 YgrmL)
<LCQ (0 02.8 " g r d )
0 02m
00281
00316
0 0256 LCQ (a w493
GGL46
00101
69 2
0 w72
6 23
00061
onis1
0 0227
CLOQ(OO118 uymL)
00125
0 0208
00157
0 0283
0 0236
0 03%
OOL,.
OOlB.
(I 0369
0 0.07
51 3
00156
6 5:
00::;
SU. Do. M W D RTD
u g l d .r % Rn
5 19
346
.17
5 28
3 57
2.42
NA
381
NA
324
4.07
264
3 91
5 45
4 68
396
I 3 21
425
9 76
4 30
0 M252
451
I
224 76
M W S D RPD
C.rn"t"U."
.~PFOSE* C WWh(0L.0.r49%2 URglnmL)
cLOQ(0 0492 u&L)
CLDQ (0 Ob91
ILDQ (0 0492 uglmL) cLCQ(0 0492 WmL)
'LDQ(0 0492 u&L)
'LDQ(0 0492 udrnL)
<LCQ(O 0492 WmL)
24 3
c m (0 0492 WmLI
400
0970
I I
410
188 0771
RSD Sed Dn. MYMSD RPD
NA NA
NA NA
462
6 16
52 7
NA
0 w992
116
I04
548
NA
6 97
761
19.8
5 71
9 27
6 1
147
178
25 8
7 08
8 35
176
25 I
- 41.7
9 0.1.
55 5
NA
6 w96
I l'
ria
t.91
NA
3M Environmental Laboratory
Page 224
3M Medical Department Study: T6316.1
M D T # 092597.1 Covance# 6329-212
Be. w-009
- EXt..Cti."
V.1 mL
- I
I
- I
- I
I I
- I
I
- I
I
- I
I
- I
I
- I
I
- I
I
- I
I
- I
I
- I
- I
I I
- I
I
- I
I
- I
- I
I
I2~I-RTSMSUL CC1712M
- I
I I
- I
I
- I
CW716M
I
CC1722M
I
~ ~ 7 2 4 ~I
CW726M
I
C911728M
I
C90735M
I
C90742M
I
TW743M
I
C'X1747M
I
CW750M
I
CW758M
I
CC1765M CW778M
C91127F
- I I I
I
I
I
I
I
I
I
I
I
I
- I I I
I
I I I I I I I I I I I I I I I I I
- I I
I I I I I I I I I I
- I I :n.hulhd
S",rn*.k Verlbd
NA NA NA NA NA NA NA NA X NA X NA NA NA NA Confimrd Htsh HA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA E NA NA NA NA NA N* NA NA .rru.llgbly.b
- PFOS St1
c.r,=,,., F.d..
- n 9275
"9275
- n 9275
0 927,
- 0 9275
1) 9275 0 9275 0 9275
0 3215
- 0 9275 n 9275 0 9275 "9275
- "0 9275 9275 1,9275 NA NA NA NA NA NA NA NA
- NA
NA
- NA
NA
- NA
NA
- NA
NA NA
NA NA NA
- NA NA "9275 0 9275 0 9275 I,9271 0 9275
"9211 1,9275 0 9215
,,0 9275 9211 0 9275
II 9275
- ,I 9275 /I 9275
,I 9175
0 9271 0 9275 11 9275 0 9175 0 027,
n 9275 n 9275 n 9275 n 9275
0 9215
- 09275 119275 n 9275 u 9275 0 9171 (I 9275 0 9215 n 9215 "0 9275 9275 09275 "9275 ,I 9275
"9275 "9275
"9275 (I 9275 0 9271
n 9275
0 9275 Q 9275 0 9275
- n 9275 n 9275
0.9275 0 9275 0 9z75
E 0 9275 0 9275 n 9275 n 1275
"U '1275 '1275
- 0 9275 0 9275
hr valid lhne
0 8640
- ,I 861" 0 116," 11.8611
- 0.86," 0 864"
0 8640
~
NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
- NA
NA
- 0 86."
n 8wn
"0 8640 R6411
Analytical Report: FACT-TOX-001 LRN-U2103
RSD
wn Sld. Der.
MWSD NA NA N* NA NA NA NA NA "% NA 17% NA I% NA 5% NA I% 4% NA
111 1111123
RI 2 0 0237
no I41
111 7 2 65
3M Environmental Laboratory
Page 225
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
NEEK 105 RAT !
croup Lhlr MeIbod B1k
CW724M CW126M C9n728M CW735M C90742M CWlkIM CM717M CW750M CW758M CW765M CWllBM C'11127F C91111F C91138f C9llUF C9ll48F C9111lF C91159F C91166F C91172F C91116F CIII8IF C9118RF C91190F C9n781M CW112M
C91235F C91216F C91212F C9IZklF
IOlL-,5109
Pms* P",i#y
C...~l*o Q..t.r
unknown Unknorn Umknowo untrown U"b0W uaknoun unknown
UOknOxO Unknown U"ls0W Unknown
unknown u...ovn untnown U"kn*W U"k"0wn
NA NA N.4 NA NA N* NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
unknown Unknown
U"b0Wuo
S.",., verw
NA NA 2ndAdy$mC NA NA NA NA NA X NA
x
NA NA NA NA CO.lmrd HIE NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA ti* NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA
NA NA NA NA N.4 NA NA NA NA NA NA NA NA N* NA NA NA NA NA NA E NA NA NA NA NA NA NA NA u & g M y .bow
- PFQW
Dllulhi F.d.
- I
I
- I
I
- I
I
- I
I
- I
I
- I - - I
I I I
- - I I I I
- I
I I
- I
I
- I
I
- NA
NA
- I
I
- NA
NA 1
- 4
I I
- NA
NA
- I
I I I 1 I I I I I I I
- I I I I I I I I I I I I I
- I I
I I
I I I I I I I I I I I I I I I I
- I I I I I E I I I I I I
- I I
137%
123%
i
lZ5%
i
143%
1.0%
128%
;
121%
i
93%
llnn
NA
NA
91%
Ins%
NA NA
72%
72%
I",%
,"I%
NA
Rso Std. M . MWMSD RID
NA NA NA NA NA NA NA NA JY. 1% 2% 3% 17% NA 12% NA ln% 3%
NA NA
NA NA
3M Environmental Laboratory
Page 226
3M Medical Department Study: T6316.1
ieEK 105 RAT SERA
lotT-llll I
W O S M QuMy c.rml*n
S"rnl.1. V"lM
hCl0,
Unknown
NA
Unknown
NA
Unknown
2nd A d y n a O K
Unknown
NA
Unknown
NA
Unknown
NA
Unknown
NA
Il~knOW
NA
I
Unknown
X
Unknown
NA
Unknown
X
""bo-
NA
I
Unkaow
NA
I
U"ln0.m
NA
U"knDWn
NA
u.know.
Con(-d Hssh
NA
NA
NA
NA
I
NA
NA
NA
NA
NA
NA
NA
NA
I
NA
NA
I
NA
NA
NA
NA
NA
NA
NA
NA
I
NA
NA
I
NA
NA
NA
NA
NA
NA
NA
NA
I
NA
NA
I
NA
NA
NA
NA
NA
NA
NA
NA
4
NA
NA
4
NA
NA
I
NA
NA
I
NA
NA
I
NA
NA
I
U"h0W
NA
I
UOknOW
NA
I
U.k"OW"
NA
I
unlnow.
NA
I
Unknown
NA
Unknown
NA
U"knOW7
NA
Unknown
NA
Unknown
NA
Unknown
NA
Unknown
N.4
""known
NA
Unknown
NA
I
Unborn
NA
llnknown
NA
Unknown
NA
Unknown
NA
llnknovn
NA
llnkmxio
NA
U"kn0W"
NA
Unknown
NA
ll"k"*-
NA
Unknown
NA
Unknown
NA
Unknown
NA
Unknown
,
NA
I
Unknown
'
NA
Unknown
~
NA
I
Unknown
NA
I
Ilnho-
NA
U.knoun
NA
Unknown
!
NA
I
U"kn0WI
NA
In
""known
NA
60
Unknown
NA
Unkmwn
NA
I
Unknown
N.4
I
Unknown
NA
in
Unknown
NA
Unknown
NA
Unknown
NA
u.k"ov.
NA
ulllnown
NA
unknown
NA
I
llnknow~
NA
Unknown
NA
I"
Unknown
NA
Unknown
NA
Unknown
NA
Ilnkmwn
NA
llnkmw.
NA
Unknown
NA
10
Unkmvn
E
E
Unknown
NA
1u
llnknow
NA
UolnOWn
NA
I
Unknown
NA
in
UOknOW
NA
1"
Unknown
NA
1"
unknown
NA
Unknown
NA
knablhmdpakan IiCUylhov. ihr vsh'
nc,
Analytical Report: FACT-TOX-001 LRN-U2103
R5D Sld. Ik" M W S D RPD
NA NA NA NA NA NA NA NA 1% NA 1% NA 8% NA 18% N* 1% 7% 1%
NA NA
NA NA
n611 E
I111 llJ811 "609 16" 4 39 2 72 I17 0 8%
62, 0 5.1
9, I I41
3M Environmental Laboratory
Page 227
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Sample D m YEEK 105 RATS,
c..up w.r MSIhod Blk
Croup 1
Low mu 3 "&E
S"...l.l. Vlllkd
ElFOSWH Di1l bn FU. .
NA
I
NA
2odAomlymOK
NA
I
NA
NA
NA N*
X
NA
X
NA
I
NA
I
NA NA
Confimrd High
NA
NA
I
NA
NA
NA
NA
NA
I
NA
I
NA
NA
NA
NA
NA
NA
I
NA
NA
I
NA
NA
I
NA
NA
N*
NA
NA
I
NA
N.4
I
NA
NA
I
NA
NA
NA
NA
NA
NA
NA
1
NA
NA
I
NA
NA
I
NA
NA
I
NA
NA
NA NA
NA
NA
NA
NA
NA
NA
NA
NA N*
NA
I
NA
NA
NA
NA
NA NA
NA
NA
NA
NA
NA
NA
I
NA
NA NA NA NA
NA
NA NA
NA
NA NA
NA
NA
NA
NA NA
NA
NA NA
NA
NA NA
NA
NA
NA NA
E
NA
N*
NA
I
NA
NA
NA
NA NA
Vly .bow Ihr valid 181
CLGQ (0 011977UgimL) ILcQ(0"2,8"g/rnL)
CWQ(""Z.8 "gl"L)
cLCQ(fl021R UpimL)
C L c q (e 02.8 "glrnL)
3.K
28%
NA
NA
33%
26%
NA
NA
2I%
25%
31%
21
NA
21%
25%
38%
2,
NA
112%
127%
21%
2%
37%
2n
39%
2n
- ~ ~ ~ ( n" Yw~ Lm) 'LGQ i n ow77 "drnL)
RSD
s*. I*".
W S D RPD N* NA NA NA NA NA NA NA 19% NA 23% NA 20% NA 17% NA 4% IIW. 4%
NA NA
NA NA
NA NA
NA NA
3M EnETSvI-5irI onmental Laboratory Excel 97
Page 228
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covanceb' 6329-212
Sample D d n EEK 105 RATS
G..W Dose
Qc-250 ppb
Bor IXIMYW
L S.mnk#
lolNBl1311k7-8 Ms% P'lly
Corrrrlbn
F.Cl..
1121171il-H20 Elk
unknown vnknorn Unknown Unborn llnhoul" Uohown Unknown Unknown IJnknown ""known Unknown U"knC.wn U"kn0W ""born unknown
U"hDWll
NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
l1"bOW"
unknown
1l"hOW.
uaknoua Unknown U"b0,". Unknown lI"h*W Unknorn unknown U"b0.x" U"b0W llnknom U"b0W
Unknown ullknown
C91166F C91171F C91176F
UDknOWa Unknown Unknown Unknorn
unborn Uatnom unknown llnhown Unknawo
U"b0W" Unboun
U"k"0W
"OknOVl
lUin"kbn*ow- a
U.hW
UBh0.M unknown Unknown Unkmua ""k"0~ unknown u.tnaw.
. Unknown
Unknown L l n kn o r Unknow Unknown Unknorn Unknown Unknown Unknorn Unborn llnkmown Unknown untnom Unknown U"hW Unknown lloboro llnbown Unknown Unknown unbowa
SW.l.1. Vl.lfkd
NA NA Ind A d y m 01 N* NA NA NA NA X NA X NA NA NA NA confirmed H'G NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA N* NA NA NA NA NA NA NA NA NA NA NA NA NA N.4 NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA N* NA NA NA NA NA E NA NA NA NA NA NA NA
Analytical Report: FACT-TOX-001 LRN-U2103
wn
Sld hr. MSlMSD RSD
NA NA NA N* N* NA NA NA fI% 4% 1% 1% 1% NA 7% NA 8% I% 3%
NA NA
NA NA
79 4 ",IS
98 I, (I 667
3M EEnTSvI-iI Ironmental Laboratory Excel 97
Page 229
3M Medical Department Study: T6316.1
AMDTU 092597.1 Covancdt 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
IEEK I05 RAT SERA
,," m y l g
CD(I716M
CW726M CW728M Cll735M CW742M
I
C9075BM CW765M
lots29
PFOSEA Purl* Comtbn
hCl.,
Uaknown Unknown Unborn UUbOXn
U.k"OW"
Umkmvn Unknown U"h*W Unknown Unhown Unhovn
URhOWll
U0kDOW" Unbow. Ulmwn U"k"0W"
NA NA NA NA NA NA NA NA NA NA NA NA NA NA N* NA NA NA NA NA NA
SlU.O,.b VWlmd
NA NA 2ndAndym OK NA NA NA NA NA X NA X NA NA NA NA Confimd High NA NA NA NA NA NA N.4 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA N.4
NA NA NA E NA NA NA NA NA NA
PFOSEA Dllvtro F.Cl..
I
NA NA
I I NA NA I I I NA I I I NA k 1 I I I
I
I E I I
I I I I
"M.""&*
LAC0
75%
NA
NA
79?,
60%
N*
NA
46%
65%
0%
2
NA
46%
56%
45%
2
NA
RJ%
87%
61Y.
MI%
57%
2
56%
2
' W ( I I M l 4 9 2 udmL1
RSD Std. Dw. MYMSD RID
NA N* NA NA NA NA NA NA 5% NA 27% NA 34% NA In% NA 4% I% 2%
NA NA
NA NA
NA NA
NA NA
3M Environmental Laboratory
Page 230
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
------- ---WEEK 105 RATS
G""P D..e
Method BIX
Mamr BIX
M1716M CW~ZM C9072,M CW726M C9n728M CII735M C90741M C94743M C911747M CX1750M CW758M CW765M C9il778M
C91127F C91131F C9113RF C9II44F C91148F CIII57F C9II5'IF CVllMF C91172F CP1176F C91183F
C9ll88F
<-(e I10391 "glrnLi "on "on "on
,,I", 121% 121% NA NA 320% !Ill% NA NA RQ% 83%
NA NA 81% 77% NA NA
72%
73% 97%
]Ill% NA N*
'W (0 00394UglrnL) .LW(Oon394 "gld)
001 00116 'w("WIP."glmL) ,10131
1.26 3 69 I89 2 19 0 502 0319
459
n 142
0 104 I1 I75 I1 317 fl86 I 42 4 56 n.87
,>n 29 184 0215 I59 I SI, 5 89
RSD std. I*". MSMSD WI
NA NA NA NA NA NA NA NA Q% NA 17% NA 4% NA 5% NA 1% 1% NA
... .
837%
123%
2
125%
1
143%
1.w
128%
2
131 "0123
87 2
n nz37
120 I .I
"QJQ,
om43
"0166
n 251
0 309
(I 129
70 7
OM21
2 65 "'.'mgr
"
I1 0220 113101
RED Sed. Dn. MSMSD W D
NA NA NA NA NA NA NA NA 3% 2% 2% 3% 17% NA 12% NA
n%
J% NA
NA NA
NA NA
64 n
UQll9
1225058 0 1037
NA NA NA NA NA NA NA NA 2% NA 2% NA 8V. NA I "% NA I% 7% 22
NA NA
NA NA
62 4 ,! 345
94 I42
3M EEnTSv8.5iIronmental Laboratory Excal 97
Page 231
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Sample Dsls
VEEK 105 RAT $
Croup n0.r Mdhod BIk
Mamr BIk
-LCQ (0 1,248 @"L)
-lDQ(OO141ugimL)
clGQ(OU148 uglmL)
14%
28%
NA
NA
33%
26%
NA
NA
21%
25%
31%
1s
NA
11%
15%
18%
2c
NA
121%
127%
26%
19%
37Tc
la
Rso su Dn. MWMSD W D
NA NA NA NA N* NA NA NA 1% NA 23% NA 20% NA 17% NA % . Ill% 4%
NA NA
NA NA
I%
NA
Y1
.6%
7%
56%
45%
1n
NA
NA
RJ%
8%
87%
61*%
I%
60%
57%
2n
1%
56%
20
NA 27%
34% NA IRK NA 1% I% 2%
NA
NA
NA
NA
NA
NA
NA
rLOQ
NA
NA NA
NA NA ""%a LAC"5I":
79. 0115
'JR (I 667
3M EnETSvII-i5 rI onmental Laboratory LlUl91
NA NA
NA NA
Page 232
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Study P d w l NumheOesf Substance) Malnr
104 Week DietaryCarsmogenicity Study with N a m w Range (98 1%) NZthyl Portlua~tancsulfonamimidoEthanol in Rats T-6316 (EIFOSE-OH)
Metho4AYRevision
Analytical Equipment SystemN u m k
Instrument SoRwa~Ncrainn Rlenam
R-SquaredValve
Slnp
Y-Intercept
Dalca of Exlraclindhalysl
Dates ofAnalysia'Analyal
Date ofData R e d u l i u d h l y a t
ample Data VEEK 105 RAT SE
Gmvp Dose
Smnplc #
Gmup 3 Mid h u 30 I1 mgkg
C90842M C'XIU44M CW8511M C'Xl85IM CH1854M C'Xl85SM CW856M CWRSSM C9088lM C908MM CW865M C90867M C90869M C'21871M C90881M C90882M CW883M C90884M C911885M CSilRR9M C'Xl893M C909UOM
C91252F C91253F C91254F C91256F C91264F C91278F C91279F C91286F C91292F C91294F C91295F C91301F C91303F C913U7F C91310F ,,e
- Etrnclioo - Vol.
mL I I I I 1 I I I I 1 I I I I I I I I I I
- 1 I I I I 1 1 I I I I I I I I
- 1 1
S"rr0p.e vermed
NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
- F'FOS Sld
- Comr11on Fartor
0 9275
n 9275
0 9275
I! 9275
t l 9275 tl 9275 n 9275
11 9275 tl 9275
n 927s
11 9275
11 9275
I1 9275
0 9275 0 9275
I1 9275
0 9275
t l 9275
n 9275
I! 9275
- n 9275 n 9275 n 9275 n 9275 n 9275 I1 9275 n 9275 n 927s I 1 9275 n 9275 I1 9275
I! 9275 t l 9275 11 9275
11 9275
- I1 9275 0 9275
- C0"C.
Og/d
1u2 115 273 224 683 483 I12 670 2nu 667 4n2 122 I55 420 4NI 592 374 391 623 I59
-578
387
577 674 I19 823 571 138 139 868 210 774 185 753 128
- 883
665
Coocmlr.tlon Of PFOS
"g/rnL 0, Y. Rcc 40 7 4 61 I 1 11 8 98 27 3 I9 4 4 49 26 9 83 2 26 7 16 I 48 9 6 22 168 I84 23 7 IS0 157 24 9 6 35 23 2 I5 5
46 2 54 I1 95 5
frJ n
45 7 I10 I12 69 5 16 9 62 n 148 , 611 4 51 4 70 8 53.3
"arm&
rooamidoacetate
M S E = N m w Range N-EIhyl Perfluomoelmrsulfonmimidaethyl alcahol
k1556 = C8Fl7S02N(Rl)cHzl:CO) PFOSEA = Perfuamtane aulbnyl rlhylamidc
RSD Sfd. Drr. MSrmSD RPD
80 0 17 6
49 7
3M
Environmental ETS-8-5 I Excel 97
Laboratory
Sera Week IO5 (2) TOXMI-ura-2I2-ItAI XIS
Page 233
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
WEEK 105 RAT SE L
GlOVP
Dole
Sample U
Group 3
CW84M
NA
Mid Dose
CW844M
NA
311 I1 mgn*
CW85OM
NA
CW85IM
AA
CW854M
EA
CW855M
C911856M
h'A
C90858M
NA
C908N1M
NA
CIIIMM
NA
C9086SM
NA
CWI867M
NA
CW869M
NA
CW871M
NA
CW881M
NA
CW88M
NA
CW883M
NA
C90884M
NA
CW885M
NA
CW889M
NA
CW893M
NA
CW'XW)M
NA
Group 3
C91252F
NA
Mid Dose
C91253F
NA
30 n
C91254F
NA
C9I256T
NA
C91264F
NA
~91278~
C91279F
NA
CY1286F
NA
C91292F
NA
C91294F
NA
C9129SF
NA
C91101F
NA
C913113F
NA
C91107F
NA
C91310F
PFOS = PernuomDetanegY I k
PFOSA = Perfluomtsnesulfonamide
PFOSAA = PerfluormdanesulfodamidoaEetate
EIFOSE = N m w Range N-Ethyl PerfluomlsneaulfonaM*,ethyl almohol
MSS6 = CSF17SO2N((H)CH2C03)
PFOSEA = Prrfuomoslane sulfonyl ethylamids
- PFOSA - Dilution
P.CtW I I I I I IO I I I I I I I I I I I I I I
- 1 I I I I 1 I IO I I I I I 1 I
- I I
- PFOSl
-Con&
OghL
I96 15s 187 81 7 287 14 6 223 217 138 272 238 4311 258 343 S36 482 436 232 414 315
-459 296 369 484 380 572 3411 71 7 206 497 447 542 306 263 368
-S36 4111
-- CO.CLOtI.tII,. -- d P F O S A
vymL or K R r 0 196 0 155 I1 187 11 0837 I1 287 11 346 11 223 I 1 217 I1 338 0 272 I1 238 I1 4311 11 258
n 143
I1 536 ii 482 I1 436 0 232 0414 11315
--0.45Y I1 296
11 169 11 484 0 380 I1 572 I1 3411 0717 I1 206 11 497 11 447 11 542 I 1 3116 I 1 263 11 368 I1 S I 6
RSD std. Dcv. MSlMSD RPD
37 9 11 116
30 9 I1 113
3M EEnTSv-8-i5rI onmental Laboratory Excel 97
Sera Weck 105 ( 2 ) TOXoOl -sera-ZI 2-1 I AI XIS
Page 234
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Sludy Roduet Numbeflest Substance)
104 Weak Dietary Carolnogendiy S M y wlh N m w Raoge (98 1%) N-Ethyl Rrflvomoctanesulfm~do Ethanol UI Rats T-6316(EtFOSE-OHI
Sample Data VEEK 105 RAT SE L
Group Dow
s.mp1. x
crovp 1
C90X42M
Mid Dose
C90844M
30 11
C9085OM
C9085IM
CW854M
CW855M
CW856M
C90858M
C90860M
CX1864M
C10865M
C90X67M
CW869M
C90871M
C908XIM
C90882M
C90883M
CW884M
C'Xl88SM
C911889M
C'X1893M C90'XiIM
crovp 1
C9125ZF
Mid DDse
C91253F
30 I1 m&g
C91254F
C91256F
C91264F
C91278F
C91279F
C91286F
C91292F
C91294F
C91295F
C91301F
C91303F
C91307F
C91310F
'OS = Pernvomrlanesul le
'OSA = Perfluomoolanes
OSA,=Pern"omrlan<
FOSE = N m w Rangeb
556 = CHF17SOZN((H)C
OSFA = Perfvomoofanesulfonyl efbylarmde
SWr0g.f. VWiIid
C o n l i i Rgh NA NA NA Nh NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
- PFOSAA - Dilution
P.tt*. IO 111 IO IO IO 10 IO Ill 10 IO IO 10 IO in IO IO IO IO IO IO
- Ill IO IO IO 111 IO in iim 111 IO in IO IO IO in
- 1u IO
- C0.C. "@lL 187 132 308 98 4 715 128 509 379 376 355 166 287 455 3311 472 3911 435 2% BIS 652
- 481 647
373 733 646 791 316 95 9 334 932 525 781 614 349 524
- 721 614
-- CoOnotl.lioo
-- ofPFOSA4
udmL or Rec 1187
1 :I2
308
n 984
7 IS
8 :!8
5 119
3 79
3 76
3 fS
1(16
287
4 f5
3 ?ll
4 il
3 $0
4?5
2 56
6 1.5
6 52
--- 4 XI
40 4
6 47
4 I4
I92
173
7 33
6 16
7 91
3 16
9 59
3 34
9 32
5 25
7 81
6 I4
3 49
--- 5 24
7 21
614
6 14
34 2 2 In
3M
Environmental ETS-8-5 I Excel 97
Laboratory
Sera Week 105 ( 2 ) TOXOOl-sera-212-1 I AI XIS
Page 235
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covancdl6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Sample Data VEEK 105 RAT SI
Group
Do.*
croup 3 Mid hss 311 I1 mgiLg
CW856M C'Xl858M C'XI8lXlM CH)864M CH1865M C'X186lM CW869M C'X1811M C'Xl88IM CW882M C'XM83M C'X1884M CW885M CHl889M C'Xl893M CXI'XxIM
C91252F C91253F C91254F C91256F C91264F C91218F C91279F C91286F C91292F C9I294F C91295F C913OIF C91303F C913lllF C9I3IUF
104 Week Dietary Carcinogenicily S M y with N m w Range (98 I%) N-Ethyl Perfluom:tancsulfoddo Ethanol in R:tls T-6316 (ElFOSE-OH) Rat Sem
ETS-84 I & ETS-8-5 1
h l i s 1162498,Davey 010799
M a d p 3 3 8134
See Below
Sec Atlachments
See Attaehmenls
See Attacbmonts I I ~ ~ I I XILIIO.~IHI.
UZJO~IIXI. m411ii RWW, SAL
0zi18/W, 0U25lOll.03/211W,00111lW, 0019/~10.06120/00,118/1lUlXI. 0 6 1 I i ~ W0.8123lM1 MMHnAS
ll2L?I/lM~, 112I29/W,02/29/W, Uidl16nX1, 06/llMxI. ll02lllW, 06/26/IXl, 081l13/1)0, I I R I l 81W IllllZSllXl MMHIIASNOJ
UnknOUm UoknOUn UhOWn UnLnom
LlnLnOUn UnLnOUn
SWO*.k VIIIlid
NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 2nd Analysis OK NA NA
EIFOSE-OH Dilution Faelor
I I I I I I I I I I
--E1F0SE43A
--C0"C. "gtoll s IS I89 5 IO 3 82 I 'XI 3 37 3 16 3 30 490 10 3 5 41 6 66 6 06 2 MI 9 89 I8 2 I86 3 89 I5 2 171
--IO 6 4 68
8 42 8 56 21 3 564 5 11
17 n
I 'XI 6 46 I5 3 128
n sin
6 03 9 21
--1 2 8 I36
Pllmsmc
AV.r.gC
E1FOSE-OH
VglolL
RSD Std. De?. MSlMSD W D
fl(HI9IZ I 1 11108
3M EEEnxTcSev-l89-i57rI onmental Laboratory
S o n Week 105 (2) TOXMXII-~n-2l2-IIAIXIS
Page 236
3M Medical Department Study: T6316.1
study
Ralucl NumkqTesl Substance)
Matrix
Melhod/Rewsmn
A~~alpicaEqluuulpmeol SystemNumkr lnsmunenl SoRwamNemon
Filename
R - s q d Valve
slop.
Y-lntereept
Dales of Exlracliodhlysf
Dales ofAnalyadhalysl
Dale of Data ReducliodAnalyst
ample Data
IEEK 105 RAT SE
GlOVP
Sample Y
os = Perllwmotanesvl
OSA = Perfluomlanes OSAA = Pernuomoelanc
CO842M C90844M CHl85OM CO85IM CHl854M CHl855M CW1856M CWI858M CHI8MM CO8MM CStt86JM CO867M CO869M CO871M CHl881M C90882M C90883M CStl884M C11885M ~~1889~ CO893M CStIStXIM C9lZJZF C912J3F C912J4F C91256F C91264F C91278F C91279F C9128W C91292F C91294F C9129JF C91301F C91303F C91307F C91310F
le
nmde
boa mdasceIaIe
co,,~llao Psclor
UnknOW
unknown UnknOUn
AMDT# 092597.1 Covsnce# 6329-212
ConfimdHieh NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
M5M Dhlion P.clOl
IO IO in in IO IO in
in
in in IO IO 1 I1 in IO IO In IO IO IO IO IO
IO Ill 10 in IO IO IO 10 Ill 10 IO IO IO in in
--M556
--Cone. ndml 254 116" 214 I69 187 162 270 610 2c-l 228 337 zn8 270 I92 378 294 J34 334 284 4411
--252 286 385 474 324 291 178 223 176 312 470 346 209 348 381
--12s 1x1
Analytical Report: FACT-TOX-001 LRN-U2103
RSD Sld. De".
1.69 187 I 62 2 7X 6 IO 264 2 28 3 37
:on
2 70 192 3 78 2 94 5 34 3 34 281 4 40
41 7 1191
2 00 3 40 3 81
35 7 I 118
3M EEEnXT-Sv1-987i-JrIonmental Laboratory
Sera Week IOJ (2) TOXOOl-~m-212-1IAI XIS
Page 5131Q.lKl1 237
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covnnce# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
ample Data YEEK 105 RAT SE
Gmvp Do*
BOX in14419 ID, s29
Correctlo"
Group 3
C90842M
NA
' I
Mid Dose
CIXl844M
NA
I
30 t i mgng
C9085UM
NA
I
C90851M
NA
I
CY1854M
NA
I
C908SSM
NA
I
CY1856M
NA
I
CYI8S8M
NA
I
CY18MM
NA
I
C90864M
NA
1
C9086SM
NA
I
C90867M
NA
I
C90869M
NA
I
C90871M
NA
I
CM881M
NA
1
C90882M
NA
I
C90883M
NA
I
C90884M
NA
I
C9088SM
NA
I
NA
I
NA
I
NA
N1
Group 3
Mid DDse 3 0 n m&g
C91253F C912S4F C91256F C912MF
C91278F
C91279F
C91286F
NA
C91292F
NA
C912!XF
NA
C91295P
NA
C91301 F
NA
C91303F
!nd Analysis OK
C91307F
NA
NA
C91310F
NA
NA
Ite
PFOSA = Perfluomostenesulfo-amidp
PFOSAA = P e r f l u o m o o t a o e s v l f o n a ~ ~ ~ l = l ~ EtFOSE = N a m w Rmge NEIhyl Perlluomoetanrsulfonarmdo ethyl alcohol
MSS6 = CXFI7SO2K((H)CH2CCO)
PFOSEA = Prrfuonwrtaoe sulfonyl elhylamide
uste EnlerediBy
~~t~ veniieuB~
Purity EnIerelWenfled
I13!116/W, 031101100. 0312il~IXI0. 3/21/W. 0411M I O . 05116/tnI, I16IIMX1. 06/2YIXI,116123/W, tl6l261oO. lI8ilS~lHIl,l9ltlSlW, 111117llXl LAG 'ICSH ~i3111iihi nj i n413nini LAC 01/191i11 LAC
3M EnEETxvcSe-i8l9-rS7oI nmental Laboratory
sera Week 10s (2) TOXW-sera-212-llAI XIS
Page 238
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Sample Data iEEK 105 RAT SE
Gm"p Dow
Sample Y
Grovp 3 Mid Dops 30 0m&g
Gmup 3 Mid Dnne 30 11 m@kg
3s =Perfl"oml?Jlesull
PFOSA = Perfluomoctanest PFOSAA = PernuomoctEtFOSE = Narmw Range N M556 =CSFI7SOZN((H)CI PFOSEA = Perrmuama'taneI
CW842M C90844M CwnsnM C90851M C90854M C!XIJIM C90856M C'X)858M C908MM C908MM C90865M cm6m l390869M CRl871M C90881M CW882M C90883M CW0884M CW88SM C90R89M l'R1893M ('90XX)M
C91252F C91253F C91254F 1391256T 17912648 13912781 1-91 27PF ll91286F C91292F C91294F C91295F C91301F C91303F C91307F 1'91310F
le LaMde
Conee"tr.floo Of PFOS
"dmL or x R4c 40 7 4 61 11 I1 8 98 27 3 194 4 49 26 9 83 2 26 7 16 1 48 9 6 22 168
18 4 23 7 IS0 IS 7 24 9 6 35 23 2 15.5
46 2 54 0 95 5 66 11 45 7 1IO 112 69 5 I69 62 0 14 8 60 4 51 4 70 8 53 3
RSD Std. I k v . MSlMSD RID
XI) n 176
49 7 27 4
11 3459MNl
n 223
11217
n 338 n 272
I1 238 n 4311
n 258 0 343
0 536 I1 482
I1 436 I1 232
0414 11315 11 459 tt.2M
0 369 n 484 0 380 I1 572 n 340 i t 71731~x1 0 206 0 497
I1 447 0 542 I1 3116 n 263 I1 368 0 536
n 4111
37 9
,1111
-
3u.9 I1 133
CO.C.Ofr.LIO.
"CPFQSAA
. VymL or Y. 187
Rs
I32
3 08
I1 984
7 I5
8 28
5 09
3 79
3 76
3 55
I66
2 87
4 55
3 30
4 72
3 XI
4 35
296
6 05
6 52
4 81
6 47
3 73
7 33
6 46
7 91
3 16
9 59
3 34
9 32
5 2s
7 81
6 I4
3 49
5 24
7 21 6 14
RSD SId. I k v . MSlMSD RPD
- 46 4 4 14
- 6 14 34 2
3M
Environmental ETS-R-5 I bXcel97
Laboratory
sen Week IO5 (2) TOXml-sera-212-1IAI XIS
Page 239 513112001
3M Medical Department Study: T6316.1
study Pmducl Numbor(Teesl Substance) Matrix Malhod/Reviaion. Amlflieal Equipment SystemNumber Inalrument SafiwanNeraion Filename R-SquaredValue slope Y-lnt~rccpl Dales oPExtracfiodAmalyst Dates nfi\nalysiaihalyst Dote ofDafa ReduFtiodi\nalyat Sample Data
L4
S.rnr,l. #
CHI84ZM CW844M CWRSOM C'XIBSIM C90854M C90855M C!X)856M CW858M cxinmM C'X8MM C4865M CW867M C90869M C90871M C90881M
cxianm
C90883M CP0884M CP0885M C4889M C!X1893M C'XMNM CPIZSZF C9I253F C91254F C91256F C912MF C91278F C91279F C91286F C9129ZF C91294F C91295F C91301F C91303F C91307F C9131OF
- 47 2
11 00430
Con.mlr.tion ofM556
uglmL or % Rrc 2 s4 11NI 2 I4 Id`) I x7 I d? 2 78 6 IO 264 2 28 3 37 2 08 2 70 I 92 3 78 294 5 34 3 34 2 84 4 40 2 52 2 86 3 85 4 74 3 24 2 91 I78 3 23 I76 3 I2 4 70 3 46 2 09 3 48 3 81 I25 I81
Analytical Report: FACT-TOX-001 LRN-U2103
RSD SLd. D w . MSJMSD RPD
NA NA
NA N*
3M EnEExTvcSe-l8i9-r57Ionmental Laboratory
Page 240
3M Medical Department Study: T6316.1
AMDW 092597.1 C o v a n d 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Study. F'rcduct Number(Test Substance)
104 Week Dietary Carcinogenicity Sludy wilh Narrow Range (98.1%) N-Ethyl PerfluomwtanesulIooaido Elhanol in Rats T-6316 (EIFOSE-OH)
MdUiX.
Rat S a m
MelhodiRevision:
ETS-8-4 1 & ETS-8-5 I
Analytical Equipment System Number lnmment SoftwareNmian:
Soup 020199, Davey 070799 Masslpx 3 3 & 3 4
Filename.
Sce Below
R-Squared Value
See Atla~hments
Slop%:
See Attachments
Y-lnterccpt
See Attachments
Dales of ExUaclionlAnalyn:
02/07/W, 02108lW. 02/09/00 RWW. SAL
Dales or Annalysidhdysl
0U18100,U28/00. 03127/00.05/31/W, 06119l00. 06120/00,08/03/W. 08/16/00, 081231CO MMHAAS
Dale of Data Reductiodhilyst:
02/21100,02/291~,31021000.6102100, WZWW. 06/21/00,08/07100, 08/18/00. 08/25/(0 MMHAASIHOJ
Sample Data 'EEK 105 RAT SE
GlOOP Dole
Group 4 Mid-High Dose
Sample #
C909MM C90908M C90910M C90911M C90916M C90926M C90927M C90928M
Box 00.009
Extr~ctl~n VOI. mL I 1 I I I I I I
Sorrobltr Verified
NA NA NA NA NA NA NA NA
- PFOS Sld - Corredioi
F*dW 0 9275 0.9275 0 9275 0.9275 0 9275 0 9275 0.9275 0.9275
l M 171
PFOS Purity Correction
Fador 0.8640 0.8640 0 8640 0 8640 0 8640 0 8640 0 8640 0 8640
- PFOS - Dilution
Fador 200 200 50 200 200 200 50 200
--PFOS
--C0"C
rig/mL 417 443 786 91 I 551 384 548 791
W62000016 DO62000017 A053100106 DO62000018 W62WW19 Do62woO20 A053100108 Do62wW23
('onerntrflo. of PFOS
IIg/rnL or % ReC 66 9 71 0 31 5 146 88.4 61 6 22 0 127
C90933M
1
NA
0.9275
0 8640
200
286
W62wW24
45.8
C90944M
I
NA
0 9275
0 8640
200
848 DO62000025
136
Group 4 Mid-High Dose
Immg/lrg
C90947M
1
C90948M
I
C90953M
I
C90955M
I
C90956M
I
CW965M
I
CW968M
I
~91315~
I
C91324F
I
C91327F
I
C91332F
I
C91335F
I
NA
0.9275
0 8640
200
899 Do62000026
144
NA
0 9275
0 8640
200
323
DO62000027
51 7
NA
0 9275
0 8640
50
324 A053100113
13 0
NA
0 9275
0 8640
200
400
DO62000030
641
NA
0 9275
0 8640
200
822 DO62000031
132
- - -- NA
0.9275
0 8640
200
857
137
NA
0 9275
0 8640
200
626
I00
NA
0 9275
0 8640
200
762
122
NA
0 9275
0 8640
200
829
133
NA
0.9275
0 8640
20
612
9.81
NA
0.9275
0 8640
504
627 W81600030
251
NA
0 9275
0 8640
200
62 1 DM2000040
99 5
C9 I336F
I
NA
0 9275
0 8640
500
504
DO81600031
202
C91338F
I
NA
0 9275
0 8640
200
875
Do62000044
140
C91340F C91341F C91342F C91356F C91357F C913WF
I
NA
0.9275
0 8640
500
628
W8IM10032
252
I
NA
0 9275
0 8640
200
474
D062WW46
76 0
1
NA
0 9275
0 8640
200
761
DO62000047
122
I
NA
0.9275
0 8640
20
386
DM2000048
6.18
I
NA
0 9275
0 8640
500
500 D081MXK33
200
I
NA
0 9275
0 8640
200
881
W62woOS2
141
C91361F
1
NA
0.9275
0 8640
200
815
DO62000053
131
C91362F
I
NA
0 9275
0 8640
200
I58
DO62000054
25.3
C91372F
I
NA
0.9275
0 8640
200
367
Do62000055
58.8
Groop 6 Mid-High Dose
C91376F C91378F C91380F C91047M C91054M
I
NA
0 9275
0 8640
200
83 I
DO62wW58
133
- - -- I
NA
0 9275
0 8640
200
682
DO62000059
109
1
NA
0 9275
0 8640
200
648
Do62woO60
IM
1
NA
0 9275
0 8640
1
231 A053 I00082
0 I85
I
NA
0.9275
0 8640
1
!7.7
A053100072
0 0222
ReC0"ery 100 mgikg
C91056M
I
C9IOM)M
I
C91065M
I
NA
0 9275
0 8640
5
293 A053100060
I18
NA
0.9275
0 8640
I
177 A053100074
0 142
NA
0.9275
0 8640
I
0.00 A05310W75 LOU (0 0198 ugimL)
Group 6
Mid-High Dose
C9107OM C91071M C91072M C91073M C91076M
C91451F C91453F
1
NA
0 9275
0 8640
1
li4 1 A053100078
00514
I
NA
0.9275
0 8640
1
.I80 A053100079 :LOU (0.0198 ug/mL)
I
NA
0 9275
0 8640
I
i6 6 A053100080
0.0454
- - -- I
NA
0.9275
0 8640
I
ll.00 A05310008I :LOO (0.0198 ugimL]
I
NA
0 9275
0 8640
I
739
A053100085
0.592
I
NA
0 9275
0 8640
10
126 A053100040
5.02
1
NA
0 9275
0 8640
10
!IO
A053100043
1.68
RCO"ny 100 mgng
C91455F
I
NA
0 9275
0 8640
10
739 A0531000M
5 92
C91459F
I
NA
0.9275
0 8640
I
0.410 A053100089 LOQ(OO198ugimL)
C91462F
I
NA
0.9275
0 8640
IO
i76
A053100046
4 61
C91467F
I
NA
0.9275
0 8640
I
:Is 8 A053100093
0 0207
C91473F
I
NA
0 9275
0 8.540
10
,479
A0531wO50
3 84
C91479F
I
NA
0.9275
0 8640
I
I1.W A053100095 LOQ (0 0198 ugimL)
C91480F
I
C91485F
I
C91487F
I
C91488F
I
- 'OS = Perlluorwctanesu late
PFOSA = Pcrlluomoctlnesulfonamidc PFOSAA PerlluarooctancsulIonaidolcefate EtFOSE = Ndmw Range N-Elhyl Pemvorwctanesulfonamido
NA NA
NA NA ~rrectedPFOS
-new LOQ is 0 01
A data is above elhvl alcohol
0 9275 0 9275
- 0 9275 0.9275 ' (0.0247 ug glmL LAC ipper limit,
0 8640
I
09 0
0 8640
10
,443
o 8Mn
0 8640
) t o include std 19101
- -- I
I. 20
10
i19
antitation and is provided as an cslimate
A0531W096 A0531XWJ 1
A053100101 A0531XW52
0 0553 3 55
LOQ (0 0198 ugimL) 4 I6
M556 = C ~ F I ~ S O ~ N ( ( H ) C H ~ C O O )
PFOSEA = Pcrfuorowtaiie sulfonyl cthylamide
- Average
- PFOS
og/mL
Sld. Dav. MSlMSD RPD
- 84 6
53 6 45.4
- 122
57 9 70.5
- 0 227
I66 0 377
- 2 41
96 3
Dale EntercdiByDate Verified/ By. purity EnteredIVcrifid.
03/06/00.03/10lW, 03120100, 03/211W. 4/15/00,5116100. 06/13/00, 6/15/00. 6/19/00, 06/22100.06123/00.06126/1!0. 08/15/00. 09105100, 10117/00 LAUCSH 04l30101 hoj /04/30101 LAC 02119/01 LAC
3M, EEnETxcSve-l8i9-r57 Ionmental Laboratory
Sera Week 105 (3) TOX-001-sera-212-1I A IXIS
Page 241
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covin& 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Study.
104 Week Dielaiy clninogenicity Study With Narmw Range (98.1%) N-EUiyl Prrfluomlanesulfonamida Ethanol in Rats
hoducl N u m W T c s I Subnmce).
T-6316 (ElFOSE-OH)
Mhi-
Rat Serum
MethodiRevision.
ETS-84.1 Bi ETS-8-5 I
Andpical Equipmen1System Number:
So"p020199.Da"ey070799
InsUUment SoRwareNersion:
Maslynx 3.3 Bi 3.4
Filename.
see Below
R-Squared Value.
See Allachments
Slope.
See AItachmmts
Y-lnlenepc Dales or ExUactiodAnalyn
See Auaehments W07100, 02/08/00, 02109100 RWW, SAL
Dates of Analysislhalyst
02/18/00. 2/28/00, 03/27/00, 05/31/00,06119/00.0612WW. 08/03/00, 08116/(Q 08/23/00 MMWIAS
Dale of Data ReductioniAnalyst.
02/21/00, 02/29/00, 3/02/00. WOUW. 06120lW. 061ZIl00,08/07/00, 08/18/(10. 08/25/00 MMWIASNOI
Sample Data YEEK 105 RAT SE L
GlOllp DOSL
crwp4
Simple I c90904M
Box M)-oo9
Iot L-15709 PFOSA Purity
Correction Factor
mknm
sorrogrtr Vrrlflrd
NA
- PFOS/ - Diludo
Facto, IO
- -- PFOSA Filename
- -- cone. nymL 56.8
P.0227W090
-- ConcrnlrPllo" -- ofPFl3SA
m%/RLor % Rec 0.5118
Mid-High Dose
C90908M
U"kn0W
NA
10
60 6 P 022700091
0 6116
IWm%Lg
C90910M C90911M
U"lm0wn U"kWwn
NA
10
I84 P 022700094
I84
NA
10
60.7 PO22700054
0 607
C90916M
U"kn0WI
NA
IO
61 2 PO22700055
0.612
C90926M
U"kn0W
NA
IO
33 0 PO22700095
0.310
C90927M
U"kn0WlI
NA
10
109 A022700096
109
C90928M
unknown
NA
10
97 9 A0227W097
0 979
C90933M
U"kn0WI
NA
10
59 3 A022700698
0 55'3
C90944M
U"hl0WI
NA
10
56 0 A022700056
0.5tQ
CW947M
Unknown
NA
10
68.5 A022700059
0.695
C90948M
unknown
NA
10
27.7 A022700060
0.2i7
C90953M
Unknown
NA
10
57.2 A022700IOI
0 572
C90955M
U"kn0wn
NA
10
61 4 A022700102
0.614
CW956M
U"kn0W
NA
10
39.0 AO227W061
0.390
croup 4
C90965M C90968M C91315F
U"kn0Wn U"lm0WlI Utllinown
- - -- -- NA
10
94.9 A0227W062
0 949
NA
10
63.8 A0227W103
0 638
NA
10
89 8 A022700077
0 898
0.701
Mid-High Dose 100 m&
C91324F C91327F
U"h0Wn UnlOlOWlI
NA
10
191 A022700080
I91
NA
10
I02
A0227W081
1 o:!
C91332F C91335F
Unlmown UilknOW
NA
10
136 A022700082
136
NA
10
205 A022700083
C91336F
U"kn0wn
NA
10
107 A022700084
C91338F
U"kn0W
NA
10
171 A322700087
1.71
C91340F
unknown
NA
10
72 I A322700088
0 721
C91341F
Unknown
NA
10
138 A322700089
I3LI
C91342F
U"h0wn
NA
10
82.6 A1227W063
0.826
C91356F
U"kn0W
NA
10
34 5 A)2270W66
0.345
C91357F
U"kn0Wn
NA
10
201 Al227W067
2.01
C91360F
U"h0Wn
NA
10
185 A)22700068
I8f
C91361F
U"h0W
NA
10
116 A'1227W069
LIf1
C91362F
U"kn0W
NA
10
72 0 A'l22700070
0.721)
C91372F
U"kn0wn
NA
10
161 A'122700073
1.61
C91376F
Unknown
NA
10
193 A'122700074
1.91
C91378F C9138OF
C91047M C91054M C91056M
U"kn0Wn U"lm0W U"kn0W U"lrn0Wn UilhOWll
- - -- -- NA
10
117 A0227W075
l.li
NA
10
89 I All22700076
0.89L
I30
NA
I
0 00 A062000022 :LOQ (0 OW23 ug/mL)
NA
I
000 Al1620MM23 :LOQ (0.W23 ugimL)
NA
I
000 AM20W026 :LOQ (0.03423 uglmL)
C9 I MOM C91065M
U"kn0wn U"known
NA
1
:LOQ (0w 2 3 UgimL)
NA
I
000 A142MM028 :LOQ (0.004'23 ugimL)
C91070M
U"h0UlI
NA
I
000 Al162woO29 'LOQ (0 004'23 UgimL)
C91071M
Unknown
NA
I
000 A(162W0030 LOQ (0 004'23 UgImL)
Group 6 Mid-High Dose
C91072M C91073M C91076M
C91451F C91453F
unknown UllhroWn
- -- NA
I
000 A1162000033 LOQ (0 004'23 ugImL)
NA
1
000 AI62000034 .LOQ (0 w493 UgImL)
NA
1
.LOQ (0 00493 ugimL)
<LOQ
NA
I
'LOQ (0 004,)3 ugimL)
NA
I
0.00 A062W0037 LOQ (0 00493 ugimL)
Rnovery I 0 0 mgikg
C91455F C91459F
NA
I
0.00 A(1620W0 LOO (0004'13 u g h L )
NA
I
0.00 A ( 6 2 0 W 1 LOQ (0.004'13 ug'mL)
C91462F
NA
1
0.00 Ai62W0042 LOQ (0 004!13 u&L)
C91467F C91473F C91479F
NA
I
000 A(162000043 LOQ (0 004!13 u&L)
NA
I
000
A(62W0044
L W ( O . W B 3 Ug'mL)
NA
I
0.00 AC62ww47 LOQ (0.004!13 ug.'mL)
C91480F C91485F
NA
I
0.M) A(162000048 'LOQ (0.004!13 ug'mL)
NA
I
OW Ai62000049 LOQ (0 W 9 3 um'mL)
C91487F
NA
I
P9911RXF
NA
I
inected PFOS LOO, 247ugi
PFOSA = Pemuorooctancsulfonaide PFOSAA = Pcrfluomoctanerulfonaidoacctnte
-n w LOQ is 0 0198 ug. L~ AC .
A data is above the upper limit o
EIFOSE =Narrow Range N-Ethyl Pcrflnarwctanesulfonaido ethyl alcohol
-- LOQ (O.W!D uy'mL)
LOQ (0.00493 uy'mL)
Is
9/01 lntitalion and is provided as ao cslimale
<LOP
M156 = CSF17S02N((H)CHZC00)
PFOSEA = Perfuomctanc sulfonyl ethylamide
RSD Sld. De". MSrmSD RPD
51 9 0 363
39.5 0.512
NA NA
NA
WA
Dale EnlerdBy Dale Verified/ By: Punty EnteredNerified:
03/06/00,03110100,03/20/00,03/21/00,4/15/00,5116100, 06113/00,6/15100,6/19lW,O6/22/00,06123/H, 06126100, 08/I5/00, 09/05/00, 10/17/00 LAWCSH 04130101 hoj /04/30/01 LAC 02/19/01 LAC
3M EnEExTcvSe-l8i9-r57 Ionmental Laboratory
Scra Week 105 (3) TOX-001-sera-212-1IAI XIS
Page 242
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covnnce# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Study Roduet Number(Tea Subnmcc) Matrix MelhodiRevisioa: Analylical Equipment System Number lnsmmenl SoftwareNenion Filename-
104 Week Dietary Carcinogenicily Study with Narrow Range (98 1%)N-Ethyl Pe~uorwetanesulfonamidcEthanol in Rats T-6316 (EtFOSE-OH) Rat Serum ETS-8-4 I & ETS-8-5 I Soup 020199. Dwey 070799 Masslynx 3 3 & 3 4 See Below
R-Squared Value. slopeY-Intercept' Dares of ExVaeIiodAnalyst Dale of AnalysisiAnalysl:
See Attachmenls See Attachmenls See Anachmene 02107100, 02lO8100. 02/09/00 RWW, SAL 02/18/00, 2128100, 03127100, 05131100,06119100. 061201W. 08103100, 08116100, 38123100 MMWlAS
Dale ofData ReductiodAnalyrt:
02121100,02129100,3102100, 06/02/00. 06120100,06121100.08107100, 08118100, 18125100 MMWIASIHOI
Sample Data
BOX 00-009
WEEK105 RATSE
IolT-7121 I
ClOOP
Sample #
PFOSAA Pmrity
surrope
Dose
Correctloll
Verified
FIdOl
croup 4
W04M
Unknown
2nd Analysis OK
Mid-High Dose
C90908M
Unknown
NA
I00 mdkg
CSfI910M
U"kn0Wn
NA
C90911M
U"kn0WI
NA
W16M
U&OW
2nd Analysis OK
C90926M
U"kn0Wn
NA
C90927M
U"kn0Wn
NA
C90928M
U"kn0wn
NA
C90933M
Unknown
NA
W44M
unknown
NA
W47M
Unknown
2nd Analysis OK
C90948M
UllknOUm
2nd Andlysis OK
W53M
U"kn0W
NA
C90955M
U"kn0W
NA
C90956M C90965M C90968M
Unknown U"kn0W
2nd Analysis OK 2nd Analysis OK
NA
Group 4
C91315F
NA
Mid-High Dose
C91324P
NA
100 mS"kK
C91327F
NA
C91332F
NA
C91335F
NA
C91336F
NA
C91338F
NA
C9134OF
NA
C91341P
NA
C91342P
NA
C91356F
NA
C91357F
NA
C91360F
NA
C91361F
NA
C91362P
NA
C91372F
NA
C91376F
NA
C91378F
NA
C91380F
NA
Croop 6
C91M7M
NA
Mid-High Dose
C91054M
NA
Recovery
C91056M
NA
100 m a g
C910M)M
NA
C91065M
NA
C91070M
NA
C91071M
NA
C91072M
NA
C91073M
NA
C91076M
NA
Croup 6
C91451F
NA
Mid-High Dose
C91453F
Unknown
NA
ReCOVOy
C91455F
Unknown
NA
100 mg/Lg
C91459F
Unknown
NA
C91462F
Unknown
NA
C91467F
U"kn0Wn
NA
C91473F
UOlrnOWn
NA
C91479F
U"lrn0W
NA
C9148OF
unknom
NA
C91485F
U"knOW0
NA
C91487F
lJnkrL0wn
NA
C91488F
UnhlOW
NA
ale
orrected PFOS LOQ (0.0
PFOSA = Pcrfluo-clancsvlfonamide P m s u = Pemuo-ctanesuironamidolcetale
-new LOQ is 0.0198 ugiml
A data is above the uppe
EIFOSE = N m w RangeN-Ethyl Pertluomoamesulfonunido dhyl alcohol
M556 = C8F17S02N((H)CH2C00)
- PFOSAA
- Dllulion FIdO,
50 50 50 50 50 10 50 50 50 50 50 50 50 50 50
- 50 50
20 20 20 20 20 20 20 20 20 20 IO 20 20 10 20 20 20
- 20 20
1 I I I I I I I
- I I
I I 1 I I I
I I
I I
- I I ug/mL) 10 AC 021191( lil ofqumtl
- PFOSAA
- Canc. "ghL 132 154 67 I 475 I77 119 193 329 134 279 174 84 112 207 71 0
- 251 I73
510 570 94 I 922 498 559 529 553 555 596 602 562 688 776 624 670 648
- 515 646
0 00 0 00
ow
OW 000 OW OW OW
- 000 000 26 I OW 000 000 OW OW ow OW
000 OW
- OW OW
ude rtd co
Do81600055 A022800018 A022800019 A022700038 Do81600058 W81600038 A022800021 A022800024 A022800025 A0227W040 DO81600059 Do81600060 A022800026 A022800027 W816W061 D081M)(X162 A022800028
0062000061 D062000062 w62oooO65 D062WMM6 D062000067 w62oooO68 DO62W69 D062oooO72 DM2000073 D06200W74 A053 1 0029 DO42000076 D062W79 A05310032 D062W0081 D062oooOBZ W62oooO83 DO62000086 w62oooO87
A062000022 4062oooO23 4062100026 4062100027 4062100028 4062100029 4062100030 4062100033 4062100034 4062100035 4062100036 %?62100037 4062100040 4062 loo04I ~mioo042 \0621oo043 to62 I Mo44 W-52100047 ~0621oo048 \062100049 ,\062100050 !\O62l 0005 1 lion facton
-- Concentration
-- olPFQSAA u#mL or % Ree 6 58
7 68
3:; 6
29.7
% 84
1.19
964 Ill5
.
6 59
14 0
8 71
4 19
5 58
10.3 3 :is
-- 12.6 8 63 10.2
11.4
18 8
18.4
IO 0
II 2
106
II I
II I
119
6.02
II 2
13 8
7 i6
I2 5
I3 4
I3 0
-- 10 3 I2 9 .LOQ (0.0248 ug/mL)
LOQ (0.0248 ug/mL)
LOQ (0.0248 ug/mL)
LOQ (0 0248 ug/mL)
.LOQ (0 0248 ug/mL)
.LCQ (0 0248 uplmL)
LOQ (0 0248 ug/mL)
LOQ (0 0248 ug/mL)
-- LOQ (o.0~48ugimL)
LOQ (0.0248 UpimL) 0.0261
LOQ (0 0248 uplmL)
LOQ (0.0248 u@L)
LOQ (0 0248 ugimimL.)
LOQ (0.0218 ug/mL)
LOQ (0.0248 ug/mL)
LOO (0 0218 ue/mL) LOQ (0 0218 ugimL)
LOQ (0 02t8 ug/mL)
LOQ (0.0248 U g h L )
-- LOQ [n 02.!8 ugimL)
LOQ (0 0248 U g h L )
on and is provided as an enimale
PFOSEA = Perfoorwelane sulfonyl elhylvnide
Average PFOSAA
uglmL
10 7
II 9 <LOQ
RSD Sld. Dev. MSIMSD RPD
74 I 7.93
25 4 3 02
NA
NA
NA NA
Dale Entered/By Dale Verified By Purity EnIercdNerified.
03106i00, 0311OlW.03120100, 03121100,4115lW. 5116i00. 06113100. 6/15/00,6/19/00, 06122100. 06123100, 04'26100,08115100, 09105100. 10;17/W LAUCSH 04130101 hoj 104130101 LAC OUl9lOl LAC
3M EnEETxvcSe-li89-r57.oI nmental Laboratory
Sera Week 105 (3) TOX-00I-sera-212-1IAl.xls
Page 51311204I 243
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Study
104 Week Dietvy Carcinogenicily Study with Nvmw Range (98 I%) N-Ethyl Pduomctanesulfonamido Ethanol i i Rals
Product NumbeflTesI Substance): M&X
T-6316 (EIFOSE4Xi) RaI Serum
McthcdlRcvisian
ETS-8-61 & ETS-8-5.1
Analylical Equipmoll System Number lnsmmcnl SoftwarcNersion
Soup 020199, Davey 070799 Masslynx3.3 Br 3.4
Filename.
See Below
R-Squued Value:
See Attachmcn~
Slope
See Attichments
Y-l"lereep1: Dates of ExUacliodAndysi.
See Allaehments 02107100, 02108100,02109100 RWW,SAL
Dates of AndyridAnalyst
OZll8l00. U28100,03127100, 0513ll00, 06119100.06120100, 08103100, 08116100,08123100 UMHAAS
Dale of Ddla ReductiodAnalysl:
02121100, 02129100, 3102100,06'02/00,06120100. WZllW, 08107100, 08118100, 08125100 IUMWlASMOJ
Sample Data
Box 00-009
WEEK 105 RAT SE
lot UnknowniSWl3
Group
Sample )I
EtPOSE-OH Purity
Dose
Correction
Pactor
Group 4
C909il4M
U"kn0Wn
NA
Mid-Hi& Dose
C90908M
Unknown
NA
Dilution FldW
COK.
Filename
A080300017 A080300018
-conrmtr~tion
-ef EIFOSE-OH
<LOOQym(0L000197%7 uagc/emL)
0 0126
Immg/kg
WIOM C90911M C90916M C90926M CW927M C90928M C90933M C90944M C90947M C90948M C90953M C90955M C90956M
U"hlOwn U"kn0wn U"kn0Wn U"lol0Wl U"kn0Wl U"knOw0 unknown Unknown U"kn0W U"kn0Wn U"kn0wn UIlblOWl U"kn0wn
NA NA 2nd Analysis OK NA NA 2nd Analysis OK NA NA NA NA NA NA NA
81 6
A080300019
00816
1
4 19
A080300020 <LOQ (0 00977 uglmL)
I
22 I
W81600053
0 0221
I I
0440
A0803W024 <LOP (0 00977 uglmL)
I
I6 4
A080300025
00164
I I
227
DO81600054
0 0227
I
II 2
A08030W27
00112
I
11.6
A080300028
0 01I6
I
7 73
A08030003I <LOQ (0 00977 ug/mL)
1
6 26
A080300032 <LO) (0 00977 ug/mL)
I
21.7
A080300033
0.0217
I
15.4
A080300034
00154
I
I28
A080300035 <LOQ (0 00977 ugimL)
C90965M
Unknown
NA
C90968M
U"kn0Wn
NA
A0803W038 A080300039
00197 0 0164
Groop 4 Mid-High Dose
lmmg/kg
C91315F C91324F C91327F C91332F C91335F C91336F C91338F C91340F
U"kn0wn U"lmOW7l UlllmOWn unknown U"hlOwn unknown U"kn0Wn
UllknOWl
2nd Analysis OK NA NA NA NA NA NA NA
I1 W81MMo47
I
344
A080300041
I
29 0
A080300042
I
31.2
A080300045
1
56.2
A080300046
1
30.0
A080300047
I
A080300048
I
A080300049
0.0672 0.0344 0.0290 0 0312 0.0562 0 0300 0 0274 00101
Group 6 Mid-High Dose
Recovery lmmg/kg
Gramp 6 Mid-High Dose
RCCOWry 100 mglkg
C91341F C91342F C91356F C91357F C9136OF C91361F C91362F C91372F C91376F C91378F C91380F C91047M C91054M C91056M C91060M C91065M C91070M C91071M C91072M C91073M C91076M
C91451F C91453F C91455F C91459F C91462F C91467F C991473F C91479F
Unknown U"kn0wn U"kn0Wn Unknown U"kn0W U"knOw0 Unknown UllknOWn U"kn0W
NA NA NA NA NA 2nd Analysis OK NA 2nd Analysis OK NA 2nd Analysis OK NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
1
43 6
A0803WO52
0 0436
I
A0803W053
0 0337
1 I
17.8
A0803wO54
I
33 5
A0803W055
1
57 3
A080300056
I
45.9
D081MMo48
I
170
A080300360
0.0178 0.0335 0 0573 0 0459' 0.0170
1
DO81600051
0 0467
1
A080300062
0 0408
- I
42 4
W81MMOSZ
0 0424
I
270
A080300066
0 0270
1
0 00
A062100022 ELOCI (0.00977 uglmL)
I
000
A062100023 <LOCI(0.00977 ugimL)
I
OW
A062100026 <LOCI(0 00977 ugimL)
I
OW
A062100027 <LOCI(0 00977 uglmL)
I
000
A062100028 cLOC (0.00977 u&L)
I
000
A0621W029 <LOCI(0.00977 ugituL)
I
000
A0621OOO30 c L N i (0 00977 ug/mL)
I
OW
A062100033 E L K ' (0.00977 uglmL)
- 9 1
000
A062100034 cLOC (0.00977 ugimL)
I
A062100035
(0.00977 u&L)
I
0 0800
A062100036 cLW (0 00977 ugimL)
I
000
A062100037 CLOQ (0 00977 uglmL)
I
0 00
A062100040 <LGQ (0 00977 ugimL)
I
0 00
AM2100041 <LO9 (0 00977 ug/mL)
I
OW
A062100042 ELOQ( 0 00977 ugimL)
I
000
A062100043 cLW (0 00977 ugimL)
I
ow
A0621MX)44 ELOQ ( 0 w977 U g i r n L )
I
OW
A062100047 <LOQ (0.00977 ugimL)
C91480F C91485F
cLOQ (0 00977 uglmL) ELOQ(0.00977 uglmL)
C91487F C91488F
PFOS = Pcrfluomoctanesu ate PFOSA = Pemuorooclanerulfonaide PFOSAA = Pemuorooclanesulfonamidoaeelate
NA
orrectedP M S LOQ (0.0247 uglmL) la inelude std correctionIxtors new LOO is 0 0198 upimL. LAC 02119101 A - data is above the upper limit ofquanlilalion and is provided is an estimatc.
-cLOQ (0
<Lop(0
00977 00977
u&L) uglmL)
EIFOSE = Nmow Range N-Ethyl Pc~uaroaclanesvlfonatnidoethyl alcohol MS56 = C8FI7S02N((H)CHZC00)
PFOSEA = Perfuorooctane sulfonyl cthylamidc
Dale EnlerediBy. Date VerifiedI By' h r i l y EntcrediVerified
miwm, O~IIOIOOM, I~OIOO,~IZIIO4Oi,isiw. 5 w w . wi31o0,6/151w, W I ~ I W0,6mm.~23100,06126100,msiw. WIO~IWI,OII~IM)LAUCSH
04130101 hoj 104130101 LAC 02119101 LAC
Average EtFOSE-OH
llghL
00182
0.0364 <LDQ <LOQ
RSD Std. Dw. MSiMSD RPD
93.3 0 0170
40 0 00145
NA NA
NA NA
3M EnEExTvcSe-li89-r57.oI nmental Laboratory
Sera Week 105 (3) TOX-001-sera-212-1INXIS
Page 244
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covsncell6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Study Product Number(Test Substmce). MaviX: MethodiRcvision. Analytical Equipment System Number. lnsmmcnl SoRwueNcrrion: Filename.
104 Week Dietary Carcinogenicity Study with Narrow Range (98.IX) N-Ehyl PerfluorwclulesulfonamidaEhmol in Rals T-5316 (EffOSE-OH) Rat Serum ETS-8-4.1 & ETS-8-5.1 Soup 020199, Davey 070799 Masslynx 3 3 & 3.4 See Below
R-Squared Value. slope: Y-lnlercept. Dates of ExUacliodAnalysl Dales of Analysidhalysl
See Altachmenls See Attachmcna See Attachmenu 02/07/00, 02/08/00. 02/09/00 RWW, SAL 02/18/00, 2/28/00, 03/27/00, 05/31100,06/19/00. 06/20/00, 08103100,08/16/00, 18/23/00 MMWIAS
Dale of Data Reductiodhalysl.
02/21/00, 02/29/00, 3/02/00,06102/00. 06/20/00. 0612IIW. 08/07/00,08/18/00. #)8/25/W MMWIASHOJ
Sample Data
Box O M
WEEK 105 RAT SE
GlOOP
Sample I)
lolNB113047-80 M556 Purity
Sllrrogpte
~ 5 % -- M556
Filename -Concrnlrrtlon
Doll Group 4
C90904M
Corrcctlon Factor
U"kn0wn
Verified NA
Dilmtlon Factor
IO
-- COW. aglmL 646
A022700090
- of M556 iiglmL or % Rcc 6 46
Mid-High Dose
C90908M
U"kn0Wn
NA
IO
766
A022700091
7 66
IO0 m a g
C90910M
Unknown
NA
50
295
A022800019
14 8
C90911M
U"h0Wn
NA
IO
610
A022700054
6 IO
C9G916M
Unknown
NA
IO
599
A022700055
599
C90926M
U"lm0W
NA
IO
MI
AO227W095
6 41
C90927M
unhown
NA
IO
824
A022700396
8 24
C90928M
Unknown
NA
IO
694
A022700097
6 94
C90933M
UnknOwO
NA
IO
899
A022700098
8 99
C90944M
UDknOWI
NA
IO
410
A022700356
4 IO
C90947M
unlmown
NA
IO
416
A022700059
4 16
C90948M
U"kn0Wil
NA
10
538
A022700060
538'
C90953M
U"lmOw0
NA
IO
401
A022700101
4 01
C90955M
Unknown
NA
IO
871
A022700102
8 71
C90956M
U"kn0Wn
NA
10
345
A022700061
3 45
C90965M
U"kn0W
NA
C90968M
U"kn0W
NA
C91315F
U"kn0WD
NA
-~- I O
42 I
AO227W062
4 21
IO
627
A022700103
6 27
IO
635
A02270W77
6 35
C91324F
Unkn0Wn
NA
IO
42 I
A022700080
421
C91327P
U"hOW7l
NA
IO
320
A022700081
3 20
C91332F
U"hOw0
NA
20
288
A022800048
5 76
C91335F
U"h0Wn
NA
IO
570
A0227WO83
5 70
C91336F
Unhown
NA
IO
753
A022700384
7 53
C91338F
U"lm0Wn
NA
IO
608
A0227WO87
6 08
C9134OF
U"kn0Wn
NA
IO
388
A022700388
3 88
C91341F
U"knOW7l
NA
IO
505
A022700089
5 05
C91342F
Unknown
NA
IO
618
A0227W063
6 18
C91356F
U"kn0Wn
NA
IO
210
A022700366
I IO
C91357F
U"kn0WlI
NA
IO
625
AO227W067
6 25
C9136OF
U"knOW7l
NA
IO
460
A0227W068
160
C91361F
U"kn0W
NA
IO
305
A022700069
3 05
C91362F
U"kn0Wn
NA
IO
512
A022700070
5 I2
C91372F
U"kn0Wn
NA
IO
606
A022700073
606
C91376F
U"lm0W
NA
IO
620
A022700074
6 20
C91378F
Unknown
NA
C91380F
U"kn0Wn
NA
C91047M
U"kn0W
NA
-. - IO
376
A022700075
176
IO
512
A022700076
5 12
I
0.0600
A061900022 LO7 (0 00494uglmL)
C91054M
NA
1
0.00
A0619WO23 LOQ (0 00494 ug/mL)
C91056M
NA
I
0.00
A061900026 LOI) (0 00494 uglmL)
C91060M
NA
I
0.270
A061900027 LO) (0 00494 ug/mL)
C91065M
NA
I
0 00
A06 I W 2 8 LO) (0 00494 ugimL)
C91070M
NA
I
0 00
A061900029 LO) (0 00494ugimL)
C91071M
NA
I
0.00
A 0 6 1 W 3 0 L a > (0 00494 u@mL)
C91072M
NA
I
4 41
A061900033 LO) (0 00494 uglmL)
Group 6
C91073M C91076M
C91451F
.- - NA
I
0.00
A061900034 Lo() (0 1W94 uglmL)
NA
1
000
A061900035 LO> (0 00494 ug/mL)
NA
1
55 3
A061900336 LOO (000494 uglmL)
Mid-Higb Dose
C91453F
U"kn0Wn
NA
I97
A061900037 L a ) (0 tK1494 ugimL)
Recovery
C91455F
Unknown
NA
0.350
A061900040 LOO (0 w494 ugimL)
100 mgitg
C91459F
Unbwn
NA
0.00
A0619wo41 L a ) (0 W 9 4 udmL)
C91462P
U"kn0Wn
NA
1.87
A061900042 LOO (0 00494 ugimL)
C91467F
U"kn0Wn
NA
OW
A061900043 LOO (0 00494 ugimL)
C91473F
U"h0Wn
NA
0 350
A0619000d4
LOO (0O M 9 4 ur/mL)
C91479F
U"h0Wn
NA
0.00
A061900047 LOO (0 00494ugimL)
C91480F C91485F C91487F C91488F
Uolmown UllhWn Unknown
UIhOWn
I NA
NA
1 NA
NA
I
0.00
A061900048 LOO (0 00494 ug/mL)
2 75
A061900049 LOO (000494 ug/mL)
2' OW
A 0 6 1 W 5 0 LOO (0 00494ugimL)
0.00
A061W51
(0 00494 "g/InL)
FOS = Pemuomocianesu~ ate
onected PFOS LOQ (0 0247 uglmL) to in l C std COrreCl U'IOTS
FOSA = Perlluomoclmer inamide
ncwLOQisO0198uglmL LACOU19I01
FOSAA = Perfluomoctul fonamidaacetate
A -data is abave the UDM limit ofaumtitation and is vmvidcd as an estimate
EtFOSE = Narmw Range N-Ehyl Pcrfluomoctanesulfonamidoethyl alcohol
M556 = C8Fl7SOZN((H)CHZC00)
PFOSEA = Pcrfuomoclmcsulfonyl elhylmide
RSD Sld. Dev.
MSMSD RPD
41 2 2 71
27 5 I 39
NA NA
NA NA
Date EnteredlBy. Date Verified/ By Purily EnleredNerified
03106100,03110100,03/ZO/W,03/21100.4/I5/W, 5/16100,06/13/00. 6115/00.6119/W. 06/22/00. 06123100, 36126/00.08/15/W, 09/05/0l). 10117100LAWCSH 04/30/01 hoj /04/30101 LAC 02119101 LAC
3M EnEETxvcSe-li89-r57oI nmental Laboratory
Sera Week IO5 (3) TOX-001-sera-212-1IN XIS
Page 245
3M Medical Department Study: T6316.1
AMDW 092597.1 Covance# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Study Fmducl Number(Tes1 Subslance). MZlriX
MethodRevirion Analytical quipmcnt System Number: Instrument SoflwarrNersion: Filename. R-Squared Value.
Slope: Y-lntereepl' Dales of EmactioniAnalyn Dales 01AnrlyddAnalyst:
Dale of Dala ReductiodAnalyst.
Sample Data
WEEK 105 RAT SI
Gl0"P
Sample #
Group 4 Mid-High Dose
IWmgkg
Croup 6 Mid-High Dose
RCC0"eV IW mgikg
CWMM C90908M C90910M C90911M C90916M C90926M CW27M C90928M W33M CWMM C90947M CW948M C90953M C90955M C90956M C90965M C90968M
C91315F C91324F C91327F C91332P C9133SF C91336F C91338F C9134OF C91341F C91342F C91356F C91357F C9I3M)F C91361F C91362F C91372F C91376F C91378F C91380F
C91M7M C91054M C91056M C91060M C9106SM C91070M C91071M C91072M C91073M C91076M C91451F C91453F C91455F C91459F C91462F C91467F C91473F C91479F C9148OF C9148SF C91487F C91488F
104 Week Dietary Carcinogenicity Study wih Narrow Range (98.1%) N-Ehyl Pem,orooetvlcsulfonamido Ehilool in Rae
T-6316 (ElFOSEeH) RaI Serum ETS-84 I & ETS-8-5 I Saup020199,Davey070799 Maslynx 3.3 & 3 4 See Below See AuachmenS See AUachmenS See Anachmenls 021071W. 02/08/00. 02109100 RWW. SAL 021181W, 2128100, 03127100, 051311W. 06119100. 06120iW.08103100, 08116/W, 08123.W W A S
02121/W,02129/00, SIOZIW, 06/02/W.06/2OlW.W211W.081071W. 08118lW. 08125.00 MMHAAS/HOl
Box W-009 lo1 529
PFOSEA Purity Correction
Unknown U"kn0Wn U"kn0W
U"kn0wn Unknown
Snrrogatc
PFOSEA
Verlfled
Dllntlor
Factor
NA
I
NA
I
NA
I
NA
I
2nd Analysis OK
I
NA
I
NA
I
2nd Analysis OK
1
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
1
NA
I
NA
I
2nd Analysis OK
1
NA
1
NA
I
NA
I
NA
I
NA
I
NA
I
NA
I
NA
1
NA
I
NA
I
NA
1
NA
2nd @alpis OK
NA
2nd Analysis OK
NA
2nd Analysis OK
NA
NA
NA
NA
I
NA
I
NA
I
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
I
NA
I
NA
1
NA
I
NA
I
NA
I
NA
1
NA orrecled PFOS LOO 1
riGzI Eaz
new LOQ is 0 0198 u>mL LAC 02119101
A. data is above the upper limil of quvllitalian
0.W OW OW 0.04 OW 0.W 0.W 3.75 OW OW 4 02 6 88 0.00 I85 0.320 OW OW OW OW I72 OW 2 40 I61 OW 0610 6 20 104 OW
0 00 OW OW OW OW OMX) OW OW OW OW
OW OW OW OW OW OW OW OW 000 OW 0.W OW rtd correction
aod is provided I
A080300018
A080300027 A08030W28 A080300031 A080300032 A080300033 A08030W34 A080300035 A080300038 A080300039 D0816W047 A0803W041 A0803W042 A0803W045 A0803W046 A0803W047 A0803W048 A0803W049 A080300052 A080300053 A080300054 A080300055 A080300056 W816W048 A0803WOMI W8 I6oW5 1 A0803MH)62 W81600052 A080300066 A061900022 A061900023 A061900026 A061900027 A061900028 A061900029 A061900030 A061900033 A061900034 A061900035 A061900036 A061900037 A061900040 A06190004I A0619W042 A061900043 AM19000M A0619ow47 A061900048 A0619W049 A061900050 A061900051 lOrS
an estimate
-- co,,cm1ration
-- or PFOSEA "gl"lL or % Rce cLOQ (0.00492 ug/mL) cLOQ (0.00492 ugimL) <LOQ (0 00492 ug/mL) <LOQ (0.00492 ug/mL) <LOQ (0.00492 ugimL) <LOQ ( 3 00492 ugimL) CLOQ (1 00492 ug/mL) <LOQ (I)w492 ug/mLl <LOQ (I) 00492 ug/mLl <LOQ (000492 ug/mL) <LOQ (0.00492 u&L) <LOQ (11,00492 ug/mL) <LOQ (1100492 ug/mL) cLQQ ( 0 OM92 ug/mL) <LOP (ll.W492 UgimL) <LOO (11,00492uglmL)
(I w 6 8 8 cLGQ ((I 00492 ugimL) <LOQ (000492 ugimL) <LOQ (11 00492 ugimL1 <LCQ ([I 00492 uglmL) cLOQ (11 00492 ugimL) <LOQ (CI 00492 ug/mL) <LOQ (C 00492 ugimL) <LOQ (C 00492 ug/mL) cLOQ (0 00492 ug/mLl <Log (0 W Y Z ugimL) <LOQ (0 00492 UgimL) <LOQ (0 00492 ugimL) <LOQ (0 00492 ugimL1
0 w620
-- <LOQ (0 OM92 ug/mL)
<LOQ (0 OM92 ugimL) cLOQ (0 00492 ug/mL) <LOO (0 00492 ugimL) <LOQ (0 00492 u&L) cLOQ (0 00492 ugimL) <LOQ (0 00492 ug/mL) <LOQ (0 00492 ug/mL) <LOQ (0 00492 ug/mL) ELOQ (0 00492 ugimL)
-- <LOQ (0 00492 ug/mLl
<LOQ (0 00492 ug/mL) cLOq (0 OM92 ugimL) cLOQ (0 00492 ug/mL) <LOQ (0 00492 ug/mL) <LOQ (0 w492 ug/mL) <LOQ (0 OM92 ug/mLl <LOQ (0 00492 ugimL1 cLOQ (000192 up/rnL) cLOQ (0 00492 u&L) CLOQ (0 1x492n@mL) <LOQ (000492 UgimL)
-- cLOQ (0 w492 ug/mL)
cLOQ (0 30492 ugimL1
Average PFOSEA
UgllnL <LOQ
<LOQ
RSD Std. De". M W S D RF'D
NA NA
NA NA
NA NA
NA NA
Date EnIerediBy. Dale Vcnfiedl By: Purity EnImedNcrified.
03106lW. 03110iW. 031201W, 031211W.41151W. Sl16/W. W131W. 611SlW. 6/191W, 06/22100.06123/W. W26,00,081151W. 091051W. IO! 17/00 LAWCSH MI30101 hoj 104130101 LAC
02119101 LAC
3M EnEExTvcSe-li89r-57.o1 nmental Laboratory
Sera Week 105 (3) TOX-001-sera-212-1IAI XIS
Page 513ll2W I 246
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Study Roducl Numbcr(Tes1 Substance)' MauiX
104 Week Dietary Cvcinogmicity Study with N m w Range (98 I%) N-Ethyl Pemuomoclviesulfonamido Ethanol in RIIS T-6316 (EIFOSEOH) Rat Serum
MethodiRcvision.
ETS-84.1 & ETS-8-5.1
Analytical Q u i p m e 1 System Number
Soup020199,Davey070799
lnsuument SaRwardVcnion: Filename. R-Squared Valuc.
Masslynx 3.3 Br 3.4 See AttaehmmU See Auachmmet
Slope.
See Atwchmcnts
Y-Intercept. Dates o f ExhactiodAnalysI-
See Attachmenet 021071W, 02108lW. 02/09/00 RWW, S A L
Dates of AndysisiAnalyst
02118100, 2/28100,03127100, 05131/00,06119100, 06120100,081031W.081161W,08/23/00 MMHllAS
Dale of Data ReducliodAnalvst.
02121100,02/29100. 3/02/00. 06102100, 0612OlW. 06121100. 08107100, 08II8100. 08125100 MMHilASlHOJ
Sample Data WEEK 105 RAT SE
Group 4
Sample X C90904M
Conceatration of PFOS
mglmL or % Rec 66 9
- Avcragr
PFOS IIglmL
RSD Std. De". MSIMSD RPD
Concrntrrtian of PFOSA
tlglmL or % Ree
0 568
AWP@ PFOSA uglmL
RSD SId De".
MSIM?
Mid-High Dose
C90908M
71.0
0 606
100 mg/kg
C90910M
313
I84
C90911M
146
0 607
C90916M
88.4
0.612
C90926M
61.61
0 330
C90927M
22.0
I09
C90928M
127
0 979
C90933M
45 8
C90944M
136
0 593 0.560
C90947M
144
0.685
C90948M
51.7
0 277
C90953M
13.0
0 572
C90955M
MI
C90956M
132
0614 0 390
Gloop 4
C90965M C90968M C91315F
- 137
53.6
100
84.6
45 4
122
0 949 0 638 0.898
0 701
519 0 %1
Mid-Htgh Dose
C91324F
133
1.91
C91327F
9 81
I .02
C91332F
251
A
1.36
C91335F
99.5
2 05
C91336F
202
A
I07
C91338F
I 40
1.71
C91340F
252
A
0 721
C91341F
76.0
I38
C91342F
122
0 826
C91356F
6.18
0 345
C91357F
200
A
2 01
CY l360F
141
I85
C91361F
131
I16
C91362F
25.3
0 720
C91372F
58.8
I61
Graop 6
C91376F C91378F C91380F
C91047M
133 IO9 104
0 185
- 122
57 9 70 5
I 93 I17
cLOQ (0 OM93 UgimL)
Mnd-High Dose
C91054M
0.0222
.LOQ (0 00493 "g/"lL)
Rccavery I00 "@kg
C91056M C91060M
1.18 0 142
CLOQ(0 00493 up/mL) :LOQ ( 0 OM93 u&L)
C91065M C91070M C91071M
:LOO (0 0198 ug/mL) 00514
:LOQ (0 0198 ug/mL)
cLOQ (0 00493 ug/mL) CLOQ(0 00493 ug/mL) CLOQ(0 00493 uglmL)
Group 6 Mid-High Dose
C91072M C91073M C91076M C91451F C91453F
0 0454 ZLOQ (0.0198 UglmL)
0 592
5.02 I68
- 0 227
166 0.377
rLOQ (0,00493 ug/mL) cLOQ (0.00493 ug/mL) cLOQ (0 00493 u&L)
:LOQ (0.00493 ug/mL) :LOQ (0.00493 ug/mL)
--NA NA
Recovery 100 mglkg
C91455F C91459F
5 92 :LOQ (0.0198 ug/mL)
:LOQ (0.00493 ug/mL) :LOQ (0 OM93 ug/mL)
C91462F
C91467F
C91473F C91479F
4.61
0.0207 3 84 :Lop (0.0198 ug/mL)
:LOQ (0 OM93 ug/mL)
ZLOQ(0 W493 ug/mL) rLGQ (0 00493 Ue'rnL) :LOQ ( 0 00493 ugimL)
C9148OP
0.0553
:LoQ (0.M93 uglmL)
CY1485F
3 55
rLOQ (0.00493 ug/mL)
C91487F
ZLOQ (0.0198 u&L)
96 3
:LOO (0.00493 up/mLl
N, !
C91488F
4.16
2.41
2 32
PFOS = Pcrfluorooclanesul ate PFOSA = Perfluorooctanesulfonvnide PFOSAA = Pc~uorwetanesulfonimidoacctlte
cc :led PFOS mL new LOO is 0 019 A - damis above U
(0 0247 ug/mL) I
EtFOSE = Narmw Rangc N-Ethyl Pemuomctancsulfonamido ethyl alcohol
M556 = C8F17S02N((H)CH2C00)
PFOSEA = Perfuorooctane sulfonyl cthylamide
Dale Entcred/By Dale Verified/ By Purity EnIerediVerified
03106100, 03110100,03120100,031211W,4llSlW. 5116AW. O6113lW. 61lSIW. 6119100,06/221W. 06123100. W26/W, 08115l(IO. 09lOSlW. 10117lW LACICSH 04130101 hoj I04130101 LAC 02119101 LAC
ConerntrPllon 01 PFOSAA
mglmL or %e Rec
6 58 7 68
33 6 23 7 8.8 I19 964 I6 5 6 69 14.0
8.7 4 19 5 58 10 3 3 55 12.6 8.63
IO 2 I1 4 I8 8 18.4 10.0 I1 2 10.6 11.1 I1 I 11.9 6 02 11 2 I3 8 7 76 12 5 I3 4 I3 0
1,.,0_.93 ,
LOQ (0 0248 ug/mL) LOQ (0 0248 ug/mL) LOO (0 0248 ug/mL) LOQ (0 0248 ugimL) LOQ (0 0248 uglmL) LOQ (0 0248 ugimL) LOQ (0 0248 ug/mL) LOO (0 0248 ug/mL) LOQ (0 0248 ug/mL) LOQ (0 0248 ug/mL)
0 03 LOQ (0 0248 ug/mL) LOQ (0 0248 ug/mL) LOQ (0 0248 uglmL) LOQ (0 0248 uglmL) LOQ (00248 UgimL) LOQ (00248 us/mL) LOQ (0 0248 ug/mL)
LOQ (00248 ug/mL)
LOQ (0 0248 ug/mL)
LOQ (0 0248 ug/mL) LOQ (0 0248 ug/mL)
RSO Std. De". MSIMSD RPD
- IO 7
MI
7 91
25.4 3.02
NA NA
NA NA
3M EnEETxvcSe-il89-r57.o1 nmental Laboratory
Sera.Week 105 (3) TOX-WI-scra-212-IIAI XIS
Page SI3112wI 247
3M Medical Department Study: T6316.1
AMDW 092597.1 Covancel) 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Study Pmducl NumbcNTest Substance).
104 Week Dietary Carcinogenicity Study with Nmow Range (98 I%N)-Ethyl Pnfiuorwclanesulfonmido Ethanol in Rats T-6316 (EIFOSEOH)
Matrix: MethodiRevision Analytical Equipment System Number InSUumcnt SoRwarcNcrrion. Filename R-Squared Value. slope: Y-lntercepl Dates of ExUactiodAnalyn. Daln of AnalysidAnndysl
Rat Semm ETS-8-4 I & ETS-8-5.1 Soup 020199. D a v q 070799 Masslynx 3.3 & 3.4 See Below See Attachments See Allachmentr; See Attachments 02/07100,02/08100, OZlO91W RWW. SAL 02118100, 2/28/00, 03121100, 05/31100,06119100,06/20100. 081011100, 08116100, 08/23/00
MMWlAS
Date of Data Reduetionihalyst
02IZllO. 02129lW. 3/02/00, 06/02/00, 06120100, 06121100, 08107100,08118100. 08125100 MMWlASfllDJ
Sample Data
BOX 00-009
WEEK105 RATSE
ClOUP
DOSC
Sample #
Corncentration of EtFOSE-OH uglmL or % Ree
Average EtFOSE-OR
ughL
RSD Std.Dw. MYMSD RPD
CO"Ce"t*atiO" 01M556
aglmL or Rec
Group 4
C90904M
:LOQ (0 00971 ugirnL1
6.46
Mid-High Dose
C90908M
00126
7.66
. WQmgkg
C90910M
0 0816
14 8
C90911M
cLOQ (0 00977 ug/mL)
6.10
C90916M
0.0221
5.99
C90926M
:LOQ (0.00977 udmL)
641
C90927M
00164
8.24
C90928M
0.0227
6 94
CSil933M
0.0112
8.99
C90944M
0 01I6
4 IO
C90947M
cLOQ (0 00971 ugirnL)
4.16
C90948M
:LOO (0 00977 ug/mL)
5 38
C90953M
00217
4 01
C90955M
0.0154
8.71
C90956M
:LOQ (0.00917 ugimL)
3.45
crollp 4 Mid-High Dose
C90965M C90968M C91315F C91324F C91327F
0.0197 00164 0 0672 0 0344 0.0290
93 3
4.21
0.0182
00170
6.21
6 35
421
3.20
41 I 8 2 71
C91332F
0 0312
5.76
C91335F
0.0562
5.70
C91336F
0 0300
1.53
C91338F
0.0274
6 08
C91340F
0 0101
3.88
C91341F
0 0436
5 05
C91342F
0.0337
6 18
C9 I356F
0 0178
2.10
C91357F
0.0335
6 25
C913M)F
0.0573
4M)
C91361F
0 0459
3.05
C91362F
0.0170
5.12
C91372F
0 0467
606
C91376F
0 0408
6.20
C91378F
0.0424
40.0
3.76
27.5
C91380F
0 0270
0 0364
0.0145
5 I2
1 xq
Group 6 Mid-High Dose
RCCOWIY
100 m g i g
Croup 6 Mid-High Dose
Rccovery loomfig
C91047M C91054M C91056M C91060M C91065M C9 I070M C91071M C91072M C91073M C91076M C9 I45 I F C91453F C91455F C91459F C91462F C91467P C91473F C91479F C91480F C91485F C91487F C91488F
:LOQ (0.00977 ugimL) :LOQ (0 00977 ugimL1 :LOQ (0.00977 ugimL) :LOO (0.00977 ugimL) :LOQ (0.00977 ug/mL) :LOQ (0.00977 ug/mL) :LOQ (0 00977 ug/mL) .LOO(0.00977 udmL) LOQ t0 00977 up mLj
, IOQi000977ugmL,
LOO 0 00977 "I rnl L& (0 00977 ug/mL) LOQ (0 00977 ug/mL) LOQ (0 00977 ug/mL)
LOQ (0 00977 ugimL1 LOQ (0 00977 ug/mL) LOQ (0 00977 u&L) LOQ (0 00977 Ug/mLl LOQ(0 OW77 ug/mL) LOQ (0 00917 ug/mL) LOQ (0 00977 ug/mL) LOO (0 00977 ug/mL)
<LOQ
LOQ ( 0 00494 ugimL)
LOQ (0 00494 ug/mL)
LOQ (0 00494 ugimL)
LOQ (0.00494 ug/mL)
LOQ (0.00494 ugimL)
M Q (0 00494 ug/mL)
LOQ (0 00494 ugimL)
LOQ (0 00494ug/mL)
NA
LOQ (0 00494 ugimL)
NA
LOQ (0.00494 ugimL)
-OQ(0.00494 ug/mL)
BQ(0.00494 ue/mL)
LOQ (0 00494 ug/mL)
LOQ (0.00494 ug/mL)
-OQ(0 00494 ug/mL)
LOQ (0 00494 ug/mL) LOQ (0 w494 "g/rnL)
-OQ(0.00494 ug/mL)
&Q (0 00494 uglmL)
LOQ (0 00494 UgIrnL)
NA
-OQ(0.00494 ugimL)
NA
B Q (0 00494 ugimL)
--
NA NA
WC
,naniide fonaniidoacelale EIFOSE = Narrow Rangc N-Ethyl Pcmuorwclanesulfonamido ethyl alcohol
,mated PFOS LO
-new LOQ is 0 0198,
A data is above the
0247 ugimL) 10 inelud L LAC 02119101 cr limit ofquantilalian and is provided as an estimate.
M556 = C8FllS02N((H)CH2C001 PFOSEA = Pcrluomwtane sulfonyl ethylmide
Conerntrltio" of PFOSEA
cLOQ (0 00492 ugimL) <LCQ (0 00492 ugimL) <LOQ (0 00492 ugimL) <LOQ (0 00492 ngimL) < L o 9 (0 00492 ugmL) <LOQ ( 0 00492 us/mL) CLOQ (0 00492 ugimL) (LOQ (0 00492 u&L) <LOQ (0 00492 ug/rnL) cLOQ (0 00492 us/mL) < M Q (0 00492 ugimL) <LOQ (0 00492 UgimL) cLOQ (0 00492 UgimL) <LOQ (0 00492 ug/mL) <LOO (0 00492 udmL) < L (0 ~00492 u&L) <LOQ (0 00492 UdmL) <LOP (0 OM92 u&L)
0 00688 cLOQ (0 00492 uglmL) <LOQ (0 00492 ugimL) <LOQ (0 00492 ugimL) <LOQ (0 00492 u&L) <LOQ (0 00492 ug/mL) (LOQ (0 00492 UgimL) <LOQ (0 00492 ug/mL) <LOQ (0 00492 ugimL) <LOQ (0 OM92 ug/mL) CLOQ (0 00492 ug/mL) <LOQ (0 00492 uglmL) ELOQ (0 00492 ugimL) <LOQ (0 00492 ugirnL)
0 W620 <LOQ,O00492upmL, cLOQ 0 00492 ug mL,
<LOO i0.00492 &Lj <COQ (0 00492 u&L) cLOQ (0.00492 UgimL) CLOQ (0.00492 UgImL) ELOQ (0 00492 ug/mL) cLOQ (0.00492 UgimL) ELOQ (0.00492 ugimL) cLOQ (0.00492 UgimL) cLOQ (0 00492 uglmL) :LOQ (0.00492 UglmL) CLOQ (0.00492 ugimL) <LOQ (0.00492 UgimL) CLOQ (0 00492 ug/mL) FLOQ (0.00492 u&L) CLOQ (0.00492 ugimL) CLCQ (003492 up/rnL.) :LOQ (0.00492 ugirnL1 <LOQ (0.00492 ug/mL) :LOQ (0 00492 ug/rnL) :LOP (0 00492 up/mL) :LOQ (0 00492 ugirnL)
Average PFOSEA
odmL
<LOP
RSD Sld. De". MYMSD RPD
NA NA
NA NA
NA NA
NA NA
Date Elcredkly. Ddle VWifiedI By Purity EntcrcdNerified
03106100, O3/10100,03120lW,03/21100.4115/00. 5llWW. 06113lW. Wl5100. 6/19/00. 06122100,06123100. 06126100,08115100,09,05100. 10117/00LAWCSH 04130101 hoj 104/30/01 LAC 02119101 LAC
3M EnEETxcvSe-l8i9-r57oI nmental Laboratory
Sera Week 105 (3) TOX-MII-srra-212-IIAI.rls
Page 248
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance 6329-212
EEK4 RATLIVERREWORK
Lot 193
C90753M
09999
NA
C10775M
I0586
NA
C91135F
1012.
NA
C91111F
IO380
NA
C91165F
I0175
NA
C91169F
I0177
NA
C9ll7lF
1-
NA
tiW"p2
CW789M
1.0591
NA
Low hII
CW814M
I0571
NA
30m p ~ ~
CW817M
I om
NA
CW831M
I UIl8
NA
CWSJIM
I0749
NA
C91198F
I0531
NA
C9lWJF
10651
NA
C91222F
I0183
NA
C912JOF
,0433
NA
0 9275 0 9271 09275 0 9275 0 9275 0 9275 0 9175
0 9275 0 9275
u 9275
0 9175 0 9175 0 9175 0 9171 0 9171 0 9275
Unknown Unhown Uokmwn Unhown Unhown Unhown Unknown
Unknown Unknown Unknown Unknown Unknown uoknown unknma Unknown Unknown
721
I
60398015
%3
I
60398046
221
I
60198050
284
I
603PSOJI
631
I
60398051
151
1
60398053
61
I
60398054
115
LM
60198111
120
IW
60538113
10487
10 5
112
IW
60598114
11723
I, 7
_ _ 169
lW
60598115
ISUll
I5 0
,lo
IW
60598116
11069
125
100
60598119
,1027
110
IW
60598120
9588
116
100
60598121
11282
106
IW
60598122
9412
941
13116
13 k
61510
6 15
86362
86 4
110931
111
121385 I
111
I91929
91 9
118167
138
151195
I51
118159 I
I18
167159
102805
163867
M
211647
169257
169
,19299
119
mom I
221
2,3655
92711
I91685
391682
MI557
691925
559479
559
557635
558
179688
380
17 I
113
I91
I
I
1 I 21(I
110
25 1
I
I
159
268
53 1
I
I
499
Analytical Report: FACT-TOX-001 LRN-U2103
60598099 60598100 6059810, 60598101 60598105 60598106 60598107 60598108 6059BIW
0 670 0 636 0635 a651 0761
I
839
(10572
MOW298059
MUW298060
Mwo298061
M07W9813 I
M0709981k
M07WP815
M07W9816
M07w9817
MOIW9810 MOIW9821
I
MU7099811
7099827 7099828 7099819 705983U 7099831 7099831 '099835 7099836 7099837 7099838
4761
5564
7036
9841
I
6639
8712
13084
9543
7302
1162 6181 11518 13154 11165 15517 18156 16151 11645 11836
6 60 5 93 741 4 16 5 57 7 04 9 81 6 61 8 72 13.1 9 5, 7 30
131 115 155
162 146 111
6 81
176
6 I4
108
1
1
114
9s i
133
56 5
8 94
5 05
IS I
I5 3
231
3M
Environmental ETSI-7 0 Ex-197
Laboratory
Page 249
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance 6329-212
Sample Data
C0.bol GTavD I
REWORK s.mph L
H20 Blk-il H20 BU-2 hbbil Lluwl3lk-l U b i , Livrr Blk.2 C90719M-MS" C90719M-MSD CW719M" CW725M C90732M C90753M C90775M C91115F CPII4IF C91165F C91169F C9ll7lF CW789M CPo811M C908I7M CW833M CW83kM C91198F
FUlrm
QFOSAA Cnk. C.n.
"8k
W39SUl4
385
61198056
ow
60398015
ow
61298017
OW-.-
60398041
131
60398113
I34
60398121
51 5
60398013
I05
I
60398011
143
I
6039800
I51
I
60398M6
119
I
60398050
113
I
6039805I
779
I
60398051
161
I
60398053
79.8
I
60398054
I15
IO
60598140
1087
IO
60598141
I9M
IO
60598142
18k6
50
60598129
9731
10
60598144
2528
10
60598147
7681
10
6059814%
1751
10
64598149
3893
64598150 M59815l
1123 4320
90298049
97855
Po298050
54290
::: 90298051
549uI
IO 9
902980Ji
19263
90298051
59731
596
90298057
46021
46 0
W298058
93774
93 8
Po298059
25750
902980W 90198061
41154
mu6
M01099819
54589
MO7099811
M194
M07099815
,1108
M07WPB16
88123
M07WPII7
56911
M07WY810
49148
MO70998ll
5368k
M07WP829
Analytical Report: FACT-TOX-001 LRN-U2103
- EtFOSE EtFOSE
C.W.
D(lut*O
9b 32 5
F.UW I
OW
I
OW
I
- .- OM
I
19,
I
133
I
ow
I
OM
I
OM)
I
30 7
I
0.w
I
ow
I
ow
I
ow
I
- ow
I
ow
I
21 5
I
ow
I
ow
I
- ow
I
ow
I
ow
I
ow
I
69 2
I
- om
I
OW
I
128
I
45 7
I
6ko
I
117
I
_ _ 79 6
I
513
I
Po298072
5, 3
49 I
I
W198073
49 I
448
I
- I , 'I
I
33 9
I
656
I
90298075
41 9
90298076
33 9
167
I
328
I
90298081
324
449
I
90298082
422
432
I
Po198081
425
610
I
161
I
151
I
- 124
I
117
I
375
I
496
I
1127
I
- I M 5
I
551
I
926
I
1459
I
751
I
- 364
I
90298105
361
371
I
90298106
166
00513 00491 00419 0 0339 0 324 0 122 0 125
0361 0 366
00442 0464
15 4 OW82
33 I 0 I54
"762
58 2 0 143
3M Environmental Laboratory
Page 250
3M Medical Department Study: T6316.1
AMDT# 091597.1 Covrnce 6329-211
Analytical Report: FACT-TOX-001 LRN-U2103
I
Grows
- PFOS
C-k.Cmc.
1u'I
ll5
C90719WMSD C90719M"
OM
~
I PI
ow
- 233
223
- 728
C90725M
647
C90712M
980
CW753M
670
C'H1775M CPlllSF
841
~
203
CPllllF
25,
C9116SF
564
C9116PF C91171F C9078PM
.02
- 418 12658
C90811M
10487
C90817M
11723
CPO833M
lSOll
C90834M C91198F
12069
~
Ila27
C91205F
9588
C91222F
13282
- C9l2lOP
9.11
C91117F
13.26
131
C90846M
6,520
64 5
C90851M
86362
86.
C90866M
110931
Ill
CW890M
109767
110
C90891M C9125IF
~ 108824 99011
C91272F
,21315
C91285P
91929
91 9
- CP1117F
1111167
138
C91191F
151495
151
C'Hn35M
128159
128
CW939M
167259
167
CW942M
202805
203
C90%1M
263167
264
CWP66M
2,164,
211
~
C91316F
169217
169
C91317F
4,9299
C91333F
22-
C913LSF C91350F C90981M
2.3655
- 92721 191685
CILOO5M
391682
C91024M
661557
662
C91033M
691925
692
C91037M
559179
559
~
C9L423F
557635
558
C91127F
379688
380
C91A3"F
,88915
489
C91443F C91448F
- 816358 740764
rnl& mmidoaceYh
113
I91
21 2
721 7%l 5083 7159 7276
(I 712 7% 5 08 7 16 7 28
,761
176
II 0
5566
5 57
110
25 3
7036
7 04
9841
9 84
6639
6M
8722
8 72
26 8
13084
13 1
I99
53 2
9543
9 54
I
I
I
I I
73"Z 10851
I I
7 30 109
1362
I36
6181
6 IS
11518
115
41 7
13154
132
499
208
11465
115
15517
I55
18156
182
16152
16:
- tI
682
I
b00571 159 108
-97855 50940
I 39263 I 59731
46022
93771
33108 88123 56911 49148
0 161 0 0798 0 115
2 09 I94 I85 9 13 2 53 761
ow
19 2
ow
0 0995
0 "390
ow
22 1
ow
ow
94 4
ow
3 63
3 42
ow
I
I
I
000
:I 1 1 ; 393
59 7
396
22 6
79 6
.6 0
511
91 8
49 I
25 8
:t:
618
::: 44 8
506
16 8
13 1
324
88 I
41 2
36 9
53 I
219
425
49 3
620
53 7
170
I I I 536
NA
738
283
NA
32 I
52 5
149
135
79 2
I
I
I 372
79 6
85 7
20 4
83 9
914
31 7
1128
29 6
739
I49
63 5
161
106
80 I
509
166
OOIlP 00339 0683
NA 0 321 0421 0 425 0620 n270 *A NA 0 235 0 372
of0 516
0914
0 719 0361 0 366
0 0442
I54 0 w682
33 I
0 464
0 I54
I
I
I
I
j 56 7
0 375
0213
I
I
47 5
0 70,
10335
0 762
"58 2 443
3M
Environmental ETSI-7 0 F X C d 97
Laboratory
Page 251
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Study Product Numkrflest Substance) Ma& MelhodiRWlSlO" Analpica1Eqwpllenl System Number Lnsvwnenl SoRwareWenion Date ofExVacttOniAnalyS1 Date ofAnalyslslAnalylt Date oflhta ReduEt~onihlyst
Sample Data
104 Week Dietary Carcmogenicq Shldy w P &'arrow Range (98 1%)
7-631 6 W O S E O H ) Rat LlVer FACT-M-I 0 & FACT-MJ 0 rewotked uine ETS-8-7 0 Cluck 080697 and Madeline 041098 MassL,m 2 3 and 3 I 06/01/98 RWWIOK 06112/98.06114/98.06/18/98.09102198 HOliKJWLAC 03116100, l1129100, 12/Ol/W, l2/101W IASMMHJKJH
06/14/98 Lot 193 Ohil8/98.12/29/98 K-Ehvl P e r f l t m m t m e s u i i o n d o E h o l rn Rats
Filmame R-Squared Value
Slope Y-Intercept
b r Llst 10 hghl See Atllfhmenl~ Set Attachments Sea Attachments
Filenames
Blb G'p 1 Crp 5 M$MSD
06/12/98 LotL-2353 09/02/98 Lot L-2353
06112/98 Lo1617 06118198 Lot 617
PFOS
PFOSA
M06189834-35B6041 A90298W2-3 & 116-117
06189852.57, I22998069-7+?3298019-31
61498013-24
I 22998041-52
61298127-128
61298127-128
06/12/98 Lot936 09/02/98 Lot 936
PFOSAA M06189834-35 &a41 06189845.57 122998055-66 61298127-128
EtFOSE
Dilutions
A90298002-3 & I l l , 111, I l l . Ill
IxI298019-31 111, Ill, 14, 111
need I l O & l IIIWW, l/lW, 1/1ooo, 1/10
90298110-111 n e e d l 5 & l , l i l , I / l , 1 / 1
HZO Bk-1 HZ0 BIk.2 Rabbit Liver Blk-l Rabbit Liwr Blk-2 C90717M-MS C90717M-MSD
C90717M C90718M c90737M c9075m C90769M C91126F C91140F C91145F C91162F C91163F
C90971M C90972M C90988M C90996M C91017M C91393F C91394F C91404F C91415F C91438F
Inilia1 WI. I
loo00 1WW I0080 I 0080 I0248 I0248 I0455 10268 1 0434 1 W89 1.W83 1 0205 I0265 10128 10160 10162 10129 I 0204 10108 10128 10116 1 0247 I0126 10149 I0244 10230
Total Mass of Liver
I NA NA 40 13
40 13 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
4/13/00, 5124/00CSH I2/lYWMMH 12/28/00 hoj (list a122998a) 12/26/00 LAC
PFOS Sld Correction
Fsrlor 0 9275 0 9275 0 9275 0 9275
NA NA 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9215 0 9275 0 9275 0 9275 0 9275 0 927s 0 9275
Lot 193
PFOSPurih I
corrrrtian Factor
UnknOUn unknown unknoun
NA NA UnknOUn UnknOWn UnknOWn UhWl UnknOHm unknown unknown
UllkllOUn unknown ClnknOwn UnknOUm UnknOWn UnknOWn
UnknO\*n IlnknOwn unknown unknown Imnknoun LlnknOW 1inknnm
PFOS
w s C0"C.
47 4 OW 33 I 1153 959 313 222 307 218 I24 270 383 558 1198 M5 137 122 136 97.3 906 96 5 103 I12 116 IS7
I PFOS
PFOS
FilmnllX
Dilullan
CdC. cone.
Fmbr
WE
OW
61298056
I
43 9
122998002
I
OW
61298057
I
30 4
122998W3
1
-1584
61298127
I
-1773
61298128
10
2776
122998073
10
2004
122998072
10
2731
122998071
10
2002
122998070
IO
I144
122998069
I
245
6189852
I
346
6189853
1
511
6189854
1
1094
6189855
1
552
6189856
IWW
1250280
61498013
IWW
1111564
61498014
two0
1249941
61498015
loo00
890177
61498016
two0
830679
61498017
IWW
873644
61498020
IWW
945819
61498021
IWW
1027570
61498022
IWW
1054710
61498023
IWKC
1423345
61498024
Icalibrationm m ,estimated value
+ CCV's failed. &la enteredas estimated
"confirmed low on 90298
++ Qualitauve data only
conrrntmuan or PFOS
wvg or *ARec. <toQ(0 0110 "pip) <LoQ (0 112 U ! 3 w <toQ(0 0110 "pig) <roQ(oll2"pig)
-1331% -14Wh
2 78 200 2 73 200 114 0 245 0 346 0511 I09 0 552
1250 1112 1250 891 831 874 946 1028 IO55 1423
M-0 PROS uvs <LW
LoQ -1410%
2 13
0 549
1067
1065
RSD Sld. Dw. MYMSD RTD
NA NA 11%
31 3 0 668
59 8 0 328
18 5 197
20 0 213
Ers-8-7 0 Exel 97
3M Environmental Laboratory
Lw Week 8 Rework T0X-W I -liver212-100 XIS
513112001
Page 252
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
study Sample Data
104 Week Dietary CarcinogenicityStudy w t h Narmw Range (98 1%)Y-Elhyl Perlluomtanesulfonamldo Ethanol m Rats
T-6316 (ElFOSEOH)
RaI Lwer
FACT-M-I 0 & FACT-M-2 0 reworked usmg ETS-8-7 0
Filnume
See LlS110 Rlghl
Chick 080697and Madclme 041098
R-Squarrd Value See Atrachmenct
MasrLym2 3 and 3 1
slaw
See Atrachmenct
06101198 RWWIOK
Y-Intercept
See Attachments
06112198,06114198,06118198,09102198 HOJiKlHiIAC
03116100, 11129100, I2lOllW, l Z I l O i 0 0 I A W M W H
WEEK 8 RAT LIVER REWORK SPrnPl. x
Method B L M a m Blk
H2O Blk-1 H2O Bk-2 Rabbit Lner Blk-1
l o t L-2353
PFOSA h"ly corrrrtion FWor
C90717M-MSD
0 0 mgilrg
c90737M C90756M
Gmup 5 wgh Dose
C91140F C91145F C91162F C91163F C90971M C90972M C90988M
C91017M
C91393F
UhUm
C91394F
C91404F
Unknown
C91415F
unknown
C91438F
PFOS = Perfluomamesulfonate
PFOSA = Perfluomoctanesulfnnamlde
PFOSAA - P e r f l u o ~ ~ t a n e s u l f o - d ~ ~ l ~ t ~
ElFOSE = N m w Range N-Ethyl Perfluomaranesulfonamldoculyl alcohol
- C0"C n#i 00
- 6 6 3 00
41 8
- 83 4
65 4
- 33 8
196 35 2 31 I
- 10 I 10 4 10 4 12 7
- 35 0 I5 2
I% 191 191 211
- 185 I54 142 I74
- 142 I77
- PFOSA - DiluUOn
FnCtOr
I I ~
I
- - I I I
I I I I
- I I I I
- 1 1
100 1W I00 IW
- 100 IW IW 100
- I 0 0 100
41 4
19353 18747 18897 20877 14071 17148 13844 17272
Conrcntmtlon o f PFOSA
uyg or % Re.
61298056
<LCQ(00119ug/g)
122998002
00663
i
61298057
<toQ(OO119ugig)
12298003
0.0414
i
61298127 61298128
40%
26%
*
0 0324
4toQ (0 0302 "gig)
0 0337
C L I X (0 0302 "gig)
ctoQ (0 0302 uglg)
ctoQ (0 0302 uglg)
C t O Q (0 0302 "gig)
<toQ(0 0302 "gig)
90298030
0 0344
ctoQ (0 0302 "gig)
12298045
194
I2298044
I8 7
12298043
I8 9
12298042
20 9
18 3
150
12298051
14 1
12298050
17 I
12298049
13 8
12298048
173
'calibration range. estm + CCVs faded. data entered as eslmted
**canfumedlow on 90298
++ Qualitative data only
Mtln PFOSA
u#g 00391 0 0267
33%
00313
00310
19 2
I5 5 "due
Dale EnlerediAnalysI Dale VefiflediAMlyjt Punty EnIeredNenenfled
4113100. 5124100CSH 121121W MMH 12128100hoi (list al22993a) 12126100 LAC
CorrectedPFOS LOQs(0.0119&00121 uglg)toinclude sldcomclion facton
new
are o 01 i n &io 112 "gig LAC n 2 w n i
RSD SIdDrv. MYMSDRPD
NA NA 44%
5 21 0.03163
6 09 OW189
5 I3 0 987
10 7 I 65
Ers-8-7 0 Excel 97
3M Environmental Laboratory
Lrr Week 8 Rework TOXml-lwer212-100 XIS
Analytical Report: FACT-TOX-001 LRN-U2103
513112Wl
Page 253
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Study. Pnoducf NumbsrlJerI Substance) Matru Method/RWlSW" Analytical Equipment System N w n k r Insmen1 SoRuweNenan a t e of ErVdetlonJAnalyst Date of Analysi~/Analy~t Dale of Data ReductioniAnalvsl Sample Data
104 Week Dletar).Carcinogemcily Study x i t h Narmw Range (98 1%) N-Ethyl PerlluamstanesulfOWamldoElbAIlOl SIl Rats
T-6316 (ElFOSE-OH)
Rat Lwer
FACTI-M-I0 & FACT-Y-2 0 reworked using ET%-7 0
Fl1e-e
See t a l 10 roght
Chick 080697 and Madeline 041098
R . s q d value See Amhmenls
MassLym 2 3 and 3 1
Slop
See Anachmenls
06101198 RWWIOK
~-intercept
See Attachments
06/12198,06114198,06/18198.09102198 HOJNHJLAC
03116/W, 11129100, 121OllW. I21lOiW IASJMMWWH
WEEK 8 RAT LIVER
C0"L 27 2
PFOSAA Dilution Factor
I
PFOSAA
Cdc. Cont.
ws
27 2
Fl1m.m 6189834
Conuo1 0 0 mgrng
C90718M C90737M C90756M
OW
1
~
130
I
- _OW_
I
88 6
I
97 6
1
76 0
1
904
1
156
I
118
1
_3 1_ 3
1
I5 6
I
OW
sW1?06w5
I2 9
6189835
OW
1w1206006
12.3
61298127
21.0
61298128
72 7
6189845
88 1
6189846
149
6189847
117
6189848
3 10
6189849
15.2
6189852
C911MF CY1145F CY1 162F
I High Dose
3W mgkg
C90972M C90988M c909%M
I 74 406
- 195 79 4
512 594 478 480 384
~
306
I 1 1 1
IMO IMO loo0 IMO 1MO IMO
I70 40.1 192 78 1 505667 581791 473002 473865 379557 298858
6189853 6189854 6189855 6189856
I22998059 I22998058 I22998057 I22998056 122998055 122998066
00781
0 0920
C91394F
272
IMO
268201
I22998065
C91404F
37s
IMO
369672
122998064
C91415F C91438F 'OS = PernuomOCmeEUlrOMte
- 293 439
IMO IMO
286207 42m3
122998063 122998062
286
429
+
330
20 3 67 2
PFOSA = Perlluomoclanesulfonarmde
+ CCVs failed data enlered as estimated
PFOSAA ~ Per~uoro~tanrrulConamldoacetatr W O S E = Narmw Range N-Ethyl Perflwmocmesulfamtdo ethyl alcohol
'*confinned low on 90298 I* Qualitatwe data only
Date Fn1eredJAna1yst Date VenfledJAnalysl Punty FnteredNenfied
4/13/00,5/24/00 CSH 121121W MMH 12126/W LAC
ComtedPFOSLoQr(OOll9 &00121 ug/g)tolncludertdcorreetionfaelorr new LCQS are n n i in & n 112 "gig LAC 02119ini
UnblO\m unknown
- EIFOSE - COW.
Ws 244
OW
- - 46 5 30 3 000 OW OW OW
- 3 9 2 OW OW OW
- OW OW
892
Ellmame
y-1 3::- Facer
90298002
90298003
90298110
90298111
OW
90298019
90298020
90298021
90298022
90298023
OW
90298027
OW
90298028
OW
90298029
OW
90298030
OW
90298031
10
OW
10
OW
883
90298036
816
- 805
I 10
OW
90298038 90298042
- 347 650
90298045 90298046
Canorntntian
of EtFOSE
"USor % RII.
(0 0298 "gig) t i
<aOW
ti
(0 0298 "gig) t i
25%
CLOQ (0 0298 "gig) t i
<LoQ(0 0298 ugig) t i
<LoQ(0 0298 "gig) t i
< L c Q (0 0298 "g/g) t i
0 0388
CLoQ (0 0298 "gig) t i
<LCQ (0 0298 "gig) ++
<LCQ (0 0298 u#g) ++
<LCQ (0 0298 ugig) ++ <LOQ(OO298ugig) ++
OW
++
OW
++
0883
++
OW
++
0807
++
0786
++
OW
++
OW
++
0339
++
0636
++
MLP" EIFOSE
ws
<toQ
31%
RSD SU. Dlv. MYMSD RPD
NA
42%
I
00316
0 wM2
<top I
0338
NA NA
137 0 463
0352
102 0 359
ETS-8-7 0 Excel 97
3M Environmental Laboratory
Lm Week 8 Reuork T O X m l - l n e r 2 1 2 - I 0 0 xls
Page 254
3M Medical Department Study: T6316.1
AMDW 092597.1 Covancd 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
. _..
T-6316 (UFOSE-OH) Rat LlV.3 FACTM-I 0 Br FACT-M-2 0 ~ r o r k r du m g ETS-8-7 0 Chxk080697and Madelm 041098 MssrL)nr 2 3 and 3 I 06101198 RWWIOK 06112198,06114198,06118198.09101/98HOJWWWLAC
031161W, Ill29IW, I2101I00, 12llOlW IASiMMHJKJH
Fileme R-SquaredValue slop Y-lnlerrepl
See Amchmenlr See AtIaChmeNS See A t ! x h t t S See A n a c h l s
WEEK8 R
&UP Daw
LIVER REWORK
Sample #
HZO BL-2 Rabbit h y e r BL-1 Rabbit Lver Blk-2
C5071N-MSD
C90717h4 I
C90718M c90737M C90756M CW769M C91126F
I C91140F
C91145F C91162F C91163F
C90971M C90972M C90988M C909%M C91017M C91393F C91394F C91404F C91415F C91438F tanesulfomte
~toQ(oollou$ig)
-1773 2776
<toQ(0 0110 "gig)
<LOG(0 I I2 "pig)
-1331%
I
2 78
2731
I144
245
346 511 1094
I
1250280 1111564 1249941 890777 830679 873644 945819 1027570 1054710 1423345
0 245 0 346 0511 109 0 552
1112
874 946 1028 1055 1423
Date Enteredlhlysf Date V e n f i e d i h l y l t Punty ENeredNenfied
4/13/00, 5124IWCSH 12112100MMH 12/28/00 ha, (list a122998a) 12126100 LAC
Comeled PFOS LCQr (0 0 I 19 Br 0 012 I upig) 10 includp 51d correction fxtors new L O Q s are 0 0110 Br 0 I 1 2 "pig LAC 02119101
<Lop <LOQ .l410%
0 549
I
1067
1065
NA NA 11%
59 8 0 328
I85 197
20 0 213
66 3 0.w 41 4 48 4 30 8
32.4 ctoQ (0 0302 ugg)
33 7
00663
i
~LCQ(OO119ug/g)
00414
i
40%
*'
26%
*'
0 0324
<top(0 0302 Udg)
00337
- Men" - PFOSA
"Yg
- 0 0391
- 0 0267
- 33%
<toQ(00302 "pig) CtoQ (0 0302 UdR)
34.4
<LCQ (0 0302ugrg)
19353
<toQ(0 0302 udg)
(0 0302 U d g ) 0 0344
4.W (U 0302 "gig)
194
_0.03_13
- 00310
I
20877
I
209
18323
I8 3
14999
I5 0
14071
14 1
17148
17 I
13844
I3 8
17272
173
* Dah above the Imar cahhation range,e r t m t e d
+ CCVs bled, dm enteredas estimated
"confirmed low on 50298
++ Qualitalrve dabonly
- 19 2
- I5 5
44%
5 21 0 W163
6 09 OW189
10 7 I 65
3 10 I5 2 I 70 401
78 I 505667 581791 473002 473865 379557 298858 268201 369672 286207 429003
0 117
!a 1 1cLOQ(0633ug/@
cLOQ (0 633 udg) I
..
..
<LCQ (0 633 Udg)
0 0980
I
0 192
00781
0 0920
474
380
483
299
268
370
286
429
330
35.8 00351
61 I 00561
15 I 72 7
20 3 67 2
0.M
cLcQ(oo298upig) i t
1 !K 1 1 1 388
00388
i t 00316
I OW
I <LoQ(00298"pig) ++I
I
0
<LoQ (0 0298 U&) ++
0 W
<LCQ (0 0298 upig) ++
0 W
<LCQ (0 0298 ugg) ++ <LCQ
000
OO' Wf
807
0 807
0 338
786
0786
it
OW
OW
tt
OW
OW
++
339
0339
it
636
0636
++ 0352
12 7 000401
NA NA
1137
0 463
102 0 359
ETS-8.70 Excel 97
3M Environmental Laboratory
LIT Week 8 Rework TOXaO1-l~ver21?-1GXIS
5'3112001
Page 255
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covancdl6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
StUdY RodwtNumbeQesl Substan-)
MakiX MdWwaian h l f l r c a l Equipment SydcmNumber l n J t m t SonwareNenion Date ofE x t r a f l i o d h l y s t Date of A n a l y s d h l y Dale of Dab R e d u c t ~ o a ~ h l y d
Sample Data
104 Week B c l a r y Carcinogenicity study with N m u Range (98 1%) X-Fthjl Pcrfluomwrrnesulfonarmdo Elhaool m Rats
Td316 (EtFOSEOH)
Rat LlVer FACT-M-I 0 & FACT-MI 0 rero&ed using ETS-8-7 0 Chick 080698, Amelm 062498, Madeline 041098, and soup 020199
F k n m Sol List to Right R-Squared Valve Le A l l a e k l s
S l a p Le Affaehmnta
M a r r L p 2 3 and 3 I
Y-lntmepl. Le Atfachmenls
06102/98.01114/99,01/17/99 RWW/IAS/SAH
06/25198,06/26/98, 12/14/98,0lll8/99.02/16/W. 02/18/99 HOIKJHIMEEDRB
04/05/00, 11!3O/W, I M I I W , IMSIW. IL'07/W.O1'OMI CSHIMMILKJH
PFOS
PFOSA
12/14/98 La1 193 06/26/98 LoIL-2353
01118l99 Lat 171 I1114l98 LofL-2353
02/16/99 La1 171 011'18l99 LofUnLnoun
02'18199 Lo1 171
PFOSAA
EtFOSE
06/16/98 Lot617 06/15/98 Lot936
11114198 Lot617 02I18I99 LotUnLnoun
02/18199 LotUnLnoun
WEEK 14 RAT 1
&UP Dose
Method Elk Malm BL W-IWppb
W .250 ppb
W-750ppb cmvp I C0"tml OOwh
Gmup 1 Low Dou 3 0 mglkg
cmvp 3 Mid Dosc 30 0 m a g
ER REWORK
Sample #
HZOBlk-l H2OBIk-2 abbil Liver Blk-I ahbit Liver Blk-2 C90768M-MS Z90768M-MSD C9078OM-MS 390780M-MSD C91174F-MS C91174F-MSD C93731M
C90880M C91281F C91288F C91299F C91304F C90905M C90907M C90917M C90921M rWwM C91337F C91355F C91370F C91379F
Inlllsl WL L
I OMX) 1 OOM) 1 0080 I 0080 IO214 10214 10166 10166 IO123 10123 10133
IOZOl I0210 10173 I0277 10099 10123 10104 10378 10~4 IOlSO I 0150 I 00%
Total Mmrs
e
NA NA 40 13 40 13 NA NA NA NA NA NA
NA NA NA NA
- NA NA NA NA
- NA NA NA NA NA NA NA
~
NA NA NA
- NA NA NA NA NA NA NA
~
NA NA NA
- NA NA NA NA NA NA
- ~ N4 NA NA NA
- NA NA
PFOS Std
cormtian F..tW 0 9275 0 9275 0 9275 0 9275 NA NA NA NA NA NA
0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 927s 0 9?75 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 9275 0 077\
0 9275 0 9275 0 9275 0 9275 0 9275
SI241W. 11107100. 12/141W I2/28100 HOJ 11126JW LAC
La1 171
PFOSPvrify PFOS
PFOS
Fileanme
Comrflou F~lor 08640
I I Corn. ndg OW
Dilulian
Faelor I
1
M011899013
08640
OW
I
S021899w3
08640 I OW I
I
1 MOll899014
08640
OW
I
S021899w4
NA
867
I
MI21498109
NA
1023
I
MI214981 10
NA
889
10
MU21699036
NA
983
10
M021699037
NA
I 40
10
so21899015
NA
IS1
10
SO21899016
08640
348
4
MOI 1899025
08640
425
4
MOI 1899026
08640
504
4
MOI 1899027
08640
383
4
MOI 1899028
I2W
I20
. 08640
286
4
MOI 1899029
901
0 901
I23
08640
133
4
MOI 1899032
417
0417
08640
I55
4
MOI 1899033
489
0 489
08640
175
4
M011899034
555
0 555
08640
766
4
M011899035
243
0 243
08640
970
4
MOI 1899036
303
0 303
0402
08640
230
125
M011899039
22950
23 0
08640
231
0.8640
247
08640
210
08640
266
08640
214
08640
235
08640
289
08640
195
08640
256
08640
263
08640
720
08640
261
125 125 I25 125 125 125 125 125 I25 2wO 2WO 2wO
M011899040 M011899041 MOI 1899042 Mol1899043 M011899046 Mol1899047 YO1 1899048 MOI 1899049 MOI 1899050 M011899053 Mol1899054 M011899055
22597 24494 20514 26220 21300 23437 28206 19334 25542
41221 114260 40451
22 6
24 5
20 5
26 2
23 4
21 3
23 4
1236
41 2
1405
08640
!%2
2WO
MOll899056
153905
08640
339
2WO
MOI 1899057
54251
8;
0x640
872
zwo
MOIMYWM
137003
08640
858
2wO
M011899061
134654
08640
709
2W0
Mol1899062
113467
08640
148
2wO
Mol1899063
233295
233
MOll8990M
84401
84 4
415193
415
543101
543
0 8640
M021699024
372033
372
0 8640
314243 3l@!*
262314
296535
248810
0 8640
MO21699032
649710
0 8640
ID00
M021699033
216709
Note PFOS dab may b b1-d bgh h on Ibe MSIM:
+ Brackelcdby a CCV ill-30% differace,&la may be b i d low LAC 02/19/01 * Reportd below the LCQ
++ PFOSAA MSihlSD mot N l y b-kefed LAC 12I14IW
i++ ElFOSE MSiUSD aported,only a 4 p i n t EWF could be eenerated LAC I Zl141W
E = Sample went to d q c s s aRer the initial analyrin No extract remaining for m l y s a 'iPUalilative &la only. h c d on MSMSD r e d i s
21 4 0262
32 I 0 129
19 I6
2 I4
?4:
63 0
398 56 0
UnLnoUn UnLn0V.n Unlvuull UnlvuUll UnLnOWn UnLnOWn UnLnOWn
UnLnOUn UnLnowo UnLnoUn UnLnOUn UnLnOWn Ul!kllOUn llnknnun
2.74
I
2 68
36 5
I
35 9
660
I
6 43
9 75
I
960
29 9
I
296
2 44
I
2 41
OW
I
OW
133
10
1319
111
10
I084
89.7
10
889
134
100
1305
98 3
IO
968
I94
I927
171
,607
158
153
IW
I77
127
1W
12659
IM
1W
15721
142
1W
14058
143
IW
14066
167
1W
16522
Corrected PFOS LCQs (0 0619 & 0 0309 =gig) lo include rld camclian factors ~ ~ w L ~ a r r 0 0 4 9 6 & 0 0 2 4 8 u g L1AgC O t l P / O l
"dg o r x kc.
MSJMSD RPD
N. .A.
. ..
NA
NA
N. .A. I
N...A.
NA
NA
MI21498014
00537
MI21498015 < C Q ( O O l ? l u#g)
76%
NA
I
I
NA
MI21498016 < O q ( O O l Z l u&)
MI21498017
00359
~ 1 2 1 4 9 8 0 2 1a o Q ( o o 1 2 1ug/g)
a w ~ 1 2 1 4 9 8 0 2 2
(o 0121 "de)
1 MI21498023
002%
MI21498024 <GQ(OOl2l uglg)
MI21498025 UCQ(OOl2l up'g)
MI21498060 I
132
I {f MI21498061
MI21498062
MI21498063
MI21498064 MI21498068
0968 I93
Ml,,d(lsN.O
I,"
00284
I I
I
00156
I I
I
I I1
13% NA NA
71 I 00202
50 2 OW784
175
0 194
24 2
M062698076 M062698077
MI21498100
127
M121498101
157
MI21498102
14 I
MI21498103
14 I
MI21498104
165
10 4
14 6
I52
~ ~ s - 8a- 7
3M EEnx-v197ironmental Laboratory
Page 256
3M Medical Department Study: T6316.1
AMDT# 092597.1 CovanceU632C212
SfUdY Roduel N u m W e o t Subotanse) M*hix
MeUlod/Re"lSion Andylical Equiuipmenl System Number Irutrumc"l SonralxNemlon Dale af ExlractiodAnalyd: Date of Analysir/Analy.l Dale ofData RedustiodAnalysf Sample Data
104 Week Dietary Cmmogenicify Study ubth N m w Range (98 I%) N-Ethyl Pernuo-tanerulfonarmdo T-6316 (EtFOSEOH)
Elhano1 in Ram
Ral Liver
Film
FACT-M-I 0 & FACT-Mf 0 Chick 080698, h l i a 062498. Madellne 041098, and Soup 02olw
RSqusvFd Valve Slope
MasrLynr 2 3 and 3 I 5111/98,6/298,01114/99 RWWIIASISAH
Y-lnlorcepl
6/5/98, 12/14/98.01/18/99,02/16/99,02/18/99 HOJXIIbMEWDRB 12/22/98, 01/20/99,0922199, 3/23/W HOJrWlMRBihLMH
See Anashmenls See Anashmenls See Anashments See Altashmeofs
Lo1 617 or UnLnawn
H20 Bk-l
unknown
Lo1 936 or Uolroown
- EtFOSE
Con*.
*OW
H2O Blk-2
NA
~
C90768M-MS C90768M-MSD C90780M-MS C90780M-MSD
C91174F-MS C91174F-MSD
C90731M
NA NA NA NA unknown
NA NA 905 1315
OW
- NA NA
_NA_ NA
- _NA_ 516
480
OW
C90746M
OW
C90748M
OW
C90768M C90780M C91129F
OW
- O W OW
C91155F
OW
C9116OF
OW
C91174F
C91181F
21 8
C90797M
- OW OW NA
C90807M
145
NA
I
NA
NA
CW818M
180
I0
MI21498062
1786
I 79
Uhown
NA
I
NA
NA
C90831M C93836M C91192F
203
I0
MI21498063
1984
198
175
10
MI21498064
1719
I 72
218
10
MI21498068
1168
2 17
18 9
185
0351
Uhoun
NA
I
NA
NA
UnLnOwn
NA
I
NA
NA
~
UhOUn
NA
I
NA
NA
C91223F
10
MI21498069
3240
3.24
UnLnOWn
NA
I
NA
NA
C91233F
262
10
MI11498070
2556
2 56
UhOWn
NA
I
NA
NA
C91241F C91248F C90843M
232
10
MI21498071
2295
229
17.4
303
10
MI21498072
3023
3 02
266
0 462
7 58
IW
MU62698067
142
0742
*
- U h O U n
NA
tihown
NA
UnLnOUn
234
I
NA
NA
I
NA
NA
I
A062598076
229
C90852M
202
1W
M062698068
20013
20 0
UhOW
Ill
I
A062598077
175
C90863M
1W
M062698069
11226
I12
UhOWn
325
I
A062598078
314
C90877M
358
1W
M062698070
3J70b
35 7
72 8
UhOUn
146
I
A062598079
146
C90880M
168
~
I
A"n,sQn"a"
367
C9l18lF
152
I
A062598083
149
C91288F
142
I
A062598084
139
C91293F
UhOWn
171
I
A062598085
171
C91299F C91304F C90905M
- M U
117
1
A062598086
115
170
1
A062598087
165
943
UhOW
NA
1
NA
NA
C90907M
749
14 0
UhUn
NA
C90917M
619
61 2
UnlmoUll
NA
C90921M C9019MM C91329F C9133lF
1209
IW
MI214981W
IC0
M121498101
, 40356 78625
1164 (07 40 4 78 6
, __ 29 7
UnkoOUn
NA
,
/PI
>:.A
UhOWl
NA
NA
Uhown
NA
I
NA
NA
C9135SF
IW
MI21498102
63619
63 6
UhUn
NA
I
NA
NA
C91370F C91379F
IW
MI21498103
50197
50 2
24 6
640
1W
MI21498104
63386
63 4
59 1
14 6
Nole PFOS dnfa m y be b l e d high bssedathe MSMSD m v e n e s
UhVn UhOwO
- NA
I
NA
I
NA NA
NA NA
PFOS = Pcrfluamoclanenulfonsl~ PFOSA = Perflw-tancrulfa&& PFOSAA = Pernuomoctan~sulfonarmdoacct.tc
+ Bmckeld by I( CCV at -30% diNaocp, dab may be b i e d low LAC 0219m1
* R s p r i d below the LCQ ** PFOSAA YSMSD n ~ful lly braekeled LAC I 2 I 4 I W
EIFOSE = N m u Range N-Ethyl Perfluomoctanesvlfondo ethyl alwhol
Date EnteredIAna1yrt.
512402, I M 7 / W , I2114JW CSHKJHILAC
+ i t EIFOSE MSIMSD reponed,only a 4 pi01EWF wuld be gencratcd LAC I2/14/W
E = samplew n ~to +*s an*. the *nitidrnalyslr xa
for -lY.i.
U Qualilalive data only, b a d on M W S D m d l n
Dale verifidhlpt
1228lW HOJ
k t y EnleredNmfied
1216IW LAC
Comcted PFOS LCQs (0 0619 & 0 0309 uglg)to include rld wmlillan fsclorr oew L C Q a . 0 04% 8- 0 0148 ue'g LAC 01'19IOl
Analytical Report: FACT-TOX-001 LRN-U2103
NA
x
NA
x
NA
x
NA
x
NA
x
NA
x
NA
u
NA
x
NA
x
0 229
U
0 175
U
0 314
U
0 "
146
!L7
#
*
0 149
#
0 139
#
0 171
u
0 115
#
0 165
#
NA
#
NA NA ? 2w 0 148
NA
x
NA
.
NA
NA
x
NA
NA NA
NA NA
32 8 "5757
IS I 0 0224
NA NA
ETS-8-7 0
3M EEnxevl9i1ronmental Laboratory
Lw Week 14 Rework TOXMll-lwer212-I0X0 IS
Page 257
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covanee# 6329-212
Study Rodwl N u m W e R Substance) Malm MclhdRcuision h a l f l i d Equipmnl System Nvmbr Innrumen1 SoRwarrNenion-
Date O f D i W n m d h a l y s t Date Of AonlyndAoalp. Date ofDataR~dwt~odAnalysl
Sample Data
104 Week betar~y~ i n o g e n e es~tuidyy with xmu,hg(9C 8 1%) N-Ethyl P d l ~ m t m ~ l S o o m dEtohanol in Rats
1 4 3 1 6 (EtFOSEUH)
Rat Liver
F,*W
S e LtR lo Rtghl
FACT-M-I 0 & FACT-M-2 0 m w d e d wmg ETS-8-7 0
R-Squand Val-
S e Altaehmnls
Chiok 080698, h l l a 062498, Madelme 041098. and Soup 020199 Mar%LLyrU23and31
slope Y-ln(empt
See AttaehmnN See Atfsbmmts
06/02/98,01/14199,01/17/99 RWIIASISAH
06/25/98,06/26/98, 12114198.01/18/99.02/16/99,02/18/99 H O 1 ~ ~ W D F . E
04/05/00. 11l30~001, 2/01100, Iz/o5iw. 12/07/00, 01/02/01 CSHIUMWKJH
WEEK14 RA' IVER REWORK
Group Dor
Melhd Bk
s.mp1. I
H2O BIk-l H2O Elk-2
PFOS Cdc. COOC.
os/r 000 000
conmtmtioo olPFOSA
vgtg w Y. Rs.
LOQ IO 00604"gig) NA
Mafm Bk QC-IWwb Qc - 250 ppb Q c . 7 5 0 ppb
labbil Liver BIL-l labbil Liver Bk-2 C90768M-MS C90768M-MSD C90780M-MS C90780M-MSD
C91174F-MS C91174F-MSD
0.00 0.00 -351 -199 -27 65 1136 I245
LOQI0 wM4 'gig) NA
81%
71%
76%
NA
NA
NA
NA
NA
13%
665
NA
1070
croup 1 C0"rnl 0 0 mukg
C90731M C90746M C90748M C90768M C90780M C91129F C91155F
1100 1332 1603 I 2w WI 417 489
00537 n O Q ( o o l 2 l 'gig)
E ;LOQ(00121 "gig)
00359 n c Q ( o O l 2 l "@E) :LCQ(00121 "@E)
0 0284
172
140
E
71 1
206
0 0202
28 5
74 5
93 4
C9llMF
555
C91174F
243
C91181F
303
002% rLCq(ool2l "gig) r L ~ ( o O l 2 "l gig)
00156
68 4
50 2
229
0 00784
11 3
C907YIM CW807M
22950 12597
132
2363
I08
1414
C90818M
24494
0 889
I786
C90831M C90835M c91192F C91223F
20514 26220 21300 23437
I31
17 5
I984
0 %8
I I1
0 194
1719
I 93
2168
2 17
I70
3240
3 24
C91233F
28206
I79
2556
2 56
Group 3 Mid%= 30 0 mgkg
C91241F C91248F CW843M CW85ZM C90863M C90877M C9088OM ~91281~ C91288F C91293F C91259F
19334 25542 41221 114260 40451 I53905 54251 1'1003 134654 113467 233295
137
~
135
*
113
+
233
+
-$ I78
I82 6 67 9 04 563 10 I
9 84-
8589
8 59
6480
6 48
7359
7 36
39 8
8935
894
4 61
2295
2 29
1 80
00831
3023
3 02
742
0742
20013
20 0
11226
I12
35 7
32557
5269
13748
12775
2%78
29 7
C91304F
84401
84
+ 141
56 0
8512
8 51
13073
13 I
C90905M
415193
415
18099
I8 I
94 3
C90917M C90921M C9096oM
C91355F C91370F
543101
543
15579
IS 6
TJ-JrL 372033
372
314243
314
316914
262
248810
I5150
I5 2
24 0
16630
166
392
17258
17 3
12659
I2 7
17?1
I5 7
14058
14 I
649710
I4 I
74 0
61232
61 2
7 28
116449
116
'0 7
40356
40 4
78625
78 6
63619
63 6
50197
50 2
16521
16 5
14 6
152
63386
63 4
Note. PFOS & my b biased lugh ba=c the MSMSD rccovmes
EtFOSE = N m w Range I\'-Ethyl Perfluo-tanesulSomonarmdo ethyl nlwhol
+ Bmcketcd b!
* Repand b l a +* PFOSAA h
-CV at -10% diNemnEe,
.I- M.-
3 may b biased law LAC 0?/19/01
ZSDnolfullyhcketed. LAC 12/14/00
+** EIFOSE h G D rrponed, only a 4 p i n 1c w o could b gemeraled LAC IY14IW
E = Sample wnt to drymessaRer the initial analysis No exlml m&g
far d y n i s
5/24/00, 1>07/00, I2/14/lN CS-C
R Qualilslivc data only. basd on MSMSD msulfs.
lU28iW HOI
12/26/00 LAC
Corrected PFOS LCQs (0 0619 & 0 0309 udg) lo include rld c o r n c l l ~ nfaclorr new LOQEare 0 04% & 0 0248 uglg LAC OY19iOI
Analytical Report: FACT-TOX-001 LRN-U2103
174 2 66
72 8
MO
I4 9
8 95
I!I
__29
11
. 7
3
24 6
59 2
14 6
M"n
RSD
EIFOSE
Std DN
ude x
M S M S D RPD
I UoQ
NA
#
d UOQ
NA
#
#
NA
NA
#
X
NA
NA
+++
b++ 547%
7%
n
#
#
#
NA
P UOQ
NA
#
#
#
1
NA
# cop
#
NA
I)
NA
d
NA
#
tJA
NA
#
NA
NA
NA
#
NA
#
NA
#
NA
a
NA
NA
X
NA
NA
229
0 229
#
0.175
x
0314
#
146
0 "
146 !17
#
0 149
0 139
0 171
0 115
15.1
165
0 165
0 0224
NA
NA
NA
NA
NA
NA
N::.A
NA NA
...N A
1VA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
UA
ETS-8-7 0
3M EEnxveli97ronmental Laboratory
Page 258
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Study: Product Number(Test Substance): Matrix: MethodRevision: Analytical Equipment System Number: Instrument SohareNersion: Date of Extractiodhalyst: Date of Analysis/Analyst: Date of Data ReductiodAnalyst:
Sample Data
104 Week Dietary CarcinogenicityStudy with Narrow Range (98.1%) N-Ethyl PerfluorooctanesulfonamidoEthanol in Rats
T-6316 (EtFOSE-OH)
Rat Liver
ETS-8-6.0 & ETS-8-7.0
Filename:
See Below
Davey 070799
R-Squared Value: See Attachments
MassLynx 3.3, 3.4
Slope:
See Attachments
2/29/00 SAL
Y-Intercept:
See Attachments
05/08/00,05/24/00, 08/2 1/00. 08/23/00 IAS/HOJ/MMH
05/09/00,05/25/00, 08/22/00, 08/28/00 IASIMMHIHOJ
Analytical Report: FACT-TOX-001 LRN-U2103
WEEK 53 RAT LIVER
Group Dose
Sample #
Method BU
RBL02290-HZO Blk-5
Matrix B L
RBL02290-HZO Blk-6 FEiL02290-Liver Blk-5
QC - 250 ppb
RBL02290-Liver BIk-6 C90714M-250 ppb-MS-5-1 C90714M-250 ppb-MS-5-2
Group 1
C90714M
Control
C90751M
0.0 mgkg
C90752M
C90754M
C90767M
Group 1
C91121F
Control
C91122F
0.0 mgkg
C91 l24F
C91133F
C91152F
Group 4
C90902M
Low Dose
C90918M
3.0 m a g
C90950M
C9095 1 M
C90957M
Group 4 Low Dose
C91323F C91347F
3.0 m a g
C91352F
C91367F
C91371F
FFOS - r"crl;uuruu~-icbuirunai.
Initial Wt. g
1.0000 l.Oo00 1.oooO I .0000 1.0093 1.0093 1.0093 1.0033 0.9994 0.9912 0.9845 0.9972 1.0073 1.0079 0.9918 1.0162 0.9925 1.0022 0.9878 1.0037 0.9880 0.9939 0.9917 0.9983 0.9908 0.9903
Lot 171
Total Mass of Liver
PFOS Std Correction
PFOS Purity Correction
Surrogate Verified
PFOS Cone.
PFOS Dilution
PFOS Calc. Couc.
Filename
g
Factor
Factor
NA
0.9275
0.8640
NA
0.9275
0.8640
40.13
0.9275
0.8640
40.13
0.9275
0.8640
NA
NA
NA
NA
NA
NA
NA
0.9275.
0.8640
NA
0.9275
0.8640
NA
0.9275
0.8640
NA
0.9275
0.8640
NA
0.9275
0.8640
NA
0.9275
0.8640
NA
0.9275
0.8640
NA
0.9275
0.8640
NA
0.9275
0.8640
NA
0.9275
0.8640
NA
0.9275
0.8640
I E I ::zI NA
0.9275
0.8640
: :g.
NA
0.9275
0.8640
NA
0.9275
0.8640
nglg
Factor
NA
2.15
1
NA
0.00
I
NA
0.00
1
NA
3.16
I
Confmed low
1239
1
Confmed low
1006
I
NA
706
1
NA
473
I
NA
993
1
NA
857
1
NA
526
1
NA
374
1
NA
383
1
NA
539
1
NA
668
1
NA
474
1
NA
739
1000
I I ;::I I NA
548
1000
E E11 NA
IO08
1000
NA
820
1000
riels
1.72 0.00 0.00 2.53 528 298
560 378 796 693 428 30 1 305 429 540 374 596825 437941 923568 gpan! 817501 661438
A0821000 16 A0821000 17 A0821000 18 A0821000 19 DO50800019 DO50800020
D0508DO50800024 DO50800025 DO50800026 DO50800027 DO50800030 DO5080003 1 DO50800032 DO50800033 DO50800034
DO50800037
I DO50800038 DO50800039 nCl5ClaClnn4Cl DO50800041 DO50800044
NA
0.9275
0.8640
NA
1065
1000
860688
DO50800045
NA
0.9275
0.8640
NA
959
1000
770046
DO50800046
NA
0.9275
0.8640
NA
776
1000
627330
DO50800047
NA
0.9275
0.8640
NA
678
1000
548628
Do50800048
' Hi& recovery was confmed on BiiiiOO, Mawas nor enrered because it was outside the caiibiration range. 4iiOiOi mmh
Concentration of PFOS
uglg or % Ree. <LOQ (0.00491 uglg)
<LOQ (0.00491 uglg)
100% 0.560 0.378 0.796 0.693 0.428 0.301 0.305 0.429 0.540 0.374 597 438 924
770 627
Mean PFOS
138% 0.571
1I I10.390 695 694
RSD Std Dev
56% 30.7 0.175
1:25.5
0.0993
17.7
ETS-8-7.0
3M EEnxcveli9r7onmental Laboratory
Lvr Week 53 TOX-001-liver212-1OO.xls
5/31/2001
4:48 PPMage 259
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covanc& 6329-212
Study: ProductNumber(Test Substance): Matrix: MethodiRevision: Analytical Equipment System Number: Instrument SoftwareNersion: Date of ExtractiodAnalyst: Date of AnalysidAnalyst: Date of Data ReductiodAnalyst:
Sample Data
104Week Dietary CarcinogenicityStudy with Narrow Range (98.1%) N-Ethyl PerfluorooctanesulfonamidoEthanol in Rats
T-6316 (EtFOSE-OH)
Rat Liver
ETS-8-6.0 & ETS-8-7.0
Filename:
See Below
Davey 070799
R-Squared Value: See Attachments
MassLynx 3.3, 3.4
Slope:
See Attachments
2/29/00 SAL
Y-Intercept:
See Attachments
05/08/00,05/24/00, 08121/00,08/23/00 IASIHOJIMMH
05/09/00,05/25/00, 08/22/00, 08/28/00 IASIMMHIHOJ
Analytical Report: FACT-TOX-001 LRN-U2103
WEEK 53 RAT LIVER
Lot L-15709
Group
Sample #l
PFOSA Purity
Surrogate
PFOSA
Dose
Correction
Verified
Conc.
Method Blk
RBL02290-H20 Bk-5
Factor Unknown
np/p
NA
0.00
RBLO2290-H20 Bk-6
Unknown
NA
0.00
Matrix Blk
QC - 250 ppb
Group 1 Control 0.0 m a g
I RBL02290-Liver Blk-5
RBL02290-Liver Blk-6
I C90714M-250 ppb-MS-5-2
C90714M
I
C90751M
C90752M
Unknown Unknown
NA Unknown Unknown
I NA
2.58
NA
0.00
I I ConfmedLow
288
I
NA
1 0.710
NA
NA
C90754M
Unknown
NA
Group 1
C90767M C91121F
Unknown
- NA
NA
Control
C91122F
Unknown
NA
5.41
0.0 m a g
C91124F C91133F
Unknown Unknown
NA
25.5
NA
C91152F
Unknown
NA
9.87
Group 4 Low Dose 3.0 mgikg
C90902M C90918M C90950M
Unknown Unknown Unknown
NA
296
NA
196
NA
289
C90951M
1 lnknnwn
NA
716
C90957M
Unknown
2nd Analysis OK
404
Group 4
C91323F
Unknown
NA
236
Low Dose
C91347F
unknown
2nd Analysis OK
216
3.0 mgikg
C91352F
Unknown
Confmed High
219
C91367F
Unknown
High, Not Confmed
264
C91371F
Unknown
High, Not Confmed
3 19
PFOSA Dilution Factor
1 1 1 1 1 I I I I 1 1 1 1 1 1 1
IO0
Inn
100
100 100
PFOSA Calc. Cone.
nglg 0.00 0.00 2.58 0.00 230 285
0.703 35.4 11.7 18.3 19.6 12.5 5.37 25.3 15.9 9.71
19579
29280
,
7lAR1
40923
21786 21911 26678 32243
Filename
DO50800004 DO50800017 DO50800005 DO50800018 DO50800019 DO50800020 A082100024 A082100025 A082100026 A082100027 A082100028 A082100031 A082 100032 A082100033 A082100034 A082100035 DO52400040 DO52400041 DO52400042
-M <.-7-A .n.n-n-A.7_
DO52400047 DO52400048 DO52400049 DO52400050 A082300016 A0823000 I7
Concentration of PFOSA
uelp or % Ref.
<LOQ (0.0123 ugig) <LOQ (0.0123 ugig) <LOQ (0.0123 u&) <LOQ (0.0123 udg)
77% 95%
0.0354
0.0117
0.0183
0.0196
0.0125
<LOQ (0.00614 upig)
0.0253
0.0159
0.00971
29.8 2lg9.63
I
1 40.9
21.8 21.9 26.7 32.2
PFOSA <LOQ CLOQ 86%
0.0182
Std Dev MS/MSD RPD
21%
I 55.1 0.0100
0.0139
0.00677
28.2
8.44
1 17.3
25.3
4.37
ETS-8-7.0
3M EEnxcveli9r7onmental Laboratory
Lw Week 53 TOX-00 1-liver2 12-1OO.xls
513 l/ZOOl
4:48 PPMage 260
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covancetf 6329-212
Study: ProductNumber(Test Substance): Matrix: MethodRevision: Analytical Equipment System Number: Instrument SofhvareNersion: Date of Extractiodhalyst: Date of AnalysisiAnalyst: Date of Data Reduction/Analyst:
Sample Data
104 Week Dietary CarcinogenicityStudy with Narrow Range (98.1%) N-Ethyl PeriluorooctanesulfonamidoEthanol in Rats
T-63 16 (EtFOSE-OH)
Rat Liver
ETS-8-6.0 & ETS-8-7.0
Filename:
See Below
Davey 070799
R-Squared Value: See Attachments
MassLynx 3.3, 3.4
Slope:
See Attachments
2/29/00 SAL
Y-Intercept:
See Attachments
05/08/00,05/24/00, 08121/00,08/23/00lAS/HOI/MMH
05/09/00,05/25/00,08/22/00,08/28/00IASlMMWHOJ
WEEK 53 RAT LIVER
Group Dose
Sample #
Method Blk
Matrix Blk
QC - 250 ppb
Group 1 Control 0.0 mgkg
Group 1 Control 0.0 mgkg
Group 4 Low Dose 3.0 mgkg
Group 4 Low Dose 3.0 m a g
RBL02290-HZO Blk-5 RBL02290-HZO Blk-6 RBL02290-Liver Blk-5 RBLO2290-Liver Blk-6 C90714M-250ppb-MS-5-1 C90714M-250 pph-MS-5-2
C90714M C90751M C90752M C90754M C90767M
C91122F C91124F C91133F C91152F
C90918M C90950M C90951M C90957M
I C91347F
C91352F C91367F C91371F
LotT-7121.1 PFOSAA Purity
Correction Factor
Unknown unknown Unknown Unknown
NA NA unknown Unknown Unknown Unknown unknown
Unknown Unknown Unknown
Unknown Unknown Unknown Unknown
Unknown Unknown Unknown
PFOSA = Perfluorooctanesulfonamide PFOSAA = Perfluorooctanesulfouamidoacetate EtFOSE =Narrow Range N-Ethyl Perfluorooctanesulfonamidoethyl alcohol M556 = CSFI7SOZN((H)CH2C00) PFOSEA = Perfuorooctanesulfonyl ethylamide Date Enteredihalyst: 05/15/00,06/12/00,09/03/00CSWLAC Date Verifiedihalyst: 06/05/00.06/06/00CSH: 02/26/01hoj Purity EuteredNerified: 02/16/01 LAC
Corrected PFOS LOQ (0.0613 ug/g) to include std correction factors new LOQ is 0.0491 ug/g. LAC 02/19/01
Surrogate Verified
NA NA NA NA Confmned Low Confmed Low NA NA NA NA NA NA NA NA NA NA NA NA NA
PFOSAA Cone. np/g 0.00 0.00 0.00 0.00 339 370 8.54 48.7 8.27 44.0 4.96 8.95 4.04 61.6 25.5 16.0 803 402 677
PFOSAA Dilution Factor
1 1 I 1 1 1 1 1 1 1 1 I I 1 1 1 100 100 100
PFOSAA Calc. Cone.
n%g 0.00 0.00 0.00 0.00 327 359 8.46 48.6 8.27 44.4 5.04 8.98 4.01 61.1 25.7 15.7
80884 40068 68551 7RA75
60700 49362 41 192 45161 46121 56329
Filename
DO50800004 DO50800017 DO50800005 W50800018 DO508000 19 DO50800020 DO50800023 DO50800024 DO50800025 DO50800026 DO50800027 DO50800030 DO50800031 DO50800032 DO50800033 DO50800034 DO5080005 1 DO50800052 DO50800053 nnOE"M54 DO50800055 DO50800058 DO50800059 DO50800060 DO5080006 I DO50800062
Analytical Report: FACT-TOX-001 LRN-U2103
Concentratiou of PFOSAA
ude or % Rec.
<LOQ (0.0307 -ugl-g,)
<LOQ (0.0307 ug/g) <LOQ (0.0307 uglg)
109% 120% <LOQ (0.0307ug/g) 0.0486 <LOQ (0.0307 uglg) 0.0444 <LOQ (0.0307 uglg) <LOQ (0.0307 uglg) <LOQ (0.0307 uglg) <LOQ (0.0307 ug/g) <LOQ (0.0307ug/g) <LOQ (0.0307 ug/g) 80.9 40.1 68.6
1P z
_".<
60.7 49.4 41.2 45.2 46. I 56.3
PFOSAA
1<LOQ
114% <LOQ
47.6
Std Dev
:2
NA
5.67
ETS-8-7.0
3M EEnxvceilr9o7 nmental Laboratory
Lw Week 53 TOX-001-liver212-I00.xls
513 112001
4:48 PPMage 261
3M Medical Department Study: T6316.1
Study: Product Number(Test Substance): Matrix MethodlRevision: Analytical Equipment System Number: Instrument SofhvareNersion: Date of ExtractiodAnalyst: Date of Analysis/Analyst: Date of Data ReductiodAnalyst:
Sample Data
WEEK 53 RAT LIVER
Group
"'"."I
AMDT# 092597.1 Covance#f 6329-212
104 Week Dietary Carcinogenicity Study with Narrow Range (98.1%) N-Ethyl PerfluorooctanesulfonamidoEthanol in Rats
T-6316 (EtFOSE-OH)
Rat Liver
ETS-8-6.0 & ETS-8-7.0
Filename:
See Below
Davey 070799
R-Squared Value: See Attacbments
MassLynx 3.3,3.4
Slope:
See Attachments
2/29/00 SAL
Y-Intercept:
See Attacbments
05/08/00, 05/24/00, 08121/00,08/23/00 IASiHOliMMH
05/09/00, 05/25/00,08/22/00,08/28/00 IASMMWHOJ
Analytical Report: FACT-TOX-001 LRN-U2103
lot Unhown
Conhol
C90754M
Control
C90767M C91121F C91122F
Unknown
NA
NR
1
Unknown
NA
NR
1
Unknown
NA
NR
1
C91124F C91133F C91152F
Unknown
NA
NR
1
Unknown
NA
NR
I
Unknown
NA
NR
1
Low Dose 3.0 m a g
Group 4 Low Dose
PFOS = ?eflAna:a-act-esc
C90902M C90918M C90950M C90951M C90957M C91323F C91347F C91352F C91367F C91371F
unknown
NA
NR
1
Unknown
NA
NR
1
Unknown
NA
NR
1
Unknown
NA
NR
I
Unknown
NA
NR
I
Unknown
NA
NR
1
unknown
NA
NR
1
Unknown
NA
NR
1
Unknown
NA
NR
1
Unknown
NA
NR
1
PFOSA = Perfluorooctanesulfonamide
PFOSAA = Perfluorooctanesulfonamidoacetate EtFOS = Narrow Range N-Ethyl Perfluorooctanesulfonamidoethyl alcohol
M556 = C8F17S02N((H)CH2C00)
PFOSEA = Perfuorooctane sulfonyl ethylamide
Date EnteredlAnalyst: 05/15/00, 06/12/00, 09/03/00 CSWLAC
Date VerifieUAnalyst: 06/05/00. 06/06/00 CSH: 02/26/01 hoj
Purity Enterewerified: 02/16/01 LAC
Corrected PFOS LOQ (0.0613 ug/g) to include std correction factors new LOQ is 0.0491 uglg. LAC 02/19/01
NR
NA
NR
NR
NA
NR
NA
NR
NR
NA
NR
NR
NA
NR
NR
NA
NR
NA
NR
NA
NR
NR
NA
NR
NA
NR
NR
NA
NR
NR
NA
NR
NP
Y.4
N?.
_k.L 1 A
NR
NA
NR
NR
NA
NR
NA
NR
NR
NA
NR
NR
NA
NR
NR
NA
NR
NA
NR
NA
NR
NR
NA
ETS-8-7.0
3M EnExvceilr9o7 nmental Laboratory
Lw Week 53 TOX-001-liver2 12-100.~1s
5/31/2001
4:48 PPMage 262
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Study: Product Number(Test Substance): Matrix: MethodIRevision: Analytical Equipment System Number: Instrument S o h a r e N e r s i o n : Date of ExtractiodAnalyst: Date of Analysis/halyst: Date of Data ReductiodAnalyst:
Sample Data
104Week Dietary CarcinogenicityStudy with Narrow Range (98. I%) N-Ethyl PerfluorooctanesulfonamidoEthanol in Rats
T-6316 (EtFOSE-OH)
Rat Liver
ETS-8-6.0 & ETS-8-7.0
Filename: See Below
Davey 070799
R-Squared VaSee Attachments
MassLynx 3.3, 3.4
Slope:
See Attachments
2/29/00 SAL
Y-Intercept: See Attachments
05/08/00,05/24/00,08/21/00,08/23/00 IASIHOJIMMH
05/09/00,05/25/00.08/22/000, 8/28/00IAS/MMH/HOJ
Analytical Report: FACT-TOX-001 LRN-U2103
WEEK 53 RAT LIVER
1
I
Group Dose
I I
Method Blk
I
II Matrix Blk
Lot NBI 13047-80
Sample #
I M556Puritv I
I I correction-
I Factor
RBL02290-H20Blk-5 I Unknown I
I I I RBL02290-H20Blk-6
R B L O ~ ~ ~ O - ~L ~kV- ~5~
Unknown
Unknown I
QC - 250 ppb
RBLO2290-Liver Blk-6 C90714M-250 ppb-MS-5-1
unknown NA
C90714M-250 ppb-MS-5-2
NA
Group I
I Control 0.0 mgkg
-
Group 1
C90714M C9075 IM C90752M C90754M C90767M C91121F
I 1 Unknown Unhown unknown Unknown Unknown Unknown
Control
C91122F
Unknown
0.0 mgkg
C91124F
Unknown
C91133F
unknown
C91152F
unknown
Group 4
C90902M
Unknown
Low Dose
C909 ISM
unknown
3.0 mgikg
C90950M
Unknown
C90951M
Unknown
C90957M
Unknown
Surroeate Verified
NA NA NA NA Confmed Low Confmed Low NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
Low Dose 3.0 mgkg
C91347F C91352F C91367F
Unknown
NA
unknown
NA
PFOSA = Perfluorooctanesulfonamide
PFOSAA = Perfluorooctanesulfonamidoacetate
EtFOSE = Narrow Range N-Ethyl Perfluorooctanesulfonamido ethyl alcohol
M556 = C8F 17S02N((H)CH2C00)
PFOSEA = Perfuorooctanesulfonyl ethylamide
Date EnteredIAnalyst:
05/15/00,06/12/00, 09/03/00 CSHLAC
Date VerifiedIAnalyst: 06/05/00.06/06/00 CSH: 02/26/01 hoj
Purity Enteremerifred 02/16/01 LAC
CorrectedPFOS LOQ (0.0613ugig) to include std correctionfactors new LOQ is 0.0491 ugig. LAC 02/19/01
M556 Cone.
O%P
0.00 0.00 0.00 0.00 296 336 0.00 37.4 0.00 29.0 8.62 5.14 0.00 10.9 8.22 7.79 860 591 546 409 522 395 297 292 307 510
Dilution Factor
11 11 1 1 1 1 1 1 1 1 1 1 I 1 1 100 100 100
1 inn ,
100
100
Calc. Cone.
0.00 0.00 0.00 294 333 0.00 37.3 0.00 29.3 8.76 5.15 0.00 10.8 8.29 7.67 86649 58978 55321
407 1 0
52862
29927 29261 30992 51513
Filename
I DO50800004 DO50800017
I DO50800005
DO50800018 DO50800019 DO50800020 DO50800023 DO50800024 DO50800025 DO50800026 DO50800027 DO50800030 DO50800031 DO50800032 DO50800033 DO50800034 DO50800051 DO50800052 DO50800053
, -nn.s- n.-an.-n-na.
DO50800055
DO50800059 DO50800060 DO50800061 DO50800062
Concentration
I of M556
ug/gor%~ee.
<LOQ (0.0308 ug/g) I
<LOQ (0.0308 udg) <LOQ (0.0308 ug/g) <LOQ (0.0308 udg)
98% 112%
0.0373 <LOQ (0.0308 ugig) <LOQ (0.0308 ug/g)
~~
<LOQ (0.0308 udg)
I <LOQ (0.0308 udg)
<LOQ (0.0308 ugig) <LOQ (0.0308 ugig)
1<LOQ (0.0308ugig) 4"? 52.9 39.7 29.9 29.3 31.0 51.5
Mean M556
Ue/P
<LOQ <LOQ 105%
<LOQ
58.9
36.3
RSD
Std Dev
MS/MSD RPD
I
NA
NA
NA
NA
13%
I NA NA
I I
1 %;
9.51
ETS-8-7.0
3M EEnxcveil r97onmental Laboratory
Lvr Week 53 TOX-00 I-liver2 12- 1OO.xls
5/31/2001
4:48 PPMage 263
3M Medical Department Study: T6316.1
AMDT# 092597.1 CovanceiY 6329-212
Study: Product Nnmber(Test Substance): Matrix: MethoaRevision: Analytical Equipment System Number: Instrument SofhvareiVersion: Date of Extractiodhalyst: Date of Analysisihalyst: Date of Data Reductiodhalyst:
Sample Data
104 Week Dietary Carcinogenicity Study with Narrow Range (98.1%) N-Ethyl PerfluorooctanesulfonamidoEthanol in Rats
T-63 16 (EtFOSE-OH)
Rat Liver
ETS-8-6.0 & ETS-8-7.0
Filename:
See Below
Davey 070799
R-Squared Value: See Attachments
MassLynx 3.3, 3.4
Slope:
See Attachments
2/29/00 SAL
Y-Intercept:
See Attachments
05/08/00, 05/24/00,08/21/00,08/23/00 IASIHOJMMH
05/09/00, 05/25/00,08/22/00, 08/28/00 IAS/MMH/HOJ
WEEK 53 RAT LIVER
lot 529
PFOSEA Purity
Correction Factor
Unknown
Unknown
Matrix Blk
RBL02290-Liver Blk-5
Unknown
RBLO2290-Liver Blk-6
Unknown
NA NA
Control
C9075 IM
Unknown Unknown
0.0 m g k g
C90752M C90754M
Unknown Unknown
C90767M
Unknown
Group 1 Control 0.0 mg/kg
C91121F C91122F C91124F C91133F C91152F
Unknown
Unknown
Unknown
NA
NR
1
Unknown
NA
NR
1
Unknown
NA
NR
I
Group 4 Low Dose 3.0 mg/kg
C90902M C90918M C90950M C90951M
Unknown
NA
NR
I
Unknown
NA
NR
1
Unknown
NA
NR
1
Unknown
NA
NR
1
Unknown
NA
NR
1
Unknown
Unknown
Unknown
Unknown
Unknown
PFOSA = Perfluorooctanesulfonamide
PFOSAA = Perfluorooctanesulfonamidoacetate
EtFOSE = Narrow Range N-Ethyl Perfluorooctanesulfonamidoethyl alcohol
M556 = C8F 17S02N((H)CHZCOO)
PFOSEA = Perfuorooctane sulfonyl ethylamide
Date EntereaAnalyst:
05/15/00, 06/12/00,09/03/00 CSWLAC
Date Verifiedihalyst: 06/05/00.06/06/00 C S H 0212610I hoj
Purity EnteredNerified: 02/16/01 LAC
Corrected PFOS LOQ (0.0613 ug/g) to include std correction factors new LOQ is 0.0491 ug/g. LAC 02/19/01
NR
NA
NR
NA
NR
NA
NR
NA
NR
NA
NR
NA
Yl
hlA
NR
NA
Analytical Report: FACT-TOX-001 LRN-U2103
NR
NR
NA
NR
NR
NA
NR
NR
NR
??!.
I,.TA.
NR
NR
NA
NR
NR
NR
NR
NA
NR
NR
NA
ETS-8-7.0
3M EEnxvceilr97onmental Laboratory
Lw Week 53 TOX-OOI-liver2 12- 1OO.xls
513 1/2001
4:48 PPMage 264
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Study: Product Number(TestSubstance): Matrix: MethodRevision: AnalyticalEquipment System Number: Instrument S o h a r e N e r s i o n : Date of ExtractioniAnalyst: Date of AnalysisiAnalyst: Date of Data ReductiodAnalyst:
Sample Data
104 Week Dietary CarcinogenicityStudy with Narrow Range (98.1%) N-Ethyl PerfluorooctanesulfooamidoEthanol in Rats
T-6316 (EtFOSE-OH)
Rat Liver
ETS-8-6.0 & ETS-8-7.0 Filename: See Below
Davey 070799
R-Squared See Attachments
MassLynx 3.3,3.4
Slope: See Attachments
2/29/00 SAL
Y-Intercept See Attachments
05/08/00, 05/24/00,08121/00, 08/23/00 IAS/HOJIMMH
05/09/00, 05/25/00,08/22/00,08/28/00 IASMMWHOJ
Analytical Report: FACT-TOX-001 LRN-U2103
WEEK 53 RAT LIVER
Group
Sample #
Concentration
Dose
of PFOS ug/g or ?'e Rec.
Method Blk
RBL02290-H20 Blk-5
<LOQ (0.00491 opig)
Matrix Blk
RBLO2290-H20 Blk-6 RBLO2290-Liver Blk-5
<LOQ (0.00491 upig) <LOQ (0.00491 upig)
QC - 250 ppb
RBLO2290-Liver Blk-6 C90714M-250 ppb-MSJ-1 C90714M-250 ppb-MS-5-2
<LOQ (0.00491 upig)
177%
*
100%
Group 1
C90714M
0.560
Control
C90751M
0.378
0.0 mg/kg
C90752M
0.796
C90754M
0.693
C90767M
0.428
Group 1
C91121F
0.301
Control
C91122F
0.305
0.0 mg/kg
C91124F
0.429
C91133F
0.540
Low Dose 3.0 mg/kg
1 C91152F
C90918M C90950M C90951M
0.374
438 924 699
C90957M
818
Group 4
C91323F
66 1
Low Dose
C91347F
86 1
3.0 mg/kg
C91352F
770
C91367F
627
C91371F
549
Mean PFOS ug/g <LOQ <LOQ 138%
0.571
10.390
RSD Std Dev MSIMSDRPD
NA NA NA NA
56%
30.7 0.175
25.5 0.0993
Concentration of PFOSA
ug/gor%Rec.
<LOQ (0.0123 udg) CLOQ (0.0123 udg)
<LOQ (0.0123 ugig) <LOQ (0.0123 odg)
77% 95%
<LOQ (0.00614 udg) 0.0354 0.0117 0.0183 0.0196
II 0.0125 <LOQ (0.00614 u d g ) 0.0253 0.0159 0.00971
695
I89
40.9
23.7
21.8
21.9
17.7
26.7
694
123
32.2
Mean PFOSA
ug/g <LOQ <LOQ 86%
0.0182
0.0139
28.2
RSD Std Dev MS/MSD RPD
NA NA NA NA
21%
Concentration of PFOSAA
ng/g or YORec.
cLOQ (0.0307 udg)
<LOQ (0.0307 udg)
<LOQ (0.0307 ugip) <LOQ (0.0307 udg)
109% 120%
<LOQ (0.0307 ugip) 0.05
<LOQ (0.0307 udg)
Mean PFOSAA
RSD Std Dev
+114%
5 5 . 7 1 ::
4.37
56.3
47.6 I
11.9 5.67
ETS-8-7.0
3M EEnxvceilr9o7 nmental Laboratory
LVTWeek 53 TOX-001-liver212-1OO.xls
513 112001
4:48 PPMage 265
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance##6329-212
Study: Product Number(Test Substance): Mat& MethodRevision: Analytical Equipment System Number: Insbument SoftwareNersion: Date of ExtractiodAnalyst: Date of Analysis/Analyst: Date of Data ReductionIAnalyst:
Sample Data
104 Week Dietary CarcinogenicityStudywith Narrow Range (98.1%) N-Ethyl PerfluorooctanesulfonamidoEthanol in Rats
T-6316 (EtFOSE-OH)
Rat Liver
ETS-8-6.0 & ETS-8-7.0
Filename:
See Below
Davey 070799
R-Squared Value: See Attachments
MassLynx 3.3,3.4
Slope:
See Attachments
2/29/00 SAL
Y-Intercept:
See Attachments
05/08/00,05/24/00,08/21/00,08/23/00 IASIHOJIMMH
05/09/00,05/25/00,08/22/00,08/28/00 IASIMMHMOJ
WEEK 53 RAT LIVER
Group Dose
Sample #
Method Blk
Matrix Blk
QC - 250 ppb
Group 1 Control 0.0 mgikg
Group I Control 0.0 mgikg
RBL02290-H20 Blk-5
RBL02290-H2O Blk-6
RBL02290-Liver Blk-5
RBL02290-Liver Blk-6
C90714M-250 ppb-MS-5-1
C907l4M-250 ppb-MS-5-2
C90714M
C90751M
C90752M
C90754M
C90767M
I
C91121F
C91122F
C91124F
C91133F
Group 4 Low Dose
C90902M C90918M C90950M C9095 IM
Low Dose 3.0 mgikg
C91347F C91352F C91367F
Concentration of EtFOSE
n& or % Rec. NR NR NR NR NR NR NR NR NR NR NR NR NR NR NR NR NR NR NR NR NR NR NR NR NR NR
PFOSA = Periluorooctanesulfonamide PFOSAA = Perfluorooctanesulfonamidoacetate EtFOSE = Narrow Range N-Ethyl Perfluorooctanesu~fouamidoethyl alcohol M556 = CSF17SO2N((H)CH2COO) PFOSEA = Perfuorooctanesulfonyl ethylamide Date EntereUAnalyst: 05/15/00, 06/12/00,09/03/00CSWLAC Date VerifiediAnalyst: 06/05/00.06/06/00CSH: 02/26/01hoj Purity EnteredWerified 02/16/01 LAC
Corrected PFOS LOQ (0.0613ug/g) to include std correction factors new LOQ is 0.0491 ug/g. LAC 02/19/01
EtFOSE
NR
I
NR
Std Dev
NA NA NA
Concentration of M556
<LOQ (0.0308 udg)
<LOQ (0.0308 udg)
98%
112%
<LOQ (0.0308 udg)
I
0.0373 <LOQ (0.0308
udg)
1
i L 0 Q (0.0308 udg)
CLOQ (0.0308 ug/g)
<LOQ (0.0308 udg)
<LOQ (0.0308 upig)
<LOQ (0.0308 udg)
<LOQ (0.0308 udg)
<LOQ (0.0308 udg)
59.0
105% <LOQ
RSD Std Dev MS/MSD RPD
NA NA NA NA 13%
NA NA
NA NA
26.2 9.5 I
Analytical Report: FACT-TOX-001 LRN-U2103
Concentration of PFOSEA
ug/g or % Rec.
NR NR NR NR NR NR
NR NR NR NR NR NR
NR
NR NR NR NR NR NR
?!P,
NR NR NR NR NR NR
Mean PFOSEA
ug/g NR NR NR
NR
NR
RSD Std Dev MSMSDRPD
NA NA NA
NA NA
NA NA
ETS-8-7.0
3M EEnxvceilr97onmental Laboratory
Lvr Week 53 TOX-001-liver212-1OO.xls
513 1/2001
4:48PPMage 266
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
3M Environmental Laboratory
Page 267
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
3M Environmental Laboratory
Page 268
3M Medical Department Study: T6316.1
I
MI' 8 0o"nhr
3M Environmental Laboratory
Analytical Report: FACT-TOX-001 LRN-U2103
Page 269
3M Medical Department Study: T6316.1
AMDTX 092597.1 Cov.rrr# 6329.212
Analytical Report: FACT-TOX-001 LRN-U2103
u...s coo=&=
3M Environmental Laboratory
Page 270
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
3M Environmental Laboratory
Page 271
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covanee# 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
IR sample x
C90842M C90844M C90850M C90851M C90854M C9085SM C90856M C90858M C908MM C90864M C9086SM C90867M C90869M C90871M C90881M C9088zM C90883M C90884M C90885M C90889M C90893M C909WM C91252F C91253F C91254F C91256T C91264F C91178F C91279F C91286F C91292F C91294F C91295F C91301F C91303F C91307F C91310F inat=
1aitl.l Wt.
I
0 9962 I OIM
o 9930
1 0565 0 9872 0 %?I I0485 I 0156 I 0370 I0137
I oms n 9923
11355 I nsii I 0129
n 9909
0 9926 0 9874 10068 I 0299 I 0178 10372 I1046 I 0730
n 9834
0 9%3 I0678 11455 I nizn I 0412 10162 I W46 1.0159 I 1103 0 9908 10083 I 0132
Tof.1 Ma..
ariiuer
D NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
SFOS Sld
Comtbo Fartor
n 927s
0 9275
n 927s
0.9275
0 9275 0 9275
0 9275
n 927s n 927s n 9275
0 9275
n 927s
0.9275
n 9275 n 927s
0 9275 0 9275
n 9275
0 9275
0 9275 0 9275
n 9275
0 9275
0.9275
0 9275 0 9275
n 9275
0 9275
n 9275
0 9275
0 9275
0 9275
0 9275 0 9275
0 9275
0 9275 0 9275
La1 171
PFOS Purity
correetion F..,.,
n 8640 a 8640 n 8640
0 8640
n 8640
0 8640
0 8640
n 8640
0 8640 o 8Mn
0 8640 0 8Mo
n 8640
0 8640
0 8640
o swn n 8640
0 8640 o 8640 0 8640
o 8640
0 8640
0 8640
0 8640 o 8an 0 8640 0 8640
0 8640
n 8640
0 8640 o 8640 0 8640
n 8640
0 8640
0 8640
0 8640
0 8640
S"WOL.l. Verified
NA NA NA NA NA NA NA NA Low, Not C o o l i d NA NA NA NA NA NA NA NA Low, Not C o n C i NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
Filename R-Squared Valve slope Y-blercept
see Below
See Attachments Ses Aua~hments See AUachmenta Box 00412. 00413
PFOS Coo*.
n& 975 268 287 7% I104 458 106 836 424 774 469 635 298 595 267 492 239 376 642 232 371 165 437 270 533 403 381 643 IW 592 124 294 56 0 235 41 1 141 319
PFOS Dilufiam Fmlor
200 2w 200
2W 2W ZW 2w 200 Iwo 2w 200 2W 200 2W 2w 2w 200 2W ZW 200 200
zw
5W 5W 500 JW 5W 5W 500 5w 5W 5W 500 5W 5w 5W 500
PFOS
C d C . cooe.
nr/s 156858
42289 46316 120793 179256 73931
~n303w038
42 3
A030Mw39
46 4
~0~03mn
121
AO303wO41
179
~n303wo44
73.9
16276
A0303M445
I6 3
131992
AO303OM46
132
337224
AO8ISwO88
337
122357
~0303~48
122
74361
A0303WSI
74 4
102548
AO303W52
103
42001
A0303W53
42 0
90688
A0303WS4
907
42229
A03030055
42 2
7%28
A0303W58
79 6
38587
A0303W59
38 6
61036
AO8ISwO91
61 0
1022%
A0303Mm)
102
36130
A0303W6l
36 1
58405
26321
158371
100973
2171in
161881
143127
231922
39747
227867
48865
I 17280
22079
84658
166184
56102 Irllm
RSD Std DE" MSIMSD RPD
78 I 70 3
54 n
68 j
ETS-8-7 0
3M EEnxevl9i7ronmental Laboratory
Lur Wuek IO5 (2) TOXM)I -liver212-lCi.x1s
Page 272 5131'2WI 4 48 PM
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
study
PmduelNumbcr(Teslsub~aoeE) Matnr MefhMevismo Aoalytioal EquipmentSydemNumber lnslrumnl SaRuareNemdn Date ofErlractiod~aiys1 Date o f h a l y s i d h l y s t :
~ a o rf m~a ~ e d ~ ~ t i ~ d ~ d ~ a
Sample Data
104 Week Dietary Csmnogelucity Study ritb X m x Range (98 1%) N-Ethyl Perflwmoftanesulfondo
14316 (EIFOSEGH) Rat Lwer ETS-8-6 0 & ETS-8-7 0 h i i s 062498, Davey 070799 MassLpx 3 3 02/141W,OY16/W RWWISAL 02/zlIW. 01/29/W, 03/01/00,03/03/00,03'041W, 07128100,OS/lS/W MMHiMEEI1AS 01/28/W, 03/01/W, 03103IM). 031OWW. 07/31/00,08/17/W IASMMH
Efhanol in Rats
WEEK 105 RAT LI\
Group Dor
Sample #
101 L-15709 PFOSA Purity
corntion
surrop.t. Verified
Group 3
NA
Mid Dose
NA
30 0 W g
NA
NA
NA
NA
NA
NA
C908MM
unLn0un
NA
CWSMM
Uhoun
NA
C9086SM
UhOWn
NA
C90867M
UhOWn
NA
C90869M
UhOWn
NA
C90871M
UnLnOUn
NA
C90881M
UlblOUll
NA
W88M
Un*ooWn
NA
C90883M
UhOUn
NA
C90884M
UnLnOUn
High. Not C a n f d
C9088SM
UnLnOUn
NA
C90889M
UhOWn
NA
C90893M
UhOW
NA
CWM
UoLnOUn
NA
Crovp 3
C91252F
UnLnOUn
NA
Mid h a e
C91X3F
UhOWn
NA
C91254F
UhOWn
NA
C91256F
UhOW
NA
C912-F
UnLnOWn
NA
C91278F
UnlawUn
NA
C91279F
UnLnOWn
NA
C91286F
UnLnOWn
NA
C91292F
UhOUll
NA
C91294F
unknoun
NA
C91295F
LinLnOUn
NA
C91301F
UhOWn
NA
C91303F
UhOW
NA
C91307F
UhOUn
NA
C91310F
LlhOUn
NA
__..
rrUI ~ esriruomocmesur,
PFOSA = Perfluomtanem
PFOSAA=Pernuoroactam
EIFOSE = Narmw Range N
M556 =CSF17S02N((H)CE
PFOSEA = Perrwmte
:
w
,nyl elbylami&
Date EnlerediAmIyst
/l4/00,03/16/W, 03/11/W,O8/l5/W, 09/03/00LAC
Dale Venfiedihalyrf
03/09/01 bo,
Fuity EnlcrrdRic6fied 01/19/01 LAC
PFOSA COW.
nplr 366 188 323 361 472 518 435 314 633 478 224 271 313 454 324 371 270 53 6 424 338 354 334 386 387 452 382 334 513 236 497 354 377 166 309 330 297 266
PFOSA Dilulbm F.CfW
0 0
20 20 20 20
0 20 20 0 20 0 20 20 20 20 0 200 20 20 20
0 20 20 0 20 20 20 0 0 20 20 0 0 0 0 20
~
PFOSA C.i'. coor.
oeh 7349 36% 6514 6828 9569 10434 8293 6178 12569 9434 4441 5466 5521 8631 6403 7493 5439 10849 8430 6567 6949 6625 6992 736 9190 7676 6251 8954 4670 9154 69M 1M9 3266 5559 66d 58% 5242
~~
A030300087 A030300088 A030300089 A030300090 A0303wo93 A030300094 A030300095 A030300096 A030300097 A03OMoIW AO303WIOI A030300102 A030300103 A0303W104 A0303W107 A030300108 A0303W109 A081500091 A0303W110 A0303WI 1I A0303MI 14 AO3U3WI I5 A030300067 A030300068 A030300069 A030300072 A030300073 A030300074 A0303wo66 A030300075 A030300076 A0303Mx)79 A030300080 A0303Mx)81 A03030008Z A030300083 A030300086
conrcotr.uon of PFOSA
Ye's or x h.
7 35 3 70 6 51 6 83 9 57 10 4 8 29 6 18 12 6 9 43 444 5 47 5 52 8 63 6 40 7 49 544 10 8 8 43 6 57 6 95 6 62 699 7 21 9 I9 7 68 6 25 8 95 4 67 9 55 6% 7 51 3 27 5 56 666 590 5 24
RSD Sld Dev M S M S D RPD
29 I 2 17
25 4
87,
Analytical Report: FACT-TOX-001 LRN-U2103
- P m s A p - cnor.
WE 291 354 506 362 180 977 545 471 583 550 241 253 705 620 350 420 295 839 866 802 430
_48_8 282 430 408 533 271 699 239 91 1 351 471 261 248 422
- 356 ??
PFOSAA Dilution Fmrtor
20 20 20
a 1w
0 20 20 20 20 20 20 20 20 20 20 0 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20
PFOSAA Cdr. Conc.
nglg 5840 6967 10194 6845 36513 19689 10390 9279 11573 108J4 4761 5093 12412 11794 6916 8486 5935 17W2 17198 15569 8459 9694 5114 8W9 8292 I0693 5070 12207 4729 17499 6906 9383 5143 4470
,,.-8525
7067
Filmam.
COn-b.1i00
dPFOSAA
uglg or x b.
A0303wO87
5 84
A030300088
697
A030300089
IO 2
A0303w090
6 85
A030303341
36 5
A030300094
19.7
A0303wo95
10 4
A0303000%
9.28
A0303W097
I1 6
A0303WlW
IO 9
A0303WIOI
4 76
A030300102
J 09
A030300103
12 4
A0303W104
II 8
A0303W101
692
AO303W108
8 49
A0303W109
594
AO815KW92
170
A0303W110
17 2
AO303Wlll
IS6
AO303W114
8 46
A030300115
A030300067
A030300068
A0303wo69
AO303CKx312
A030300073
A030300074
A030300066
A030300075
A030300076
A030300079
A030300080
A030300081
A030300082
."~"~"""", A030300083
~YI",wo"
Mesa PFOSAA
Yglg
RSD Sld D r v MS4MSD W D
W8 6 95
43 6 3 48
ETS-8-7 0
3M EnExvceli9r7 onmental Laboratory
L I T W e e l 105 (2) TOXM)I-liver2l2-IW XIS
5/31,2MI
4 48 PPMage 273
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covanceil6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
WEEK 105 RAT L
hUP
Dose Group 3 Mid Dose 30.0 &g
Gr0.p 3 Mid Dose 30 0 mgkg
. .Drnr~."."....",..,~.. ~ -1.
:R
Smnph #
C9084zM C90844M C90850M C908SIM CH1854M C908SSM C90856M C90858M C908WM C9086dM C9086SM C90867M C90869M C90871M C90881M C90882M C90883M C9088bM C90885M C90889M C90893M C909wM C912S2F C91253F C91254F C9125bT C91264F C91278F C91279F C91286F C91292F C91294F C9129SF C91301F C91303F C91307F C91310F
lot unknown
ElFOSE Purity Ca.-tiO. F..tO, Unknoun unknoun UnknOUll UnknOW UnLm*ll unknown Unl;MWI
UnknOW UllklWUll UnknOWl UhWI unknoun UnknOUlI
lJhU?l UnknOWI
Unknown Un*OO*rn
UhOWI Ur*naUIl UnknOWn unknown lin*m.w UbWn UnknOUn
unknoun UnknOUn UhW UnknO*ll UnknOull UnknOSIl UnknO*ll UnknOUn unknoun unknoun unknoun UnLnOUll UnknO*rn
EIFOSE
EIFOSE
EIFOSE
Fileomme
Concealratio
Mc.n
RSD
C00.2.
Dilution
C.k. Coar.
ofEtMSE
ELFOSE
Sld I*v
OYl
F.Ct0,
nS/s
M W S D RPD
NA
95 0
I
95 3
A072800017
NA
168
1
166
A072800018
NA
39 I
1
39 3
A072800019
NA
167
I
IS8
~n7280~20
NA
39 I
I
NA
963
I
39 6
A072800021
no
~072800024
NA
34 5
1
319
A012800015
NA
662
I
65 2
AO~Z~OM)~~
NA
8n s
I
80 0
~n72800027
NA
76 3
I
75 2
~n72nwo28
NA
137
135
A072800031
NA
80 6
1
81 2
A072800032
NA
86 0
I
7s 7
~0728~033
NA
51 3
I
48 8
~0728~034
NA
58 8
I
58 n
A072800035
NA
153
1
I55
A072800038
NA
I8 4
I
18
A072800039
NA
72 4
I
73 3
~n728w040
NA
219
I
218
~07?8~041
NA
49 2
I
47 7
A072800042
NA
81 3
I
NA
OW
I
NA
84 I
I
NA
I12
I
79 9
AO7t8000IS
OW
A0728w046 UCQ(00614ugig)
n 0883
76 2
~ ~ 2 8 ~ 0 4 7 o 0762
10s
A0728wO48
n 10s
47 I 00415
NA
969
1
985
A072800049
0 098s
NA
97.8
I
98 I
A072800052
o 0981
NA
111
I
104
A071803353
0 104
NA
147
129
A071800054
0 I29
NA
24 I
1
23 8
AO728000SS <LCQ(OO614ug/g)
NA
111
107
A0728wO56
0 107
NA
154
NA
138
151
A0728000S9
0 151
137
~n728mm
n 137
NA
9 69
NA
660
9 54
A072800061 <LOQ (0 0614 "pig)
59 4
~0728~062
n 05%
NA
I In
NA NA
- 89 I 33 1
122
A072800063
0 I22
88 I
~n7280~66
0 0884
33 3
A072800067 CLOQ (0 0614 ug/g)
0 103
~
26 9
o 0276
M556
C.k. cooc.
NA
345
20
NA
421
20
NA
614
2n
NA
797
20
NA
427
2n
NA
255
20
NA
590
2n
NA
778
20
nE/L
10857 6798 8480
A030300088 A030300089
680
I
848
11631
A030300090
I1 6
16151
~0303~093
162
8M3
A0303W094
860
4869
A030300095
487
11618
A030300096
II 6
15449
~030300097
is4
NA
591
2Q
NA
399
zn
NA
312
20
NA
453
20
NA
S45
20
11779 7888 6286 798s 10364
AO~O~WIW 118
A0303WIOI
7.89
~n3n3win~
619
A0303W103
79
A0303M104
104
NA
326
20
NA
520
20
NA
264
2n
6427
AO303W107
643
insw
AO303W108
105
5327
A0303W109
5 33
NA
729
20
NA
618
20
NA
413
20
NA
393
20
NA
272
20
NA
537
2n
NA
455
20
NA
770
20
14760 12272 802s 7724 5398 9729 8473 15661
AO~ISW~?
148
AO303WIIO
123
AO303Wlll
803
A0303WII I
7 72
~ 0 3 0 3 ~ 1 1 s 540
A030300067
9.73
A0303wo68
847
~03n300069
157
NA
512
20
NA
3S7
20
10275 6689
~n303~072
io3
A030303373
669
NA
584
20
NA
226
20
NA
123
2n
NA
479
20
NA
517
20
NA
isn
20
NA
415
20
NA
620
20
NA
268
20
Ndl
zy
2:
10199 4468 IW5I 9421 10286 2961 7474 Its22 5325 ~rnn"r" "
~0303~074
102
A030300066
447
A03030007S
I01
AO303WO76
942
~ 0 3 0 3 ~ 0 7 9 in3
A0303wO80
296
~n3n3~081
747
.-.-.~""", A030300082
A0303WO83
I.",",yyyDy
12s
,^. 5~ 3 2 "1
RSD Sld I*v M W S D RPD
34 6 3 29
38 8 J 33
ETS-8-7 0
3M EEnxcvel9i7ronmental Laboratory
L\T Week 105 (2) TOXdOl-l1\cr112-100 1.
5 3I'ZWI
4 I 8 PPMage 274
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covancdl6329-212
StUdY m u d Sum!m(Teest S u h c e ) Malm MethdRevamn Analfllsal Equipmmt SystemNumber I n s t m o t SoRwmNemion
Date ofExtractiodAnaly* Date o f h l y s d A n a l y s 1 Dale of Dals RcducI~on/Analyst
Sample Data
104 Week BeIary Carcmopnxlty Study wlh S a m w Range (98 1%) A-Ethyl PerfluomtanenulfooamidoEthanol m Rats
T-6316 (ElFOSEOH)
Rat Llwr
Filename
See Below
ETS-8-6 0 R ETS-8-7 0 Armlib 062498, Davey 070799
R-Squared ValuSee Allaobmoltr
Slop
See A t l ~ n t s
MassLynr 3 3
Y-Intercept See Attschmenla
02141W. DYl6iW RWWiSAl 02/21/W, 01/29/W,O3/01lW.03103100,03/041W,07128100,08115lW MMIUMEEAAS
BorW012,W013
o z 1 2 8 i ~0. 3rni/w,O ~ I O ~ IVW~,I M I W07. 1311~0. 8117m IASIMMH
I`EEK 105 RAT L mse
ER
s.mpi. #
Sulrogmtr
vlnnd
Gmup 3
C90842M
NA
Mid Dose
C90844M
NA
30 0 m g k g
C90850M
NA
C90851M
NA
C90854M
NA
C9085JM
NA
C90856M
NA
C90858M
NA
C908MM
NA
C0864M
NA
C9086SM
NA
C93867M
NA
C90869M
NA
C90871M
NA
C90881M
NA
C90882M
NA
C90883M
NA
C90884M
NA
C93885M
NA
C90889M
NA
C90893M
NA
C909WM
NA
Group 3
C91252F
NA
Mid -re
C912S3F
NA
30 0 m a g
C91254F
NA
c91256F
NA
C91264F
NA
C91278F
NA
C91279F
NA
C91286F
NA
C91292F
NA
C91294F
NA
C9129SF
NA
C91301F
NA
C91303F
NA
C91307F
NA
C91310F
~
NA
,mate
PFOSA = PerfluomodanenulfonarmdP
PFOSAA= ~rnuomoctanesvlronarmdoacclate
EIFOSE = Narmr Range S-Ethyl PFrflvomactanesulfonamidoethyl alcohol
M556 = C 8 F 1 7 S O l N ( ( H ~ H 2 C ~ )
PFOSEA = Perfuomoslane sulfonyl clhylarmdc
Date EnferedIAnalyst 03/14/W, 03/16JW, 03117lW. 08/15l00,09103lW LAC
Date VcrificlAnalyrt 03109/01hoj
Fumy EnteredNsnGed 02119l01 LAC
PFOSEA
C*"C
OYg OW OW OW OW 294 2 53 3 93 160 OW OW OW OW 0 780 364 6 14 OW OW 0 180 3 29 OW 3 43 000 I03 0 230 OW OW 4 13 2 91 OW 3 35 OW 2 55 000 3 18 OW 16 8 OW
DilYLiOll
I I
1 I I I I I I I
I I I I I I I
C.lC. Con;r.
OW OW 298
OW 0 687 3 46 6.06 OW OW 0 182 3 27
OW 2 54 OW 2 86 OW 16 6 OW
Fik..U.e
A072800017 A072800018 A0728W19 A072800020 A012800021 A072800024 A072800025 A072800026 A072800027 A072800028 A072800031 A072800032 A0728W33 A072800034 A0728W035 A072800038 A072800039 A072800040 A0728W41 A072800042 A0728WMS A0728CiM46 A072800047 A072800048 A072800049 A072800052 A072800053 A072800054 A0728WOSS A072800056 A072800059 A0728000M A0728ooo61 A072800062 A072800063 A0728W66 A072800067
Con-mim
OfPFOSEA
Ys/gor%Rec.
< L o p (00307 "dg)
<CQ (0 0307 "pig)
aw UCQ(00307 udg) (o 0307 <LCQ (0 0307 "pig) <W (0 0307 "pig) UW (0 0307 "gig) UCQ(0 0307 udg) C W (0 0307 "pig) a W (00307 "gig) <W (00307 "gig) <La2(0 0307 "gig) C W (0 0307 ngip)
aw <W (0 0307 "pig) (0 0307 "gig)
<W (0 0307 uglg)
aw aCQ(0 0307 uglg) (0 0307 "gig)
<LOP (0 0307 `pig)
UCQ(00307 "pig)
<W (0 0307 uglg)
<CQ (0 0307 "gig) a C Q (0 0307 "ale)
n w am CLCQ(0 0307 q l g ) (0 0307 "pig)
(00307 "gig)
nCQ(0 0307 <LW(00307 "gig) CLOQ (0 0307 "gig) UW (0 0307 `pig) aoQ(0 0307 "pig)
uw aOQ(0 0307 "gig) (00307 "gig)
aw < L o p (0 0307 "gig) (0 0307 "dg) <W (00307 ugip)
noo (0 0307 "PIF)
Hem PFOSEA
"gig
UW
4 r*?
RSD
Std I*r M M S D RPD
NA NA
NA N 4
Analytical Report: FACT-TOX-001 LRN-U2103
ETS-8-7 0
3M EnExcveli97ronmental Laboratory
LITWCCI~O5 ( 2 ) TOX001-hver2l2-lCC XIS
5/3112WI
4 48PPMage 275
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
Dale of Dab RcducliodAnalynl
Sample Data
104 Weak Dlemy Canmogerucdy Sfudy with N-u Range (98 1%) N-Ethyl PerfluomarlanenulfonarmdoEthanol in Rats
T-6316 (EIFOSE-OH)
Rat Liver
Filenam
See Altachmenfi
ETS-8-60 d ETS-8-10
R - S q w d Valva See Allachmeots
Amlia 062498, Darey 070799
SlOpC
Sce Allnshmnls
MnssLp 3 3
Y-Inlmopt
See Attachments
02/14/00.02116/00 RWWISAL
0221IW. 02/29lW, 03/0liW. 03,031W. 03104iW.071281W. 08ll51W MMSCWE54.5
02/281W,01101/W, 03/03100,03/06/W,07/31/W. 08/17/W LASiUMH
WEEK 105 RAT LI
R sample n
PfOS CdC. cone.
GGmmUuDp 3 Mid Dose 30 0 mgkg
C90842M C90844M C90850M
wg 156858 42289 46376
C90851M c90854M C90855M C90856M C90858M C908M1M C90864M C9086SM C90867M C90869M C90871M C90X81M C908X2M C90883M C90884M
120793 179256 73931 16276 131992 337224 122357 74361 102548 42WI 90688 42229 79628 38587 61036
C908XSM C90889M C90893M
102254 36130 58405
omup 3 Mid Dou
C90900M C91252F C91153F
26321 158371 IW973
30 0 m#he
C91254F C91256F C91264F C91278F C91279F
217110 161881 143127 231922 39747
C91286F C91292F C91294F
227867 48865 I17280
C91295F C91301F
22079 84658
.r.ru>=rer,,uomart*nu
C91303F C91307F C91310F
ate
166184 56102 126168
PFOSA = Perflw-laoe.
PFOSAA = Perfluomfar
EIFOSE = N-w Ranp I
MSJ6 =C8F17SOZN(o( :oO)
PFOSEA = P e r f m m l a n c sulfonyl ethyl-&
Date EntemdIAnalyrf
03114/~,03/16'00,03117100, 08!151W,
Dale VcritiedImlyd
03/09101 haj
pwity EnlcmdNeriTrsd OY19101 LAC
coo.rot..tiia of PFOS
uglg or Y. Rec. 157 42 3 46 4 I21 179 73 9 163 132 337 I22 74 4 103 42 0 91 42 2 79 6 38 6 61 0 102 36 1 58 4 26 3 158 101 217 162 143 232 39 7 228 48 9 117 22 I 84 7 166 56 I 126
091031W LAC
RSD
PMSA
CWIC~~f..fiO~
Std Ikv
Cdr. Cooc.
afPFOSA
MSMSDRPD
ns/e
uyg or K r(re.
7349
7 35
36%
3 70
6514
651
6828
6.83
9569
9 57
10434
IO 4
8293
8.29
6178
6 18
12569
12.6
9434
9 43
4441
4 44
5466
5 47
5521
5 52
8631
8 63
6403
6 40
7493
7 49
5439
5 44
10849
10 8
8430
8 43
6567
6 57
78 1
6949
6 95
901
70 3
6625
6 62
6992
699
7206
7 21
9190
9 19
7676
7 68
6251
6 25
8954
8 95
4670
4 67
9554
9 55
6960
6%
1509
7 51
3266
3 27
5559
5.56
6664
666
54 0
5896
590
I 27
- 68 5 ~
5242
5 24
RSD sld D e MSIMSD RPD
29 1 2 17
25 4 I 72
PFOSAA Cak.COW.
ogls 5840 6967 10194 6845 365 I 3 1%89 10390 9279 11573 10854 4761 5093 12412 11794 6916 8486 5935 17W2 17198 I5569 x459 9694 5114 8009 8292 10693 5070 ' 12207 4129 17499 6906 9383 5143 4470 8525 7067 6657
Eaoeenmtion OrPposIuI
uyg or K b.
5 84 697 10 2 6 85 36 5 I9 7 10.4 9 28 II 6 10 9 4 76 5 09 124 11 8 6 92 8 49 5 94 17.0 17 2 IS 6 8 46 9 69 5 II 8 01 8 29 IO 7 5 07 12.2 4 73 17 5 6 91 9 38 5 I4 4 47 8.52 7 07 665
Analytical Report: FACT-TOX-001 LRN-U2103
RSD std Ik" MSMSDRID
60.8 6 95
43 6 2 de
EtFOSE C.lC corn.
95.3 166 39 3 I58 39 6 970 32.9 65 2 80 0 75 2 135 81 2 75 7 48 8 58 0 I55 48 8 73 3 218 47 7 79 9
ow
76 2 105 98 5 98 I 104 129 23 8 IO7 I51 137 9 54 59 4 122 88 4 33 3
Conrrnlr.Hoo ofElFOSE
uygorY.Rre.
0 0953 <LOy (0 0614 "gig) ~LCQ(00614u~g)
a IS8 aw)(00614 wk)
0 0970 UoQ(OO614ug/g)
0.0652 0 0800
0 0752 0 135 00812 ~LCQ0(O07O56714ug/g)
Mean EIMSE
"gk
<LcQ(oM14"#e) 0 I55
<Oy(O0614u#g) 0 0733
'La) (00.2016814 udg)
0 0799 aw)(O0614ug/g)
0 0762 0 105 0 0985 0 0981 0 104 0 I29 < L o p (0 0614 "gig) 0 107 0 151 0 137 SLCQ (0 0614 "gig) 0 0594 0 122
00883
RSD sld DW MSMSD RPD
47 1 00415
26 9 0 olio
ETS-8-7 0
3M EEnxcveli97ronmental Laboratory
L w Week IO5 (2) TOXa01-liucr212-I00XIS
513112001
4 48 PPM age 276
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covancdl6329-212
Sample Data
WEEK 105 RAT L
:R s.mpir x
M556 C.l.2. Cow.
n#g
C90842M
inns7
Md h
C908MM
6798
6 80
CM8SOM
8480
8 48
CW851M
11631
I1 6
C90854M
16151
162
CM8SSM
8603
863
C90856M
4869
4 87
CM8SXM
11618
I1 6
C9086oM
15449
15 4
cwn64M
11779
11 n
C90865M
78x8
7 89
CM867M
6286
6 29
C90869M
7985
799
CM871M
1n3~
10 4
CW881M
6427
6 43
cmnm
ins00
10 s
CM883M
5327
5 33
C90884M
14763
1476
CM885M
12272
I? 3
C90889M
802s
n 03
7724
7 72
CM900M
5398
5 40
Gmvp 3
C9IzS2F
9729
9 73
Mid Dore
C91253F
8473
I47
30 o mene
C912S4F
1s64.1
I5 7
c91256F
10275
10 3
C912MF
6689
6 69
C91278F
10199
10 2
C9127YF
446s
4 47
C91286F
1w51
IO 1
C91292F
9421
9 42
C91294F
10286
10 3
C91Z9SF
2961
2%
C913OIF
7474
7 47
C91303F
l2SZ2
1:s
C91307F
5325
5 32
C9I3IOF
SW6
s ni
PFOS ~ Pcrfluomoclvles mte
PFOSA = Perfluomoctmnl bnarm&
PFOSAA ~ Pcrfluomaclanesulfondos~tate
EtFOSE = Narmw Rango N-Ethyl Perfluomaelanenulfonamidoethyl alcohol
MS56 =C8F17SOW((H)H2CoO)
PFOSEA = Pcrfwmactane sulfonyl ethylamidr
~~i~~~ t ~ r r d / ~ n s i0~31~14tiw. O ~ I I O Wn,3/17iw, nniis!w, 09103iw LAC
Date VctiliediAnaly~ 03/09/01 hoj
Punty EnnteredNenlied OL'lYIOl LAC
OM)
000
0 182
3 27
OW
34 6
3 37
3 29
00
n 932
0214
000
OW
3 87
2 54
OW
3 22
ow
2 54
0.W
2 86
OW
38 8
I6 6
3 33
OM
Analytical Report: FACT-TOX-001 LRN-U2103
NA NA NA
3M
Environmental ETS-8-7 0 Excel 97
Laboratory
Lvr Week 105 (2) TOXM)I-bver2l2-IW XIS
S,3lrx!ill
4 4P8 PaM ge 277
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-213
Analytical Report: FACT-TOX-001 LRN-U2103
EEK 1M RAT LI
Cnup raw
1 S.mpkX
1"llhl W'
I
T.L.1r.f". dL*a
PFOS s *
C."=dh"
Sung.* V"W
- PFOS
C.=.
PmS C.*. cos.
I
Q.Ct.
n ,0750
NA
9275
n I OM1
NA
9275
I0130
NA
09275
NA
867
NA
829
NA
250
IUh
321257
1,337.
313
98979
990
0 9881
NA
09275
09911
NA
0 9275
IOU8
NA
0 9275
I0776
NA
0 9275
I os2
NA
0 9275
,0884
NA
0 9275
NA
8M
718021
718
NA
584
236132
236
NA
311
,20112
I20
NA
70.6
26240
26 2
NA
7%
628332
628
NA
416
153299
I51
0 9935
NA
IWW
10069
NA
09275
0 9872
NA
0 9275
I0290
NA
0 9275
I WII
NA
0 9275
Hi&, Not Confirm4
561
NA
742
NA
464
NA
I55
NA
M3
565041
565
295155
295
186556
I87
60124
601
265167
265
,0111
NA
lwMl
Hsgb. Not Co-fiimrd
407
201182
201
0 9%2 I1561
NA
0 9275
NA
0 9275
NA
857
689313
689
NA
642
,4103,
U5
0 993,
NA
0 9275
NA
570
23w
230
C91132F C'II315F C9139f.P
I 0 5989 0 9827 I I502 I1177 IO214
NA
09275
NA
09275
NA
0 9275
NA
0 9275
NA
(I 9175
NA
635
NA
778
NA
542
NA
614
NA
841
509159
509
31737
I1 7
377842
178
220157
220
129837
I10
C91318F CPII4OF
NA
0 9275
NA
09275
NA
851
3,IJSP
341
NA
718
579769
580
C9lJllF
,0145
NA
0 9275
NA
0 9275
NA
626
242581
243
NA
891
355109
355
CP1356F C91157F C913WF
I0115 IO112
VA
0 9271
NA
0 9275
NA
0 9275
NA
21.
NA
.SI
NA
522
41389
42 4
192%)
193
206612
207
C91361F
NA
09275
NA
889
711319
712
C91362F
,0130
NA
0 9275
NA
220
868%
86 9
C91372F
NA
0 9215
NA
639
257881
C91376F C91378P C91lBOF C91017M
0 9840 0 988,
" NA
0 9275
NA
9275
NA
0 9275
NA
0 9275
NA
668
- NA
853
NA
797
NA
151
251932 14C458 324616 2014
C91054M
I0156
NA
0 9275
NA
251
198
C91056M
NA
0 9275
Lov,nolCoofimd
131
10494
C91060M
I w62
NA
0 9275
C91065M
09918
NA
0 9275
NA
252
2w6
NA
.I 2
16 5
CPlOiOM C91071M C11072M
0 9.1
0 9971
n986
NA
U 9275
NA
0 9275
NA
0 927q
NA
25.
205
NA
JI 2
I, I
YA
479
384
C11073M
IWl6
NA
0 9275
NA
I04
83 I
C91076M
I0102
NA
09275
Lgb. NolConfimd
613
502s
C91451F
I0161
NA
0 9275
195
I53%
C914JIF
IO133
NA
0 9275
572
,525
C9145F
10117
NA
0 9l75
217
18803
C91459F C91462F
,0140 I W82
NA
0 9175
YA
0 9275
62 6
221
1W
*9 4 17533
C91467F
IO110
NA
0 9275
174
I
111
C91473F COI47PF
0 9879 I WII
NA
0 9275
NA
a 9275
171
IW
I' s
13901 :c7
CPllSOF C9148SF C9I487F C9148PF
0 9882
NA
09812
NA
- 10175 IO101
NA KA
0 9275
0 9115
n 9175 n 9275
183
I
251
50
- 19 I 143 10"WC MC8
149 10129 62 8 11169
Irntm. LAC
ETS-8-70
3M EnL Cvd9i7ronmental Laboratory
Page 278
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covance# 6329-212
- - PFOSA PFOSA
- - COK
DUIb.
wr
F.d..
NA
316
50
q'g .r x h.
NA
316
50
NA
251
50
NA
367
50
I8 J
NA
353
50
178
NA
84 9
50
406
NA
249
50
NA
358
50
116
NA
288
50
NA
2w
50
I5 I
NA
198
50
A030I00080
NA
I86
50
A030I0008I
NA
206
50
NA
291
50
N*
176
50
- NA
407
50
NA
- 384
50
16616
1 100
145
868
20 1 16 6
~
NA
25.
50
128w
128
NA
324
50
16226
162
NA
zm
50
1M27
10 6
NA
392
50
17062
A0301W094
I7 I
NA
325
50
14551
A0301W095
1.6
NA
105
50
14949
A03OIwu%
11.9
NA
361
50
18058
A030low97
I8 I
NA
319
50
16126
A0301W1w
16 I
NA
116
50
15274
AO3OIWIOI
151
NA
338
10
16810
AU~QIWIO~
I6 B
NA
125
50
6157
A0301W103
6 16
NA
336
50
16831
AO0301WIM
16 8
NA
364
50
17955
AO301WIO7
180
NA
446
50
22312
AOJOlMlOS
22 3
NA
220
50
10883
AOlOlWlW
109
NA
186
50
I9451
A0301WIIO
195
NA
3u
50
162%
A0301Wlll
16 3
- - NA
380
50
18952
A00301Wll4
I t0
NA
303
50
NA
2 I4
I
NA
2 50
I
NA
43 0
I
NA
IS,
I
NA
272
I
NA
171
I
NA
2 52
I
NA
2 67
I
- NA
0 85
I
NA
I 76
I
NA
166
I
NA
I31
I
NA
1 66
L
NA
0 380
I
NA
2 51
I
NA
2 71
I
NA
2 30
I
NA
I62
I
NA
0 870
I
NA
22,
I
- - NA
0910
I
NA
. 2 91
I
V.luc.8l
** h U n v
A-5a-k
Analytical Report: FACT-TOX-001 LRN-U2103
- PFOSAA - C.u.
sir
459
392 5m
6% 475 37 3 333 819 403 157 358 226 377 5.8 95 5 l0Jl 622
~
314 564 758 585 408 402 ll8 537 524 613 149 413 577
631 608 SM 57s
- 604 604
217 198 74 7 44 8 28 6 19 0
17 7
30 0 21 8 20 1
~
ow OW
ow
OW OW ow 0.W "Y -""
I1 I 7 07
- OW I3 I
- P m A h - mi.#*.
F.U.,
50 50 50 50 50 50 50 50 50 50 50 50 50 50 50 50 50
~
50 50 50 50 50 50 50 50 50 50
0 50 50 50 50 50 50
- 50 50 I I I I I I
i I I
~
I I I I I I I
I I
- I I
- P F O S U
m*mm
C.rnl.t",*"
A Cmk.C o r
21358
A0301W066
dPFOSAA
ugtgor K w.
21,
18476
A0301W067
I85
448.7
A0301W068
448
35222
A00301~9
352
23991%
A0301wO72
23 9
1784
A0301WV73
178
15462
A0301wO74
I55
40328
A030100075
403
l8Sll
A030100076
185
23W8
A030100079
230
17773
A030l00080
178
11445
AO3OlOM8l
114
I8340
A030100082
183
27358
A030100083
271
471
A030100086
472
51758
A030100087
518
26905
A030100088
269
,579,
A0030100089
158
28252
A0301wO90
281
38590 2548
AO301wO91 AO30IwO94
386 151
I8251
A0301Wu95
183
IS76
A0301KQ96
197
20954
AOlOlWu97
210
26299
AOJOlWlM
26.3
25334
AOJOlWlOl
253
33469
A030100102
33.5
17210
AUO33001I0W01IM03
20686
2107 72
28490
A030100107
28.5
31554
AO301W108
31 I
3W22
AO301W109
300
42332 X1.,
A030100110 AW3DIM111
423 271
- ,0114 30712 220
195
74 5
44 5
28 9
19 I
?3 I
30 I
21.8
20 I
ow
ow
I OW
OW
A042800030 <LC6 0123
OW
OM
0.M
000
112
7 21
- OW 12 9
MI.ll PFOSAA
w,
23 6
RSD Sld Der MYMSD W D
56 5 133
26 3 7.08
1111 00614
NA NA
3M Environmental Laboratory
Page 279
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covancd 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
Sur..,.U V"iM
NA NA NA NA NA N.4 N* YA NA NA NA NA NA NA N* NA NA NA NA N* NA NA NA NA NA N.4 NA NA hA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
,.A NA NA NA NA NA
NA NA NA NA NA NA NA NA NA
- EtFOS
-c.n. nr'. k69
293
813
464
331
ow
113
314
363 32 I 310 232 213
466
314 1020 594
~
(39 377
274
4% 776 I79 916 416 746
182 88.
8.2
611
1106 211 518 774
- 1062 5.9 ow ow ow 000 "W ow om
"W
ow
- ow
ow ow ow ow ow uw ow ow ow ow
- OW ow
Y d V L tltl
** mbnu
ElFOSE
I EtFOSE I Flklrm
I
110
A080100020
I
334
A080100021
I
OW
A080100024
I
291
AGBDL00025
I
309
AUII00026
0 3W
I
31.
A080100027
0331
I
323
AOSOI00028
0.323
I
308
A080100031
0.308
I
135
A080100032
0 235
I
207
AQt.0100033
0 207
I
466
A080100034
0 166
I
110
AD80100035
0310
I
1024
A080100038
I02
I
514
I
442
051.
n 442
2
755
(1751
I
279
A080100042
I
432
AO801m015
2
1389
I
469
A0801W317
1
917
A080100018
I
408
A080100049
I
71I
A08010N52
I
777
A0801W353
I
182
I
843
AOZOl00055
10
603.
AOllJWlW
I
llu6
A080100059
I
211
I
522
A0801CW61
1
731
2
2117
A030400085
I
557
A0801M066
I
OW
A081400028
RSD S I 1 Drr MsiMSD RPD
57 8 0 229
131 I30
N* NA
NA NA
Sur"l.l VI-
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA HA NA
NA NA NA NA NA NA NA NA N.4 Nk NA NA NA NA NA
M% cor. Wh
623 633 619 688 641 177 5W 626 553 517 351 510 420 727 I88 8877 8666 457 653 193 710 552 553 614 636 542 839 228 516 307 889 480 789 717 475 656
270 318 OW
Ow
OW
Ow
OW
ow ow
"W
M3% C.k.C.a.
ol/l 28960 29855 30567 32781 32395 8k69 23216 30818 25101 27552 l7w6 25822 20389 36299 9313 US51 37172 22980 32766 9807 32164 24677 27071 30741 3ll5I 26187 41708 11248 16842 25014 lUhl 23712 39723 33977 23656 33352 273 3 I3 OW OW OM OW cc.3
OW
Flklvmr
AOIOIW066
A0101~7
AO301w068
A0301wo69
A030100072
A030100013
AO3OIWOIk
A030100075
A030100076
A030100079
A030100080
A030100081
A030100082
A0301WO13
A030100086
A030I00087
A030100088
A030100089
A0301WOW
A030100093
A03OIWW1
AOJOlWW5
A0301wo96
A030100097
AUIOIWIW
AOJOlWlOl
A0301W102
A03010(111)3
A0301W101
A0301WI07
. AO3OIOO108 A0301wIO* A0301M110
A0301Wlll
AOIOIWII1
AOSOIWII5
A0811wO28
A081400029
A042800035
A042800016
A042800011
A04280WlS
I
*""%-:? A,;2800042328wUIZ
AM2800026
OW
A0428wo30
OW
AO4280003l
OW
A0428W332
OW
A042800033
A081400052 AO8I400055
29 9 30 6 32 8 32 1 8 47 23 2 30.8 25 1 17.6 I14
25 8 20.1 36 3 9.31 44 6 37 5 23 0 32 8 9.81 32 2 21 7 27.1 30 7 31 2 26 2 41 7 I1 2 26 I 25 0 1. I 23 7 39.7
RSD SM Drr MYMSD W D
34.7 9 11
,I I 8 86
NA NA
NA NA
3M Environmental Laboratory
Page 280
3M Medical Department Study: T6316.1
AMDTU 092597.1 Covanc& 6329-212
C9IMIF c911.2F C91356F C91357F CP1160F c91361F C91362F C9l371P c91376P
- S W n l - V I M
NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA N* NA NA NA NA NA NA NA NA
- NA N* NA NA NA NA NA NA NA Y4
NA NA NA NA NA NA NA NA NA NA NA NA
-NA NA
- QF0SE.A
- C.*. Wk OW
21 7
34 I
ow
2 39 50 1
37s
31 I 31 7
54..
ow
26 0
ow ow
111
21s
3 03 57 8
31.7
32 7
2 31
461 10 I
11 0
1.9 107
10 9
56 7 115 25 6 23 2 2 16
26 6
25 6
- 28 I 25 6
ow
(I 00
ow
00
ow ow
"W
ow ow ~ ow ow ow ow
OM
ow ow ow
OM
ow ow
- nw uw
"" V d u r r s t l
u.D *=sum,.
- PFOSEA
Csk. Cam.
0.W 20 5 33 7 OM
241 48.3 3 48 307 29 I 54 8
000 263
ow ow
,I5
236
- 2.62 58 I
32 7 33 3
2 03 4 12 10s
130
1, L
10 I IO 8 56 0 I15
25.2 23 2
2 82 26 8 2.3
- 28 6 26 0 ow OW am ow ow ow ow ow ow ow
~ ow ow ow ow ow ow ow
"M
ow ow
- OW OM
L I oc*r Ulit cvs YIrn'l 5'01. ".lyu
Analytical Report: FACT-TOX-001 LRN-U2103
RSD S I 1 Drr W S D RPD
I39 00566
57 6 om9
NA NA
NA PA
3M Environmental Laboratory
Page 281
3M Medical Department Study: T6316.1
AMDT# 092597.1 Covancdl6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
'LIVER bnpk #
PFOS C.L. C.X.
111
990
718
236
120
161
628
I33
365
293
I87
CW953M
60 3
163
201
689
C91315F C91336F C91338F C91340F C91311F C91112F C9IJSLP C91357F C913WF C91361F C91362F
1 210157 329817 341389 579769 242581 355109 ,2189 191963 206612 712319 868%
C91380F
C9IO54M CPIO56M C9106OM CP1065M C91070M
CilOiil
324616 l0.94
41 I
I
38.
C91453F C9I455F CP1b39F C91k62F C91467F
4525 I8803
I7533 137
C91b85F
1 1031858
325
203 n 198 105 201 0 0365 0 205
"a0411 $8. "0831 5 024960
I5 4 4 53 188
onw
175 0 137 13 9 L W i O 0245 ugtjl 0 I49 1033
00628 111
M"0
rms
"8'8
313
11679 11920 12376 I8544 17812
I1539
11218 15070
14511 8680
17M2 14551 1.949 18058 16126 15274 ,6810 6157 16831 17955 22322 10883 19454
18952
I ,5385 2 li 246 429 I 83 2 71
I
267
ugh .r Jb b.
1.7 I. 9 I24 I83 178 406 11.5 176 I3 2 I5 I 9 82 941 ID0 11.5 8 68 20 I 166 128 I6 1 106 I7 I 146 I4 9 181 16 I 153 16 8 62 16 8 180 22 3 IO 9 1') 5 I6 3 I90
Rso suDe MYMSD RPD
31 3 4 23
23 I 3 61
NA NA
NA NA
21358
44847 33222 23948 1784 134662 40321 18511
17773 11115 18340 27358 4725 51758 26905 I5794 18152 385W 23421 1825, 19676 2W51 16199 25331 11k69 ,7230 IMS6 28.W 3,551 3022 41332 27417 30114 30712
no
IPS 74 5 14 5 28 9 I9 I
OM OM OW OW
U8 35 1 23 9 I78
1 I55 40 3
I I85
23 0
183 17 4 4 72 51 8 26 9 15.8 28.3 38 6 25 4 I83 19 7 21 0 26 3 25 3 33 5 172 20 7 28 5 31 6 30 0 12 3 27 1 30 I 30 7
a 2u1 no195 n 0745 0 0415 00289 00191
""IW 00301 00218 "0201
'IW (0 0113 "ye <LW(00123 ads
<Lcq(Oom"glg CLcQ(00123"dB cLcq(aol23y%ig <LW(OOl23u~lg <LW(00123 UYg
.lCQ(O 0123 uwg CLOG (0 0123 udg r l W (0 0123 ug/g ( l W ( O O 1 2 3 uglg
RSD Sld D.* MYMSD RPD
308
0 308
I 235
0235
207
0 207
I 466
0466
36 5 133
75s 179 131 1389 469 917 408 721 777 182 843 6034
0 755 0 279 0 432 I389 0.69 0.917 0 408 0721 0 777 0 182 0 843 6 03 I II
522 734
I
0522 073,
16 3
708
118 00614
NA N*
3M Environmental Laboratory
Page 282
3M Medical Department Study: T6316.1
AMDT# 092591.1 CovanceU 6329-212
Analytical Report: FACT-TOX-001 LRN-U2103
R Swkl
- MSY
- Cak. Cow. ulh 28%0
29855
29 9
30567
30 6
32781
32.8
32395
32 4
8469
8.47
13116
21 2
30818
30 8
25WI
25 1
27552
27 6
17406
17,
25822
25 8
20389
20 6
36199
36.3
1313
931
us54
1.6
37472
37.3
22980
13.0
12766
318
9807
981
32164
32.2
14677
24.7
27071
27 I
30744
30 I
31154
26187
41708
11218
26812
25014
44467
23712
19723
011761
,3977
CYI~F C9138OF C9IOOM
- 23656 33352 2 73
3 I3 ow
ow
ow
OM
ow ow ow ow ow ow ow
0.w ow
oca ow
I36
ow
4 71
- I 1 9 293
7 MYMSD RPD
34 7 2.62 58 I 32 7 33 3 2 03 4 12 IO 5 13 0 26 I 103 10 8
I :"6 I 160 115 25 2 23 1
ow
NA
0.w
RSD Std Dr MYMSDRPD
I39 0 OSM
57 6 00139
NA NA
NA NA
3M Environmental Laboratory
Page 283
3M Medical Department Study: T6316.1
3M Medical Department Study: T-6316.1
~
Appendix F: Example Calculations
Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
~~
Formula Used for Sera Analyses in Study FACT TOX-001
AR (ng/mL) x DF x SC x PF x FV (mL) x 1.0 pg = Reported Concentration (pg/mL)
EV (mL) 1000 ng
Calculation Used for Group 2, Week 105, Animal ID C90783M, determination of PFOS
189.2 ng/mL x 10 x 0.9275 x 0.8640 x 1 mL x 1.0 pg = 1.52 pg/mL 1 mL 1OOOng
AR-Analytical result from MassLynx summary DF-Dilution factor SC-PFOS salt correction constant (0.9275) PF-Purity correction factor FV-Final extract volume (1.O mL unless otherwise noted) EV-Volume of sera extracted
Formula Used for Liver Analyses in Study FACT TOX-001
a AR (ng/g) x 3 curve (I) x SC x PF x DF x sample
(') a curve is assumed to be: 1 g liver
5 mI, HZO
1.0 pg = Reported Concentration ,gg/g) 1000 ng
Calculation Used for Group 2, Week 105, Animal ID C90783M, determination of PFOS
488.16 ng/g x 1 g / 5 mL, x 0.9275 x 0.8640 X 20 x 1.0 pg = 7.91 pg/g
0.9895 g/ 5 mL
1000 ng
AR-Analytical result from MassLynx summary
3 curve-Density of the liver standard curve, assumed to be l g liver/ 5 ml water 3 sample-Density of the liver sample (g sample/ 5 mL H20)
SC-PFOS salt correction constant (0.9275) PF-Purity correction factor DF-Dilution factor
3M Environmental Laboratory
Page 284
3M Medical Department Study: T6316.1
3M Medical Department Study: T-6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
Appendix G: Interim Certificates of Analysis
3M Environmental Laboratory
Page 285
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
L m
3048 Research Drive Phone: (814) 231-8032
State College, PA 16801 Fax: (814) 231-1253 or (814) 231-1580
INTEMM CERTIFICATE OF ANALYSIS
Revision 1(9/7/00)
Centre Analytical Laboratories COA Reference #: 023-018B
Test Name
3M Product: PFOS, Lot 171 Reference #: SD-009 Purity: 86.4%
Specifications
-
Purity'
Result
86.4%
Appearance
Identification
NMR
Metals (ICPIMS) 1. Calcium 2. Magnesium 3. Sodium 4. Potassium' 5. Nickel 6. Iron 7. Manganese
Total % Impurity (NMR) Total % Impurity (LCiMS) Total % Impurity (GCNS) Related Compounds POAA Residual Solvents (TGA) Purity by DSC Inorganic Anions (IC)
1. Chloride 2. Fluoride 3. Bromide 4. Nitrate 5. Nitrite 6. Phosphate
' 7. Sulfate4
Organic Acids (IC) 1. TFA 2. PFPA 3. HFBA 4. NFPA
Elemental Analysis': 1. Carbon 2. Hydrogen 3. Nitrogen 4. Sulfur 5. Fluorine
White Crystalline Powder
-
Conforms
Positive
1. 0.017 wt./wt.% 2. 0.007 wt./wt.%
3. 1.355 wt./wt.%
4. 6.552 wt./wt.%
5. 0.003wt./wt.%
6. 0.004 wt./wt.% 7. <0.001 wt./wt.%
1.oo wt./wt.%
10.60 wt.lwt.%
None Detected
1. Theoretical Value = 17.8% 2. Theoretical Value = 0% 3. Theoretical Value = 0% 4. Theoretical Value = 5.95% 5. Theoretical Value = 60%
0.30 wt./wt.% None Detected Not Applicable3
1. c0.015 wt./wt.% 2. 0.27 wt./wt.% 3. C0.040 wt./wt.% 4. co.009 wt./wt.% 5. c0.006 wt./wt.% 6. C0.007 wt./wt.% 7. 8.82 wt./wt.%
1. co.1 wt./wt.% 2. co.1 wt./wt.% 3. co.1 wt./wt.% 4. C0.25 wt./wt.%
1. 12.08 wt./wt.% 2. 0.794 wt.lwt.% 3. 1.61 wt./wt.% 4. 10.1 wt./wt.% 5 . 50.4 wt./wt.%
COA023-018B
3M Environmental Laboratory
Page 1 of 3 Page 286
3M
Medical
Department
-Study: T6316.1 Ilr.
Analytical Report: FACT-TOX-001
LRN-U2103
lytical Laboratories, Inc.
3048 Research Drive Phone: (814) 231-8032
State College, PA 16801
Fax: (814) 231-1253 or (814) 231-1580
INTERIM CERTIFICATE OF ANALYSIS
Centre Analytical Laboratories COA Reference ##: 023-018B
Date of Last Analysis: OW31/00
Expiration Date: 08/31/01
Storage Conditions: Frozen 5-10C
Re-assessment Date: 08/31/01
'Purity = 100% - (sum of metal impurities, 1.39% +LC/MS impurities,
10.60%+InorganicFluoride, 0.27%+NMR impurities, 1.OO%+ POAA, 0.30%)
Total impurity from all tests = 13.56%
Purity = 100% - 13.56% = 86.4%
2Potassiumis expected in this salt form and is therefore not considered an impurity.
'Purity by DSC is generally not applicable to materials of low purity. No endotherm was observed for this sample.
4Sulhrin the sample appears to be converted to so4 and hence detected using the
inorganic anion method conditions. The anion result agrees well with the sulhr determination in the elemental analysis, lending confidence to this interpretation. Based on the results, the SO4 is not considered an impurity.
'TFA HFBA NFPA PFPA
Trifluoroacetic acid Heptafluorobutyric acid Nonofluoropentanoic acid Pentafluoropropanoic acid
'?heoretical value calculations based on the empirical formula, CgFF;7S03X+(MW=538)
' This work was conducted under EPA Good Laboratory Practice Standards (40 CFR 160).
COA023-0 18B
3M Environmental Laboratory
Page 2 Of 3 Page 287
3M Medical Department Study: T6316.1
I
3048 Research Drive
Analytical Report: FACT-TOX-001 LRN-U2103
- -State Colleae. PA 16Rni
INTERKM CERTIFICATE OF ANALYSIS
Centre Analytical Laboratories COA Reference #: 023-018B
LCMS Purity Profile:
Impurity c4 c5 C6 c7
Total
Note: The C4 and C6 values were calculated'usingthe C4 and C6 standard calibration curves, respectively. The C5 value was calculated using the average response factors fiom the C4 and C6 standard curves. Likewise, the C7 value was calculated using the average response factors fiom the C6 and C8 standard curves.
ru#- Prepared By:
Dayd S . Bell
Date
lytical Laboratories
Date anager, Centre Analytical Laboratories
COA023-0188
3M Environmental Laboratory
Page 3 of3 Page 288
3M Medical Department Study: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
F4.
1
,;
t
CEntrE Analytical Laboratories, Inc.
3048 Research Drive
State College, PA 16801
Phone: (814) 231-8032 Fax: (814) 231-1253 or (814) 231-1580
Test Name
Specifications
Result
1. Carbon 2. Hydrogen 3. Nitrogen 4. Sulfur 5. Fluorine
COA023-022-2
3M Environmental Laboratory
1. TheoreticalValue = 25.2% , 1. 25.04 wt.lwt.%
2. Theoretical Value = 1.75%
2. 1.69 wt.lwt.%
3. TheoreticalVaIue = 2.45%
3. 2.61 wt.lwt.%
4. TheoreticalValue = 5.60%
4. 8.88 wt./wt?h
5 . TheoreticalValue = 56.6%
5. 56.8 wt.fwt.%
Page 1of3 Page 289
3M Medical Department Study: T6316.1
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P
't
CEntrE Analytical Laboratories, Inc.
3048 Research Drive
State College, PA 16801
Phone: (814)231-8032 Fax: (814)231-1253or (814)231-1580
INTERLM CERTIFICATE OF ANAI,YSIS
Centre Analytical Laboratories COA Reference #: 023-022-2 3M Product: EtF'OSE-OH
Test Control Reference #: TCR-00017-52
Date of Last Analysis: 11/26/00
Expiration Date: 11/26/01
Storage Conditions: <-lo "C
Re-assessment Date: 11/26/01
'P~ty= 100%- (totalNMR impurities, 1.26%+ GCMS impurities, 1.29 +POAA,
0.10%)
- Total impurity from all tests = 2.65% Purity = 100% 2.65% = 97.4%
2~~~
Trifluoroacetic acid
fl
HFBA
Heptafluorobutyric acid
NFPA
Nonafluoropentanoic acid
PFPA . Pentafluoropropanoic acid
3Theoreticalvalue calculations based on the empirical formula, C ~ ~ H ~ O F ~ ~ N O ~ S (Mw=571)
COAO23-022-2
3M Environmental Laboratory
Page 2 of 3 Page 290
3M Medical Department Study: T6316.1
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L m
3048 Research Drive Phone: (814) 231-8032
State College, PA 16801 Fax: (814) 231-1253 or (814) 231-1580
INTERIM CERTIFICATE OF ANALYSIS
Centre Analytical Laboratories COA Reference #: 023-022-2 3M Product: EtFOSE-OH
Test Control Reference #: TCR-00017-52
GCMS Purity Profile
Peak #
1 2 Total
Retention Time
Wn) 13.934
17.307
Identity
PFOSDEA
c7
-
% Impurity
0.36 0.93 1.29
This work was conducted under EPA Good Laboratory Practice Standards (40 CFR 160).
Prepared By: Scientist
Centre Analytical Laboratories
COAO23-022-2
3M Environmental Laboratory
///6dd
Date Page 3 o f 3 Page 291
3M Medical Department Study: T6316.1
I
-.-.
.. .. _ _
Analytical Report: FACT-TOX-001 LRN-U2103
CEntrE Analytical Laboratorks, Inc.
P\
c
3048 Research Drive Phone: (814) 231-8032
State College, PA 16801
Fax: (814) 231-1253 or (814) 231-1580
INTERIM CERTIFICATE OF ANALYSIS
Centre Analytical Laboratories COA ]Reference#: 023-022-1
3M Product: EtFOSE-OH Test Control Reference fir: SD-013
Purity: 88.9%
1. Calcium 2. Magnesium 3. sodium 4. Potassium 5. Nickel 6. Iron
r?
2. Fluoride 3. Bromide 4. Nitrate
2. Hydrogen 3. Nitrogen 4. Sulfu
COA023-022-1
3M Environmental Laboratory
1. <0.001 wt.fwt.% 2. co.001 wt.fwt.% 3. <0.001 wt.lwt.% 4. 0.002 wt.lwt.% 5. <0.001 wt.lwt.%
1. Theoretical Value = 25.2' 2. Theoretical Value = 1.75% 3. Theoretical Value = 2.45% 4. Theoretical Value = 5.60%
1. <0.015 wt.lwt.% 2. C0.005wt.lwt.% 3. C0.040wt.lwt.%
4. <0.009 wt./wt.%
5 . dl.006wt.fwt.% 6 . ~0.007wt.fwt?h
1. co.1 wt.lwt.% 2. co.1 wt.fwt.% 3. <0.1 wt.lwt.%
1. 24.42 wt.fwt.% 2. 1.78wt.lwt.% 3. 2.72 wt.fwt.%
Page I of3 Page 292
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CEntrG Analytical Laboratorks, Inc.
3048 Research Drive Phone: (814)231-8032
State College, PA 16801 Fax: (814) 231-1253or (814)231-1580
7-3
RVTEMM CERTIFICATE OF ANALYSIS
Centre Analytical Laboratories COA Reference # 023-022-1 3M Product: EtFOSE-OH
Test Control Reference # SD-013
Date of Last Analysis: 11/26/00
Expiration Date: 11/26/01
Storage Conditions: <-lo "C
Re-assessment Date: 11/26/01
'purity = 100% - (total metal impurities, 0.002% + total NMR impurities, 0.90% + GCMS impurities, 10.21 + POAA,0.03%)
Total impurity fiom all tests = 11.14%
Purity = 100% - 11.14%= 88.9%
2~~~
Trifluoroacetic acid
r"
HFBA
Heptafluorobutyric acid
NFPA
Nonafluoropentanoic acid
PITA
Pentafluoropropanoic acid
3Theoreticalvalue calculationsbased on the empirical formula, C ~ ~ H ~ O F ~ ~ N O ~ S (MW=5 71)
COA023-022-1
3M Environmental Laboratory
Page 2 of 3
Page 293
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- I
L
Analytical Report: FACT-TOX-001 LRN-U2103
3048 Research Drive
State College, PA 16801
Phone: (814) 231-8032 Fax: (814) 231-1253 or (814) 231-1580
INTERIM CERTIFICATE OF ANALYSIS
Centre Analytical Laboratories COA Reference #: 023-022-1 3M Product: EtFOSE-OH
Test Control Reference #: SD-013
GCMS Purity Profile
11
16.379
c5
12
16.801
C6
- - 13
17.222
c7
Total
1.07 3.30 0.93 10.21
This work was conducted under EPA Good LaboktoryPractice Standards (40 CFR 160).
Prepared By: Scientist
ratories
Centre Analytical Laboratories
COAO23-022-1
3M Environmental Laboratory
Date Page 3 Of3 Page 294
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W ANALYTICAL REPORT
STUDY TITLE
PURITY DETERMtNATION OF SAMPLE LOTS OF PFOS
Sample # TCR-00065-022
DATA REOUIREMENTS
Test Article Characterization STUDY DIRECTOR
"THISISAN EXACTCOW OF
THE ORIGINAL DOCUMENT"
Kevin Lloyd
ANALYTICAL REPORT COMPLETION DATE
October 25,2000
W;
PERFORMING LABORATORIE/ TESTING FACILITIES
Centre Analytical Laboratories, Inc. (Centre) 3048 Research Drive
State College, PA 16801 Phone: 814-231-8032
STUDY SPONSOR
3M Environmental Technology and Safety Services Building 2-3E-09 PO Box 33331
St. Paul, MN 55133-3331
PROJECT IDENTIFICATION Centre Study Number: 023-045
Total Pages: 15
3M Environmental Laboratory
Page 295
--3MMedicalDepartmentStudy: T6316.1
Analytical Report: FACT-TOX-001 LRN-U2103
Centre Study No.: 023-045
W
GOOD LABORATORY PRACTICE COMPLIANCE STATEMENT
Centre Study Number 023-045, entitled "PurityDetermination of Sample Lots of PFOS, Sample # TCR-00065-022" conducted for 3M Environmental Laboratory, was performed
in compliance with US EPA Good Laboratory Practice Standards (40 CFR Part 160) by
Centre Analytical Laboratories,Inc. with the following exceptions:
The automated data collection systems used in this study were not fully compliant with 21 CFR 58.130 (e).
Kevin Lloyd
Date
Study Director
Centre Analytical Laboratories,Inc.
L/ Date
Spohkor Representative
3M Environmental Technology and Safety Services
:. . . > .
.. , . . . . .
SV-
. .. , .
Centre Analytical Laboratories, Inc. 3M Environmental Laboratory
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Centre Study No.: 023-045
w
QUALITY ASSURANCE STATEMENT
Centre Study Number 023-045, entitled "Purity Determination of Sample Lots of PFOS, Sample # TCR-00065-022"was reviewed by Centre Analytical Laboratories' Quality Assurance Unit. All reviewed phases were reviewed for conduct according to Centre Analytical Laboratories' Standard Operating Procedures, the Study Protocol, and ail applicable Good Laboratory Practice Standards. All findings were reported to the Study Director and to management.
&%
1. Protocol Review
Date Inspected
10119/00
Date Reported to Study Director and Centre Management
10/25/00
Date Reported to Sponsor Manaaement
10/25/00
2. Raw Data Review 10/19/00
10/25/00
10/25/OO
V
3. Report Review
10/24/OO
10/25/00
10/25/00
Wiliiam spare Quality Assurance Officer
/o z x o*
Date
"THIS IS AN EXACT COPY OF
THE ORIGINAL DOCUMENT"
W
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Centre Study No.: 023-045
CERTIFICATION OF AUTHENTICITY
This report, for Centre Study Number 023-045, is a true and complete representation of the raw data for the study.
Submitted by:
Centre AnaIytical Laboratories, Inc. 3048 Research Drive State College, PA 16801 (814) 231-8032
Study Director, Centre:
Kevin Lloyd
Date
Study Director
Centre Analytical Laboratories, Inc.
Centre Analytical Laboratories, Inc. Facility Management:
/ Richard A. drazzi President Centre Analytical Laboratories,Inc.
Date
'WE IS AN EXACT COW OF
THE ORIGINAL DOCUMENT-
V
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Centre Study No.: 023-045
W
STUDY IDENTIFICATION
PURITY DETERMINATIONOF SAMPLELOTS OF PFOS Sample # TCR-00065-022
TYPE OF STUDY:
Characterization
TEST SYSTEM:
Not Applicable
TEST ARTICLE:
PFOS,Test Control Reference # TCR-00065-022
SPONSOR:
3M EnvironmentalTechnology and Safety Services Building 2-3E-09 PO Box 33331
St. Paul, MN 55133-3331
W
STUDY DIRECTOR.
Kevin Lloyd
CenterAnalytical Laboratories,Inc.
Phone:(814) 231-8032
TESTING FACTLITlES:
Centre Analytical Laboratories,Inc. (Centre)
3048 Rcsearch Drive
State College, PA 16801 Phone: 814-231-8032
ANALYTICAL PHASE TIMETABLE:
Study Initiation Date: Analytical Start Date: Analytical Termination Date:
09/28/00
10/05/00 10/24/00
"THISI S AN EXACT COPY OF
THE ORIGINAL DOCUMENT"
BY KT6 DATE ,&&e
Centre Analytical Laboratories, Inc. 3M Environmental Laboratory
Page 5 of 15 Page 299
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Analytical Report: FACT-TOX-001 LRN-U2103
Centre Study No.: 023-045
PROJECT PERSONNEL
The Study Director for this project was Kevin Lloyd at Centre Analytical Laboratories, Inc. The following personnel from Centre Analytical Laboratories, Inc., were associated with various phases of the study:
Name Gerry Shero David S. Bell Emily R. Stauffer Mark Ammerman
& T Scientist Scientist Scientist Sample Custodian
"THIS IS AN EXACT COPY OF
THE ORIGINAL DOCUMENT"
Centre Analytical Laboratories, Inc.
3M Environmental Laboratory
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. . Analytical Report: FACT-TOX-001
Centre
S
t
u
d
y
No
. .
LRN-U2103 023-045
TABLE OF CONTENTS
F&g
TITLE PAGE ...................................................................................................................... 1 GOOD LABORATORY PRACTICE COMPLIANCE STATEMENT ............................. 2 QUAL.ITY ASSURANCE STATEMENT.......................................................................... 3 CERTIFICATIONOF AUTHENTIClTY........................................................................... 4 STUDY IDE"ICATI0N ............................................................................................... 5 PROJECT PERSONNEL.................................................................................................... 6 TABLE OF CONTENTS .................................................................................................... 7 1.0 SUMMARY............................................................................................................... 8 2.0 INTRODUCTION......................................................................................................... 8 3.0 TEST SYSTEM ............................................................................................................ 8 4.0 TEST ARTlCLE............................................................................................................ 8 5.0 EXPERIMENTALPROCEDURES ............................................................................. 9 6.0 RESULTS AND DISCUSSION.................................................................................. 10
8.0 CIRCUMSTANCES THAT MAY HAVE AFFECTED THEDATA.................... 10 9.0 RETENTION OFDATA AND S A M P L E S ............................................................ 10
Table I. Results From LCNS forTCR-00065-022........................................... 11
w .
Figure 1.PFOS Calibration Standard (Cl00500-4)at 269pgL .............................1.2
Figure 2.PFOS Calibration Standard (ClOO500-2) at 539pgL .............................. 13 Figure 3. PFOS (TCR-00065-022) at 25Opg/L. ESI Negative Ion Mode ...................... 14
Appendix A: Study Protocol OOP-023-045:PURITY DETERMINATION OF
SAME'E LOTS OF PFOS. Sample # TCR.00065.022. Including Amendment 1.........15
'7HIS IS AN EXACT COPYOF
THE ORIGINAL DOCUMENT
Centre Analytical Laboratories. Inc.
3M Environmental Laboratory
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Centre Study No.:023-045
purity).
1.0 SUMMARY
m sampleffTCR
was determinedfrom the E M S
pure as compared with the PFOS control (TCR-00017-046,97.9%
2.0 INTRODUCTION
This report details the results of the analysis of PFOS,Test Control Reference# TCR-
00065-022. The test was analysis by liquid chromatography- mass spectrometry
(LCMS). The LCMS was conducted at Centre.
The study was initiated on September28,2000 when the Study Director signed protocol
number OOP-023-045.The analytical start date was October 5,2000, and the experimental termination date was October 9,2000.
3.0 TEST SYSTEM
W There is no test system associated with this characterization study, therefore the GLP
requirement for test system description,justification, and identificationdo not apply. The route of administration, levels and frequency of administration also do not apply to characterization studies.
4.0 TEST ARTICLE
"THISIS AN EXACTCOPY OF
THE ORIGINAL DOCUMENT"
BY . s r f D A . L & i ?
The test article was PFOS,Test Control Reference# TCR-00065-022. 3M Environmental Laboratory supplied the test article and it was logged at Centre Analytical Laboratories, Inc. as follows:
Compound
PFOS
TCR-00065-022
Lot or NB
Number
t
Centre Control No.
00-023-068
Puritv TBD
Date Received
10/05/OO
The sample received was a white, crystalline solid. It was received under frozen conditions and was stored in a temperature-monitored freezer kept at <-1O"C.
W
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The analyticalkontrol standard PFOS was:
Control Article Lot Number
PFOS
TCR-00017-046
Centre Control No.
00-023-042
Punty 97.9%
- Expiration Date 8/3 112001
The chemical and physical data for PFOS is as follows.
Common Name: Molecular weight: CAS Number:
Structure:
PFOS 499 (c~F17so3-) 2795-39-3
II0 II cfi17s 0-0'K'
0
?.ate: the neutral mc,2cule and standard form that L,e PFOS \&an) is derived from is potassium perfluorooctanesulfonate ( C ~ F I ~ S O ~mKo)le, cular weight 538.
5.0 EXPERIMENTAL PROCEDURES
LCMS Spectral Analysis
PFOS sample TCR-00065-022was analyzed for purity using liquid chromatography/mass spectrometry(LCMS). The sample was analyzed accordingto the following procedure.
The samplewas prepared at about 250 &mL in methanol and analyzed by LCMS using a Hewlett-Packard 1100 HPLC system interfaced with a Hewlett-Packard 1100 mass selective detector. The mass spectrometer was run in negative ionization mode using electrospray ionization @SI) using Selective Ionization Monitoring for ion m/z 499. The liquid chromatography system was operated in reversed-phase mode using a C 18 silica-based column.
Each resulting chromatogram was calculated against the analytical control article (TCR-
00017-046) calibration curve.
"THIS IS AN EXACT COPY OF THE ORIGINAL DOCUMENT"
V
Centre Analytical Laboratories,Inc. 3M Environmental Laboratory
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Centre Study No.: 023-045
6.0 RESULTS AND DISCUSSION
LCMS Spectral Analysis
Responses were observed for the PFOS sample in negative ion mode using an ESI interface. Quantitation was performed using SIM mode, mlz 499, and PFOS was detected at 7.8 minutes. TH-PFOSwas used as the internal standard,m/z 427, and was detected at 7.5 minutes. The total percent purity, calculated against the analytical control article (TCR-00017-046c)alibration curve was determined to be 88.0% from the average of three replicate analyses.
8.0 CIRCUMSTANCES THAT MAY HAVE AFFECTED THE DATA
Electronic records are not fully compliant with 21 CFR 11,"Electronic records;
Electronic Signature." However, approved SOPSwere in place and all instrumentation used in this study was fully calibrated and operational. All original raw data were printed as hard copies and fully audited by quality assurance. Verified exact copies and the electronic data will be stored in the archives at Centre Analytical Laboratories. Original raw data will be returned to the Sponsor.
9.0 RETENTION OF DATA AND SAMPLES
When the final report is final, all original paper data generated by Centm Analytical Laboratories, Inc. will be shipped to the sponsor. This does not include facility-specific raw data such as instrument logs, however exact copies of temperature logs will be submitted. Exact copies of all raw data, as we11 as a signed copy of the final analytical report and all original facility-specificraw data, will be retained in the Centre Analytical
Laboratories,Inc. archives for the period of time specifiedin 40 CFR Part 160. Retained
samples of reference substances are archived by the sponsor.
`THIS IS AN EXACT COPY OF
THE ORIGINAL DOCUMENT"
Centre Analytical Laboratories, Inc. 3M Environmental Laboratory
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Centre Study No.:023-045
Table I. Results From L C M Of TCR-00065-022,ESI Negative mode
c
3M ID
TCR-00065-022 TCR-00065-022 TCR-00065-022
Retention Time (min)
7.79 7.80 7.80
Mass
~
499 499 499
Standard Standard Standard Standard
7.69 499 7.73 499 7.77 499 7.79 499
Value Pn/L 250 250 250
11 11 54 54
Determined
Pa
219 220 220
% Recovery
88.0 88.0 88.0
loo*
*
17* 1 *
60
110
50
93
Standards Average =
Std Dev =
7
* First two injections during instrument warm up, not reported.
CCV = standard in run used to check calibration (C100500-4 at 269pgL)
"THISIS AN EXACTCow Of
THE ORIGINAL DOCUMENT"
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...
...' , ' ;... ., . .. ...'.^.
'. .:
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.. . ,
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W
Instrument 1
Mon, 23. Oct. 2000 00:12:06 pm
Pa94 1 af 1 ';..
---- 6;. ro/bs]Ld . 'THIS IS AN EXACT COPY OF
THE ORIGINAL DOCUMENT"
I . _.__ .e....-.*.A. -.,..-.
>. . ,
BY " '*_
Centre Analytical Laboratories, Inc. 3M Environmental Laboratory
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Centre Study No.: 023-045
Figure 2. PFOS Calibration Standard (ClOOSOO-3) at 539pg/L
c
Sample Name:C100500-3
Sample Info:
1
Data f i l e :C:\HPC?IEM\1\DATA\100600\10060015.D
==l~lw=9~=lw9ll~lllLw~9D~.~~~~9~9w~~~9w~~~~~~w~w9wD~-9~w~w
Injection Date P * A C o~perator
Instrument Dilution
: 10/6/2000 : OS GI ~ C
: Instrument 1 :1
1:13:21 PM U
Seq Line : Vial No. :
Inj. No. : Inj. Vol. :
13 1s
1 5 P1
Acq. Method
t PF0S.M
Analyuie Method Last Changed
I
:\HPcHEM\1\METHODS\lOO6OO.M
!0/9/2000
01:45:43
pm
(modified after loading)
Analysio or PFOS .
I
1
Instrument 1
Mon, 9. Oct. 2000
01:46:00 pm
V
Centre Analytical Laboratories,Inc. 3M Environmental Laboratory
Page 1 of 1
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3M Medical Department Study: T6316.1
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Centre Study No.: 023-045
Figure 3. PFOS (TCR-00065-022)at 250pg/L, ESI Negative Ion Mode
I
Sample Name :L29092-1 Sample Ino:C100500-8
Data file :C:\HPCHEM\1\DATA\lOO600\10060019.D
E=rlL-ll~r=ri~ri~irillllll~1llllllllllll9111111~~1~-=1111~~1~1~~g~~~~~g=~
Injection Date r A c q Operator
Instrument Dilution
: 10/6/2000 : GS 6% w&'
: Instrument 1 :1
2:20:49 PM
Seq Line :
Vial No. :
Inj. No. : Inj. Vol. :
17
21 1
5 Pl
Acq. Method
; PF0S.M
Analysin Method : C:\HPCHEM\l\METHODS\lOO600.M
L a s t Changed
: '10/23/2000
11:44:26 am
Analysis for PFOS
.st--
.. .
m.BIM.mm:var
;(
!
j
j
i
i
Instrument 1
Mon, 23. O c t . 2000 00:10:19 pm
Page 1 of 1
"THIS ISAN EXACT COPY OF
I
THE ORIGINAL DOCUMENT"
Centre Analytical Laboratories, Inc. 3M Environmental Laboratory
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Centre Study No.: 023-045
APPENDIX A
Study Protocol
Purity Determination of Sample Lots of
U'
PFOS
Including Amendment 1
`?HIS IS AN EXACT COPY OF
THE ORIGINAL DOCUMENT"
V
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3M Medical Department Study: T-6316.1
Appendix H: Report Signature Page
Analytical Report: FACT-TOX-001 LRN-U2103
Analytical Report: FACT TOX-001 LRN-U2103
John L. Butenhoff, Ph.D., Study Director
Date
.Marvin T. Case, D.V.M., Ph.D., Sponsor Representative
%w. *I
Date
6</31 10 I
Kristen J. Hansen, Ph.D., Principal Analytical lnvestigator
Date
William K. Reagen, Ph.D., Laboratory Manager
Date
3M Environmental Laboratory
Page 310