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3M Medical Department Study: T-6316.5
3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Analytical Report: FACT TO X -013 LRN-U2095
Study Title
Analytical Study 2(N-Ethylperfluorooctane sulfonamido)-ethanol in Two Generation Rat Reproduction
Amended Analytical Laboratory Report
Determination of the Presence and Concentration of PFOS, M556, PFOSAA, and PFOSA in the Liver and PFOS, M556, PFOSAA, PFOSA, and EtFOSE-OH in the Sera of Crl:CDBR VAF/Plus Rats Exposed to EtFOSE-OH
Data Requirement Not Applicable
Author 3M Environmental Laboratory
Study Completion Date May 31, 2001
Performing Laboratories
Sera Analyses
Liver Analyses
3M Environmental Laboratory Building 2-3E-09, 935 Bush Avenue
St. Paul, MN 55106
Battelle Memorial Institute 505 King Avenue
Columbus, OH 43201-2693
Project Identification 3M Medical Department Study: T-6316.5
Argus In-Life Study: 418-009 Analytical Report: FACT TOX-013 3M Laboratory Request No. U2095
Total Number of Pages 143
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3M Medical Department Study: T6316.5
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Analytical Report: FACT TOX-013 LEN-U2095
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GLP Compliance Statement
Analytical Study: FACT-TOX-013 LRN-U2095
Analytical Study: FACT TOX-013 LRN-U2095
Analytical Laboratory Report Title: Determination of the Presence and Concentration of PFOS, M556, PFOSAA, and PFOSA in the Liver and PFOS, M556, PFOSAA, PFOSA, and EtFOSE-OH in the Sera of Crl:CDBR VAF/Plus Rats Exposed to EtFOSE-OH
Study Identification Number: T-6316.5, FACT TOX-013, LRN-U2095
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. All raw data, protocol, analytical report and samples for this study are retained in archives at the 3M Environmental Laboratory and will be retained for a period of at least ten years. The analytical phase completed at the 3M Environmental Laboratory was performed in accordance with 3M ET&SS Standard Operating Procedures.
Exceptions to GLP compliance:
There were two study directors in this study. This study was designed as two separate studies. The in-life phase 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.
Some changes made in the standard preparation logs obscured the original entry, did not document the reason for the change and/or were not initialed and dated by the person making the change.
The samples that were analyzed on 3/16/00 utilized standards that had an expiration date of 2/00.
Liver values generated at contract laboratories were corrected by 3M Environmental Laboratory to reflect the official purity values from the COA. Revised final reports will be solicited from the contract laboratory and will be added as a report amendment at a later date.
Expiration dates on some reagents and solutions were missing.
The analytical report from Battelle is not signed or dated by the Principal Analytical Investigator or laboratory management.
The Quality Assurance Statement in the Battelle analytical report does not include the dates of the QA inspection activities or the dates reported to the Study Director and laboratory management. The Quality Assurance Statement is not signed.
The Argus and Battelle analytical reports do not include the names of all the contributing
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GLP Study-- Quality Assurance Statement
Analytical Laboratory Report Title: Determination of the Presence and Concentration of PFOS, M556, PFOSAA, and PFOSA in the Liver and PFOS, M556, PFOSAA, PFOSA, and EtFOSE-OH in the Sera of Crl:CDBR VAF/Plus Rats Exposed to EtFOSE-OH
Study Identification Number: T-6316.5, FACT TOX-013, LRN-U2095
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
Phase
Date Reported to Management Study Director
10/12/99
Extraction
10/26/99
10/26/99
6/5/00-6/14/00
Data
6/16/00
6/16/00
9/11/00-9/13/00
Draft report
9/14/00
9/14/00
5/14/01
Amended report
5/14/01
5/14/01
QAU Representative
3 O'-n- t l
Date
2oQ 1
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Table of Contents
Analytical Study: FACT-TOX-013 LRN-U2095
Analytical Study: FA C TTO X -013 LRN-U2095
GLP Compliance Statement............................................................................................... 3
GLP Study--Quality Assurance Statement....................................................................... 4
Study Personnel and Contributors......................................................................................7
Introduction and Purpose................................................................................................... 8 Test System.................................................................................................................... 8 Specimen Collection and Analysis.................................................................................9
Specimen Receipt and Maintenance..................................................................................9
Chemical Characterization.................................................................................................... 10 Dose Confirmation Analyses............................................................................................10
Method Summaries............................................................................................................... 11 3M Environmental Laboratory..........................................................................................11 Preparatory Method..................................................................................................... 11 Analytical Method........................................................................................................ 11 Analytical Equipment................................................................................................... 11 Deviations......................................................................................................................... 12
Data Quality Objectives and Data Integrity.......................................................................... 12
Data Summary, Analyses, and Results............................................................................... 13 Summary of Quality Control Analyses Results................................................................13 Summary of Sample Results............................................................................................14
Statistical Methods and Calculations....................................................................................14
Statement of Conclusion...................................................................................................... 14
Appendix A: Chemical Characterization, Control Matrices and Dose Confirmation Analyses................................................................................................................................ 15
Appendix B: Protocol............................................................................................................ 18
Appendix C: Extraction and Analytical Methods..................................................................37
ETS-8-4.1, Extraction of Potassium Perfluorooctanesulfonate or Other Fluorochemical Compounds from Serum for Analysis Using HPLC-Electrospray/Mass Spectrometry, (14 pages).............................................................................................................................38
ETS-8-5.1, Analysis of Potassium Perfluorooctanesulfonate or Other Fluorochemlcals in Serum Extracts Using HPLC-Electrospray/Mass Spectrometry, (9 pages).................... 52
Appendix D: Data Summary Tables.................................................................................... 61
Appendix E: Data Spreadsheets......................................................................................... 64
Appendix F: Example Calculations......................................................................................70
Appendix G: Contract Lab Report..................................................................................... 71 .
Appendix H: Interim Certificate of Analysis........................................................................ 137
Appendix I: Report Signature Page....................................................................................141
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Appendix J: Amendment 1 to FACT TOX-013 Final Report
142
List of Tables
Table 1. Test System Population Demographics and Dosage Levels for Study (418-009)....................................................................................................... 8
Table 2. Characterization of the Test Article in Study FACT TOX-013 ...............................10 Table 3. Negative Ions Monitored in 3M Laboratory Analyses........................................... 12 Table 4. Deviation Summary for FACT TOX-013...............................................................12
Table 5. Determinations of the LOQ in the Analyses of Serum Extracts............................13 Table 6. Characterization of the Control Matrices Used for Sera Analyses in
Study FACT TOX-013 .............................................................................................15
Table 7. Characterization of the Control Matrices Used for Liver Analyses in Study FACT TOX-013 ............................................................................................. 15
Table 8. Characterization of the Analytical Reference Materials Used for Sera Analyses in Study FACT TOX-013.........................................................................................16
Table 9. Characterization of the Analytical Reference Materials Used for Liver Analyses in Study FACT TOX-013.........................................................................................16
Table 10. Tween Dosing Confirmation for Study In-life #418-009...................................... 17
Table 11. Tween Dosing Confirmation-- Matrix Spikes for Study In-life #418-009............17
Table 12. Reported Fluorochemical Levels in Sera Analyses in Study FACT TOX-013... 61 Table 12. Reported Fluorochemical Levels in Sera Analyses in Study FACT TOX-013
(continued).............................................................................................................62 Table 13. Reported Fluorochemical Levels in Liver Analyses in Study FACT TOX-013...62 Table 13. Reported Fluorochemical Levels in Liver Analyses in Study FACT TOX-013
(continued)............................................................................................................ 63
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Study Personnel and Contributors
Study Director
Marvin T. Case, D.V.M., Ph.D, Study Director 3M Corporate Toxicology - Medical Department 3M Center, Building 220-2E-02 ^ St. Paul, MN, 55144-1000 651-733-5180
r - Sponsor
John L. Butenhoff, Ph.D., Sponsor Representative 3M Corporate Toxicology - Medical Department 3M Center, Building 220-2E-02 St. Paul, MN 55144-1000
^ Analytical Chemistry Laboratories
Sera Analyses 3M Environmental Laboratory (3M Lab) ^ Kristen J. Hansen Ph.D., Analytical Investigator
Liver Analyses Battelle Memorial Institute Jon C. Andre, Ph.D., Analytical Investigator
3M Lab Contributing Personnel
David R. Bamidge. Ph.D. Lisa A. Clemen Lisa Dick, Ph.D. Kelly J. Dorweiler Mark E. Ellefson Sara E. Estes Barb A. Gramenz Sarah A. Heimdal Cari S. Hewitt Marlene M. Heying
Harold O. Johnson Kelly J. Kuehlwein Sally A. Linda Joseph C. Pilon Scott R. Post Ian A. Smith Kathy M. Stock Anh-Dao Vo Bob W . Wynne
Location of Archives
All original raw data, protocol, and analytical report have been archived at the 3M Environmental Laboratory. The test substance 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. Control sera and liver will be maintained at the contract lab along with the test substance.
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Introduction and Purpose
The purpose of the study is to determine the presence and concentration of PFOS, PFOSA, PFOSAA, and M556 in liver samples and PFOS, PFOSA, PFOSAA, EtFOS&OH, and M556 in sera samples collected from rats exposed to EtFOSE-OH. This study was initiated on 1 October 1998.
T e s t System
Five groups of FO generation male and female rats and 3 groups of F1 generation male and female rats were used as the test system. Table 1 outlines the rat population demographics and dosage levels for study 418-009.
On day 4 of lactation, litters were culled to four male and four female pups, where possible. On day 21 of lactation, 25 male and 25 female pups in Groups I, II, and III were selected for continued evaluation. F1 generation male and female rats were given appropriate dosages of the test article via gavage beginning on day 22 of lactation or postpartum through the day before sacrifice.
The test system species and strain selected was the CitCCPBR VAF/Plus* (Sprague-Dawley) rat received from Charles River Laboratories, Inc., and assigned temporary numbers until assigned to the study. Rats were permanently identified using MoneF self-piercing ear tags when assigned to the study. FO generation rats were identified with ear tags. Pups were not identified during lactation, as parameters were evaluated in terms of the litter. At weaning, each F1 generation rat selected for continued observation was identified with a Monelseif-piercing ear tag. FO female rats were approximately 65 days of age and weighed approximately 1 7 9 -2 2 9 g when received. FO male rats were approximately 5 8 -6 7 days of age and weighed approximately 223-331 g when received. Weight data are included in Argus Research Laboratories, Inc. final report (study number 418-009).
Table 1. Test System Population Demographics and Dosage Levels for Study (418-009)
Population
Number of F0 Generation Rats
per Sex
Number of F1 Generation Rats
per Sex
Dosage (mgfkg/day)
Dosage Group I (Control) Dosage Group II Dosage Group III
Dosage Group IV
Dosage GroupV
35
35 35 35 35
25 0 (vehicle)
25 1 25 5 -- 10 -- 15
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Spoolm en C ollection and A nalysis
Sample specimens were collected by Argus (study 418-009) and sent to the 3M Environmental Laboratory for analysis. Liver and sera specimens were collected from F0 male rats at the completion of the cohabitation period and F0 female rats on day 21 postpartum. Liver specimens were collected from F0 generation litters, and stomach content specimens were collected from the F0 and F2 generation litters. The analysis of the stomach contents were not part of the scope of analysis determined by the study director. The number and type of specimens collected for analyses in the analytical phase of this study are presented below.
Specimens Collected from Study Groups I through V (through 11/30/98): Serum Specim ens-- 45 specimens Liver Specimens-- 65 specimens
Blood specimens were centrifuged after collection. Serum was then harvested and immediately frozen on dry ice and maintained frozen at -70C until shipped to the 3M Environmental Laboratory. Liver specimens collected from each animal were frozen and retained at -70C until shipped to the 3M Environmental Laboratory. Stomach content specimens were frozen at -20C until shipped to the 3M Environmental Laboratory. Liver, sera, and stomach content specimens were shipped to the 3M Environmental Laboratory frozen and on dry ice.
Sera and liver samples were extracted beginning on October 1 1 ,1 9 9 9 using an ion pairing reagent and methyl-ferf-butyl ether (MtBE) for the sera and ethyl acetate for the liver samples. Liver samples were homogenized prior to the extraction procedure. Sample extracts were analyzed using high-performance liquid chromatography-etectrospray/tandem mass spectrometry (HPLC-ESM SM S) in the multiple response monitoring mode. PFOS, PFOSA, PFOSAA, EtFOSE-OH, and M556 levels were quantitated by external calibration. PFOSEA was not analyzed due to inconsistent analysis and failed QC. Analytical details are included in this report.
Specimen Receipt and Maintenance
The 3M Environmental Laboratory received from Argus, serum, liver and stomach content specimens collected at predetermined time points during and at the end of thein-life phase of Argus study 418-009 on 8 -4 -9 8,1 0-1-98 and 1-29-99. All specimens were received frozen on dry ice and were immediately transferred to storage at -20C 10C. Specimens that were analyzed at Battelle were shipped frozen on dry ice.
Control matrices used in liver and sera analyses were obtained from commercial sources and are presented in Table 6 and 7. Samples analyzed at the 3M Environmental Laboratory will be maintained for a period of 10 years and will be stored at the laboratory at -20C 10C.
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Chemical Characterization
EtFOSE-OH CAS Number: 1691-99-2
Chemical Formula: CgF17S 0 2N(CH2CH3)CH2CH20 H Molecular Weight: 571.0
Chemical characterization information on the test article is presented in tabular form below. Chemical characterization information on the analytical reference materials used in this study is presented in tabular form in Appendix A (see Tables 8 and 9) and the interim Certificate of Analysis available in Appendix I.
Table 2. Characterization of the Test Article in Study FACT TOX-013
Test Article
Chemical Name Source
EtFOSE-OH FM-3929
2(N-Ethyfperfluorooctane sulfbnamido)-ethanol
3M
Expiration Date
05/2000
Storage Conditions
Ambient temperature
Chemical Lot#
Physical Description
30035, 30037, 30039 Waxy Solid
Purify
To be determined*
* The purity of the test article determined nominally by NMR analysis. Subsequent chemical characterization is occurring and this analytical reportwill be amended to indicate the purity when a certificate ofanalysis is issued.
Doss C onfirm ation A nalyses
The dose confirmation data were collected according to a method that was not fully validated. Dose confirmation analyses were performed on test article samples taken at the start of dosage, at 6 weeks, and at the end of dosage during the in-life phase of the study.
Dose confirmation analyses were performed on 3 dose levels collected during the in-life phase of the study: the results are presented in Appendix A (see Tables 10 and 11).
Dose confirmation was performed by diluting the Tween dose samples with Miili-Q water into the linear range of the instrument. For each sample, a matrix spike was prepared (at approximately 5 0-100% of the expected dose level). In all cases, samples were analyzed versus an unextracted curve using HPLC-ES/MS/MS. The instrumental parameters and analytical conditions described in ETS-8-5.1 were used for dose solution analyses.
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Method Summaries
Following is a brief description of the methods used during this analytical study by the 3M Environmental Laboratory. Detailed descriptions of the methods used are located in Appendix C. The methods and analytical equipment settings used by Battelle are presented in the Battelle final report (see Appendix G).
3IM Environm ental Laboratory
Preparatory Method
ETS-8-4.1, "Extraction of Potassium Perfluorooctanesulfonate or Other Fluorochemicai Compounds from Serum for Analysis using HPLC-Electrospray/Mass Spectrometry"
Sera samples were extracted using an ion-pairing extraction procedure. An ion pairing reagent was added to the sample and the analyte ion-pair was partitioned into MtBE. The MtBE extract was transferred to a centrifuge tube and put onto a nitrogen evaporator until dry. Each extract was reconstituted in 1.0 mL of methanol, then filtered through a 3cc plastic syringe attached to a 0.2pm nylon filter into a glass autoviai.
Analytical Method
ETS-8-5.1, "Analysis of Potassium Perfluorooctanesulfonate or Other Fluorochemicals in Serum Extracts Using HPLC-Electrospray/Mass Spectrometry"
The analyses were performed by monitoring one or more product ions selected from a Single primary ion characteristic of a particular fluorochemicai using HPLC-ESMSMS. For example, molecular ion 499, selected as the primary-ion for PFOS (Q F 17S 0 3-) analysis, was fragmented further to produce ion 99 (FSQ,-). The characteristic product-ion 99 was monitored for quantitative analysis.
Analytical Equipment
The following equipment and parameters are representative of those used during the analytical phase of this study.
Liquid Chrom atograph: Hewlett-Packard* Series 1100 Liquid Chromatograph system Analytical column: Keystone* BetasilTM C182x50 mm (5 pm) Column temperature: Ambient Mobile phase components:
Component A: 2mM aqueous ammonium acetate Component B: methanol Flow rate: 300 pL/min Injection volume: 10 pL Solvent Gradient: 10 minutes
Start at 40%B Hold at 40% B for 1 minute Increase to 95%B over 3.5 minutes
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Hold at 95% B for 2 minutes Return to 4 0 % 8 over 0.5 minutes Hold at 40% B for 3 minutes
Mass Spectrom eter: Micromass* API/Mass Spectrometer Quattro 11TMTriple Quadrupole system Software: Mass Lynx" 3.2 Cone Voltage: 2 0-60 V Collision Energy: 2 5 -4 5 eV Mode: Electrospray Negative Source Block Temperature: 150C 10C Z-spray source Analysis Type: Multiple Reaction Monitoring (MRM)
Table 3. Negative Ions Monitored in 3M Laboratory Analyses
Target Analyte
Primary Ion (AMU)
Product Ion (a m u )
PFOS
499.0
99.0
PFOSA PFOSAA EtFOSE-OH
498.0 584.0 630.0
78.0 169.0 59.0
M556 THPFOS
556.0 427.0
78.0, 169,0 80.0
D eviations Deviations from the original protocol and methods are documented in the table below:
Table 4. Deviation Summary for FACT TOX-013
Deviation
0ate(8) of Occurrence
Impact on Study
Pipette was used instead Oxford dispenser
0.2-1 .OmL of sample was used for extraction instead of 1.OmL.
Milk curd samples were not analyzed.
10/12/99 10/12/99 Entire study
Standards and samples were prepared identically. No adverse impact on study.
Current work indicates that volumes 0.5 mL provide results equivalent to 1 mL extraction volumes. Results of sample volumes <0.5 mL have not been validated and wiK be marked in the data table.
No milk curd data is available for the final report
Data Quality Objectives and Data Integrity
The following data quality objectives (DQOs) were indicated in the method performance section of ETS-8-5.1, "Analysis of Potassium Perfluorooctanesulfonate or Other Fluorochemicals in Serum Extracts Using HPLC-Electrospray/Mass Spectrometry":
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Linearity: The coefficient of determination (r2) equal to or greater than 0.980
Lim its o f Quantitation (LO Q ): The LOQ for PFOS is 5.55 ppb, PFOSA is 4.79 ppb, PFOSAA is 20.5 ppb, EtFOSE-OH is 36.2 ppb, and M556 is 19.2 ppb.
Acceptable Spike Recoveries: 70-130%
Data Summary, Analyses, and Results
With the exceptions noted in this report, data quality objectives for the analytical phase of this study outlined in the 3M Environmental Laboratory method ETS-8-5.1 (see Appendix C) and the Battelle final report (see Appendix G) were met. Although extraction and analysis were initiated in September 1998, the study was reprioritized and put on hold. Upon restarting the study, the decision was made to reextract and analyze the specimens. No data from the original analysis are included in this report. The data in this report reflect only that obtained from specimens extracted on, or after October 11,1999.
Sum m ary o f Q u ality C ontrol A nalyses R esults
Linearity: The coefficient of determination (r2) of the standard curves were0.980.
Calibration Standards: Quantitation of the target analytes was based on linear regression analysis (1/x weighted) of two extracted matrix curves bracketing each group of samples. High or low points on the curve may have been deactivated to provide a better linear fit over the concentration range most appropriate to the data. Ail active curve points are accurate to within 70% of theoretical value. 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 outlier curve point may have been deactivated. Quantitation of each analyte was based on the response of one or more specific product ion(s) using the multiple response-monitoring mode of the instrument (see Appendix C).
Lim its o f Quantitation (LO Q ): The LOQ is equal to the lowest accepted standard in the calibration curve (defined as a standard with a concentration that is within 30% of the theoretical value, and which has at least two times the analyte peak area detected in the extraction blanks).
Table 5. Determinations of the LOQ in the Analyses o f Serum Extracts
Analyte
Method LOQ
FFOS PFOSA PFOSAA EtFOSE-OH M556
5.55 ppb 4.79 ppb 20.5 ppb 36.2 ppb 24.9 ppb
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Blanks: All blanks were below the lower limit of quantitation for the compounds of interest. To simplify analyses that were complicated by endogenous levels of fluorochemicals in unexposed rat sera, rabbit sera was selected as a suitable surrogate matrix for standard curves.
Precision: Precision was determined by analysis of M S/M SD and was reproducible to within 10%.
M atrix Spikes: Matrix spikes and matrix spike duplicates were extracted with each set of samples and analyzed during analytical runs. With the exception of M556, all sera matrix spikes were within 30% of the theoretical concentration. Both matrix spikes showed a recovery of 69% for the M556. These results were verified. Data quality objectives will be adjusted to reflect this recovery.
Surrogates: The surrogate (THPFOS) was added to all samples and standards. THPFO S was not used for quantitation, but was used to monitor for gross instrument failure. 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.
Assuming spike recovery studies form a suitable indication of endogenous analyte recovery, sera data are quantitative to 30% for all analysis but M556; M 556 data is quantitated to 31% . The validity of this assumption has not been verified by other techniques.
Sum m ary o f Sam ple R esults Sam ples from Control Anim als: Low levels of PFOS, PFOSA, PFOSAA, EtFOSE-OH, and
M 556 were often detected in the sera and liver of the control animals. These levels were significantly lower than those found in the low dose test animals.
Sam ples from Dosed Anim als: In general, PFOS, PFOSA, PFOSAA, EtFOSE-OH, and M556 levels found in the sera and liver of the test animals increased with dose group. 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-013.
Statement of Conclusion
v
Under the conditions of the present studies, PFOS, PFOSA, PFOSAA, EtFOSE-OH, and M556 were observed in the sera and liver of rats dosed with EtFOSE-OH during the in-life phase of the study.
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Appendix A: Chemical Characterization, Control Matrices and Dose Confirmation Analyses
Table 6. Characterization o f the Control Matrices Used for Sera Analyses in Study FACT TOX-013
Location
3M Lab
Control Matrix
Rat Serum (TN-A-2001)
Rabbit Serum (TN-A-2573)
Source Expiration Date Storage Conditions Chemical Lot # Physical Description N/R--not recorded
Sigma
2010
Ambient 17H9306 Rat Serum
Sigma
2010
Ambient 118H8418 Rabbit Serum
Table 7. Characterization o f the Control Matrices Used for Liver Analyses in Study FACT TOX-013
Location
Battello Memorial Institute
Control Matrix
Rat Liver
Source Expiration Date Storage Conditions Chemical Lot # Physical Description
N/R--not recorded
Harlan N/R N/R N/R
R a tU v e r
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Table 8. Characterization of the Analytical Reference Materials Used for Sera Analyses in Study FACT T O X -013
Location
i5M Lab
Materials
PFOS
C aF^SO *
PFOSA
CBF17S 0 2NH2
PFOSAA
CbF17S 0 2N((CH2CH3) (CHjCOOH))
Source Expiration Date
3 M Specialty C hem icals
08/3 1/01
N /R 0 1/0 1/20 1 0
N /R 0 1/0 1/20 1 0
Storage Conditions
Chemical Lot Number
Physical Description
A m bient tem perature
A m bient tem perature
171 L -15709
W h ite crystalline powder
Light yellow w axy solid
A m bient tem perature NB 112999-99 Tan w axy solid
Purity
8 6.4%
TBD
TBD
` Surrogate standard-- 1H,1 H,2H,2H-Tetrahydroperfluorooctanesulfonic acid N/R-- not recorded TBD--to be determined NA-- not applicable
EtFOSE-OH
CbF17S 02N(CH2CH3) c h 2c h 2o h
3M IC P /P C P Division 0 1/0 1/20 1 0
A m bient tem perature
936
A m b er w axy solid
TBD
M556
CbF17S 02N ((H)(CHjCOOH))
3M
0 1 /0 1 /2 0 1 0
A m bient tem perature
THPFOS*
c bh4f13s o 3h
IC N B iom edicals 0 1/2 01 0
A m bient tem perature
N B 113047-80
53406
W h ite pow der TBD
Brown w axy solid NA
Table 9. Characterization of the Analytical Reference Materials Used fo r Liver Analyses in Study FACT TOX-013
Location
Battelle Memorial Institute
Materials
PFOS
M556 PFOSAA PFOSA THPFOS*
Source
3M 3M 3M 3M
Expiration Date
Storage Conditions
Chemical Lot Number
Physical Description
0 8 /3 1 /0 1
0 1/0 1/20 1 0
A m bient tem perature
A m bient tem perature
171 NB 113047-80
/Vhite crystalline powder
W h ite pow der
2010 A m bient tem perature
617
N /R
0 1 /0 1 /2 0 1 0
A m bient tem perature
L -1 5 7 0 9
Light yellow w axy solid
Purity
8 6.4%
TBD
TBD
TBD
` Surrogate standard-- 1H,1H,2H,2H-Tetrahydroperfluorooctanesulfbnic add N/R--not recorded TBD--to be determined NA-- not applicable
IC N N /R A m bient tem perature 59909
N /R NA
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Table 10. Tween Dosing Confirmation for Study In-life #418-009
Group Dose
Sample Number
Expected Cone. Measured Cone. EtFOSE (ng/mLJ EtFOSE (ng/mL)
Group 1-- Control 0 mg/mL Group 2--0.2 mg/mL Group 3-- 1.0 mg/mL Group 4-- 2.0 mg/mL Group 5--3.0 mg/mL
B-418-009-A, 06/08/98 B-418-009-A, 07/15/98 B-418-009-B, 06/08/98 B-418-009-B, 07/15/98 B-418-009-C, 06/08/98 B-418-009-C, 07/15/98 B-418-Q09-D, 06/08/98 B-418-009-D, 07/15/98 B-418-009-E, 06/08/98 B-418-009-E, 07/15/98
0.00 NA 200000 200000 1000000 100000 2000000 2000000 3000000 3000000
0.00 NA NA NA 1020000 942000 2190000 2750000 3060000 3640000
Homogeneity Samples-- 3.0 mg/mL
B-418-009-A, 05/08/98 1 0f6T
B-418-009-A, 06/08/98 3of6M
B-418-009-A, 06/08/98 5of6B
3000000 3000000 3000000
3250000 3690000 3790000
NA = Not applicable
EtFOSE % Recovery Accuracy
NA NA NA NA 102 94 110 138 102 121
108
123
126
Table 11. Tween Dosing Confirmation--Matrix Spikes for Study In-life #418-009
Sample Number
Expected Cone. EtFOSE (ng/mL)
Measured Cone. EtFOSE (ng/mL)
EtFOSE % MS Recovery Accuracy
B-418-009-B, 06/08/98-MS B-418-009-B, 07/15/98-MS B-418-009-C, 06/08/98-MS B-418-009-C, 07/15/98-MS B-418-009-D, 06/08/98-MS B-418-009-0,07/15/98-M S B-418-009-E. 06/08/98-MS B-418-009-E, 07/15/98-MS
1200 1200 900 900 900 900 1100 1100
NA NA 818 826 910 733 973 1089
NA NA 91 92 101 81 88 99
B-418-009-A, 05/08/98 1 of6T-MS
B-418-009-A, 06/08/98 3of6M-MS
B-418-009-A, 06/08/98 5 Of 6 B-MS
1100 1100 1100
949 1053 944
86 96 86
NA Not applicable
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Appendix B: Protocol
Analytical Study: FACT-TOX-013
LRN-U2095
Analytical Report: FACT TOX-013 LRN-U2095
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' Analytical
A
3M Environmental Laboratory____________
P ro to c o l - A n a lytical Stu d y
2(N-Ethylperfluorooctanesulfonamido)-ethanol in Two Generation Rat Reproduction
In-vivo study reference num ber: Argus 418-009 Study num ber: FACT 060998.1 T est substance: 2(N-Ethylperfluorooctanesulfonamido)-ethanol (N-EtFOSE-OH)
Name and address of Sponsor:
Marvin Case 3M Toxicology Services 3M Center Building 220-2E-02 St. Paul, MN 55144
-
Nam e and address o f testing facility: 3M Environmental Technology and Services 935 Bush Avenue, Building 2-3E-09 * St. Paul, MN 55106
Experim ental start date: Expected term ination date: December 31,1998 M ethod num bers and revisions:
FA C T-M -1.0, Extraction o f Potassium Perfluorooctanesulfonate or Other A nionic Surfactants from Liver for Analysis Using HPLC-Electrospray/Mass Spectrometry
FA C T-M -2.0, Analysis o f Fluorochemicals in Liver Extracts U sing HPLCElectrospray/Mass Spectrometry
FA C T-M -3.0, Extraction o f Potassium Perfluorooctanesulfonate or Other Anionic Surfactants from Serum for Analysis U sing HPLC-Electrospray/Mass Spectrometry
FA C T-M -4,0, Analysis o f Fluorochemicals in Serum Extracts U sing HPLCElectrospray/Mass Spectrometry
Author: Lisa Clemen
------- ------------------
Kris Hansen
Date
Study Director
Marvin Case Sponsor Representative
D ate
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Analytical Report: FACT T O ^ ftK 'U 2095
LRN-U2095
1.0 Purpose
_________________________________________________________
The analytical portion o f this dosing study is designed evaluate the levels o f perfluorooctane sulfonate (PFOS), or another metabolite o f 2(N-ethylperfluorooctanesulfonamido)-ethanol (NEtFOSE-OH) designated by the study director, in the liver o f the parent and subsequent generations o f the test system, or in die serum as necessary.
The in life portion o f this study was conducted at Argus Research Laboratories.
2.0 Regulatory Compliance_________________________________________________ ____
This study is conducted in com pliance with the Food and Drug Administration Good Laboratory Practices regulation as stated in 21 CFR 58. Any exceptions w ill be noted in the final report.
3.0 Test Materials_________________________________________________ _______________
3.1 Test, control, and reference substances and matrices
3.1.1 Analytical reference substance: Potassium perfluorooctanesulfonate (PFOS), lot #217
3.1.2 Analytical reference substance matrix: Rat liver and serum
3.1.3 Analytical control substance: None
3.1.4 Analytical control substance matrix: Rat liver and serum
3.2 Source o f materials 3.2.1 Analytical reference substance: 3M Specialty Chemical D ivision; traceability information w ill be included in the final report
3.2.2 Analytical reference substance matrix: Argus Research Laboratories; traceability information w ill be included in the final report
3.2.3 Analytical control matrix:
3 .2 3 .1 Rat liver - Argus Research Laboratories; traceability information w ill be included in the final report; or
Rabbit liver - Covance Laboratories; traceability information w ill be included in the final report
3.2.3.2 Rat serum - Sigm a Chemical Company; traceability information w ill be included in the final report
3.3 Number o f test and control sam ples. Liver samples for testing were received from 40 test animals and 10 control animals. Serum samples w ill be tested at the discretion o f the Study Director.
3.4 Identification o f test and control samples: The samples are identified using the Argus Research Laboratories identifiers, which consist o f a letter follow ed by the Argus project number, the animal number, the group designation, and the draw date.
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3.5 Purity and strength o f m aterials: Characterization o f the purity and identity o f the reference material is the responsibility o f the Sponsor.
3.6 S tability o f test m aterial: Characterization o f the stability o f the test material is the responsibility o f the Sponsor.
3.7 Storage conditions for test m aterials: Test materials are stored at room temperature. Samples are stored at --20 10 C.
3.8 D isposition o f test and/or control substances: Biological tissues and fluids are retained per GLP regulation.
3.9 Safety precautions: Refer to the material safety data sheets o f chemicals used. Wear appropriate laboratory attire, and follow adequate precautions for handling biological materials and preparing samples for analysis.
4.0 Experimental - Overview___________________________ I_________________________
Tissues from animals dosed as described in Argus Research Laboratories Protocol #418-009 are received for analysis o f fluorine compounds. At the discretion o f the Study Director, a series o f analytical tests w ill be performed on select tissues.
Initially, all liver samples w ill be analyzed for PFOS by electrospray/mass spectrometry (ES/M S). On the basis o f findings from these analyses, additional sample matrices may be evaluated or other metabolites may be targeted. If additional analysis is performed, a protocol amendment w ill be written.
5.0 Experimental - A nalytical M ethods
5.1 FA C T-M -1.0, Extraction o f Potassium Perfluorooctanesulfonate or Other Anionic Surfactants from Liver for Analysis Using HPLC-Electrospray/Mass Spectrometry
5.2 FA C T-M -2.0, Analysis o f Fluorochemicals in Liver Extracts Using HPLCElectrospray/Mass Spectrometry
5.3 FA C T-M -3.0, Extraction o f Potassium Perfluorooctanesulfonate or Other Anionic pmm. Surfactants from Seram for Analysis U sing HPLC-Electrospray/Mass Spectrometry
5.4 FA C T-M -4.0, Analysis o f Fluorochemicals in Serum Extracts U sing HPLCElectrospray/Mass Spectrometry
JP*"*
6.0 Data Analysis
6.1 D ata transform ations and analysis: Data w ill be reported as the concentration (weight/weight) o f fluoride per tissue or sample, or o f PFOS per unit o f tissue or fluid.
6.2 Statistical analysis: Statistics used may include regression analysis o f the serum concentrations over time, and standard deviations calculated for the concentrations within each dose group. If necessary, sim ple statistical tests, such as Student's t test, may be applied to evaluate statistical difference.
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LRN-U2095
7.0 Maintenance of Raw Data and Records / V
7.1 The follow ing taw data and records w ill be retained in the study folder in the archives fissa, according to AMDT-S-8:
7.1.1 Approved protocol and amendments
7.1.2 Study correspondence
7.1.3 Shipping records
7.1.4 Raw data
7.1.5 Electronic copies o f data
7.2 Supporting records to be retained separately from the study folder in the archives m m according to AMDT-S-8 w ill include at least the following:
7.2.1 Training records
'
r* 7.2.2 Calibration records 7.2.3 Instrument maintenance logs
7.2.4 Standard Operating Procedures, Equipment Procedures, and M ethods
7.2.5 Appropriate specimens.
8.0 References
8.1 3M Environmental Laboratory Quality System Chapters 1 ,5 and 6
8.2 Other applicable 3M Environmental Laboratory Quality System Standard Operating Procedures
r* 9.0 Attachments
9.1 FA C T-M -1.0, Extraction o f Potassium Perfluorooctanesulfonate or Other A nionic Surfactants from Liver for Analysis Using HPLC-Electrospray/Mass Spectrometry
9.2 FA C T-M -2.0, Analysis o f Fluorochemicals in Liver Extracts U sing HPLCElectrospray/Mass Spectrometry
SSHOES
9.3 FA C T-M -3.0, Extraction of Potassium Perfluorooctanesulfonate or Other Anionic Surfactants from Serum for Analysis Using HPLC-Electrospray/Mass Spectrometry
pm * 9.4 FA C T-M -4.0, Analysis o f Fluorochemicals in Seram Extracts U sing HPLCElectrospray/Mass Spectrometry
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ws 3M Medical Department Study: T6316.5
Analytical Study: FACT-TOX-013 Analytical Report: FACT TOX^ ^ 'U 2095
LRN-U2 095
Study Title Combined Oral (Gavage) Fertility Developm ent and'Perinatal/Postnatal
Reproduction Toxicity Study o f N-EtFOSE in Rats
PROTOCOL AMENDMENT NO. 1
Amendment Date: July 2 8 ,1 9 9 9
Performing Laboratory 3M Environmental Technology & Safety Services
3M Environmental Laboratory 935 Bush Avenue
S t Paul, M N 55106
Laboratory Project Identification ET&SS FACT-TOX-013 L IR N U 2095
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Analytical Report: FACT T O ^ M 'U 2095
LRN-U2095
Protocol FACT-TOX-013 Amendment 1
T h is am endm ent m o d ifies the fo llo w in g p o rtio n (s) o f th e p rotocol:
1. PROTOCOL reads: The proposed study com pletion date is listed as 12/31/98. AMEND TOread: The proposed study com pletion data is 6/30/00.
REASON: The proposed com pletion date w as changed to allow tim e for analyzing all matrices o f interest.
Amendment Approval
Marvin Case Ph.D., Sponsor Representative
/ T A - - J . Kris J. Hansen Ph.D., Study Director
g/ -2-)5
D ate
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Analytical Report: FACT TOXLRN-U2095
LRN-U2095
Study Title Combined Oral (Gavage) Fertility Development and Perinatal/Postnatal
Reproduction Toxicity Study o f N-EtFOSE in Rats
PROTOCOL AMENDMENT NO. 2
Amendment Date: September 10,1999
Performing Laboratory 3M Environmental Technology & Safety Services
3M Environmental Laboratory 935 Bush Avenue
St. Paul, M N 55106
Laboratory Project Identification ET&SS FACT-TOX-013 L IR N U 2095
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Protocol FACT-TO X-013 Amendment 2
T h is am endm ent m odifies th e fo llo w in g p o rtio n (s) o f th e pro to co l:
1. PROTOCOL reads: The protocol states that liver w ill be extracted and analyzed at the 3M Environmental Laboratory.
AMEND to read: The liver specimens w ill be extracted and analyzed at Battelle M em orial Institute, 505 King Avenue, Columbus, Ohio 43201-2693.
REASON: The liver specim ens w ill be sent to Battelle M emorial Institute for extraction and analysis due to time constraints in the 3M Environmental Laboratory.
2. PROTOCOL reads: The protocol states that serum specim ens w ill be extracted and analyzed follow ing methods:
FACT-M -3.0, "Extraction o f Potassium Perfluorooctanesulfonate or Other A nionic Surfactants from Serum for Analysis U sing HPLC-Electrospray/Mass Spectrometry" FA CT-M -4.0, "A nalysis o f Fluorochemicals in Serum Extracts U sing HPLCElectrospray/Mass Spectrometry"
AMEND to read: The serum specimens w ill be extracted and analyzed follow ing methods:
ETS-8-4.1, "Extraction o f Potassium Perfluorooctanesulfonate or Other Fluorochem ical Compounds from Serum for A nalysis U sing HPLC-Electrospray M ass Spectrometry" ETS-8-5.1, "A nalysis o f Potassium Perfluorooctanesulfonate or Other Fluorochem ical Compounds in Serum Extracts HPLC-Electrospray M ass Spectrometry"
REASON: The extraction and analytical methods FACT-M -3.0 and FACT-M -4.0, respectively, were updated on 04/27/99 to ETS-8-4.1 and ETS-8-5.1.
!--* 3M Environmental Laboratory
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"
Analytical Study: FACT-TOX-013
' Analytical Report: FACT TOX^ f t ^ U 2095
LRN-U2095 Protocol FACT-TOX-013
Amendment 2
3. Protocol reads: The protocol states that liver specim ens w ill be extracted and analyzed " follow ing methods:
FA C T -M -1.0, "Extraction o f Potassium Perfluorooctanesulfonate or Other A nionic
- surfactants from Liver for analysis U sing HPLC-Electrospray/Mas Spectrometry"
FA C T -M -2.0, "A nalysis o f Frluorochemicals in Liver Extracts U sing HPLC-
.
Electrospray/M ass Spectrometry"
AMEND to read: The liver specim ens w ill be extracted and analyzed follow ing method:
M ethod for A nalysis o f Perfluorooctane Sulfonate (PFOS) in Rat liver by LC/M S/M S, V ersion 1.0
REASON; Since the liver extraction and analysis was sub-contracted to Battelle M emorial Institute, this amendment w as written to include their liver methods and titles.
Amendment Approval
Marvin Case Ph.D ., Sponsor Representative
k i--
___________
Kristen J. Hansen Ph.D ., Study Director
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Analytical Study: FACT-TOX-013 Analytical Report: FACT TOX^ f t ^ 'U 2095
LRN-U2095
Study Title Analytical Study 2(N-Ethylperfluorooctanesulfonamido)-ethanol in
Two Generation Rat Reproduction
PROTOCOL AMENDMENT NO. 3
Amendment Date: October 4 ,1 9 9 9
Performing Laboratory 3M Environmental Technology & Safety Services
3M Environmental Laboratory 935 Bush Avenue
St. Paul, MN 55106
Laboratory Project Identification ET&SS FACT-TOX-013 L IR N U 2095
_ 3M Environmental Laboratory
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LRN-U2095
Protocol FACT Tox-013 Amendment Number 3
T h is am endm ent m o d ifies th e fo llo w in g p o rtio n (s) o f th e pro to co l:
1. Protocol Reads: Kristen J. Hansen, Ph.D. is the Study Director.
Amend to Read: James K. Lundberg, Ph.D. is the Study Director.
Reason: Original study design has changed due to availability o f resources and James K. Lundberg w ill begin serving as the study director for FACT-TOX-013 as o f 4 October 1999.
2. Protocol Reads:
-
Section 7.1 states that the follow ing raw data and records w ill be retained in the study folder
in the archives according to AM DT-S-8: Approved protocol and amendments; study
correspondence; shipping records; raw data; and electronic copies o f data. Additionally,
Section 7.2 states that supporting records to be retained separately from the study folder in
the archives according to AM DT-S-8 w ill include at least the following: Training records;
calibration records; instrument maintenance logs; Standard Operating Procedures, Equipment
Procedures, and Methods; and appropriate specimens.
Amend to Read: Section 7 states: "The original data, or copies thereof, w ill be available at the 3M Environmental Laboratory to facilitate audits o f the study during its progress and before acceptance o f the final report. When the final report is com pleted, all original paper data, including: approved protocol and amendments, study correspondence, dripping records, raw data, approved final report, and electronic copies o f data w ill be retained in the archives o f the 3M Environmental Laboratory. A ll corresponding training records, calibration records, instrument maintenance logs, standard operating procedures, equipment procedures, and methods w ill be retained in the archives o f the facility performing each analysis.
Reason: To direct subcontract laboratories in the disposition o f the item s listed above.
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LRN-U2095
Protocol FACT Tox-013 Amendment Number 3
3. Protocol reads: D isposition o f test and control substances: B iological tissues and fluids are retained per GLP
regulation.
Amend to read: Specim ens w ill be maintained in the 3M Environmental Laboratory specim en archives. A ll specim ens sent to sub-contract laboratories w ill be returned to the 3M Environmental Laboratory upon com pletion o f analysis and subm ission o f the sub-contract laboratory(s) final report. The specimens w ill be returned with the follow ing documentation: the signed original chain o f custody and records o f storage conditions w hile at the sub-contract facility.
Reason: To define in detail the appropriate disposition o f specim ens analyzed at subcontract
laboratories.
-
Amendment Approval
Marv Case, D .V .M ., Ph.D., Sponsor Representative
D ate
" lb Kristen J. Hansen, Ph.D., Previous Study Director
D ate
Dale L. Bacon, PhrBT 3M Environmental Laboratory Management
3M Environmentsl Laboratory 3M Environmental Laboratory
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Analytical Study: FACT-TOX-013
A n a ly tic a l R eport: FACT TOXLR ' U2095
LRN-U2095
Study Title Analytical Study o f 2(N-Ethylperfluorooctanesulfonamido)-ethanol in
Two Generation Rat Reproduction
PROTOCOL AMENDMENT NO. 4
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-U2095 FACT TOX-013 Argus Study: 418-009
3M M edical Department Study: T-6316.5
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Analytical Report: FACT TOXLR ' U2095
LRN-U2095 Protocol LRN-U2095 Amendment Number 4
T h is am endm ent m o d ifies th e follow ing portio n(s) o f the protocol:
1. Protocol reads: The study director for the present study was identified in the protocol as James K. Lundburg, Ph.D. A mend to read: The role of study director for the present study was reassigned to Marvin T. Case, D .V.M ., Ph.D., as of 20 January 2000. The previous study director, James K. Lundburg, 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).
2. Protocol reads: The sponsor for the present study was identified as Marvin T. Case, D .V.M ., Ph.D. Amend to read: The role of sponsor for the present study was reassigned to John L. Butenhoff, Ph.D., as of 20 January 2000. Reason: To ensure that the study director does not also carry the duties of study sponsor, the sponsor role was reassigned. In this manner, personnel responsibilities and workload are more evenly balanced.
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Analytical Study: FACT-TOX-013
LRN-U2095
Analytical Report: FACT TOX-013 LRN-U2095
Protocol LRN-U2095 Amendment Number 4
Amendment Approval
John L ButenhoffP h D ., Sponsor Representative
D ate
3 tk I M arvin T. Case, D. V.M., P h D ., Incoming Study Director
JO .--
eh^L Date &
3M Environmental Laboratory 3M Environmental Laboratory
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Analytical Study: FACT-TOX-013
Analytical Report: FACT TOX L R N 'U2095
LRN-U2095
Study Title Analytical Study o f 2(N-Ethylperfluorooctanesulfonamido)-ethanol in
Two Generation Rat Reproduction
PROTOCOL AMENDMENT NO. 5
Amendment Date: August 31, 2000
Performing Laboratory 3M Environmental Technology & Safety Services
3M Environmental Laboratory 935 Bush Avenue
St. Paul, MN 55106
Laboratory Project Identification FACT -T O X -013
ET&SS LRN U2095 Argus Study: 418-009 3M Medical Department Study: T6316.5
r* 3M Environmental Laboratory
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Analytical Study: FACT-TOX-013 Analytical Report: FACT TOxLfftM 'U2095
LRN-U2 095
Protocol FA C T TO X-013 Amendment No. 5
T h is am endm ent m odifies th e fo llo w in g po rtio n (s) o f th e protocol:
- 1. PROTOCOL READS: The Principle Analytical Investigator for the present study was identified as James K. Lundberg, Ph.D.
2. AMEND TO read: The role o f Principle Analytical Investigator for the present study was reassigned to Kristen J. Hansen Ph.D.
REASON: The role of Principle Analytical Investigator was reassigned due to availability of resources.
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Analytical Study: FACT-TOX-013 LRN-U2095
Analytical Report: FACT TOX-013 LRN-U2095
Protocol F A C T TOX-013 Amendment No. 5
Amendment Approval
John L. Butenhoff, Ph.D., Sponsor Representative
Date
Marvin T. Case, D. V.M., Ph.D., Study Director
^ O^ht-b Date
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Analytical Study: FACT-TOX-013
LRN-U2095
Analytical Report: FACT TOX-013 LRN-U2095
Appendix C: Extraction and Analytical Methods
This appendix includes the following methods: ETS-8-4.1, Extraction of Potassium Perfluorooctanesulfonate or Other Fluorochemical Compounds from Serum for Analysis Using HPLC-Electrospray/Mass Spectrometry, (14 pages) ETS-8-5.1, Analysis of Potassium Perfluorooctanesulfonate or Other Fluorochemicals in Serum Extracts Using HPLC-Electrospray/Mass Spectrometry, (9 pages)
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3M Medical Department Study: T6316.5
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Analytical Study: FACT-TOX-013 Analytical Report: FACT TOXLR ' U2095
T.DM _TTOftQC
3M Environmental Laboratory. 1 I T I !f 1 n * "
r 1 ! I v l " C m J L J *--/r x J L / V f l v t l . X V/X% M .
pm
M ethod
p m E x t r a c t io n ,o f P o t a s s iu m P e r f l u o r o o c t a n e s u l f o n a t e o r O t h e r
HPLC-F l u o r o c h e m ic a l c o m p o u n d s f r o m S e r u m f o r A n a l y s is U s in g
E l e c t r o sp r a y /M a ss Sp e c t r o m e t r y
(m m
M ethod N um ber: ETS-8-4.1
Adoption Date: 03/01/99
Author: Lisa Clemen, Glenn Langenburg
R evision Date:
Approved By:
- 0 1 1 S-- -
Laboratory Manager
/m m ,
fy i* (J tT ^ v -
-- --------------------
Group Leader
pm
C/iM, A
Technical Reviewer
Date
Date
... o v / W s ?
Date
pm
1.0 Scope and A pplication 1.1 Scope: This method is for the extraction o f potassium perfluorooctanesulfonate (PFOS)
or other fluorochemical compounds from serum. 1.2 A pplicable com pounds: Fluorochemical surfactants or other fluorinated compounds. 1.3 M atrices: Rabbit, rat, bovine, monkey, and human serum or other fluids as designated in
the validation report.
Word 6/95
fmm
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2.0 Summary of M ethod___________________________________________________________ 2.1 This method describes the procedure for extracting potassium perfluorooctanesulfonate
(PFOS) or other fluorochemical surfactants from serum, or other fluids, using an ion pairing reagent and methyl-iert-butyl ether (MtBE). In this method, seven fluorochem icals were extracted: PFOS, PFOSA, PFOSAA, EtFOSE-OH, PFOSEA, M 556, 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 evaporator until dry. Each extract is reconstituted in 1.0 m i. o f methanol, then filtered through a 3 cc plastic syringe attached to a 0.2 jum nylon filter into glass autovials. 2.2 These sample extracts are analyzed follow ing method ETS-8-5.1 or other appropriate m ethods.
3.0 Definitions___________________________________________________________________ 3.1 PFOS: perfluorooctanesulfonate (anion o f potassium salt) C8F17S 0 3` 3.2 PFOSA: perfluorooctane sulfonylam ide C8F17S 0 2NH2
3.3 PFOSAA: perfluorooctane sulfonylamido (ethyl)acetate C8F17S 0 2N(CH2CH3)CH2CO2'
3.4 EtFOSE-OH: 2(N-ethylperfluorooctane sulfonamido)-ethyl alcohol C8F17S 0 2N(CH2CH3)CH2CH20H
3.5 PFOSEA: perfluorooctane sulfonyl ethylamide C8FI7S 0 2N(CH2CH3)H
3.6 M 556: C8FnS 0 2N(H)(CH2C 0 0 H )
3.7 Surrogate standard: 1H-1H-2H-2H perfluorooctane sulfonic acid
4.0 Warnings and Cautions_________________________________________________________ 4.1 H ealth and safety w arnings
4.1.1 U se 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 follow ing equipment is used w hile performing this method. Equivalent equipment is
acceptable. 6.1.1 Vortex mixer, VWR, Vortex Genie 2 6.1.2 Centrifuge, Mistral 1000 or IEC 6.1.3 Shaker, Eberbach or VWR
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6.1.4 Nitrogen evaporator, Organomation 6.1.5 Balance ( 0.100 g)
7.0 Supplies and Materials________________________________________________________ 7.1 Gloves 7.2 Eppendorf or disposable pipettes 7.3 N algene bottles, capable o f holding 250 mL and 1 L 7.4 Volumetric flasks, glass, type A 7.5 I-CHEM vials, glass, 40 mL glass 7.6 Centrifuge tubes, polypropylene, 15 mL 7.7 Labels 7.8 Oxford Dispenser - 3.0 to 10.0 mL 7.9 Syringes, capable o f measuring 5 pL to 50 pL 7.10 Graduated pipettes 7.11 Syringes, disposable plastic, 3 cc 7.12 Syringe filters, nylon, 0.2 pm, 25 mm 7.13 Timer 7.14 Crimp cap autovials and caps 7.15 Crimpers Note: Prior to using glassware and bottles, rinse 3 tim es with methanol and 3 tim es w ith
M illi-QTM water. Rinse syringes a minimum o f 9 times with methanol, 3 rinses from 3 separate vials.
8.0 Reagents and Standards______________________________________________________ 8.1 Type I reagent grade water, M illi-QTM or equivalent; all water used in this method should
be M illi-QTM water and may be provided by a M illi-Q TOC PlusTM system 8.2 Sodium hydroxide (NaOH), J.T Baker or equivalent 8.3 Tetrabutylammonium hydrogen sulfate(TBA ), Kodak or equivalent 8.4 Sodium carbonate (NajCOj), J.T. Baker or equivalent 8.5 Sodium bicarbonate (N aH C 03), J.T. Baker or equivalent 8.6 M ethyl-T-Butyl Ether, Omnisolv, glass distilled or HPLC grade 8.7 Methanol, Omnisolv, glass distilled or HPLC grade 8.8 Serum or blood, frozen from supplier 8.9 Fluorochem ical standards
8.9.1 PFOS (3M Specialty Chemical D ivision), molecular weight = 538 8.9.2 PFOSA (3M Specialty Chemical D ivision), molecular weight = 499
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8.9.3 PFOSAA (3M Specialty Chemical D ivision), molecular w eight - 585
8.9.4 EtFOSE-OH (3M Specialty Chemical D ivision), molecular weight = 570
8.9.5 PFOSEA (3M Specialty Chemical D ivision), molecular weight = 527
8.9.6 M 556 (3M Specialty Chemical D ivision), molecular w eight = 557
8.9.7 Surrogate standard: 4-H, periluorooctane sulfonic acid (l-H .l-H , 2-H, 2-H C8F13S 0 3H) molecular weight = 428
8.9.8 Other fluorochemicals, as appropriate
8.10 R eagent preparation
NOTE: When preparing larger volumes than listed in reagent, standard, or surrogate preparation, adjust accordingly.
8.10.1 10 N sodium hydroxide (NaOH): W eigh approximately 200 g NaOH. Pour into a 1000 mL beaker containing 500 mL Milli-QTM water, m ix until all solids are dissolved. Store in a 1 L Nalgene bottle.
8.10.2 1 N sodium hydroxide (NaOH): Dilute 10 N NaOH 1:10. Measure 10 mL o f 10 N NaOH solution into a 100 mL volumetric flask and dilute to volum e using Milli-QTM water. Store in a 125 mL N algene bottle.
8.10.3 0.5 M tetrabutylammonium hydrogen sulfate (TBA): W eigh approximately 169 g o f TBA into a 1 L volumetric containing 500 mL Milli-QTM water. Adjust to pH 10 using approximately 44 to 54 mL o f 10 N NaOH (W hile adding the last mL o f NaOH, add slow ly because the pH changes abruptly). Dilute to volum e with Milli-QTM water. Store in a 1 L Nalgene bottle.
8.10.3.1 TBA requires a check prior to each use to ensure pH = 10. Adjust as needed using 1 N NaOH solution.
8.10.4 0.25 M sodium carbonate/sodium bicarbonate buffer (Na2C03/N aH C 03): W eigh approximately 26.5 g o f sodium carbonate (N a^ O j) and 21.0 g o f sodium bicarbonate (NaH C03) into a 1 L volumetric flask and bring to volum e with M illiQTM water. Store in a 1 L Nalgene bottle.
8.11 Standards preparation
8.11.1 Prepare PFOS standards for the standard curve.
8.11.2 Prepare other fluorochemical standards, as appropriate. Multicomponent fluorochemical standards are acceptable (for example, one working standard solution containing 1.00 ppm PFOS, 1.02 ppm PFOSA , 0.987 ppm PFOSAA, and 1.10 ppm EtFOSE-OH.)
8.11.3 W eigh approximately 100 mg o f PFOS into a 100 mL volumetric flask and record the actual weight.
8.11.4 Bring to volum e with methanol for a stock standard o f approximately 1000 ppm (ug/m L ).
8.11.5 D ilute the stock solution with methanol for a working standard 1 solution o f approximately 50 ppm.
8.11.6 D ilute working standard 1 w ith methanol for a working standard 2 solution o f approx. 5.0 ppm.
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8.11.7 D ilute working standard 1 with methanol for a working standard 3 solution o f approx. 0.50 ppm.
8.12 Surrogate stock standard preparation 8.12.1 W eigh approximately 50-60 mg o f surrogate standard 1-H,1-H, 2-H, 2-H, C8F,3S 0 3H into a 50 mL volumetric flask and record the actual weight. 8.12.2 Bring to volum e with methanol for a surrogate stock o f approximately 1000-1200 ppm. " 8.12.3 Prepare a surrogate working standard. Transfer approximately 1 mL o f surrogate stock to a 10 mL volumetric flask and bring to volum e with methanol for a working standard o f 100 ppm. Record the actual volum e transferred.
9.0 Sample Handling_________________________________________ ^____________________ 9.1 A ll samples are received frozen and must be kept frozen until the extraction is performed. 9.2 A llow samples to thaw to room temperature prior to extraction.
10.0 Quality Control ____________________________________ 10.1 Solvent B lanks, M ethod blanks and m atrix blanks
10.1.2 Extract two 1.0 mL aliquots o f Milli-QTM water follow ing this procedure and use as method blanks.
10.1.3 Extract two 1.0 mL aliquots o f the serum follow ing this procedure and use as matrix blanks. See 11.1.4.
9.2 M atrix spikes
10.2.1 Prepare and analyze matrix spike and matrix spike duplicate samples to determine the accuracy o f 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 concentrations w ill fall in the mid-range o f the initial calibration curve. Additional spikes may be included and may fall in the low-range o f the initial calibration curve.
10.2.4 Prepare one matrix spike and matrix spike duplicate per 40 samples, w ith a minimum o f 2 matrix spikes per batch.
0.3 C ontinuing calibration checks
10.3.1 Prepare continuing calibration check samples to ensure the accuracy o f the initial calibration curve.
10.3.2 Prepare, at a minimum, one continuing check per group o f 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 w ill fall within the mid-range o f the initial calibration curve. Additional spikes may be included that fall in the low-range o f the initial calibration curve. This is necessary if the analyst must quantitate using only the low end o f the calibration curve (for exam ple, 5 ppb --100 ppb, rather than 5 ppb - 1000 ppb).
11.0 Calibration and Standardization ___________________________________________
11.1 Prepare m atrix calibration standards
11.1.1 Transfer 1 mL o f serum to a 15 mL centrifuge tube.
11.1.2 If m ost sample volum es are less than 1.0 mL, extract standards with matrix volum es equal to the sample volum es. D o not extract less than 0.50 mL o f matrix. Record each sample volum e on the extraction sheet.
11.1.3 W hile preparing a total o f twenty aliquots in 15 mL centrifuge tubes, m ix or shake between aliquots.
11.1.4 Two 1 mL aliquots, or other appropriate volum e, serve as matrix blanks. Typically use the standard concentrations and spiking amounts listed in Table 1, at the end o f this section, to spike, in duplicate, two standard curves, for a total o f eighteen standards, two matrix blanks, and two method blanks.
11.1.5 Refer to validation report ETS-8-4.0 & ETS-8-5.0-V -1, which lists the working ranges and the Linear Calibration Range (LCR) for calibration curves.
11.1.6 U se Attachment D as an aid in calculating the concentrations o f the working standards. See Section 13.0 to calculate actual concentrations o f PFOS in calibration standards.
11.2 To each standard, blank, or continuing check, add appropriate amount o f surrogate working standard for the concentration to fall within the calibration curve range 5 ppb 1000 ppb.
11.3 Extract spiked matrix standards follow ing 12.6-12.16 o f this method. U se these standards to establish each initial curve on the mass spectrometer.
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Table 1
Approxim ate spiking am ounts for standards and spikes
U sing 1.0 mL o f m atrix
Working standard
pL Approx, final cone, o f
(approx, cone.)
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
15 0.750 ppm
50.0 ppm
20 .
1.00 ppm
12.0 Procedure___________________________________________________________________
12.1 Obtain frozen samples and allow to thaw at room temperature or in a lukewarm waterbath.
12.2 Vortex m ix for 15 seconds, then transfer 1.0 mL or other appropriate volum e to a 15 mL polypropylene centrifuge tube.
12.3 Return unused samples to freezer after extraction amounts have been removed.
12.4 Record the initial volume on the extraction worksheet.
12.5 Label the tube with the study number, sample ID, date and analyst initials. See attached worksheet for documenting the remaining steps.
12.6 Spike all sam ples, including blanks and standards, ready for extraction w ith surrogate standard as described in 11.2.
12.7 Spike each matrix with the appropriate amount o f standard as described in 11.1, or T able 1 in that section, for the calibration curve standards. A lso prepare matrix spikes and continuing calibration standards.
12.8 Vortex m ix the standard curve samples, matrix spike samples, and continuing calibration sam ples for 15 seconds.
12.9 Check to ensure the 0.5 M TBA reagent is at pH 10. I f not, adjust accordingly.
12.10 To each sample, add 1 mL 0.5 M TBA and 2 mL o f 0.25M sodium carbonate/sodium bicarbonate buffer.
12.11 U sing an Oxford Dispenser, add 5 mL methyl-terf-butyl ether.
12.12 Cap each sample and put on the shaker at a setting o f 300 rpm, for 20 minutes.
12.13 Centrifuge for 20 to 25 minutes at a setting o f 3500 rpm, or until layers are w ell separated.
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12.14 Label a fresh 15 mL centrifuge tube with the same information as in 12.5.
12.15 Rem ove 4.0 mL o f the organic layer to this clean 15 mL centrifuge tube.
12.16 Put each sample on the analytical nitrogen evaporator until dry, approximately 1 to 2 hours.
12.17 Add 1.0 mL o f methanol to each centrifuge tube using a graduated pipette.
12.18 Vortex m ix for 30 seconds.
.
12.19 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 mL glass autovial or low-volum e autovial when necessary.
12.20 Label the autovial with the study number, animal number and gender, sample tim epoint, matrix, final solvent, extraction date, and analyst(s) performing the extraction.
12.21 Cap and store extracts at room temperature or at approximately 4 C until analysis.
12.22 Complete the extraction worksheet, attached to this document, and tape in the study notebook or include in study binder, as appropriate.
13.0 Data Analysis and Calculations_____ ;________________________________________
13.1 C alculations
13.1.1 Calculate actual concentrations o f PFOS, or other applicable fluorochem ical, in calibration standards using the follow ing equation:
mL o f standard x concentration o f standard fug /m D ___________________ = mL o f standard + mL o f surrogate standard + initial matrix volum e (mL)
Final Concentration (pg/mL) o f PFOS in matrix
14.0 Method Performance__________________________________________________________
14.1 The method detection lim it (MDL) is analyte and matrix specific. Refer to M DL report for specific MDL and lim it o f quantitation (LOQ) values (see A ttachm ents B and C).
14.2 The follow ing quality control samples are extracted with each batch o f sam ples to evaluate the quality o f 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 o f the extraction.
14.2.3 Continuing calibration check samples to determine the continued accuracy o f the initial calibration curve.
14.3 Refer to section 14 o f ETS-8-5.1 for method performance criteria.
15.0 Pollution Prevention and W aste Management_________________________
15.1 Sample waste is disposed in biohazard containers, flammable solvent w aste 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 summaty 17.3 Attachment C, Calibration standard concentration worksheet
18.0 References__________________________________________________________________
18.1 The validation report associated with this method is E T S-8-4.0 & 5.0-V -l.
18.2 FACT-M -3.1, "Analysis o f Serum or Other Fluid Extracts for Fluorochem icals using HPLC-Electrospray M ass Spectrometry"
19.0 Affected Documents________ ;________________________________________________
19.1 ETS-8-5.1, "Analysis o f Serum or Other Fluid Extracts for Fluorochemicals using HPLC-Electrospray M ass Spectrometry"
20.0 Revisions__________________ :________________________________________________
R evision Number
1
Reason For R evision Section 12.21 Changed to include sample storage at room temperature. Section 12.13 Added the shaker speed. Section 12.17 Final volum e is 1.0 mL; not adjusted for initial volum es less than 1,0 mL.
R evision D ate
04/02/99
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Extraction Worksheet ETS-8-4.1
Study# Matrix Box# Wk/Day
DateSpiked/Analyst CCV MS MSD
Surrogate Std approx, ppm actual ppm #
FC-Mix approx. 0.5 pm actual ppm #
FC-Mix approx. 5 ppm actual ppm #
FC-Mix approx. 50 ppm actual ppm #
Comments
--. * ----
---
-
--
--
--
--
--
--
--
Blank
Std #
amount =
Serum Extraction Method
:
Vortex 15 sec.
Pipette Matrix
Volume
mL
Pipette 1 mL of 0.5 M TBA, pH 10. pH =
Std. #
Pipette 2 mL of 0.25 Na?COV0.25M NaHCCh buffer
Std. #
Dispense 5 mL of methyl-t-butyl ether
TN-A-
Shake 20 min.
Shaker speed:
Centrifuge 20-25 min.
Centrifuge speed:
Remove a 4 mL aliauot of organic layer
Put on Nitrogen Evaporator to drvness
Temperature:
Add methanol
Volume
mL TN-A-
Vortex 30 sec.
Filter using a 3cc B-D svringe with a 0.2um filter into a 1.5 mL autosample vial Cont. Cal. Verifications used same matrix as for std curve.
-
-
-
-
-
-
-
-
-
-
-
-
-
mL
Date & Initials
i""* Attachment A 3M Environmental Laboratory
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MDL/LOQ values for rabbit serum
Com pound MDL LOQ Linear C alibration R ange (LCR)
(PPb) (PPb) A pproxim ate concentrations to be used for preparing the Standard C alibration Curve
PFOS
1.74 5.55 5 p p b - 1000ppb
PFOSA
1.51 4.79 5 ppb - 1000 ppb
PFOSAA
3.46 20.5 5 ppb - 1000 ppb
EtFOSE-OH 11.4 36.2 5 ppb - 1000 ppb
M556
6.03 19.2 5 ppb - 1000 ppb
PFOSEA
5.71 18.2 5 ppb - 1000 ppb
MDL/LOQ values in rat, bovine, monkey, and human serum, and monkey plasma were not statistically
determined. Two curves in each o f these matrices were extracted and analyzed with the rabbit serum
curves to determine equivalence. Responses in the rat, bovine, monkey, and human were equivalent to
the rabbit responses, therefore, their MDL and LOQ will be the same values as determined in rabbit
serum.
Please see LOQ Summary and MDL study in ETS-8-4.0 & 5.0-V-l for further information.
Attachment B: MDL/LOQ Summary 3M Environmental Laboratory
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p"**
SBW r*
i r 1 (mm
Compound: PFOS Prepared range
Rabbit Serum o f standards (ppb) (ng/mL)
Full Range Low Curve High curve
1/X
0.995 - 978 4.94 - 248 97.8 - 978 0.995 - 978
Compound: PFOSA
Prepared range Rabbit Serum of standards
(ppb) (ng/mL)
Full Range Low Curve High curve
1/X
0.993 - 976 4.93 - 97.6 24.8 - 976 0.993 - 976
Compound: PFOSAA
Prepared range Rabbit Serum of standards
(ppb) (ng/mL)
Full Range Low Curve High curve
1/X
0.991-974 4.92 - 247 49.2 - 974 0.991 - 974
LCR from curve (PPb)
(ng/mL)
24.8 - 978
4.94 - 248
97.8-978
4.94 - 978
% Recovery Range
83-108 85-104 85-106 94-111
LCR from curve (PPb)
(ng/mL)
4.93 - 976
4.93 - 97.6
24.8 - 978
4.93 - 976
% Recovery Range
88-103 87-105 93-102 94-103
LCR from curve (PPb)
(ng/mL)
24.7 - 974
9.74 - 247
97.4 - 974
9.74 - 974
% Recovery Range
81-111 97-107 85-108 95-115
RSD Range
4.67-11.0 5.34-12.0 4.84-9.80 4.60-10.5
RSD Range
5.10-14.7 9.85-14.7 5.08-13.9 5.10-14.5
RSD Range
4.18-10.6 6.38-21.8 4.33-12.5 4.11-23.2
^ Attachment B: MDL/LOQ Summary
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Compound: EtFOSE-OH
Prepared range Rabbit Serum o f standards
(ppb) (ng/mL)
Full Range Low Curve High curve 1/X
0.993 - 976 4.93 - 97.6 49.3 - 976 0.993 - 493
LCR from curve (ppb)
(ng/mL) 49.3 - 976
9.76 - 97.6
97.6 - 976
9.76 - 976
% Recovery Range
77-110 97-107 90-109 86-111
Com pound: PFOSEA
Prepared range Rabbit Serum o f standards
(ppb) (ng/mL)
Full Range Low Curve High curve 1/X
0.993 - 976 4.93 - 248 49.3 - 976 0.993 - 976
LCR from curve (PPb)
(ng/m L ) 24.8 - 976
9.76 - 248
49.3-976
9.76 - 976
% Recovery Range
96-106 91-110 86-106 95-117
Compound: M556
Prepared range Rabbit Serum o f standards
(ppb) (ng/mL)
Full Range Low Curve High curve 1/X
0.993 - 976 4.93 - 97.6 97.6 - 976 0.993 - 976
LCR from curve (Ppb)
(ng/m L ) 24.8 - 976
9 .7 6 -9 7 .6
97.6 - 976
9.76 - 976
% Recovery Range
88-106 100-105 81-111 97-110
RSD Range
11.2-25.5 14.1-21.3 11.5-19.6 11.1-21.2
RSD Range
10.1-16.2 11.8-19.5 10.2-18.2 10.1-19.1
RSD Range
4.82-17.9 5.95-18.2 5.11-9.74 4.77-19.5
Attachment B: MDL/LOQ Summary
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Ion Pair Standard Curves - Fluids
Prep date(s):
Standard number:
Analyte(s):
Equipment number:
Sample matrix:
Final solvent and TN:
Blank fluid/identifier:
M ethod/revision:
Target analyte(s): _
FC mix std approx. 0.500 ppm:
FC mix std approx. 5.00 ppm:
FC mix std approx. 50.0 ppm:
Surrogate std approx. 100 ppm:
Actual concentrations of standards in the FC mix
PFOS PFOSA PFOSAA EtFOSE PFOSEA
Std cone Std cone Std cone Std cone Std cone
ug/mL ug/mL
ug/mL
ug/mL ug/mL
0.500
0.507
0.532
0.501
0.521
0.500
0.507
0.532
0.501
0.521
5.00 5.07 5.32 5.0! 5.21
5.00 5.07 5.32 5.01 5.21
5.00 5.07 5.32 5.01 5.21
50.0 50.1 53.2 50.1 52.1
50.0 50.1 53.2 50.1 52.1
50.0 50.1 53.2 50.1 52.1
50.0 50.1 53.2 50.1 52.1
M556 Std cone ug/mL
0.501 0.501 5.01 5.01 5.01 50.1 50.1 50.1 50.1
All Amt spiked mL 0.010 0.020 0.005 0.010 0.020 0.005 0.010 0.015 0.020
All Final vol
mL 1.015 1.025 1.010 1.015 1.025 1.010 1.015 1.020 1.025
C alculated concentrations of standards in the sam ple m atrix
PFOS PFOSA PFOSAA EtFOSE PFOSEA M556 Surrogate
Final cone Final cone Final cone Final cone Final cone Final cone Std cone
ng/mL
ng/mL
ng/mL
ng/mL
ng/mL
ng/mL
ng/mL
4.93 5.00 5.24 4.94 5.01 5.13 100
9.76 9.89 10.4 9.78 9.93 10.2
24.8 25.1 26.3 24.8 25.2 25.8 Surrogate
49.3 50.0 52.4 49.4 50.1 51.3 Final cone
97.6 98.9
104
97.8 99.3
102 ng/mL
248 251 263 248 252 258 500
493 500 524 494 501 513
735 746 782 737 749 766
976 989 1038 978 993 1017
All Ain't spiked
mL
0.005
Validated ranges - approximate concentrations
Serum
PFOS
PFOSA
PFOSAA EtFOSE-OH PFOSEA
M556
Rabbit
5.00-1000 | 5.00-1000 | 5.00-1000 | 5.00-1000 | 5.00-1000 | 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 Standard Curves
ETS-8-4.1
Extraction o f PFOS from Serum
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M ethod
A n a l y sis o f P o t a ssiu m P e r fl u o r o o c t a n e su l fo n a t e o r O t h e r F l u o r o c h e m ic a l s in Ser u m E x t r a c t s U sin g H P L C -E l e c t r o spr a y /M a ss S pe c t r o m e t r y
- M ethod Num ber: ETS-8-5.1
Author: Lisa Clemen, Robert Wynne
Approved By:
) X i l i --
W* Laboratory Manager
Group Leader
AL .
pm* A CIawc-u __
Technical Reviewer
A doption D ate: 03/01/99
R evision Date: H / ^ b P ^
^ y 2. c f
D ate
D ate
dh/ u / m
D ate
1.0 Scope and Application_________________________________________________________ 1.1 Scope: This method describes the analysis o f serum extracts for fluorochem ical surfactants
using HPLC-electrospray/mass spectrometry.
1.2 A pplicable C om pounds: Fluorochemical surfactants or other fluorinated compounds, or other ionizable compounds.
1.3 M atrices: Rabbit, rat, bovine, monkey, and human serum, or other fluids as designated in the validation report.
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2.0 Summary of Method____________________________________________ _______________
2.1 This method describes the analysis o f fluorochemical surfactants extracted from serum or other fluids, using HPLC-electrospray/mass spectrometry, or similar system as appropriate. The analysis is performed by monitoring a single ion characteristic o f a particular fluorochem ical, such as the perfluorooctanesulfonate (PFOS) anion, m /z= 499. Additionally, samples may be analyzed using a tandem mass spectrometer to further verify the identity o f a compound by detecting daughter ions o f the parent ion.
3.0 Definitions
_______________________________________________________________
3.1 A tm ospheric Pressure Ionization (API): The Micromass Quattro II triple quadrupole system s allow for various methods o f ionization by utilizing various sources, probes, and interfaces. These include but are not limited to: Electrospray Ionization (ESI), Atmospheric Pressure chem ical Ionization (APcI), Thermospray, etc. The ionization process in these techniques occurs at atmospheric pressure (i.e., not under a vacuum).
3.2 E lectrospray Ionization (E S, ESI): a method o f ionization 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 o f a strong electrical field.
3.3 M ass Spectrom etry, M ass Spectrom eter (M S), Tandem M ass Spectrom eter (M S/M S): The API Quattro II triple quadrupole system s are equipped with quadrupole mass selective detectors. Ions are selectively discriminated by mass to charge ratio (m /z) and subsequently detected. A single MS may be employed for ion detection or a series (M S/M S) for more specific fragmentation information.
3.4 C onventional vs. Z-spray probe interface: The latest m odels o f Micromass Quattro II triple quadrupole systems (post 1998) utilize a "Z-spray" conformation. The spray emitted from a probe is orthogonal to the cone aperture. In the conventional conformation it is aimed directly at the cone aperture, after passing through a tortuous pathway in the counter electrode. Though the configuration is different, the methods o f operation, cleaning, and maintenance are the same. However, Z-spray components and conventional components are not compatible with one another, but only with similar system s (i.e., Z-spray components are compatible with some other Z-spray system s, etc.)
3.5 M ass L ynx Software: System software designed for the specific operation o f these Quattro II triple quadrupole systems. Currently MassLynx has W indows 95 and W indowsNT 4.0 versions. A ll versions are similar. For more details see the manual specific to the instrument (Micromass Quattro II triple quadrupole M assLynx or MassLynx NT User's Guide).
4.0 Warnings and Cautions_____________________________________________________ 4.1 H ealth and Safety W arnings:
4.1.1 U se caution with the voltage cables for the probe. When engaged, the probe em ploys a voltage o f approximately 5000 Volts.
4.1.2 When handling samples or solvents wear appropriate protective gloves, eyewear, and clothing.
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4.2 Cautions:
4.2.1 Do not operate solvent pumps above capacity o f 400 bar (5800 psi) back pressure. If the back pressure exceeds 400 bar, the HP 1100 w ill initiate automatic shutdown.
4.2.2 D o not run solvent pumps to dryness.
5.0 Interferences________________________________________________________________
5.1 To m inim ize interferences when analyzing samples, teflon should not be used for sample storage or any part o f instrumentation that comes in contact w ith the sample or extract.
6.0 Equipment____________________________________________________________________
6.1 Equipment listed below may be m odified in order to optim ize the system . Docum ent any m odifications in the raw data as method deviations.
6.1.1 6.1.2
Micromass Quattro II triple quadrupole Mass Spectrometer equipped w ith an electrospray ionization source
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 to approximately 100 psi (H ouse 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 Reagents and Standards___________________________________ ;_____________________ 8.1 Reagents
8.1.1 Methanol, HPLC grade or equivalent
8.1.2 Milli-QTM water, all water used in this method should be Milli-QTM water or equivalent, and may be provided by a M illi-Q TOC 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 Sample Handling___________________ '__________________ ,_______________________
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.
^
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9.2 I f analysis w ill 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 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 duplicate per forty samples, w ith a minimum o f 2 spikes per batch.
10.2.4 Matrix spike and matrix spike duplicate concentrations w ill fall in the mid-range o f the initial calibration curve. Additional spike concentrations may fall in the low range o f the initial calibration curve.
10.3 Continuing Calibration Verifications
10.3.1 Continuing calibration verifications are analyzed to verify the continued accuracy o f the calibration curve.
10.3.2 Analyze a mid-range calibration standard after every tenth sample, with a minimum o f one per batch.
11.0 Calibration and Standardization___________________________________________ 11.1 Analyze the extracted matrix standards prior to and follow ing each set o f extracts. The
average o f two standard curves w ill be plotted by linear regression (y = my + b), weighted 1/x, not forced through zero, using M assLynx or other suitable software.
11.2 I f the curve does not meet requirements, perform routine maintenance or reextract the standard curve (if necessary) and reanalyze.
11.3 For purposes o f accuracy when quantitating low levels o f analyte, it may be necessary to use the low end o f the calibration curve rather than the full range o f the standard curve. Example: when attempting to quantitate approximately 10 ppb o f analyte, generate a calibration curve consisting o f the standards from 5 ppb to 100 ppb rather than the full range o f the curve (5 ppb to 1000 ppb). This w ill reduce inaccuracy attributed to linear regression weighting o f high concentration standards.
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12.0 PROCEDURES_________________________________________________________________________ 12.1 A cquisition Set up
12.1.1 Click on start button in the Acquisition Control Panel. Set up a sample list. A ssign a filename using M O-DAY-last digit o f year-sample number, assign a method (M S) 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 appropriate m asses. A full scan is usually collected along w ith the SIRs. Save acquisition method. If MS/MS instruments are em ployed, additional product ion fragmentation information may be collected. See Micromass M assLynx GUIDE TO DATA ACQUISITION for additional information and MRM (Multiple Reaction Monitoring).
12.1.3 Typically the analytical batch run sequence begins with a set o f extracted matrix standards and ends with a set o f extracted matrix 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 analyte carryover and are not considered samples but may be included as such.
12.2 U sing th e A utosam pler
12.2.1 Set up sample tray according to the sample list prepared in Section 12.1.1.
12.2.2 Set-up the HP1100/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 Inject/sample = 1
12.2.2.3 Cycle time = 13.5 minutes
12.2.2.4 Solvent ramp =
T im e
0.00 min. 8.50 min. 11.0 min. 12.0 min.
MeOH
40% 90% 90% 40%
2.0 mM Ammonium acetate
60% 10% 10% 60%
12.2.2.5 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 o f the probe. U se an eyepiece to check the tip. The tip should be flat with no jagged edges. I f the tip is found to be unsatisfactory, disassem ble 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 com ing out o f the tip o f the probe. A llow to equilibrate for approximately 10 minutes.
12.3.5 Turn orr the nitrogen. A fine mist should be expelled with no nitrogen leaking around the tip o f the probe. Readjust the tip o f the probe if no m ist is observed.
12.3.6 The instrument uses these parameters at the follow ing settings. These settings may change in order to optimize the response:
12.3.6.1 Drying gas 250-400 liters/hour 12.3.6.2 ESI nebulizing gas 10-15 liters/hour 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 w ill not go any further. Connect the voltage cables to the probe.
12.3.8 Print the tune page, with its parameters, and store it in the study binder w ith a copy taped into the instrument log.
12.3.9 U sing the cross-flow counter electrode in the ES/MS source is recommended for the analysis o f biological matrices.
12.3.10C lick on start button in the Acquisition Control Panel (this may vary among M assLynx versions, see appropriate MassLynx USER'S GUIDE). Press the start button. Ensure start and end sample number includes all samples to be analyzed.
13.0 Data Analysis and Calculations____________;_____________________________ 13.1 Calculations:
13.1.4 Calculate matrix spike percent recoveries using the follow ing equation:
% Recovery = Observed Result - Background Result x 100 Expected Result
13.1.5 Calculate percent difference using the follow ing equation:
% D ifference = Expected Cone. - Calculated Cone, x 100 Expected Cone.
13.1.6 Calculate actual concentration o f PFOS, or other fluorochemical, in matrix (pg/m L ):
fag o f PFOS calc, from std. Curve x Dilution Factor) x 1 pg (Initial Volum e o f matrix (mLl + mL o f Surrogate Standards 1000 ng
Final Volum e (mL)
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14.0 Method Performance________________________________________________________ 14.1 M ethod Detection Limit (MDL) and Limit o f Quantitation (LOQ) are method, analyte, and
matrix specific. Please see ETS-8-4.1, A ttachm ent B, for a listing o f 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 values are must be below the low est standard in the calibration curve
14.3 Calibration Curves
14.3.1 The r2value 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 30% o f the spiked concentration.
14.5 Continuing Calibration Verifications ,
14.5.1 Continuing calibration verification percent recoveries must be 30% o f the spiked concentration.
14.6 I f 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 I f data are to be reported when performance criteria have not been met, the data must be footnoted on tables and discussed in the text o f 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 R e c o r d s ____________________________________________________________________________ 16.1 Each page generated for a study must have the follow ing 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 1/x, then print these graphs and store in the study folder.
16.4 Print data integration summary, integration method, and chromatograms, from M assLynx, 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 A ttachm ent A for an example o f a summary spreadsheet.
16.6 Back up electronic data to appropriate medium. Record in study notebook the file name and location o f backup electronic data.
17.0 Tables. Diagrams. Flowcharts, and Validation Data______________________ 17.1 Attachment A: ETS-8-5.1 Data summary spreadsheet.
18.0 References__________________________________________________________________ 18.1 FACT-M -4.1, "Extraction o f Potassium Perfluorooctanesulfonate or Other Fluorochem ical
compounds from Serum for Analysis Using HPLC-Electrospray/Mass Spectrometry
18.2 ETS-9-24.0, "Operation and Maintenance o f the Micromass Atmospheric Pressure Ionization/M ass Spectrometer Quattro II triple quadrupole System s"
18.3 The validation report associated with this method is ETS-8-4.0 & 5 .0 -V -l.
19.0 Affected Documents_________________________________________________________
19.1 ETS-8-4.1, "Extraction o f Potassium Perfluorooctanesulfonate or Other Fluorochem ical Compounds from Serum for Analysis Using HPLC-Electrospray/Mass Spectrometry"
20.0 Revisions___________________ ________ '_________________________________________
R evision Number.
1
Reason For R evision Section 6.1.2 Clarification o f HP1100 system components. Section 11.1 Average o f two curves, not standard values, are used for plotting linear regression and added the 1/x weighting o f the curve. Section 12.2.2.4 Clarification o f solvent ramp. Section 17.1 Changed from attachment B to A.
R evision D ate
04/02/99
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Laboratory Study #
Study:
Test Material:
Matrix/Final Solvent:
Method/Revision:
-
Analytical Equipment System Number:
Instrument Software/Version:
Filename:
R-Squared Value:
Slope:
Y Intercept:
Date o f Extraction/Analyst:
Date o f Analysis/Analyst:
Group Dose
Sample#
Concentration ug/mL
Initial Vol. mL
Dilution Factor
Final Cone. ug/mL
Slope: Taken from linear regression equation. Group/Dose: Taken from the study folder. Sample#: Taken from the study folder. Concentration (ug/mL): Taken from the MassLynx integration summary. Initial Volume (mL): Taken from the study folder. Dilution Factor: Taken from the study folder. Final Cone. (ug/mL): Calculated by dividing the initial volume from the concentration
Attachment A: Summary Spreadsheet
ETS-8-5.1
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Appendix D: Data Summary Tables
Table 12. Reported Fluorochemical Levels in Sera Analyses in Study FACT TOX-013
Dosage Group
Specimen ID
PFOS (pg/mL)
1 10097F
0.0394
1 10105F
0.0181
1 10106F
0.0258
1 10107F
0.0343
1 10108F
0.0253
1 9922M*
0.0115
1 9930M*
0.0134
1 9931M
0.00725
1 9932M
0.0162
i 9933M*
0.0156
II 10121F
9.62
II 10126F
19.8
II 10136F
5.96
II 10140F
6.27
II 10142F
13.1
II 9961M *
34.8
II 9964M
30.4
II 9965M *
74.9
II 9967M
25.1
II 9970M *
38.9
III 10155F*
87.8
III 10156F
76.1
III 10164F
49.6
III 10172F
68.4
III 10177F
42.2
III 9997M
108
III 9999M *
178
III 10001M
94.9
III 10002M
113
III 10004M
130
IV 10187F
89.5
IV 10194F
73.4
IV 10203F
126
IV 10211F
99.7
IV 10214F
98.3
IV 10019M
302
IV 10024M*
477
IV 10029M*
296
IV 10033M
272
IV 10034M
249
* = Tentative values, initial volum e w as <0.5 mL
PFOSA (pg/mL)
<LOQ (4.79 ppb) <LOQ (4.79 ppb) <LOQ (4.79 ppb) <LOQ (4.79 ppb) <LQ (4.79 ppb) <LOQ (4.79 ppb) <LOQ (4.79 ppb) <LOQ (4.79 ppb) <LOQ (4.79 ppb) <LOQ (4.79 ppb)
0.0682 0.112 0.0663 0.0507 0.0665 0.0962 0.188 0.114 0.147 0.165 0.328 0.352 0.265 0.325 0.335 0.574 0.579 0.480 0.393 0.465 0.461 0.576 0.651 0.670 0.569 0.613 0.553 0.610 0.804 0.637
PFOSAA (pg/mL)
<LOQ (20.5 ppb) <LOQ (20.5 ppb) <LOQ (20.5 ppb) <LOQ (20.5 ppb) <LOQ (20.5 ppb) <LOQ (20.5 ppb) <LOQ (20.5 ppb) <LOQ (20.5 ppb) <LOQ (20.5 ppb) <LOQ (20.5 ppb)
1.59 4.55 1.18 0.690 2.09 1.40 5.86 1.86 1.26 5.55
9.9 6.91 4.66 8.17 4.58 11.8 18.7 12.1 10.4 14.9 8.00 10.6 19.0 10.2 12.3 22.5 40.5 28.8 24.5 31.4
EtFOSE-OH (pg/mL)
M566 (pg/mL)
<LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ <36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb)
<LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb)
<LOQ (24.9 ppb) <LOQ (24.9 ppb) <LOQ (24.9 ppb) <LOQ (24.9 ppb) <LOQ (24.9 ppb) <LOQ (24.9 ppb) <LOQ (24.9 ppb) <LOQ (24.9 ppb) <LOQ (24.9 ppb) <LOQ (24.9 ppb)
1.86 4.19 0.952 1.15 2.45 4.69 5.18 4.54 3.44 6.11 43.3 22.3 18.0 17.0 17.9 29.1 73.6 25.1 38.1 37.8
39.0 25.6 39.6 28.8 33.8 71.3 102 94.9 90.9 56.7
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Table 12. Reported Fluorochemical Levels in Sera Analyses in Study FACT TOX-013 (continued)
Dosage Group
Specimen ID
PFOS (pg/mL)
V NR
NR
V NR
NR
V NR
NR
V NR
NR
V NR
NR
V 10042M
238
V 10044M
235
V 1004SM
326
V 10051M
162
V 10054M
182
NR * Sample not received or reported
* = Tentative values, initial volume was <0.5 mL
PFOSA (pg/mL)
NR NR NR NR NR 0.791 0.972 0.897 0.574 0.669
PFOSAA (pg/mL.)
NR NR NR NR NR 25.2 20.7 26.8 14.0 15.8
EtFOSE-OH (pgftnL)
NR NR NR NR NR <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb) <LOQ (36.2 ppb)
M656 (pg/mL)
NR NR NR NR NR 62.4 55.6 93.8 30.7 55.5
Table 13. Reported Fluorochemical Levels in Liver Analyses in Study FACT TOX-013
Dosage Group
I I 1 1 1 1 1 1 I 1 1 1 i 1 1 II il il il il II il II II 11 II (I It II
II
Specimen ID
10097F 10105F 10106F 10107F 10108F 9922M 9930M 9931M 9932M 9933M 10097M 10105M 10106M 10107M 10108M 10121F 10126F 10136F 10140F 10142F
9961M 9964M 9965M 9967M 9970M 10121M 10126M 10136M 10140M 10142M
PFOS (pg/g)
0.149 <LOQ 0.121 <LOQ <LOQ 0.585 0.816 0.836
1.04 1.01 0.281 0.242 0.226 0.221 0.251 25.1 22.9 39.6 23.7 22.1 116 102 89.9 80.7 87.3 54.7 67.8 53.7 28.0 71.5
PFOSA (pg/g)
<LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <1.00 <LOQ <10Q <LOQ <LOQ <LOQ <LOQ <LOQ 0.514 0.708
1.40 0.601 0.508 4.49 4.10 2.88 3.88 5.42
1.90 2.65 2.35 1.22 2.06
PFOSAA (pg/g)
<LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <UOQ <LOQ <LOQ <LOQ <LOQ
2.68 4.34 5.01 2.67 2.67 11.0 15.6 9.79 6.62 10.4 5.87 14.6 9.44 2.82 6.55
M556(pg/g)
<LOQ <LOQ <UOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ
1.19 1.75 2.86 1.55 1.41 12.8 10.2 11.6 8.95 11.6 5.39 7.75 4.64 3.27 4.58
3M Environmental Laboratory
3MEnvironmental Laboratory
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3M Medical Department Study: T-6316.5
: 3M Medical Department Study: T6316.5
Analytical Study: FACT-TOX-013
LRN-U2095
Analytical Report: FACT TOX-013 LRN-U2095
Table 13. Reported Fluorochemical Levels In Liver Analyses in Study FACT TOX-013 (continued)
Doug* Group
III III III III III III III III III III III III III III III IV IV IV IV IV IV IV IV IV IV IV IV
IV IV IV V V V V V
Spadnw n ID
10155F 10156F 10164F 10172F 10177F 9997M 9999M 10001M 10002M 10004M 10155M 10156M 10184M 10172M 10177M 10187F 10194F 10203F 10211F 10214F 10019M 10024M 10029M 10033M 10034M 10187M 10194M 10203M 10211M
10214M 10042M 10044M 1004SM 10051M 10054M
p f o s (pg/g)
102 130 179 119 105 415 234 498 257 386 89.0 219 203 188
164 240 344 255 264 831 791 556 781 556 226 277 448 457 344 1218 1356 1132 1063 1054
PFOSA (pg/g)
2.22 2.24 1.94 2.17 2.88 10.8 9.41 8.67 8.29 8.41 5.11 6.14 6.26 6.20 6.91 2.80 4.06 3.14 3.39 4.56
12.8 11.0 11.2 12.6 11.0 6.36 9.96 9.93 11.4 8.11 16.4 13.0 10.9 9.80 | 10.8
PFOSAAQjg/g)
15.6 20.2 22.7 11.9 20.0 73.5 28.6 85.2 34.2 64.9 12.0 27.3 29.4 33.7 17.1 31.1 51.5 49.5 46.6
51.4 122 148 86.2 129 135 27.4 45.5 76.0 56.2 60.0 188 206 150 157 165
M 5S6(p(ft)
7.17 7.64 8.41 5.87 8.16 63.5 39.3 66.4 38.0 54.6 11.5 33.3 43.1 29.9 31.4 19.8 26.8 26.6 27.5 29.3
84.5 97.5 78.2 117 82.2 39.9 39.5 67.8 65.4 64.5
128 152 133 118 161
3M Environmental Laboratory
3MEnvironmental Laboratory
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3M Medical Department Study: T-6316.5
3M Medical Department Study: T6316.5
Appendix E: Data Spreadsheets
Analytical Study: FACT-TOX-013
LRN-U2095
Analytical Report: FACT TOX-013 LRN-U2095
3M Environmental Laboratory
3MEnvironmental Laboratory
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$MMedica| Department Sturdy: .T-6316.5
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3MEnvironmental Laboratory
F A C T -T O X -013 A rus#418-009
Argus 418-009, Two-Geaeralioo Reproductif Study of EtFOSE-OH in
Produci NumbcrfTest Substance):
ErFOSE-OH (T-6316.5)
Matrix:
R a Seront
BTS-8-4.1& ETS-8-5.1
Auletica! E
Davey 070799, Soup 020199
Instrument Software/Verekm:
Mu$Lyox3J
flau ste R-Squared Vaiue:
See Haiag to theright SccAjtachmests
,
Slope:
See Attachments
Y-loMcepC Date* of Extraction/Aialyst:
See Attachments (QT12/99 RWW
Dates of Analysb/AaalysL
UY14/99, 100099,10/22/99.03/16/00 MMH/1AS
DaeofDasaRedoctton/Analya:
m m , 10/21/99,10/25/99,03/17/30.03/23M0 MMH/IAS
Sample Data
RAT SERA n
Group Dose
Sumpia#
l-M -l Val I,
PFOS Croc. sfaL
Crocantrutfro
o f PFOS
0ta L e r % R e c
M ero PFOS uasteL
RSD S tr L D tv . MS/M SDRPD
Method Bile
IOI29-H20Bik-l 101294120 Blk-2
1 l
0.00 <LOQ< 2 4 5 R b) 0.00 <LOQ
<LOO
NA
Matrix Bik
RRS10l29-SoaBik-l
l
o.oo <LOQ< 24.8 ppb)
RBS10129-SoaBtk-2
1
0.00
<LOQ
QC-l00ppb
RBSI0129-MS-1
1
23 i
93
<UX)
NA
RBS 10129-MSD-l
1
213
86
90 8
G ivapl
10097F 0.70 34.4
0.0394
Control
10105F 0.70 1S.8
O.OmgAgAday
10106F
O.S0
16.1
0.0181 0.0258
Omg/mL
10107F 0.60 25.7
10108F
0.60
19.0
0.0343 0.0253
0.0286
29.2 0.00834
9922M** 9930M** 9931M
0.40 0.40 050
5.74 6.71 4.69
0.0115 0.0134 O.O752
9932M 9933M "
0.50 0.40
10.1 7.78
0.0162 0.0156
0.0129
27.4 0.00352
Group 2
10121F 0.70 336
9.62
1 mg/kgAlay
10126F
0.50
495
02tng/mL 10136F 1.00 297
19.8 5.96
10140F i.no 313 I0142F 0.60 394
627 13.1
52.4 10.9 5.74
9961M** 9964M 9965M**
0.40 0.50 0.20
347 379 374
34.8 30.4 74.9
9967M 9970M**
050 0.40
313 389
25.1 38.9
48.4 4 05 19.7
G ro u p ?
10155F**
0.40
434
87.8
5mg/kg/day
10156F
0.60
572
l.Omg/ml.
J0J64F
0.70
433
10172P
0.60
515
76.1 49.6 68.4
28.9
10177F 0.70 369 9997M 0.70 379
42.2 108
64.8 18.8
9999M** 10001M
100Q2M 10004M
0.30 0.70 0.60 O.SO
259 331 340 324
178 94.9 113 130
25.8 125 32.2
Group 4
10I87F 0.60 686
89.5
UMhtif/kgAky
10194F
0.80
7
73.4
2.0mg/mL 10203F* 0.70 1100
126
102HF*
0.80
995
99.7
19.6
10214F 0.70 842
98.3
97.4 19.1
I0019M
0.60
446
302
10024M** ioo2m **
0.30 0.40
360 296
477 296
10033M 10034M
0.50 0.50
340 311
272 249
28.4 319 90.6
Group?
NR NR NR
NR
15.0mgAgAi*y
NR
NR NR
NR
3.mg/roL
NR
NR NR
NR
NR NR NR NR M l NR
NR NR
NR NR NR
10042M 10044M 1045M 10051M 1054M
0.80 0.80 0.50 1.00 0.90
475 469 405 401 404
238 235 326 162 182
27.8 229 63.7
Limit of Onantation (LOQ): PFOS * 5 55 ng/mL, PFOSA =4.79Rib. PF5AA - 2 0 5 ppb.ElF O SE -362 ppb.PFOSEA 18.2 ppb,M 556-19 2 ppb
Correction factors not applicable for MS/MSD QC data
Tentative value, PFOS concentration w js am within the ringe o f the c u m . it's approximately 15 above tbc highest standard. LAC 03/24/00
D ae Entend/By.
0VI1/00,03/23/00,03/24/00 LAC
Date Verified/ By.
Purity Eucred/VcriOcd: 09/13/00 LAC, hoj 9/13/00
** Tentative values, initial voiumcbdowO-SrnL. LAC08/31/00
Analytical Study: FACT-TOX-013
11
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3M^Medical^Department Study: T-6316.5
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FACT-TOX-OI3 Argus# 418-409
Study:
Argtu 418-009. Two-GererailoflReproduction Study of EtFOSE-OH in Rau
Prodart Namb(Test Sabstaoce):
EtFOSB-H (T-63165)
Matrix: Methodfitevisfac
RatSemm &TS-4-4.I&ETS-8-5.1
Analytical Equipment SystemNumber
l>avey0TO799. Soup 020199
Instrument SoftwareA'ertion: Filename:
M tssLytu33 Seelisting to the right
R'SquxcdV ato:
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Slope
S Attachment*
Y-Iatocept
SeeAnactmmu
Datesof Extraokw/Analyst
UY12A9 RWW
Dales o f AndyotfAnalyst:
V W .10/20/99.1(V22/.03/LM MMHAAS
L hieoiD aa Reductioo'AndySt
10/15/9*. m m , 10/25/99, 03/176)0.03/2300 MMH/lAS
SaapleDat*
RATSERA F#____________
Gmy Deae
Method Blk
Matrix B k QC-IOOr *
SM fkt
10129-H2O Bk-1 10129-H2O Bflt-2 RBS10129>SeraBfc-l RBSW129-Sn Bk-2 RBS10129-MS-1 RBS10I29-MSD-1
laWal VaL L
1 111 11
PFOSA Cm c
0r.W00*
1.57 OOO
122507
215
C a s s a ta tien f PFOSA
a jtte L o r % Rc
<LOQ <LOO <OQ
<LOO 89% 87
M a PFOS ML
<LOO
<LOO
88%
RSD SM. Der. M S/M S D R P D
NA
NA
3
G m pl
10097F
0.70
1.46
<LOQ
Conard
0QOTngtfcg&y mgAnf.
10105F 10106F 10107F 10108F 9922M* 993<W-
0.70 0.50
00.6600
040
040
128
1.15 1.44 1.14 2.41 1.89
<LOQ
tLOQ LOQ <LOO <LQ <LOQ
<LOO
NA NA
9931M
050
1.44
<LOQ
9932M
050
1.41
<LQ
NA
9933M
040
133
<LOQ
<LOQ
NA
G raop
1mg&gftxy 0. 2 n t j t o i -
10121F 10126F 10136F 10140F 10142F 9961M** 9964M 9965M"
9967M 9970M*
0.70
011.5.00000
060 040
002500
050
0.40
47.7 S6.0 66.3 50.7 39.9 38.5 94.2 22.7
7636..62
00..0161822
0.0663 0.0507 0.0665
03)962 0.188 0.114
0147 0165
0.0727 0.142
31.7 0.0231
26.4 0.0376
G reap3 Smg/kgAtoy I.OtngAnLr
10155F 10156F 10164F 10172F 10177F 9997M
9999M I0001M
0.40 0.60 0.70 0.60 0.70 070 030 070
211311
185 195 235 402 174 336
0328 0352 0.265 0325 0.335 0574 0579 0.480
0521
103 0.0331
10002M 10004M
060 0.50
236 233
0393 0.465
0.498
15.8 0.0786
Group 4
2.010X1ag/kgtfay ogfaL
10187F 10194F 10203F IG ltlF I0214P 10019M 10024M** 10029M** 10033M 10034M
060 080 070 0.80 070 .6Q 050 0.40 050 050
276 461 456 536 398 368 166 244 402 318
0461 0.576 0651 0670 0569 0613 0553 0610 0804 0.637
0565 0.643
14.1 0.0826
14.8 0.0951
Groop S 15.0n/fcK/dsy
NR NR
NR NR NR NR
NR NR
3.0mgAoL
NR
NR NR
NR
NR NR 1042M I0044M
NR NR oso 080
NR NR 633 778
NR NR 0.791 0972
NR
NR NR
1004M 10051M 10054M
015.000
090
448 57* 602
0897 0.374 0669
0.780
208 O.J63
Limit of Quantitilioo (LOQ): PFOS = S55 nj/mL, PFOSA e 4.79 ppt>. PFOSAA * 205 ppb, EtFOSE 36.2 ppb, PlNR > Sample am received oof rpond.
Correction facto not ppticafcie far MS/MSDQC data
Tentativevalue,cwweotraiioowas4witliiBlbet)feoflltecotve,it's^imini*ieiylS**ove(Jkhighen sondanl- LAC 03/2400 faeEntsetf&y: QA1*, 05/23/00,05/14LAC
Date Verified/Uy:
*Tentative vafces, Initial volume below0.5 aL . LAC08/31A
Analytical Study: FACT-TOX-013
....1
LRN-U295
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Analytical Report: FACT TOX-013 LRN-U2095
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Page 67
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3M Medical Department Study: T-6316.5
3M Medical Department Study: T6316.5
Analytical Study: FACT-TOX-013
LRN-U2095
Analytical Report: FACT TOX-013 LRN-U2095
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3M Environmental Laboratory
3MEnvironmental Laboratory
P^rr# 6ft Page 68
3M Medical Department Study: T-6316.5
, 3M Medical Department Study: T6316.5
Analytical Study: FACT-TOX-013
LRN-U2095
Analytical Report: FACT TOX-013 LRN-U2095
t
3M Environmental Laboratory
3MEnvironmental Laboratory
Page 69
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3M Medical Department Study: T-6316.5
imw
: 3M Medical Department Study: T6316.5
Analytical Study: FACT-TOX-013
LRN-U2095
Analytical Report: FACT TOX-013 LRN-U2095
Appendix F: Example Calculations
Formula Used for Sera Analyses in Study FACT TOX-013
AR (ng/mL) x DF x SC x FV (mL) x 1.0 ng x PC = Reported Concentration (pg/mL) EV (m L) lOOIFng
Calculation Used for Group 4, Anim al ID 10033M 340 ng/mL x 500 x 0.9275 x 1 mL x 1.0 pg x 0.864 = 272 pg/mL 0.5'mU 1000"Sg~
AR-- Analytical result from MassLynx summary DF-- Dilution factor SC-- PFOS salt correction constant (0.9275) FV-- Final extract volume (1.0 mL unless otherwise noted) EV-- Volume o f sera extracted PC-- PFOS purity correction factor (86.4%)
3M Environmental Laboratory
3MEnvironmental Laboratory
Page 70
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3M Medical Department Study: T-6316.5
3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Analytical Study: FACT TOX-013 LRN-U2095
Appendix G: Contract Lab Report
This appendix includes the following contract laboratory report:
B a tte lle M e m o r ia l In s titu te , Study Number: N003604-D, 2 (N-Ethylfluorooctanesulfonamido)-ethano! in Two Generation Rat Reproduction, (65 pages)
3M Environmental Laboratory
3MEnvironmental Laboratory
Page 135
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
BIOLOGICAL SAMPLE ANALYSIS Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
... P u t t i n g T e c h n o l o g y T o W o r k
FINAL REPORT
2 (N-Ethylfluorooctanesulfonamido)-ethanol in Two Generation Rat Reproduction
SPONSOR
3M Toxicology Services 3M Center
Building 220-2E-02 St. Paul, MN 55144
Testing Facility
Battelle Memorial Institute 505 King Avenue
Columbus, Ohio 43201-2693
Prepared Bv
Patrick L. South, B.S.
3MEnvironmental Laboratory
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratoiy Study Number: FACT 060998.1
FINAL REPORT
2 (N-EthylfluorooctanesuIfonamido)-ethanoI in Two Generation Rat Reproduction
CV Joi/a. Andre, Ph.D. Battelle Principal Investigator
Battelle Senior Program Director
'Lac (
3MEnvironmental Laboratory
it
Page 73
3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
2 (N-Ethylfluorooctanesulfonamido)-ethanol in Two Generation Rat Reproduction
EXECUTIVE SUMMARY
Rat liver samples sent to Battelle by 3M Environmental Technology and Services were analyzed by the previously validated method "Method for Analysis of Potassium Perfluorooctanesulfonate (PFOS) in Rat Liver by LC/MS/MS". Samples were extracted and analyzed by High-Performance Liquid Chromatography Mass Spectroscopy (LC/MS/MS) for PFOS, M-556, PFOSAA, and PFOSA content only. Related fluorochemicals mentioned in the analytical method were not investigated.
The results for the concentration determinations in the liver samples from this study are attached as appendices to this report. Concentrations are reported as mass of analyte (fig) per gram of liver tissue extracted.
3MEnvironmental Laboratory
m
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
QUALITY ASSURANCE STATEMENT
This study was inspected by the Quality Assurance Unit and reports were submitted to the task leader, study director, and associated management as follows:
Date Reported
to Battelle Task
Phase Inspected
Inspection Date Leader/ Battelle
___________________________________________________ M anagem ent
Date Reported to Offsite Study Director/ Management_______
Sample weights Sample homogenization Extraction Sample analysis Audit study file Audit final report Audit study file Audit final report
10/12/1999 10/12/1999 10/13/1999 10/13/1999 12/9/1999 12/9/1999 2/21/2001 2/21/2001
11/1/1999 11/1/1999 11/1/1999 11/1/1999 12/9/1999 12/9/1999 2/21/2001 2/21/2001
3/30/01 3/30/01 3/30/01 3/30/01 3/30/01 3/30/01 3/30/01 3/30/01
Hality Assurance Unit ^ attelle Memorial Institute
Date
3MEnvironmental Laboratory
IV
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
GOOD LABORATORY PRACTICES COMPLIANCE STATEMENT
Study Title. 2 (N-Ethylfluorooctanesulfonamido)-ethanol in Two Generation Rat Reproduction
This study was conducted in compliance with the Food and Drug Administration's Good Laboratory Practice Regulations (21 CFR 58), with the exception that the mass spectrometry data for the liver samples was collected and processed with the MassLynx software system (version 3.1), which was not fully validated. The study was listed on Battelle's Master List o f regulated studies.
Battelle Principal Investigator
Marvin T. Case, DVM, Ph.D. Study Director
3MEnvironmental Laboratory
V
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
Table of Contents
Page Executive Summary................................................................................................................................................iii Quality Assurance Statement................................................................................................................................ iv Compliance Statement........................................................................................................................................... v Table of Contents...................................................................................................................................................vi 1.0 Introduction............................................................................................................................................... 1 2.0 Reference Substances............................................................................................................................... 1 3.0 Receipt of Samples................................................................................................................................... 1 4.0 Analysis of Samples................................................................................................................................. 1
4.1 Summary of Method.................................................................................................................... 1 4.2 Results......................................................................................................................................... 3
4.2.1 Quality Control..............................................................................................................3 4.2.2 Sample Results............................................................................................................. 3 5.0 Conclusions................................................................................................................................................3 6.0 Acknowledgements................................................................................................................................... 4 7.0 Specimen Storage and Record Archives.................................................................................................. 4
List of Tables Table 1. Example of Instrument Parameters Used to Analyze Samples.............................................................2
Appendix A (Results) Summary Results for Rat liver Sample Analysis................................................................................................. A-l
Appendix B (Daily Acceptance Criteria Summary) Daily Acceptance Criteria Summary....................................................................................................................B-l
Appendix C (Sample Inventory List) Sample Inventory List............................................................................................................................................C-l
Appendix D (Chromatograms) Representative Chromatograms............................................................................................................................D -l
Appendix E (Protocol, Amendments, and Deviations) Protocol, Amendments, and Deviations.................................................................................................................E-l
Appendix F (PFOS Purity Report) PFOS Purity Report...............................................................................................................................................F-l
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
1.0 Introduction This report presents a description of the method used to analyze PFOS, M-556, PFOSAA, and
PFOSA in rat liver samples from 3M Study Number FACT 060998.1 (TOX-013) and the results from this analysis. See Appendix E for a copy of the study protocol, amendments, and protocol deviation reports).
2.0 Reference Substances The analytical reference substances for this study were supplied by 3M. The following lot number or
tracking number designations apply: PFOS (lot 171), M-556 (TN-A-2203), PFOSAA (TN-A-1283) and PFOSA (L-15709). Note that based on information supplied to Battelle from 3M, PFOS has two equivalent names. The name appearing on the Material Safety Data Sheet and bottle label is potassium perfluoroalkyl sulfonate. The name more commonly used by 3M in analytical methods and correspondence is potassium perfluorooctanesulfonate. The latter name will be used in this report. See Appendix F for purity data supplied by 3M to Battelle. The reference substances were stored at room temperature.
The surrogate standard was 1H,1H,2H,2H-Perfluorooctane sulfonic acid, lot number 59909, supplied by ICN. The surrogate standard was stored at room temperature.
3.0 Receipt of Samples Samples were received frozen and intact at Battelle, from 3M Environmental Technology and
Services, in one batch on October 6,1999. Samples were generated by Argus Research under protocol number 418-009. See Appendix C for a copy of the inventory list. The samples were stored at approximately -20C.
4.0 Analysis of Samples
4.1 Summary of Method
Samples were analyzed by a previously validated method (Battelle study number N003604-A). The current version of the method is attached to this report in Appendix E. Samples were analyzed by LC/MS/MS, and an example of the instrument parameters is listed in Table 1. Note that only PFOS, M-556, PFOSAA, and PFOSA (and the surrogate) were quantitated. The other related fluorochemicals, although present in the stock solutions, were not monitored. Quadratic regressions weighted 1/x were used to construct the calibration curves.
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Table 1. Example of Instrument Parameters Used to Analyze Samples
LC/MS/MS System
Autosampler HPLC pumps VIass spectrometer Analytical column Mobile phase components Gradient profile
Injection volume Flow Column temp HPLC pressure MS source Dcsolvation as Nebulizer as Source block temp Desolvation temp Cone voltage
Collision energy Collision gas Multiplier Resolution Ions monitored
Total run time Approximate retention times:
Make: Gilson
Model: 234
Make: Gilson
Models: 305 and 306
Make: Micromass______ Model: Quattro LC with Z-spray source
Keystone Betasil C 18,5 urn, 2 x 50 mm, Part No. 055-701 -2
Component A: Ammonium acetate(2mM):methanol, 60:40, v:v
Component B: Ammonium acetate(2mM):methanol, 5:95, v:v
Time, min
%B Flow. mL/min
0 0 0.3 1 0 0.3
4.5 100 0.3 6 100 0.3 6.1 100 0.6
8.5 100 0.6 9 0 0.3 11 0 0.3
10 UL______________________________________
LC column flow at start split to 20 pL/min into the MS
Ambient_______________________________________
Approximately 840 psi at gradient start_____________
Electrospray, Negative Ion_______________________
Nitrogen at ~575 L/hr___________________________
Nitrogen at ~80 L/hr_____________________________
140C__________________________________________
250C__________________________________________
70 V for SS, PFOS
20 V for M-556, PFOSAA, PFOSA________________
40 eV__________________ _______________________ Argon, gas cell, at ~2.5xl0'3 mb
650 V__________________________________________
12,0 for MSI; 10,0 for MS2_______________________
427> 81 MRM transition for SS
499>99 MRM transition for PFOS
556>78 MRM transition for M-556
584> 169 MRM transition for PFOSAA
498>78 MRM transition for PFOSA_____ _________
11 minutes_____________________________________
SS: 4 min
PFOS: 4.2 min
M-556: 4.4
PFOSAA: 4.5
PFOSA: 5
2
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4.2 Results
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
4.2.1 Quality Control
System suitability acceptance criteria were established during the method validation and are included in Appendix E, Section IX Acceptance Criteria. Relevant statistics from each sample set are provided in Appendix B. Representative chromatograms are given in Appendix D.
4.2.2 Sample Results
The results of the sample analyses as well as a method detection limit determination are presented in Appendix A. All liver samples were initially extracted as undiluted homogenates. After the data were reviewed, dilutions of the homogenates were performed in order to bring analyte concentrations within the calibration range. The first analysis that provided acceptable data for an analyte was used in reporting. Four extraction sets were required to provide data for each analyte.
The limit of quantitation is defined as the concentration of the lowest standard which meets acceptance criteria for accuracy (25% RE; see Appendix E for definition). The notation BLOQ denotes "Below Limit of Quantitation" for samples that had concentrations lower than the theoretical concentration for the 0.13 pg/g calibration standard. The notation ALOQ denotes "Above Limit of Quantitation" for samples that had concentrations higher than the theoretical concentration for the 13 pg/g calibration standard. Samples that were initially ALOQ were diluted with blank liver homogenate and re-extracted. Samples that were expected to be ALOQ were first diluted with blank liver homogenate before extraction. The "Corrected PFOS Cone" presented in the results tables is the concentration found for the diluted sample multiplied by its dilution factor (final volume + sample homogenate volume).
The method detection limit (MDL) of PFOS was calculated in Battelle study N003296F to be0.0173 pg/g from the analysis of 7 replicate preparations of 0.13 pg/g calibration standard. The MDL was calculated by multiplying the standard deviation of the found concentrations of the 7 reps by 3.143; the Signal-to-Noise (S/N) ratio was calculated by dividing the mean found concentration of the 7 reps by their standard deviation. The method of MDL determination was provided by the Sponsor.
5.0 Conclusions
All analyses met acceptance criteria unless otherwise noted.
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6.0 Acknowledgements
Acknowledgement of principal contributors participating in the performance of this study at Battelle is presented in the following list.
Participant
Title
Jon C. Andre, Ph.D. Richard W. Slauter, Ph.D., D.A.B.T. Patrick L. South, B.S. Gerke H. van der Zwaag, M.S.
Battelle Principal Investigator Senior Program Director Mass spectroscopist Sample preparation chemist
7.0 Specimen Storage and Record Archives
See Appendix E, protocol amendment 3 for records archival information. All residual liver samples, extracts, and unused test article will be disposed of or returned to the Sponsor as directed by the Sponsor.
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APPENDIX A -RESULTS
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PFOS, M-S56, PFOSAA, PFOSA IN RAT LIVER
BATTELLE STUDY:
N003604-D
SPREADSHEET SOFTWARE:
DATA ENTERED:
MANUALLY
EXCEL 97
Sample
Dose Group
Animal Number
1 1 9922 2 1 9930 3 1 9931 4 1 9932 5 1 9933 6 2 9961 7 2 9964 8 2 9965 9 2 9967 10 2 9970 11 3 9997 12 3 9999 13 3 10001 14 3 10002 15 3 10004 16 4 10019 17 4 10024
18 4 10029 19 4 10033 20 4 10034 21 5 10042 22 5 10044 23 5 10045 24 5 10051 25 5 10054 26 1 10097 27 1 10105 28 1 10106 29 1 10107
30 1 10108
31 2 10136
32 2 10140 33 2 10142 34 2 10121
35 2 10126 36 3 10177 37 3 10155
38 3 10156 39 3 10164 40 3 10172
41 4 10187
42 4 10194
43 4 10203
44 4 10211
45 4 10214 46 1 10097
47 1 10105
48 1 10106 49 1 10107 50 1 10108 51 2 10136 52 2 10140 53 2 10142 54 2 10121 55 2 10126
56 3 10177
57 3 10155 58 3 10156 59 3 10164 60 3 10172
61 4 10187
62 4 10194 63 4 10203 64 4 10211
65 4 10214
BLOQ = BELOW LIMIT O F QUANTITATION
Analysis date key:
Sample Type
Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal
Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Maternal Maternal Maternal Maternai Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal
PFOS Cone,
iig/g
6.77E-01 9.44E-01 9.68E-01 1.20E+00 1.17E+00 1.34E+02 1.18E+02
1.04E+02 9.34E+01
1.01E+02 4.80E+02 2.71 E+02 5.76E+02 2.97E+02 4.47E+02 9.62E+02 9.15E+02 6.43E+02 9.04E+02 S.43E+02 1.41E+03 1.57E+03 1.31E+03
1.23E+03 1.22E+3 1.72E-01
BLOQ 1.40E-01
BLOQ BLOQ 4.61 E+01 2.74E+01 2.56E+01 2.906+01 2.65E+01 1.21 E+02 1.18E+02 1.50E+02 2.07E+02 1.38E+02 1.90E+02 2.78E+02 3.98E+02 2.95E+02 3.06E+02 3.25E-01 2.80E-01 2.61E-01 2.56E-Q1
2.90E-01 6.21 E+01 3.24E+01 8.28E+01 6.33E+01 7.85E+01 1.77E+02 1.03E+02 2.53E+02 2.35E+02 2.18E+02 2.S2E+02 3.21 E+02 5.19E+02 5.29E+02 3.98E+02
M-556 Cone, pg/g
BLOQ BLOQ BLOQ BLOQ BLOQ 1.28E+01 1.02E+01 1.16E+01 8.95E+00 1.16E+01 6.35E+01 3.93E+01 6.64E+01 3.80E+1
5.46E+01 8.45E+01 9.7SE+01 7.82E+01
1.17E+02 8.22E+01 1.28E+02 1.52E+02 1.33E+02 1.186+02 1.616+02
BLOQ BLOQ BLOQ BLOQ BLOQ 2.86E+00 1.55E+00 1.41F+00 M .19E+00 1.75E+00 8.16E+00 7.17E+00 7.64E+00 8.41E+00 5.87E+00 1.98E+01
2.68E+01 2.66E+01 2.75E+01
2.93E+01 BLOQ BLOQ BLOQ BLOQ BLOQ
4.64E+00
3.27E+00 4.56E+00 5.39E+00 7.75E+00
3.14E+01 1.15E+01 3.33E+01 4.31 E+01 2.99E+01 3.99E+01 3.96E+01 6.78E+01 6.54E+01 6.45E+01
PFOSAA Cone, pg/g
BLOQ BLOQ BLOQ BLOQ BLOQ 1.10E+01 1.56E+01 9.79E+00 6.62E+00 1.04E+01 7.35E+01 2.86E+01 8.52E+01 3.42E+01
6.49E+01 1.22E+02 1.48E+02 8.62E+01
1.29E+02 1.35E+02 1.88E+02 2.06E+02 1.50E+02 1.57E+02 1.656+02
BLOQ BLOQ BLOQ BLOQ BLOQ 5.01 E+00 2.67E+00 2.67E+00 2.68E+00 4.34E+00 2.00E+01 1.56E+01 2.02E+01 2.27E+01 1.19E+01 3.11 E+01 5.15E+01 4.95E+01 4.66E+01 5.14E+01 BLOQ BLOQ BLOQ BLOQ BLOQ 9.44E+00 2.82E+00 6.55E+00 5.87E+00 1.46E+01 1.71 E+01 1.20E+01 2.73E+01 2.94E+01 3.37E+01 2.74E+01 4.55E+01 7.60E+01 5.62E+01 6.00E+01
PFOSA
Cone,
ua/a
BLOQ BLOQ BLOQ BLOQ BLOQ 4.49E+00 4.10E+00 2.88E+00 3.86E+00 5.42E+ 1.08E+01 9.41 E+00 8.67E+00 8.29E+00 8.41 E+00 1.28E+01 1.10E+01 1.12E+01 1.26E+01 1.10E+01 1.64E+01 1.30E+01 1.09E+01 9.80E+00 1.08E+01 BLOQ BLOQ BLOQ BLOQ BLOQ 1.40E+00 6.01 E-01
5.08E-01
5.14E-01
7.08E-01 2.88E+00 2.22E+00 2.24E+00 1.94E+O0 2.17E+00 2.80E+00
4.06E+00
3.14E+00
3.39E+00 4.56E+00
BLOQ BLOQ BLOQ BLOQ BLOQ 2.35E+00
1.22E+00 2.06E+00
1.90E+00
2.65E+00
6.91 E+00 5.11 E+00
6.14E+00
6.26E+00 6.20E+00
6.36E+00 9.96E+00
9.93E+00
1.14E+01
8.11 E+00
Normal font = October 13,1999 Underline = October 16,1999 Bold - October 18,1999
Bold Underline - October 20,1999
All sam ples undiluted All sam ples undiluted All sam ples diluted All sam ples diluted
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METHOD DETECTION LIMIT (MDL) RESULTS STUDY: N003604-D ANALYSIS DATE AND INSTRUMENT ID: DATA ENTERED: SPREADSHEET SOFTWARE:
130ct99; 9053 Electronically and manually Excel 97
All cones in (ig/g
Calculated Concentration o f Replicate 1 Calculated Concentration o f Replicate 2 Calculated Concentration o f Replicate 3 Calculated Concentration o f Replicate 4 Calculated Concentration o f Replicate 5 Calculated Concentration o f Replicate 6 Calculated Concentration o f Replicate 7
Mean Concentration Std. Dev.
M -556 0.1269 0.1220 0.1433 0.1368 0.1670 0.1225 0.1190
0.1339 0.0170
Spike Level
0.1331
MDL determined S/N
0.05345 7.88
Valid
Yes
LOQ (det. from 10 x std.dev. "noise") LOQ (det. from cal curve low std.)
0.17005 0.1331
Curve Coeff of Determination
0.9978
Date analyzed Method
130ct99 LC/MS/MS
Key 1 - Spike Level too high; Spike Level must be < lOx MDL 2 - Spike Level too low; Spike Level must be > MDL 3 - S/N too low; S/N must be > 5 4 - Coeff o f Det o f calibration curve unacceptable
PFO SA A 0.1484 0.1281 0.1484 0.1605 0.1661 0.1513 0.1385
0.1488 0.0128
0.1334
0 04011 11.66
Yes
0.12763 0.1334
0.9937
130ct99 LC/MS/MS
PFO SA 0.1167 0.1325 0.1521 0.1441 0.1490 0.1382 0.1413
0.1391 0.0119
0.1315
0.03725 11.74
Yes
0.11853 0.1315
0.9891
130ct99 LC/MS/MS
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APPENDIX B-DAELY ACCEPTANCE CRITERIA SUM M ARY
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PFOS et al IN RAT LIVER
STUDY NUMBER: N003604-D
DATA ENTERED: MANUALLY
SOFTWARE:
EXCEL 97
REGRESSION PARAMETERS
Analysis Date October 1 3 ,1999
October 1 6 ,1999 October 1 3 ,1999
October 20 ,1 9 9 9
Analyte
PFOS M-556 PFOSAA PFOSA
PFOS M-556 PFOSAA PFOSA
PFOS M-556 PFOSAA PFOSA
PFOS PFOSA
X2Coeff
-0.0164 0.00646 0.00232
-155
-0.00389 8.88E-06 0.00360
-250
0.00393 0.0221 0.00370 -71.9
0.00615 -1 5 3
X Coeff
1.88 0.627 0.0970 1.50E+04
1.82 0.578 0.0931 1.73E+04
2.17 0.312 0.0853 1.23E+04
2.07 1 .68E + 04
Intercept
-0.0772 -0.0213 -0.00398
-872
-0.00920 -0.00807 -0.00321
-986
-0.0905 -0.00269 -0.000603
-722
-0.0381 -1 0 2 P + 0 3
Coeff of Determination
0.984 0.996 0.994 0.989
0.999 0.998 0.998 0.990
0.985 0.984 0.993 0.996
0.997 ft SQQ
Comments/ Deviations
One rep of Cal pt 1 excluded One rep of Cal pt 1 excluded One rep of cal pt 7 excluded One rep of cal pt 5 excluded
One rep of cal pt 7 excluded One rep of pts 1, 3, 5 excluded
One rep of pts 4, 7 excluded
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PFOS et al IN RAT LIVER
STUDY NUMBER: N003604-D
DATA ENTERED: MANUALLY
SOFTWARE:
EXCEL 97
QC Results Analysis Date
October 13, 1999
Analyte PFOS
M-556
PFOSAA
PFOSA
October 16,1999
PFOS M-556 PFOSAA PFOSA
October 18, 1999
PFOS M-556 PFOSAA PFOSA
October 2 0 ,199 9
PFOS PFOSA
QC Level, ng/m L
10 3.3 0.7 0.16 10 3.3 0.7 0.16 10 3.3 0.7 0.16 10 3.3 0.7 0.16
10 3.3 0.7 0.16 10 3.3 0.7 0.16 10 3.3 0.7 0.16 10 3.3 0.7 0.16
10 3.3 0.7 0.16 10 3.3 0.7 0.16 10 3.3 0.7 0.16 10 3.3 0.7 0.16
10 3.3 0.7 0.16 10 3.3 0.7 0.16
%RSD
6.6 3.8 7.9 3.1 4.7 11.7 3.0 11.5 6.5 5.1 8.7 14.5 16.9 9.2 5.8 4.6
5.5 4.5 8.3 9.7 3.4 2.7 8.0 17.7 4.3 2.1 7.4 17.7 11.6 6.1 8.0 8.6
8.7 11.7 7.0 15.1 14.7 17.0 21.2 28.8 14.7 11.4 15.1 21.3 16.7 11.5 12.6 6.4
2.4 2.0 3.7 5.3 2.3 4.0 2.3 3.4
%RE
-4.0 -4.6 -6.4 -12.2 -2.4 2.5 -6.6 -5.1 -1.7 -10.4 -13.0 8.2 -4.3 -2.1 1.3 3.9
14.8 15.5 8.8 -2.7 -2.8 5.7 -3.7 4.5 -0.8 -2.9 -7.0 15.8 -3.9 5.4 -4.4 13.7
-4.5 -1.7 -20.3 -6.1 -2.9 23.4 11.6 15.4 0.8 -1.8 -20.6 -18.5 0.0 13.7 0.0 16.0
-8.0 -12.0 -21.7 -16.0 -1.6
6.5 1.9 11.5
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APPENDIX C-SAMPLE INVENTORY LIST
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Study TOX-013, Argus 418-009. Sample Information for shipment to Battelle
Sample 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60 61 62 63 64 65
Sample Description F0-9922-orpl-M
FO-9930-grpl-M F0-9931-grpl-M F0-9932-grpl-M FO-9933-gipl-M F0-9961-grpll-M F0-9964-grpll-M F0-9965-grpll-M F0-9967-grpll-M F0-9970-grpll-M F0-9997-grplll-M F0-9999-grplll-M FO-10001-grplll-M F0-10002-grplll-M
F0-100O4-qrplll-M F0-10019-grplV-M F0-10024-grplV-M FO-10029-grplV-M F0-10033-grplV-M F0-10034-grplV-M F0-10042-grpV-M F0-10044-grpV-M FO-10045-grpV-M F0-10051-grpV-M F0-10054-grpV-M
FO-10097-flrpl-F F0-10105-grpl-F F0-10106-grpl-F F0-10107-grpl-F F0-10108-grpl-F F0-10136-grpll-F F0-10140-grpll-F FO-10142-grpll-F FO-10121-grpH-F FO-10126-prpH-F F0-10177-grpUI-F F0-10155-grplll-F F0-10156-grplll-F F0-10164-grplll-F
F0-10172-grplil-F F0-10187-grplV-F F0-10194-prplV-F FO-10203-arplV-F FO-10211-grplV-F F0-10214-grplV-F FO-10097-grpl-F F0-10105-grpl-F FO-10106-grpl-F
FO-10107-grpl-F FO-10108-grpi-F FO-10136-grpll-F FO-10140-prpll-F FO-10142-grpH-F F0-10121-grpll-F FO-10126-grpH-F FO-10177-grplH-F F0-10155-qrplll-F F0-10156-grplll-F FO-10164-grplH-F FO-10172-grplll-F F0-10187-grplV-F
F0-10194-grplV-F F0-10203-grplV-F FO-10211-grplV-F F0-10214-grplV-F
Sample Type Maternal Rat Liver Maternal Rat Liver Maternal Rat Liver Maternal Rat Liver Maternal Rat Liver Maternal Rat Liver Maternal Rat Liver Maternal Rat Uver Maternal Rat Liver Maternal Rat Liver Maternal Rat Liver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Liver Fetal Uver Fetal Liver Fetal Uver Fetal Uver Fetal Uver Fetal Uver Fetal Uver Fetal Uver Fetal Uver Fetal Uver Fetal Uver Fetal Uver Fetal Uver Fetal Liver Fetal Liver Fetal Uver Fetal Uver Fetal Uver Fetal Uver Fetal Liver Maternal Rat Uver Maternal Rat Liver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Liver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver Maternal Rat Uver
Maternal Rat Uver Maternal Rat Liver Maternal Rat Uver
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APPENDIX D-REPRESENTATIVE CHROMATOGRAMS
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
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APPENDIX E-PROTOCOL, AMENDMENTS, AND DEVIATIONS
3MEnvironmental Laboratory
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fir r c . ' TOA - l)/~$
3M Environmental Laboratory
P r o t o c o l - A n a l y t ic a l S t u d y
2(N-Ethylperfluorooctanesulfonamido)-ethanol in Two Generation Rat Reproduction
In-vivo study reference number: Argus 418-009 Study number: FACT 060998.1 Test substance: 2(N-Ethylperfluorooctanesulfonamido)-ethanol (N-EtFOSE-OH)
Name and address of Sponsor:
Marvin Case 3M Toxicology Services 3M Center Building 220-2E-02 St. Paul, MN 55144
Name and address of testing facility: 3M Environmental Technology and Services 935 Bush Avenue, Building 2-3E-09 St. Paul, MN 55106
Experimental start date: Expected termination date: December 31,1998 Method numbers and revisions:
FACT-M-1.0, Extraction of Potassium Perfluorooctanesulfonate or Other Anionic Surfactants from Liver for Analysis Using HPLC-Electrospray/Mass Spectrometry
FACT-M-2.0, Analysis of Fluorochemicals in Liver Extracts Using HPLC-
Electrospray/Mass Spectrometry
' FACT-M-3.0, Extraction of Potassium Perfluorooctanesulfonate or Other Anionic Surfactants from Serum for Analysis Using HPLC-Electrospray/Mass Spectrometry
FACT-M-4.0, Analysis of Fluorochemicals in Serum Extracts Using HPLCElectrospray/Mass Spectrometry
Author: Lisa Clemen
Kris Hansen Study Director
Date Marvin Case
Date
Sponsor Representative
3MEnvironmental Laboratory
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Analytical Study: FACT-TOX-013 L R N -U 2095
_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
1.0 Purpose ____________________________________________________________ The analytical portion of this dosing study is designed evaluate the levels of perfluorooctane sulfonate (PFOS), or another metabolite of 2(N-ethylperfluorooctanesulfonamido)-ethanol (NEtFOSE-OH) designated by the study director, in the liver of the parent and subsequent generations of the test system, or in the serum as necessary.
The in life portion of this study was conducted at Argus Research Laboratories.
2.0 Regulatory Compliance________________________________________________ This study is conducted in compliance with the Food and Drug Administration Good Laboratory Practices regulation as stated in 21 CFR 58. Any exceptions will be noted in the final report.
3.0 Test Materials_________________________________________________________ 3.1 Test, control, and reference substances and matrices
3.1.1 Analytical reference substance: Potassium perfluorooctanesulfonate (PFOS), lot #217
3.1.2 Analytical reference substance matrix: Rat liver and serum 3.1.3 Analytical control substance: None 3.1.4 Analytical control substance matrix: Rat liver and serum 3.2 Source of materials 3.2.1 Analytical reference substance: 3M Specialty Chemical Division; traceability
information will be included in the final report 3.2.2 Analytical reference substance matrix: Argus Research Laboratories;
traceability information will be included in the final report 3.2.3 Analytical control matrix:
3.2.3.1 Rat liver - Argus Research Laboratories; traceability information will be included in the final report; or Rabbit liver - Covance Laboratories; traceability information will be included in the final report
3.23.2 Rat serum - Sigma Chemical Company; traceability information will be included in the final report
3 3 Number of test and control samples. Liver samples for testing were received from 40 test animals and 10 control animals. Serum samples will be tested at the discretion of the Study Director.
3.4 Identification of test and control samples: The samples are identified using the Argus Research Laboratories identifiers, which consist of a letter followed by the Argus project number, the animal number, the group designation, and the draw date.
2
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
3.5 Purity and strength of materials: Characterization of the purity and identity of the reference material is the responsibility of the Sponsor.
3.6 Stability of test material: Characterization of the stability of the test material is the responsibility of the Sponsor.
3.7 Storage conditions for test materials: Test materials are stored at room temperature. Samples are stored at -20 10 C.
3.8 Disposition of test and/or control substances: Biological tissues and fluids are retained per GLP regulation.
3.9 Safety precautions: Refer to the material safety data sheets of chemicals used. Wear appropriate laboratory attire, and follow adequate precautions for handling biological materials and preparing samples for analysis.
4.0 Experimental - Overview___________________________________________________
Tissues from animals dosed as described in Argus Research Laboratories Protocol #418-009 are received for analysis of fluorine compounds. At the discretion of the Study Director, a series of analytical tests will be performed on select tissues.
Initially, all liver samples will be analyzed for PFOS by electrospray/mass spectrometry (ES/MS). On the basis of findings from these analyses, additional sample matrices may be evaluated or other metabolites may be targeted. If additional analysis is performed, a protocol amendment will be written.
5.0 Experimental - Analytical Methods__________________________________________
5.1 FACT-M-1.0, Extraction of Potassium Perfluorooctanesulfonate or Other Anionic Surfactants from Liver for Analysis Using HPLC-Electrospray/Mass Spectrometry
5.2 FACT-M-2.0, Analysis of Fluorochemicals in liver Extracts Using HPLCElectrospray/Mass Spectrometry
5.3 FACT-M-3.0, Extraction of Potassium Perfluorooctanesulfonate or Other Anionic Surfactants from Serum for Analysis Using HPLC-Electrospray/Mass Spectrometry
5.4 FACT-M-4.0, Analysis of Fluorochemicals in Serum Extracts Using HPLCElectrospray/Mass Spectrometry
6.0 Data Analysis____________________________ ,_____________________________
6.1 Data transformations and analysis: Data will be reported as the concentration (weight/weight) of fluoride per tissue or sample, or of PFOS per unit of tissue or fluid.
6.2 Statistical analysis: Statistics used may include regression analysis of the serum . concentrations over time, and standard deviations calculated for the concentrations within
each dose group. If necessary, simple statistical tests, such as Student's t test, may be applied to evaluate statistical difference.
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_ B attelle Study Num ber: N 0 0 3 6 0 4 -D 3M Environm ental Laboratory Study Num ber: F A C T 060998.1
7 .0 Maintenance of Raw Data and Records
7 .1 T h e fo llo w in g raw data and records w ill b e retained in the study fold er in the arch ives according to A M D T -S -8: 7.1.1 A pproved protocol and am endm ents 7 .1 .2 Study correspondence 7 .1 .3 Shipping records 7 .1 .4 R aw data 7 .1 .5 E lectronic copies o f data
7 .2 Supporting records to b e retained separately from the study fold er in the arch ives according to A M D T -S -8 w ill inclu de at least the follow in g: 7 .2 .1 T raining records 7 .2 .2 C alibration records 7 .2 .3 Instrum ent m aintenance logs 7 .2 .4 Standard O perating P rocedures, E quipm ent P rocedures, and M eth od s 7 .2 .5 A ppropriate sp ecim en s.
8 .0 References
_
8.1 3 M E n v ir o n m e n ta l L a b o r a to r y Q u a lity S y s t e m C h a p te r s 1 , 5 a n d 6
8.2 O th e r a p p lic a b le 3 M E n v ir o n m e n ta l L a b o r a to r y Q u a lity S y s t e m S ta n d a r d O p e r a tin g
Procedures
9 .0 Attachments 9 .1 F A C T -M -1 .0 , Extraction of Potassium Perfluorooctanesulfonate o r O th er A n io n ic
Surfactants from L iver for A n alysis U sin g H PL C -E lectrospray/M ass Spectrom etry
9 .2 F A C T -M -2 .0 , A n alysis o f F lu orochem icals in L iver E xtracts U sin g H PL C E lectrospray/M ass Spectrom etry
9 .3 F A C T -M -3 .0 , E xtraction o f P otassiu m P erfluorooctanesulfonate or O ther A n io n ic Surfactants from Serum for A n alysis U sin g H PL C -E lectrospray/M ass Spectrom etry
9 .4 F A C T -M -4 .0 , A nalysis o f R u oroch em icals in Serum E xtracts U sin g H PL C E lectrospray/M ass Spectrom etry
| !
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_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FORANALYSIS OFPOTASSIUM PERFLUOROOCTANESULFONATE (PFOS) INRATLIVERBYLC/MS/MS
Version 1.0
. ' Study N o.!_________________________
A nalyst/Sate:___________________________
R evisions to the method
D ru e o l'R e v is io n
R e v ised bv
A pprov cd bv
IBI^B^^BIB^BHBB
BIB^Bk^^^Bh^^^Bb b b b ^ b b b b h b b b b B B B ^ B B B i BBBBBH^HB b b b b b b b BflHBHHB^BHBHBB iB B B B B B b b b b b b b b b
W ritten by:
Patrick L. South
_________Date: /ip s 3 iv > 9 9 *
Approved by:
C< ____________ Date:
JJcdpt/lCc . Andre., P h D . ger, B ionalydcal Chem istry
Gm j j Jt <9
f. f W
>
3MEnvironmental Laboratory
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A nalytical Study: FACT-TO X-013 L R N -U 2095
_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FORANALYSIS OFPOTASSIUM PERFLUOROOCTANESULFONATE (PFOS) IN RATLIVERBY LC/MS/MS
V ersion L0
Study No.:
Analyst/D ate: _
L Summary
The extraction and analysis o f potassium perfluorooctanesulfonate and related fluorochemicals in rat liver is performed. Calibration standards are prepared by spiking blank liver homogenate w ith solvent standards from two independently-prepared stocks. The calibration standards are fortified
w ith surrogate standard, buffered, and extracted with ethyl acetate. The organic phases are evaporated to dryness and reconstituted in methanol for analysis by LC/MS/MS.
EL P u r po se
To extract and analyze potassium perfluorooctanesulfonate and related fluorochemical compounds found in Sprague-Dawley rat liver.
in . Samples
See Chain o f Custody records if applicable.
IV . G e n e r a l I n st r u c t io n s
Calibrate all required balances according to the SOP on balance usage.
Make equivalent dilutions when the volume needed varies from the volume stated in the
method.
Label all standard and reagent solutions as specified in the appropriate SOP. I f you intend tn
reuse a solution for future tasks, be sure tire label includes the preparation date and study
number for which the solution was initially prepared.
Sign on the final page a fth is m ethod to signify that you have followed the method as written,
all materials and reagents are current, and all equipment has been properly calibrated. Ifyou
deviate from the method, document the change, and obtain the approval o f the unit manager,
study director, or task leader as soon as possible.
Initial and date all data entries on the page on which they were made. If only one person
enters all data on a single day, the documentation may be made in a single location on that page.. I f multiple staff make entries, the additional entries must be initialed and dated by the
person malting the entry.
Line-outs or NA denotes "Not Applicable".
The method is w ritten in general chronological order, but the sequence o f steps may be altered
if the analyst deems it appropriate, unless the order for certain activities is specified.
Stocks w ill be used fo r the duration o f the study unless consumed or unless stability is
considered suspect
No correction will be made for purity o r salt content o f any test article but PFOSAA.
Use glass volumetric, Eppendorf repeater, or positive-displacement pipets for dispensing
methanolic solutions.
Contact with Teflon by the test article should be minimized.
.
V. Materials
See Table 1 for all required chemicals, reagents, and solvents. Use Table 1 fo r documentation. Check all labels carefhlly to ensure that all materials are not expired and that they are the proper purity o r grade.
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
. METHOD FORANALYSIS OFPOTASSIUM PERFLUOROOCTANESULFONATE (PFOS) INRATLIVERBYLC/MS/MS
. Version 1.0
Study N<w_________________________ Analyjt/D ate:___________________________
M aterials
U se
Potassium Perfluorooctanesulfbnate (PFOS) lH ,nU K t2H Perfluorooctane Sulphonic A dd
M-536
. MS70
PFOSAA
PFOSA
PFOSEA
R at Liver
A nalytical Standard
Surrogate Standard
A nalytical Standard A nalytical Standard A nalytical Standard A nalytical Standard A nalytical Standard M atrix
Ammonium Acetate, N ILCJLO ,
Sodium Hydroxide, NaOH
Tetrabutylammonium Hydrogensulfate (TBA),
iCHsfCHALNiHSCM Sodium Carbonate, NiteCO, Sodium Bicarbonate, NaHCOi Ethyl Acetate
M obile Phase Reagent Prep E xtra Prep
E x tra Prep E x tra Prep E xtra Prep
T a b let. M aterials
S u p p lier
G rade o r
P u ri tv
3M
ICN
3M 3M 3M 3M 3M H arlan
SpragueDawley
S to rag e Tem o
Room Temp
Room T em p
Room Temp Room Ternn Room Temp Room Temp Room Temp --20C
RT
RT
RT
Lot o r ID
RT RT RT
M ethanol M illi-Q Water pH 7 Buffer pH 10 Buffer
M obile Phase, Stocks, WS
Reagent Prep, M obile Phase
pH m eter calibration pH m eter calibration
M illipore
RTASTM Typel RT
RT RT
I
R.T means Room Temperature.
V L E q u ipm en t
See Table 2 for all required major pieces o f equipm ent Use the table to document the actual piece (e.g. make, model) o f equipm ent Check calibration ofall equipment requiring calibration (e.g. balances) to ensure i t is current
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Analytical Study: FACT-TOX-013 L R N -U 2095
_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FORANALYSIS OFPOTASSIUM PERFLUOROOCTANESULFONATE (PFOS) INRATLIVERBYLC/MS/MS
- - Version 1.0
Study N o.:_________________________
Analyst/D ale:___________________________
E q u ip m en t
Analytical Balance
W eight Set
U se
W eigh Standards or R eagents
Calibrate Balance
Table X Equipment
M an u factu rer
M odel.
X Lm -SN
1
Pipettor
Pipet Samples
Pipettor
Pipet Samples
Pipettor Pipettor
Pipet EtOAc extraction phase Pipet Reagents, WIS
Eppendorf - Repeater
Vortexer-
M ix Samples
Freezer (-20C)
R efrig erato r a -9 Q
Centrifuge
Store QCs, Blank L iv e r
Store Buffer, Stocks
Phase separation
T est Tubes Centrifuge Tubes
T est Tubes Transport tubes M agnetic stirrer O rbital Shaker
E v a p o ra to r
Liver sample hom ogenization Extract Samples
Evaporate Extracts
Store QCs
Stir matrix Extract Samples
Evaporate E xtracts
Stockwell Scientific Blue Falcon
Blue Falcon
Elkay
Polypropylene, 15 mL
Polypropylene, 15 mL
Polypropylene, 12 x75 mm 5 mL
polypropylene
SW8599 2096 . 2002
127-T160-56P
Zymark
Turbovap L V
Syringe Filters
Filter Extract
H om oeenizer pH meter Electrode
Volumetric Flasks, Class A
Volumetric Pipets, G ass A
Transfer Pipets. Plastic
Grind liver Determine Buffer pH Determine Buffer pH
M ake Volumetric D ilutions
M ake Volumetric D ilutions
Transfer Extracts to Centrifuge Filters and LC Inserts
NA NA Samco
NA NA
NA NA
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A nalytical Study: FA CT-TO X-013 L R N -U 2095
_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
J
METHOD FOR ANALYSIS OF POTASSIUM PERFLUOROOCTANESULFONATE (PFOS) IN RAT LTVER BY LC/MS/MS
V enan 1.0
Study No.:
Analyst/Date: _
VEL PROCEDURE
A. Preparation of2 mMAmmoniumAcetate
W eigh 0.1500 j; 0.0020 g o f ammonium acetate and transfer to a 1000-mL volumetric flask. Dissolve the solid in w ater and dilute to volume with water. Solution may be used fo r one month stored a t room temperature.
Actual mass o f ammonium acetate:__________ Actual final volum e:_________ Date o f preparation:____________________ Study No: ____________
B. Preparation of~29% SodiumHydroxide Solution
W eigh 200 2 g of sodium hydroxide into a beaker. Add 500 mL o fMOli-Q w ater and m ix to dissolve. Cool and transfer to a polypropylene bottle for storage. Solution may be stored for 6 months a t room temperature.
Actual m a o f sodium hydroxide: _ _ _ _ _ _ Actual volume M illi-Q w a te r_________ Date o f preparation:____________________ Study N o :_______________
C. Preparation of--2.9%SodiumHydroxide Solution
'
Add 10 mL o f--29% Sodium Hydroxide Solution to a 100-mL volumetric flask and dilute to volume w ith M illi-Q water. Transfer to a polypropylene bottle for storage. Solution may be stored fo r 6 months at room temperature.
Actual volume o f-29% NaOH so lu tio n :__________
Actual final volume: _________
D ate o f preparation:
____
Study N o:_______________
'
D. Preparation ofTetrabutylammoniumHydrogensulfate (TBA) Solution, 0.5M, (pH 10)
pH M eter Calibration
pH buffer 7 pH buffer 10
pH reading:________ pH reading:________
Add 169* IgafT B A to-S O O m L afM illi-Q w aterinabeaker. Adjust the pH to 10.00 t 0.02 using -55-60 mL o f 29% Sodium Hydroxide Solution, dilute to 1000 mL wife . Milli-Q water, and mix. Adjust the pH to 10.00 * 0.02 using -2.9% NaOH and mix. Transfer to a polypropylene bottle for storage. Solution may be used for one month Stored at room temperature, but the pH m ust be checked n rio r to each use. Adjust to
pH 10.0 i 0.02 with 2.9% Sodium Hydroxide Solution as necessary.
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_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHODFORANALYSIS OFPOTASSIUM PERFLUOROOCTANESULFONATE (PFOS) INRATLIVERBYLC/MS/MS
' Version 1.0 Study No.: `
A n alyit/D ate:___________________________
Actual m ass o f T B A :__________ Actual final volum e:_________ . Actual final p H :__________ Date of preparation:____________________ Study N o :_______________ pH after techedring and/or readjusting:_________
E . P re p a ra tio n o f 0 .2 5 M C a rb o n a te B u ffe r
Weigh 2 6J 0.1 g o f sodium carbonate and 21.0 * 0.1 g o f sodium bicarbonate and transfer to the same 1000-mL volumetric flask. Dissolve the materials in M illi-Q water, dilute to volume w ith M illi-Q water, mix, and transfer to a polypropylene bottle for storage. Solution may be used fo r 1 month when stored refiigerated.
Actual mass o f sodium carbonate: __________ Actual mass of sodium bicarbonate:__________ Actual final volume: _________ Date o f preparation:____________________ Study N o:_______________
F . P re p a ra tio n o f M o b ile P h a se
Component A: M ix together 600 mL of 2 mM ammonium acetate and 400 mL of methanoL Solution may be used fo r 1 month when stored at room temperature.
Actual volume of 2 mM ammonium acetate:________ mL Actual volume o f methanol: ________mL Date ofpreparation:____________________
Study N o:_______________
Component B: M ix together SO mL of 2 mM ammonium acetate and 950 mL of methanoL Solution may be used for 1 month when stored at room temperature.
Actual volume o f 2 niM ammonium acetate:
Actual volume of methanol:
m l.
Date ofpreparation:____________________
Study N o :_______________
mL
G . P re p a ra tio n o f S to ck S u rro g a te S ta n d a rd a n d W o rk in g S u rro g a te S ta n d a rd (W SS)
1. Stock Surrogate Standard (250,000 ng/mL):
W eigh 25 t 2 mg o f 1H, 1H, 2H, 2H,-pcrfluorooctane sulphonic ad d and transfer to a 100-mL volumetric flask. Dissolve in methanoL dilute to volume with m ethanol, and mix. Store refiigerated, protected fiom UV light
Actual W eight:________________ Actual Dilution Volum e:___________________
Date ofPreparation:__________________ Study No: _________________
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FORANALYSIS OFPOTASSIUM PERFLUOROOCTANESULFONATE (PFOS) INRATLIVERBYLC/MS/MS
V ersion 1.0
Study N o.:____________ ;____________
A nalyst/D ate:___________________________
2. WSS (1000 ng/mL):
D ilute 100 /JL ctfstock, surrogate standard to 25 mL with m ethanol and m ix..
Actual Volume of Stock Internal Standard:___________ Actual D ilution V olum e:___________________ Date ofP rep aratio n :__________________
H. Preparation ofCalibration Solvent Stocks andWorking Standards
1. Solvent Stocks:
For each analyte weigh the specified amount of standard (independently weighed as A and B replicates) listed in Table 3 and transfer into separate volum etric flasks. Dissolve in methanol, dilute to volume w ith methanol, and m ix well. Store refrigerated, protected from UV light.
2. M ixed Solvent Stocks:
.
P ipetthe specified amount of each analytical standard Replicate A as listed in Table 3 and transfis' into a single volumetric flask. Dissolve in methanol, dilute
to volume w ith methanol, and mix well. Store refrigerated, protected from UV lig h t Repeat the process with Replicate B stocks. The mixed solvent stocks are used to prepare Ike working standards.
Date ofpreparation:____________________ Study N o :_______________
>
3. W orking Standards (WS):
D ilute the m ixed stocks and working standards with m ethanol as specified in Table 3 and m ix well.
4 Date of preparation:_______________________________
S tan d a rd
Stodc 1A Stodc IB Stock 2A Stodc 2B Stock 3A Stock 3B Stock 4A Stock 4B Stodc SA Stodc SB Stodc 6A
S o u rce
PFOS PFOS M-SS6 M -556 M 570 M 570 FFOSAA PFOSAA PFOSA PFOSA PFOSEA
Table 3. Calibration Solvent Stocks and W orking Standards
T arget
A ctu al A m ount
T arget
A ctu al
A m ount
A n aly tical S td .
F in al V ul
S tu d i, o r W S
im L )
SO X 1 mg
10
25 0.S mg
- me-
10
SO X 1 mg H H B f f i S B
10
25 X0.5 mg
10
50 X 1 mg
mg* I
10
25 X0.5 mg
MB* 1 10
93 X 1 mg L
> ME*
10
46 X0.5 mg
mg* 10
50 X 1 mg
10
25 X 0.5 mg "> ' > m g*
10
50 X 1 mg ______________ M L
10
F in a l V ol.
(mL)
' - ,, -P
s. '**
Kn::: ' n.... -
*
4
N om inal
C one
(n/m L >
5,000,000 2^00,000 5,000,000 2J00.000 5,000,000 2,500,000 5.000,000 2.500,000 5,000.000 2,500,000 5.000,000
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASSIUM
PERFLUOROOCTANESULFONATE (PFOS) IN RAT LIVER BY LC/MS/MS
V ersion 1.0
-
Study N o.:__________
A nalyst/D ate:___________________________
Stock 6B FFOSEA 25 0.5 mg
m tm
10
rr'wmi ....w....irvr j
2.500.000
Mixed Stocks 1 thru
Stock A
6 Rep A
5 mL each**
-----------"L each
j. > i*
!>k
50
9o*J*
d8L> ~}
}.
500,000
Mixed Stocks I thru
Stock B
6RepB
5 mL each** 7
50 250,000
- I vt* <* *
WS 1
Mixed Stock A
1 mL**
.
mL
stm r Xi
25
bgs.sa::.t;.w.s::::.::::::?-::.::*:TM:-::: :;>:x:j.
20,000
W S2
M ixed Stock B
1 mL**
m L 25
10,000
^........: . ' ' ' '
W S3
WS 1
2 mL**
mTt- 10 * a y >.
4000
WS 4
W S2
2 mL**
m L 10
" 2000
WS 5
WS 3
2.5 mL**
mL 1
10
1000
W S6
W S4
2.5 mL**
m L 10
500
WS 7
W S5
2 mL**
10
::;ti**r;
200
* Weigh all analytical standards to a t least the nearest 0.01 mg. ** Use volum etric or positive-displacement pipet(s).
L Preparation of Calibration Standards and Blanks
l . Liver homogenate
Prepare blank liver homogenate in bulk by weighing approximately 40 g o f blank liver into a 500 mL Nalgene bottle containing 200 mL of Milli-Q water. Grind to a homogeneous suspension. Aliquot into approx 30 mL portions for frozen (approx -2 0 Q storage.
Actual M ass o fLiven____________
Actual volume o f w ater___________ Date o fp re p :___________________
Study:_____________________
Determine density o f calibradon/QC matrix:
MIX HOMOGENATE THOROUGHLY and determine the mass in milligrams o f 10 replicate weighings o f 1 mL portions of the THOROUGHLY MIXED homogenate. M K HOMOGENATE IMMEDIATELY PRIOR TO EACH ALIQUOT REMOVAL.
R eplicate# Mass (inai
a
2. Liver Calibration Standards
Prepare each Ever calibration standard by adding 0.45 mL o f undiluted liver homogenate (STIR HOMOGENATE WHILE ALIQUOTING) into a 15 mL extraction tube and adding 50 pL o f WS or MeOH. Prepare triplicate cal standards and 6 blanks. See Table 5 for volumes. The diluted liver density is assumed to be approximately 150 mgfatL. M ix well.
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Analytical Study: FACT-TOX-013 L R N -U 2095
_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASSIUM PERFLUOROOCTANESULFONATE (PFOS) IN RAT LIVER BY LCM S/M S
V ernon 1.0
Study No.: A nalyst/D ate: _
C al S tii/B lan k
1
2 3 4 5 6 7 Blank
S ource
W Sl WS 2 WS 3 W S4 WS 5 WS 6 WS 7 MeOH
T a ra e t Voi
G aL)
50 50 50 50 50 50 50 50
T ab les. C alibration Standard and B lanks
A ctual V oi
T arget
A ctual
N om inal
G aL )
F in al Voi
F inal V oi
C one
' -
.
*> *i
1...........' ' '
:
(m L )
0.5 0.5 0.5 0.5 0.5 0.5
(m L )
8 8 6S i8S & :tynxK*S::K::>fc::? : * *'- 1 v ' 1;, *J '/
i> >> ,
(n s/m U
2000 1000 400 200 100
50
i:!i: ! 0.5
20
1 0.5
iililllli
0
N o m in al
C one
(u a /a )
13 6.6 2.6
1J
0.66 0.33 0.13
0
Date o f preparation o f cal stds/blank:____________________________
J. Preparation of Quality Control Liver Samples (QCs)
1. Quality Control Working Standards
D ilute the following source volumes m ethanol in volumetric flask.! and mix w ell. Prepare fresh when used. Actual volumes are in parentheses.
S o in ID OC WS 1 QCW S2 QC WS 3 QCW S4
Z
S ource
M ixed Stock A M ixed Stock B
QC WS 1 QCW S2
T abled. QC WS P reparation
V oi S o u rc e . mL
F in al V oi. mL
I 3 .(........... i i f i l l i to ffc ' ~ * r `
l i > 50 f
- 7.5 (
100 f
1 1
sg& m sm -> . 1 50(
)
Preparation o f Quality Control Liver Samples
C one, n a/m L
15.000 5000 1125 250
Prepare each QC in bulk by filling the volumetric flask approximately h alffull w ith u n diluted liv e r homogenate (S T IR HO M O G EN ATE W H ILE
ALIQUOTING), adding the appropriate QC WS, mixing, and diluting to volume w ith undiluted Uver homogenate (SU R HOMOGENATE WHILE
ALIQUOTING). MIX THOROUGHLY and dispense Z5-mL aliquots into polypropylene tubes and store at approximately -2 0 C
Table 7. Q C P reparation
QC
S ource
Voi S ource. m L
F in al V oi. m L
C one. na/m L
C o n e , lui/ n
1 OCWS 1 25 C
i
1500 1 10
2 QC WS 2
3 QCW S 3 Z5C . . 2* t
i
500 112.5
3.3 0.7
4
OCWS 4
Z5
)
25 0.16
Date ofQC prep:___________________ Study._____________________
K. Preparation of MS Check Standard for System Suitability
Pipet 250 mL of WS 2 a t--10,000 ng(mL and Z 5 mL of WSS at -1000 ng/mL in methanol into the same 50-mL volumetric flask. Dilute to volume with MeOH and mix.
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASSIUM PERFLUOROOCTANESULFONATE (PFOS) IN RAT LIVER BY LC/MS/MS
V ersion L0 . Study N o.:____________________________
A nalyst/D ate:______________________________
L. Preparation of homogenizer recovery liver samples
.
M.
To determine the recovery from the homogenization process, nnhom ogeaized blank liver w ill be fortified in duplicate a t 3 concentration levels and homogenized as follows. This needs to be done every day that homogenization of study samples is performed.
1. Place approximately 0.3 g o f unbomogenized blank liver into each o f 6 ,1 5 mL
polypropylene centrifuge tubes. Record weights o f liver.
X Add 100 pL o f WS 1 ,3 , and 4 (one WS per duplicate tubes) to prepare
- fortifications a t approximately 4, 0.8, and 0.4 pg/g.
3. M ultiply the mass ofliver in g by 2.5 and add this manymL ofw ater.
4. Homogenize each liver sample, and rinse homogenizer probe with another
volume o f w ater used in step 3, adding rinse to homogenized sample.
.
5. Clean homogenizer w ith MeOH between samples.
6. Cap and vortex homogenate for use in extraction.
Preparation of Dilation Check Sample
1. Place 2.95 mL o f undiluted liver homogenate (STIR HOMOGENATE WHILE
ALIQUOTING) into a 15 mL extraction tube and add 50 pL o f M ixed Stock A.
X D ilute 50 pL of step 1 solution (VORTEX SOLUTION WHILE
ALIQUOTING) with 0.45 mL of undiluted liver homogenate (STIR.
HOMOGENATE WHOLE ALIQUOTING) in 3,1 5 mL extraction tubes.
3. This sample should be prepared for extraction only on days when study samples
w ill be diluted and extracted.
.-
N. Homogenization of study samples
1. Place approximately 0.5 g of unhomogenized study sample liver into a 15 mL polypropylene tube. Record weights ofliver.
X M ultiply the mass o f liver in g by X5 and add this manymL of water. 3. Homogenize each liver sample, and rinse homogenizer probe with another
volume o f water used in step X adding rinse to homogenized sample. 4. C lean hom ogenizerw ith M eO H between samples. 5. Cap and vortex homogenate for use in extraction.
O. Analysis Standards, Blanks, QCs, and Samples
1. M IX LIVER HOMOGENATES THOROUGHLY BEFORE ALIQUOTING and p ip 500 /jL of each QC (4 replicates per level), and other samples being extracted into 15-mL polypropylene extraction tubes. The cal stds an d blanks
are already aliquoted. X To the B lanks-IS (3 reps), add 100 jL o f MeOH and vortex. 3. To the Blanks + IS (3 reps) and to the remaining samples, add 100 iL WSS and
vortex. 4. Add 0.5 mL o f 0.5 M TBA (pH 10) to all tubes and vortex briefly. 5. Add 1 mL o f 0X5 M carbonate buffer and vortex briefly. 6. Add 2 J mL of ethyl acetate. Place the tubes sideways on the orbital shaker at a ' setting o f300 for -2 0 minutes. 7. Centrifuge tubes at a setting o f3500 rpm for -2 0 minutes to separate layers. 8. Transfer 2 mL of the top organic layer to a dean polypropylene tube.
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASSIUM PERFLUOROOCTANESULFONATE (PFOS) IN RAT LIVER BY LC/MS/MS
Version 1.0 Study N o.:___________________________
Analyjt/Date: ______________________________
9. Evaporate to dryness tm der nitrogen at a setting of 30*C fo r-6 0 minutes. 10. Reconstitute the residues in 500 mL o f methanol with vortexing. 11. Syringe-filter extracts into antosnmplcr vials for analysis. Store vials refrigerated
(up to 1 month) if LC/MS/MS will not be performed the same day. Since 3-day room temperature extract stability was demonstrated during validation, the - extracts o f the cal stds, blanks, and QCs may be reused for up to 3 days after ' their initial preparation if held at room temperature (recap the vials if reusing).
Date of cal std/blank extract prep:________________________ Date of QC extract prep:_______________________________
P. LC/MS/MS Analysis
.
8 .
1. Use the system conditions specified in Table y f. The conditions which are
designated may be modified by the analyst to produce acceptable peak shape.
L C /M S /M S S ystem
Table 8 - LC/M S/M S Conditions
A u to sam p fcr H PLC Pum ps M ass S pectrom eter
M ak e:____ Make: ____ M ake:
M odel: M odel: M odel:
ID: ID:
ID:
A n a ly t ic a l c o lu m n Keystone Betasil C18, 5m. 2 x 50 mm. Part No. 055-701-2,
S/N: :L oc
M o b ile P h ase C o m p o n en ts
Component A Ammonium acetatem ethanol, 60:40, v x Comoonent B: Ammonium acetate:methanol. 5:95. v x
'
G ra d ie n t p rofile
Tim e, min 0
% B Flow. mL/min 0 0.3
1 0 0.3
4.5 100 0.3
6 100 0.3
6.1 100 0.6 8.5 100 0.6
9 0 0.3 '
11 0 0.3
In je ctio n volum e d im split
10 uL (
______________________________:_______________________
LC column flow split to *30 ML/min ( uL/m inl into the MS at run start
C o lu m n T em p
Ambient
lU 'L C P ressu re
1000 psi at gradient start (
osi)
'
M S Source
Electrosnrav. Negative Ion
U esolvatinn as N eb u lizer as
Nitrogen at 575 L/hr ( Nitrogen at 80 L/hr (
L/hr) L/hr)
S o u r c e B in d s T e m p *140C(
o
1)cmiI\ a t i o n T e m p *250C f
a
C o n e voltage
*70 V (___ *20 v r
V) P F O S , - V) PFOSA, PFOSAA PFOSEA, M-556, M570
C ollision energy
*40 eV (___ eV) PFOS, I t PFOSA PFOSAA, M-556, M570
*30 eV (
eV) PFOSEA
C ollisio n as
1 Argon at *2.5 x HT* mb gas cell (
mb)
M u ltip lie r R estitution
I 650 V ( ___ Y)___ ____ ._________________________________ ___________ 1
1 *12.0 for MSI (
): *10.0 for M S2
)
JV/ouAi ACft " S f" }
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_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASSIUM PERFLUOROOCTANESULFONATE (PFOS) IN RAT LIVER BY LC/MS/MS
V enion 1.0
Study No.: Analyst/Date: _
Ions m onitored
Total run time A pproxim ate retention times:
427>81 MRM transition for Surrogate Standard (SS)
1 499>99 MRM transition for PFOS
1 556>78 MRM transition for M-556
570169 MRM transition for M570
1 584>169 MRM transition for PFOSAA
1 498>78 MRM transition for PFOSA
526>169 MRM transition for PFOSEA
*11 minutes (
min)
SS: 4 min (
min)
PFOS: 4.3 min ( ___min)
M-556: 4 a min ( ____min)
M 570:4.6 min ( __ min)
PFOSAA: 4.7 m in e
min)
PFOSA: 5.1 min (______min)
PFOSEA: 5.7 min 1
min)
* Parameters that may be changed by the analyst Actual values in ( ).
2. The above conditions should be suitable for the Micromass Quattro LC (S/N
9053). Modifications may be necessary if another Micromass Quattro Series
spectrometer is used. Split the flow post-column via a Keystone BIO-tee or
sim ilar device.
3. Calibrate the mass spectrometer using a suitable reference compound, o r verity
that the calibration is suitable by visual inspection (on the tune page) that a
suitable mobile phase ion is still accurately determined. Resolution may need to
be higher than that used for analyzing samples.
-'
4. To check the proper performance o f the instrument, inject the instrument check
standard. The results should be comparable to a recent injection if available.
5. Use an automated chromatography integration software system to collect the
output from the analysis.
6. Loading O rder See the loading report from the automated chromatography
integration software system.
7. Make single injections of each cal standard, QC, study sample, or blank. Make
at least 4 injections of the instrument check standard.
8. Run set sizes should typ ica lly no t exceed 80 injections due to instrum ent
response roll-off considerations. Longer runs may be performed, but they pose a
risk o f yielding unacceptable curve results.
VUL CALCULATIONS
1. Spreadsheet Software: ___________________ V ersion________ 2. MS Analysis Software:_____________________ V ersion_______ 3. Calculate the average density of the liver homogenate (10 reps) in mg/mL. 4. Using the average density of the homogenate, calculate its liver density
(mg of liver per mL of diluted homogenate):
Undiluted liver density (mg/mL) - (g o f liver x average density o f homogenate)/(g o f liver + g of water)
where g of liver and g o f water are masses used to prepare bulk homogenate; density of water is assumed to b e l g/mL.
Diluted liver density (mg/mL) " Undiluted density + D iln Factor
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASSIUM
PERFLUOROOCTANESULFONATE (PFOS) IN RAT LIVER BY LC/MS/MS
' V ersion 1.0 Study N o.:___________________________
A n alyit/D ate:_____________________________
W here diin factor " 2/1.8 m 1.1111 to accountfor 10% rtfln ofliver homogenate in cal std and QC matrices.
5. Calculate the actual concentration (ng/mL) ofPFOS and other flnorochemicals in the suspensions of calibration standards and QCs by using the mass of analytes and dilution factors only (no liver density collection). Use purity correction for FFOSAA only.
6 . fa lm tn ti the actual concentration o f PFOS and other fln n m rhe m ira lt In liw r fnr rim calibration standards and QCs as follows:
Conc(|ig/g) " Cone (ng/mL) * Diluted Liver density (mg/mL) x 1000 mg/g x 10 pg/ng
7 . Assure that the integrations o f the peak areas of the test article and surrogate standard are
correct Flag manual integrations where performed. Calculate the exact concentration of each .- liver standard.
8. Calculate the regression equation relating the peak response ratio (test article/SS) o f each calibration standard (y-axis) to test article concentration in liver (x-axis) for PFOS, M -556, M570, and FFOSAA. Calculate the regression equation relating the peak area of r h calibration standard to test article concentration in liver for PFOSA and PFOSEA. PFOS, M 356, M570, and FFOSAA are quantitated by using the surrogate standard as an internal standard: PFOSA and PFOSEA are quantitated without reference to the surrogate fexternal standard calibration curve). Use a quadratic regression weighted 1 /x , origin excluded, fo r all analytes.
9. Calculate a determined concentration for each injection of calibration standard, QC, and ' sample using the regression parameters and the peak response ratios or areas.
10. rnlm lati the relative error, average relative error, standard deviation, and relative standard deviation for all QCs. Calculate foe relative error for each injection of calibration standard.
11. rn lm la tK the average recovery fo r die hom ngenrar nera veiy fnTtifiratifin e
12. Calculate the relative standard deviation for foe PFOS to SS peak area ratio o f the replicate
*
o f the
standard.
IX. a c c e p t a n c e C r it e r ia
A. MS Check Standard (System Suitability)
At least 3 injections of foe MS Check Standard must provide a %RSD of 10% or less for the PFOS to SS peak area ratio.
B. Calibration Standards
The percent relative errors for the concentration-level averages of the calibration standards should m eet the following limits:
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Analytical Study: FACT-TOX-013 L R N -U 2095
_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASSIUM PERFLUOROOCTANESULFONATE (PFOS) IN RAT LIVER BY LC/MS/MS
V ersion L0 Study No.:
Analyst/Date: _
Table 9. Calibration Standard Acceptance lim its
ANALYTE
% Error
PFOS
20 05% at LOO)
M -556
20 05% at LOO)
M570
20 05% at LOO)
PFOSAA
20 05% at LOO)
PFOSA
20 05% at LOO)
PFOSEA
25f30% atL 001
Up to 5 calibration standard injections may be excluded from the curve, provided that one injection remains per level. Removal o f an entire level may be done if approval is obtained. If an entire level is-.removed, the samples bracketed by the remaining calibration range w ill be - considered acceptable. The calibration curve should have a coefficient of determination o f 0.97 or better.
C. QCj
The concentration-level average percent relative errors and percent relative standard deviations ofthe QCs should meet the following limits:
Table 10. QC Acceptance limits
ANALYTE
%
PFOS M -556 M570
20 20 20
PFOSAA
20
PFOSA PFOSEA
20 25
Removal of individual values from the QC calculations may be done if accompanied by a reasonable explanation (e.g_, instrument m alfunction or Dixon's Q test results).
I f d ie average determ ined concentration fo r any Q C level exceeds the acceptance lim it, the tad : leader or study director should be notified. The nin may be repeated or a portion of the run may be considered acceptable. F or example, if the low QC fails the stated requirements, samples may be accepted that have concentrations bracketed by the highest calibration standard and a mid-level QC concentration.
D. Homogenizer Recovery and Dilution Check Samples
The average recovery across the 3 levels o f homogenizer recovery samples as well as that o f the dilution check samples should fill w ithin the range o f70-130% inclusive. Removal of individual outliers fiom the calculations may be done if accompanied by a reasonable explanation.
E. Sensitivity (LOQs)
' The validated lim its o f quantitation are nominally 0.13 pg/g each for PFOS, M -556, M570, and PFOSAA.
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_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASSIUM PERFLUOROOCTANESULFONATE (PFOS) IN RAT LIVER BY LC/MS/MS
VenioB 1.0 Study N o.:___________________________
. ' Anaiyrt/Date: _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _
For PFOSA and PFOSEA, the validated LOQs are nominally 0.33 pg/g each. Due to the nature of die preparation of die calibration standards, lower concentrations afPFO SA and PFOSEA w ill be carried through the extraction. These lower concentration values w ill be evaluated with each run set, and may be included in the regressions if they m eet acceptance criteria. If they are included, study samples which are quantitated to have concentrations below the validated level (nominally 0.33 pg/g) w ill be appropriately flagged.
F. Specificity
The method suffers from endogeneous m atrix interferences a t levels sometimes exceeding 20% o fLOQ. The intercept o f die calibration curve appears to offer some correction fo r any - effect on quantitations. Acceptai performance (error) o f the lowest used standard, therefore, w ill be considered sufficient evidence that bracketed study samples are quantified property.
G. General
The above acceptance criteria indicate that this method is capable o f producing occasional errors outside the normal acceptance criteria of a validated method (15% normally). Where indicated, replicate analyses lessen die impact o f these occasional outliers.
X . RESULTS
See attached hard copy o f spreadsheet or see file on network drive.
XL C o m m e n t s
3MEnvironmental Laboratory
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T? t n
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A nalytical Study: FA CT-TO X-013 L R N -U 2095
_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FORANALYSIS OFPOTASSIUM PERFLUOROOCTANESULFONATE (PFOS) INRATLIVER BYLC/MS/MS
Verjion U> Study No.: -
Analyst/D ate:____
X3L C o n c l u sio n s
XHL S ig n a t u r e s
Analysts
_____________________________________________ . - - _____________________________________ _____________________________________________ _____________________________________________
TechnicalReview
QCReview
D ate: ' Date:
D ate: D ate:
Date: D ate:
D ate: Date:
3MEnvironmental Laboratory
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A nalytical Study: FA CT-TO X-013 L R N -U 2095
_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
Study Title
C om b in ed Oral (G avage) F ertility D ev elo p m en t and Perinatal/Postnatal R eproduction T oxicity Study o f N -E tF O SE in R ats
PROTOCOL AMENDMENT NO. 1
Amendment Date:
July 2 8 ,1 9 9 9
Performing Laboratory
3M E nvironm ental T ech n ology & Safety Services 3M E nvironm ental Laboratory 935 Bush A venue S t Paul, M N 551 0 6
Laboratory Project Identification
ET& SS F A C T -T O X -013 L IR N U 2095
3M Environmental Laboratory
3MEnvironmental Laboratory
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Analytical Study: FACT-TOX-013 L R N -U 2095
_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
Protocol FACT-TOX-013 Amendment 1
This amendment modifies the following portion(s) of the protocol:
1. PROTOCOL READS: The proposed study completion date is listed as 12/31/98.
A m end TO READ: The proposed study completion data is 6/30/00.
Reason: The proposed completion date was changed to allow time for analyzing all matrices of interest.
Amendment Approval
r Marvin Case Ph.D., Sponsor Representative
Kris J.
Ik
Ph.D., Study Director
g /2 -/^ 5 Date
3M Environmental Laboratory
3MEnvironmental Laboratory
T"' ^ f l
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Analytical Study: FACT-TOX-013 L R N -U 2095
_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
Study Title Combined Oral (Gavage) Fertility Development and Perinatal/Postnatal
Reproduction Toxicity Study of N-EtFOSE in Rats
PROTOCOL AMENDMENT NO. 2
Amendment Date: September 10,1999
Performing Laboratory 3M Environmental Technology & Safety Services
3M Environmental Laboratory 935 Bush Avenue
St. Paul, MN 55106
Laboratory Project Identification ET&SS FACT-TOX-013 LIRNU2095
i
3M Environmental Laboratory
3MEnvironmental Laboratory
t: 0-2
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Analytical Study: FACT-TOX-013 L R N -U 2095
_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
Protocol FACT-TOX-013 Amendment 2
This am endm ent m odifies the follow ing portion(s) o f the protocol:
1. PROTOCOL reads: The protocol states that liver will be extracted and analyzed at the 3M Environmental Laboratory.
AMEND TO read: The liver specimens will be extracted and analyzed at Battelle Memorial Institute, 505 King Avenue, Columbus, Ohio 43201-2693.
REASON: The liver specimens will be sent to Battelle Memorial Institute for extraction and analysis due to time constraints in the 3M Environmental Laboratory.
2. PROTOCOL reads: The protocol states that serum specimens will be extracted and analyzed following methods:
FACT-M-3.0, "Extraction of Potassium Perfluorooctanesulfonate or Other Anionic Surfactants from Serum for Analysis Using HPLC-Electrospray/Mass Spectrometry" FACT-M-4.0, "Analysis o f Fluorochemicals in Serum Extracts Using HPLCElectrospray/Mass Spectrometry"
AMEND to read: The serum specimens will be extracted and analyzed following methods:
ETS-8-4.1, "Extraction o f Potassium Perfluorooctanesulfonate or Other Fluorochemical Compounds from Serum for Analysis Using HPLC-Electrospray Mass Spectrometry" ETS-8-5.1, "Analysis o f Potassium Perfluorooctanesulfonate or Other Fluorochemical Compounds in Serum Extracts HPLC-Electrospray Mass Spectrometry"
REASON: The extraction and analytical methods FACT-M-3.0 and FACT-M-4.0, respectively, were updated on 04/27/99 to ETS-8-4.1 and ETS-8-5.1.
3M Environmental Laboratory
3MEnvironmental Laboratory
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
Protocol FACT-TOX-013 Amendment 2
3. PROTOCOL reads: The protocol states that liver specimens will be extracted and analyzed following methods:
FACT-M-1.0, "Extraction of Potassium Perfluorooctanesulfonate or Other Anionic
surfactants from Liver for analysis Using HPLC-Electrospray/Mas Spectrometry"
FACT-M-2.0, "Analysis o f Frluorochemicals in Liver Extracts Using HPLC-
.
Electrospray/Mass Spectrometry"
AMEND TO read: The liver specimens will be extracted and analyzed following method:
Method for Analysis of Perfluorooctane Sulfonate (PFOS) in Rat liver by LC/MS/MS, Version 1.0
REASON: Since the liver extraction and analysis was sub-contracted to Battelle Memorial Institute, this amendment was written to include their liver methods and titles.
Amendment Approval
*
_ ________
Marvin case Ph.D.-, Sponsor Representative
h p f .l is p .
f o b hk
Kristen J. Hansen Ph.D., Study Director
3M Environmental Laboratory
3MEnvironmental Laboratory
r nr
Date
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_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
Study Title Analytical Study 2(N-Ethylperfluorooctanesulfonamido)-ethanol in
Two Generation Rat Reproduction
PROTOCOL AMENDMENT NO. 3
Amendment Date: October 4,1999
Performing Laboratory
3M Environmental Technology & Safety Services 3M Environmental Laboratory 935 Bush Avenue St. Paul, M N 55106
Laboratory Project identifcation
ET&SS FACT-TOX-013 LIRNU2095
3MEnvironmental Laboratory
3MEnvironmental Laboratory
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_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
*
j.
Protocol FA C T Tox-013 Amendment Number 3
This amendment modifies the following portion(s) of the protocol:
1. P ro to co l Re a d s :
Kristen J. Hansen, Ph.D. is the Study Director.
A mend to Read:
James K. Lundberg, Ph.D. is the Study Director.
Reason:
Original study design has changed due to availability o f resources and James K. Lundberg will begin serving as the study director for'FACT-TOX-013 as o f 4 October 1999.
2. Protocol Reads:
Section 7.1 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; study correspondence; shipping records; raw data; and electronic copies o f data. Additionally, Section 7.2 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: Training records; calibration records; instrument maintenance logs; Standard Operating Procedures, Equipment Procedures, and Methods; and appropriate specimens.
A mend to Read:
Section 7 states: "The original data, or copies thereof, will be available at the 3M Environmental Laboratory to facilitate audits o f the study during its progress and before acceptance o f 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 o f 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 o f the facility performing each analysis.
Reason:
To direct subcontract laboratories in the disposition of the items listed above.
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_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
Protocol FACT Tox-013 Amendment Number 3
3. Protocol reads:
Disposition o f test and control substances: Biological tissues and fluids are retained per GLP regulation.
Amend to read: Specimens will be maintained in the 3M Environmental Laboratory specimen archives. All specimens sent to sub-contract laboratories will be returned to the 3M Environmental Laboratory upon completion o f analysis and submission of the sub-contract laboratory(s) final report The specimens 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 o f specimens analyzed at subcontract laboratories.
Amendment Approval
Marv Case, D.V.M., Ph.D., Sponsor Representative
H (^ r Date
f t L & -----------
,__________^ ________ ;______________________ t O / Z f U
Kristen J. Hansen, Ph.D., Previous Study Director
Date
\
Dale L. Bacon, PteT 3M Environmental Laboratory Management
3M Environmental Laboratory
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Study Title A nalytical Study o f 2(N -Ethylperfluorooctanesulfonam ido)-ethanol in
Tw o Generation Rat Reproduction
PROTOCOL AMENDMENT NO. 4
Amendment Date: 20 January 2000
Performing Laboratory 3M Environmental Technology & Safety Services
3M Environmental Laboratory 935 Bush Avenue
St. Paul, M N 55106
Laboratory Project Identification ET&SS LRN-U2095 FACT TOX-013 Argus Study: 418-009
3M M edical Department Study: T -6316.5
3M Environmental Laboratory
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Protocol L R N -U 2095 Amendment Number 4
This amendment modifies the following portion(s) of the protocol:
1. Protocol reads: The study director for the present study was identified in the protocol as James K. Lundburg, Ph.D. A mend to read: The role of study director for the present study was reassigned to Marvin T. Case, D.V.M ., Ph.D., as of 20 January 2000. The previous study director, James K. Lundburg, 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 C FR Part 58).
2. Protocol reads: The sponsor for the present study was identified as Marvin T. Case, D.V.M ., Ph.D. A mend to read: The role of sponsor for the present study was reassigned to John L. Butenhoff, Ph.D., as of 20 January 2000. Reason: To ensure that the study director does not also carry the duties of study sponsor, the sponsor role was reassigned. In this manner, personnel responsibilities and workload are more evenly balanced.
m j r*
_____________ i _ i i _ l
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Protocol LRN-U2095 Amendment Number 4
Amendment Approval
John L B utenhoffP h D ., Sponsor Representative
to , D ate
3 h t A M a rv in T. Case, D . V.M ., P h D ., Incom ing Study Director
J .P __ R -U aju Date V
Q ^tr
3 M Environmental I ahnratnrv
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Study Title Analytical Study o f 2(N-Ethylperfluorooctanesulfonamido)-ethanol in
Two Generation Rat Reproduction
PROTOCOL AMENDMENT NO. 5
Amendment Date: August 31,2000
Performing Laboratory 3M Environmental Technology & Safety Services
3M Environmental Laboratory 935 Bush Avenue
St. Paul, MN 55106
Laboratory Project identification FACT-TOX-013
ET&SS LRN U2095 Argus Study: 418-009 3M Medical Department Study: T6316.5
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- Protocol FA C T TO X-013 Amendment No. 5
This am endm ent m odifies th e follow ing portion(s) of the protocol:
1. PROTOCOL r e a d s : The Principle Analytical Investigator for the present study was identified as James K. Lundberg, Ph.D.
2 . AMEND TO r e a d : The role o f Principle Analytical Investigator for the present study was reassigned to Kristen J. Hansen Ph.D.
REASON: The role o f Principle Analytical Investigator was reassigned due to availability of resources.
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Amendment Approval
Analytical Study: FACT-TOX-013 L R N -U 2095
Protocol F A C T TO X-013 Amendment No. 5
John L. Butenhoff, Ph.D., Sponsor Representative
; rc ^
M arvin T. Case, D .V .M ., Ph.D., Study Director
Date Date
Fnwirnnmontal I ahnm tnn/
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_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
DEVIATION REPORT
B attelle Study N um ber: N 003 6 0 4 -D 3 M E nvironm ental T ech n ology and S ervices Study N um ber: F A C T 0 6 0 9 9 8 .1
2 (N -E th ylp erflu orooctan esu lfon am id o)-eth an ol in T w o G eneration R at R eproduction
TYPE OF DEVIATIONS: PROTOCOL
DATES O F DEVIATIONS:
October 18, 1999
NA TU RE O F DEVIATIONS: Some o f the analytical method acceptance criteria were not met for the LC/M S/M S analysis conducted 180ct99 at Battelle. These deviations relate to protocol amendment 2. See below for summary.
A nalvte
A cceptance criterio n n o t m et
PFOS M -556 M -556 M -556 M -556
PFOSAA PFOSAA
QC3 exceeded 20 error (-20.3 actual! QC2 exceeded 20% error (23.4 actual) ( QC3 exceeded 20% RSD (21.2 actual) QC4 exceeded 20% RSD (28.8 actual) Dilution recovery exceeded 130% (131.5 actual with 21.6 RSD) QC3 exceeded 20 error (-20.6% actual) QC4 exceeded 20 RSD (21.3 actual)
CAUSE O F DEVIATIONS: Sample preparation and/or LC/M S/M S variabilities over the course o f the sample set may have contributed to the deviations.
IM PA C T O F DEVIATIONS O N T H E STUDY: The errant QC values w ere bracketed by acceptable QC concentration levels w hich demonstrates that the calibration curves generally provided good accuracy over tho tested range. The dilution recovery for M-556 was not considered to be exceedingly high enough, at only approximately 1.5 above the normal acceptance level, to have significantly impacted the data.
CORRECTIVE ACTION :This protocol deviation summary was prepared for inclusion in the final report.
APPROVED BY:
Cv
Jon dyA ndre, Ph.D. Battelle Principal Investigator
Z . - Z . l - ' C 'i
Date
k u v/W k J~~C xsij--
Jam es-K . Lwndbarg , PhrD . Study D irector
f r s t>V*\ f t p J
/ fi'yuu Q-4- (
Date
N003604-D Protocol Deviation 1, Page 1 of 1
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_ Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
DEVIATION REPORT
B attelle Study N um ber: N 0 0 3 6 0 4 -D 3M E nvironm ental T ech n ology and S ervices Study N um ber: F A C T 0 6 0 9 9 8 .1
2 (N -E th ylp eifluorooctan esulfonam ido)-eth anol in T w o G eneration R at R eproduction
TYPE OF DEVIATIONS: PROTOCOL
DATE O F DEVIATIONS:
October 20, 1999
NA TU RE O F DEVIATIONS: PFO S QC3 exceeded the 20% RE method requirement (actual -2 1 .7 % ). The dilution recovery check standard did not meet the 70-130% recovery requirement (actuals 5.0% for PFOS and 4.6% for PFOSA). These method deviations relate to amendment 2 o f the study protocol.
CAUSE O F DEVIATIONS: Sample preparation and/or LC/M S/M S variabilities over the course o f the sample set may have contributed to the QC deviation. Sample preparation error appears to have been the cause for the dilution recovery results.
IM PA CT OF DEVIATIONS ON T H E STUDY: The errant QC value level w as bracketed by acceptable QC concentration levels which demonstrates that the calibration curves generally provided good accuracy for study samples over the tested range.
A comparison o f the results obtained for the diluted study samples from 20Oct99 and previous results that w ere Slightly LO Q (130ct99 and 180ct99) demonstrated good agreem ent betw een the 2 determinations. This w ould indicate that the dilution o f the study samples was perform ed correctly 20Oct99 so that no impact on the quantitations occurred.
CORRECTIVE ACTION: This protocol deviation summary was prepared for inclusion in the final report.
APPROVED BY:
Battelle Principal Investigator
o
D ate
Study Director
Date
j
N003604-D Protocol Deviation 2, Page 1 of 1 E-36
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- Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
DEVIATION REPORT
B attelle Study N um ber: N 00 3 6 0 4 -D 3M E nvironm ental T ech n ology and S ervices Study N um ber: F A C T 0 6 0 9 9 8 .1
2 (N -E thylperfluorooctanesulfonam ido)-ethanol in T w o G eneration R at R eproduction
T Y P E O F D EV IA T IO N S: PR O TO C O L
D A T E S O F D E V IA T IO N S: O ctober 12, 1999 through O ctober 2 0 ,1 9 9 9
N A T U R E O F D E V IA T IO N S: T he lot num ber o f PFO S used w as not 2 1 7 as per section 3 .1 .1 o f th e p rotocol. T h e sou rce o f reference substance m atrix w as not A rgu s R esearch L aboratories as sp ecified in section 3 .2 .2 o f the protocol. In itial an alyses o f liver did not exclu sively target P F O S as p er section 4 .0 o f p rotocol.
C A U S E O F D E V IA T IO N S : O nly P F O S lo t num ber 171 w as available at B attelle. H arlan w as th e supplier o f control rat livers used to prepare blanks, standards, and Q C s fo r th e analytical portion o f th e study. A ll 4 analytes o f interest (P F O S, M -5 5 6 , P F O S A A , and P F O S A ) w ere m onitored during each analysis.
IM P A C T O F D E V IA T IO N S O N T H E S T U D Y : PFO S lot num ber 171 and H arlansupplied liv er w ere both u sed fo r B attelle's valid ation o f the analytical m eth od (B attelle study num ber N 0 0 3 6 0 4 -A ). T h ese m aterials a llo w ed achievem en t o f th e reported m ethod acceptance criteria so that there is no im pact on the study. T he concurrent analysis o f P F O S and m etab olites w as an efficien cy im provem ent.
C O R R E C T IV E A C T IO N : T h is protocol d eviation report w as prepared.
APPROVED BY:
C Cud'_L_
Jon(G . A ndre, P h .D . B attelle P rincipal Investigator
z- zz^
D ate
r _______
Jam es K . Lundberg, P h .B . Study D irector
N003604-D Protocol Deviation 3, Page 1 of 1 E-37
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APPENDIX F - PFOS PURITY REPORT
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^651 778 4226
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I 2I
From: Subject:
D a te:
3M SPECIALTY ADHESIVES & CHEMICALS ANALYTICAL LABORATORY
L isa Clem en - (8-5568) - ET& SS- 2-03-09
Request # 57830
T om K estner - (3 -5 6 3 3 ) - SA & C Analytical Lab 236-2B -11
Chemical Characterization ofPOSF-BasedFluorochemieals by `H-NMR &1}F-NMR Spectroscopy
M atch 2 4 ,1 9 9 9 : Prelim inary report for FC -95 (PFO S), lot 171
SAMPLE DESCRIPTION
F C -9 5 , lo t 171 (P F O S ), TN-A-0834; N o m in a l product = C F ir S 0 3(-) K (+ ) (w h ite p o w d er)
INTRODUCTION:
T h is sa m p le w a s s u b je c te d to 'H -N M R and 1SF -N M R spectral a n alyses to determ in e the p u rity o f th e n o m in a l product and to characterize as m any impurity com ponents as possible.
A portion o f the sam ple w as accurately w eighed, spiked with a known amount o f 1,4-bis(tiifluorom eth yl)b en zene (p-H F X ), and then totally dissolved in DM SO-d for subsequent analysis by N M R . A 400 M H z 'H -N M R sp ectru m ( # h 5 7 8 3 0 .4 0 1 ) and a 3 7 6 M H z t9F -N M R spectrum ( # (5 7 8 3 0 .4 0 1 ) w e re acquired u s in g a V a r ia n U N IT Y p lu s 4 0 0 F T -N M R spectrom eter. U se o f the p-H FX internal standard w as intended to perm it the determ ination o f the absolute w eigh t percent concentrations o f the assigned com ponents w ithout n ecessarily needing to identify or quantify all the com ponents in the sam ple mixture.
RESULTS:
T he com bined N M R spectral data w ere used to assign all o f the major and m ost o f the minor com ponents in this sam p le as r ec eiv ed . T h e qu alitative and quantitative com positional results that w e re derived fro m the sin g le trial N M R internal standardization an alyses are summarized in T A B L E -1 on the follow in g page. 1 have reported both relative and absolute w eig h t percent concentrations. One possible reason that the absolute wt.% values add up to m ore than 100% m ay be due to the fact that I assum ed all o f the com ponents contained 8 carbons. If there w ere any shorter chain hom ologs present (i.e., 7, 6, S, ere. carbons), then the average com pound m olecular w eigh ts w o u ld h a v e b e e n so m e w h a t le s s than th ose used in the calcu lation s. In general, the f*F -N M R te ch n iq u e is n o t particularly w ell suited for identifyin g or quantifying sm all amounts o f various fluorochem ical h o m o lo g impurity com ponents u n less the chains are very short. A more com plete characterization o f any other fluorochem ical h om ologs w ould require analysis b y electrospray M S or a sim ilar technique.
A d dition al w ork w ou ld b e required in an effort to positively verify the tentatively assigned com p on en ts listed in T A B L E -1 (den oted by p o ssib le). S m all amounts o f other unidentified im purities are also detected in the N M R spectra, but additional w ork w ou ld b e required in an effort to identify or quantify th ese other m aterials.
C op ies o f the N M R spectra w ill be provided for you at a later date. If you have any questions about the results in this initial report for FC -95, lot 171. please let m e know. I apologize for the delay in com pleting this initial work.
T om K estner c: Rick Payfer - SAAC Analytical L ab -2 3 6 -2 B -l!
Fik iUfcrcncs: LC37S30CC061
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Analytical Study: FACT-TOX-013 L R N -U 2095
_ Battelle Study Number: N 003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
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SA & C A nalytical Lab Request # 37830 Initial R eaort fo r F C -93. lo t 171
"
TABLE-1
Sam ple: FC -95, lot 171 (PFOS), TN -A -0834 O v er a ll Q u an titative C o m p o sitio n a l R e su lts b y 'H /`*F-N M R Internal S tan d ard ization A n a ly s e s
Structural A ssig n m e n ts
C F 3( C F ^ - S 0 3(-) K (+ ) (N orm al chain; assum e x =7 for calculation purposes)
NM R A bsolute W eight% C on cen tration s
(initie trial m easurem ent)
7 0 .3 %
NM R R ela tiv e W eight* C oncentrations
(tin a ie trial measurement)
6 8 .6 %
C F ^ C F J i -CFCCFjK C F jJj-S O jM K (+ ) (Internal m onom ethyl branch;
assum e x+ y 5 , a * 0 , A y * 0, for calculation purposes)
17.7%
173%
(C F j) jC F -(C F j)*-SO j( - ) K (+ ) (Isopropyl branch; assum e x =3 for calculation purposes)
QFji-CF(CFi)-SOi(-) K M
(A lpha branch; assum e x * 6 for calculation purposes)
P o ssib le F -S F ^ -C J V S O jL ) K (+) (assum e x 3 for calculation purposes)
C F jK C F ^ -C C C F jJ H C F ^ -S O jH K (+ ) (Internal gem -dim ethyl branch: assum e x+y - 4 and x * 0 for
calculation purposes)
03P o s s ib le CFj-S F *-C |F u -S (-) K (+ )
(assum e x * 7 for calculation purposes)
P ro b a b le C iH j r S O j(") K (+ ) (H ydrocarbon sulfonate salt; assum e x a 3 for calculation purposes)
(C F 3) 3C -<C Fj) x-S 0 3 (-) K (+ )
(t-butyl branch; assum e x * 4 for calculation purposes)
10.3% 3.3% 0 .3 7 % 0 .1 6 %
. 0.11% 0 .0 3 1 % 0 .0 2 7 %
10.2% 3 .2 % 036% 0 .1 6 %
0 .1 0 % 0 .0 3 0 % 0 .0 2 6 %
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Analytical Report: FACT TOX-013 LRN-U2095
Appendix H: Interim Certificate of Analysis
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proB)
3M M e d i c a l D e p a r t m e n t S t u d y : T 6 3 1 6 . 5
Analytical Study: FACT-TOX-013
LRN-U2095
A n a l y t i c a l R e p o r t : FACT T O X -013 L R N -U 2095
INTERIM CERTIFICATE OF ANALYSIS
Revision 1(9/7/00)
Centre Analytical Laboratories COA Reference #: 023-018B
3M Product: P F O S ,L otl71
Reference#: SD-009
_____________________ Purity: 86.4%
Test Name
Specifications
PurityJ
Result 86.4%
Appearance
Identification NMR
Metals (ICP/MS) 1. Calcium 2. Magnesium 3. Sodium 4. Potassium2 5. Nickel 6 . Iron 7. Manganese
Total % Impurity (NMR)
Total % Impurity (LC/MS) Total % Impurity (GC/MS)
Related Compounds POAA Residual Solvents (TGA) Purity by DSC Inorganic Anions (IC)
1. Chloride 2. Fluoride 3. Bromide 4. Nitrate 5. Nitrite 6 . Phosphate 7. Sulfate4
Organic A cids5 (IC) 1. TFA 2. PFPA 3. HFBA 4. NFPA
Elemental Analysis6: 1. Carbon 2. Hydrogen 3. Nitrogen 4. Sulfur 5. Fluorine
White Crystalline Powder
1. Theoretical Value = 17.8% 2. Theoretical Value = 0% 3. Theoretical Value = 0% 4. Theoretical Value ==5.95% 5. Theoretical Value = 60%
Conforms
Positive
1. 0.017 wt./wt.% 2. 0.007 wt/wt.% 3. 1.355 wt/wt.% 4. 6.552 wt./wt.% 5. 0.003 wt./wt.% 6 . 0.004 wt./wt.% 7. <0.001 wt./wt.%
1 .0 0 wt./wt.% 10.60 wt./wt.%
None Detected
0.30 wt./wt.% None Detected Not Applicable4
1 . <0.015 wt/wt.% 2. 0.27 wt./wt.% 3. <0.040 wt./wt.% 4. <0.009 wt/wt.% 5. <0.006 wt/wt.% 6 . <0.007 wt/wt.% 7. 8.82 wt/wt.%
1 . <0 .1 wt/wt.% 2 . <0 .1 wt/wt.% 3. <0.1 wt/wt.% 4. <0.25 wt/wt.%
1 . 12.08 wt/wt.% 2. 0.794 wt/wt.% 3. 1.61 wt/wt.% 4. 10.1 wt/wt.% 5. 50.4 wt/wt.%
COA023-018B
3M E n v i r o n m e n t a l L a b o r a t o r y
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A nalytical Study: FACT-TO X-013
LRN-U2095
Analytical Report: FACT TOX-013 LRN-U2 095
INTERIM CERTIFICATE OF ANALYSIS
Centre Analytical Laboratories COA Reference #: 023-018B Date o f Last Analysis: 08/31 /0Q
Expiration Date: 08/31/01
Storage Conditions: Frozen <-10C
Re-assessment Date: 08/31/01
Purity = 100% - (sum o f metal impurities, 1.39% +LC/MS impurities, 10.60%+Inorganic Fluoride, 0.27%+NMR impurities, 1.00%+ POAA, 0.30%)
Total impurity from all tests = 13.56% Purity = 100% -13.56% = 86.4%
2Potassium is expected in this salt form and is therefore not considered an impurity.
3Purity by DSC is generally not applicable to materials o f low purity. N o endotherm was observed for this sample.
4Sulfur in the sample appears to be converted to SO4 and hence detected using the inorganic anion method conditions. The anion result agrees w ell with the sulfur determination in the elemental analysis, lending confidence to this interpretation. Based on the results, the SO4 is not considered an impurity.
5TFA HFBA NFPA PFPA
Trifluoroacetic acid Heptafluorobutyric acid Nonofluoropentanoic acid Pentafluoropropanoic acid
^Theoretical value calculations based on the empirical formula, CsFi7S03*K+ (MW=538)
This work was conducted under EPA Good Laboratory Practice Standards (40 CFR 160).
COA023-018B
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A nalytical Study: FACT-TO X-013
LRN-U2095
Analytical Report: FACT TOX-013 LRN-U2095
INTERIM CERTIFICATE OF ANALYSIS
Centre Analytical Laboratories COA Reference #: 023-018R
LC/MS Purity Profile:
Impurity C4 C5 C6 C7
Total
wt./wt. % 1.03 1.56 6.38 1.63 10.60
Note: The C4 and C6 values were calculated using the C4 and C6 standard calibration curves, respectively. The C5 value was calculated using the average response factors from the C4 and C6 standard curves. Likewise, the C7 value was calculated using the average response factors from the C6 and C8 standard curves.
Prepared By: ________________________________
____
David S. Bell
Date
Scientist, Centre Analytical Laboratories
Reviewed B y :__________________________ ;_____
____
John Flaherty
Date
Laboratory Manager, Centre Analytical Laboratories
COA023-018B 3M Environmental Laboratory
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,3M M edical D epartm ent Study: T-6316.5 , 3M Medical Department Study: T6316.5
Analytical Study: FACT-TOX-013
LRN-U2095
Analytical Report: FACT TOX-013 LRN-U2095
Appendix I: Report Signature Page
T ^-
Marvin T. Case D.V.M., Ph.D., Study Director
Date
John L. Butenhoff, Ph.D., Sponsor Representative
Date
^
fCm'S
FA!
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Analytical Study: FACT TO X -013 LRN-U2095
Appendix J: Amendment 1 to FACT TOX-013 Final Report
TO X-013 Final Study Report Am endm ent 1
Study number: TOX 013
Study title: Analytical Study 2(N-Ethylperfluorooctane sulfonamido)-ethanol in Two Generation Rat Reproduction
Study Director: Marvin T. Case, D.V.M., Ph.D. Amendment date: May 7, 2001
Amendment number: 1
This amendment modifies the following portion of the final report:
A final signed report from Battelle Memorial Institute, presenting the results for PFOS, PFOSAA, PFOSA, and M-556 levels in rat liver specimens, replaces the draft Battelle report in Appendix G.
Liver results in this report are identical to those presented in the original TOX-013 report (Table 13, pages 22-23). As in the original liver data, the PFOS values reported in the Battelle report were corrected by 3M for purity of the reference standard material.
The final Battelle report differs from the draft report in the following ways: All signature pages are signed and dated. The Quality Assurance Statement page has four additional audit dates added. Table of Contents page numbers were corrected. Two Battelle participants were eliminated from page 4, `Acknowledgements.'
T h e s to ra g e a n d arch iv e instructions (p a g e 4 ) a re n o w fo u n d in th e 3 M T O X - 0 1 3
protocol amendment 3. Inclusion of 3M TOX-013 protocol amendments 4 and 5, thus changing the total
number of pages. Minor wording changes.
Other changes to the TOX-013 report include: The cover page was updated to reflect the total number of pages and the title was changed to say "Amended Final Report." The Table of Contents was updated to reflect the added amendment. The additional audit date of the Amended Analytical Laboratory Report TOX013 was added to the Quality Assurance Statement.
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3M M edical D epartm ent Study: T-6316.5
3M Medical Department Study: T-6316.5
Approved by:
A nalytical Study: FA CT-TO X-013 L R N -U 2095
Analytical Study: FACT TO X-013 LRN-U2095
Kristen H. Hansen, Ph.D., Principal Analytical Investigator
0 S -/3 O /O I
Date
Marvin T. Case, D.V.M., Ph.D., S tu d y D ire c to r Bill Reagan, Ph.D., Environmental Laboratory Manager
Date
O J /J y /o /
Date
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