Document JJXagqzy6gvqnDyGrGrqXvYK2
3M Medical Department Study: T6316.5
Analytical Report: FACT TOX-013 LRN-U2095
Study Title
Analytical Study 2(N-Ethylperfluorooctane sulfonamido)-ethanol in Two Generation Rat Reproduction
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 Crt:CD*BR VAF/Plus*
Rats Exposed to EtFOSE-OH
Data Requirement Not Applicable
Author 3M Environmental Laboratory
Study Completion Date At signing
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 o f Pages 135
3M Environmental Laboratory
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3M Medical Department Study: T6316.5
Analytical Report: FACT TOX-013 LRN-U2095
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3M Environmental Laboratory
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3M Medical Department Study: T6316.5
Analytical Report: FACT TOX-013 LRN-U2095
GLP Compliance 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:CCfBR 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.
Study Director
Z
Sponsor Representative
Date
______ O^-fo
Date
9, ZjO O O
3M Environmental Laboratory
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3M Medical Department Study: T6316.5
Analytical Report: FACT TOX-013 LRN-U2095
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:CD*BR 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
QAU Represntetive
3M Environmental Laboratory
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3M Medical Department Study: T6316.5
Analytical Report: FACT TOX-013 LRN-U2095
Table of Contents
GLP Compliance Statement...............................
3
GLP Study--Quality Assurance Statement.........
4
Study Personnel and Contributors.......................
,7
Introduction and Purpose...................................
Test System................................................. Specimen Collection and Analysis.................
.8 .8 .9
Specimen Receipt and Maintenance..................
Chemical Characterization................................ Dose Confirmation Analyses.........................
Method Summaries........................................... 3M Environmental Laboratory........................ Preparatory Method.................................. Analytical Method...................................... Analytical Equipment................................ Deviations....................................................
Data Quality Objectives and Data Integrity..........
.9
.10 .10
.11 .11 .11 .11 .11 ..12
..12
Data Summary, Analyses, and Results.............. Summary of Quality Control Analyses Results Summary of Sample Results........................
Statistical Methods and Calculations.................
Statement of Conclusion..................................
..13 ..13 ..14
..14
..14
Appendix A: Chemical Characterization, Control Matrices and Dose Confirmation Analyses..............................................................................................................
Appendix B: Protocol................................................................................................................. Appendix C: Extraction and Analytical Methods....................................................................
15 18 37
EJS-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 Fluorocherrucals in Serum Extracts Using HPLC-Electrospray/Mass Spectrometry, (9 pages)................. .52
Appendix D: Data Summary Tables...................................................................................... Appendix E: Data Spreadsheets............................................................................................. Appendix F: Example Calculations........................................................................................
.61
.64 .70
Appendix G: Contract Lab Report.......................................................................................... .71 Appendix H: Interim Certificate of Analysis........................................................................... .131
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Appendix I: Report Signature Page................................................................................135
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 Fiuorochemical Levels In Sera Analyses in Study FACT TOX-013.....61 Table 12. Reported Fiuorochemical Levels in Sera Analyses in Study FACT TOX-013
(continued)..................................................................................................... 62 Table 13. Reported Fiuorochemical Levels in Liver Analyses in Study FACT TOX-013.....62 Table 13. Reported Fiuorochemical 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
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 lan 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, EtFOSEOH, and M556 in sera samples collected from rats exposed to EtFOSE-OH. This study was initiated on 1 October
1998.
Test 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 Crl:CCfBR VAF/Pluse (Sprague-Dawley) rat received from Charles River Laboratories, Inc., and assigned temporary numbers until assigned to the study. Rats were permanently identified using MoneP 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 Monel*self-piercing ear tag. FO female rats were approximately 65 days of age and weighed approximately 179-229g when received. FO male rats were approximately 58-67 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 (mg/kg/day)
Dosage Group I (Control) Dosage GroupII
Dosage GroupIII
Dosage Group IV
Dosage GroupV
35
35 35 35 35
25 0 (vehicle)
25 1 25 5 -- 10 -- 15
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Specim en Collection and Analysis
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 Specimens--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 11, 1999 using an ion pairing reagent and methyl-tert-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-electrospray/tandem mass spectrometry (HPLC-ESMSMS) 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 8-4-98, 10-1-98 and 1-29-99. All specimens were received frozen on dry ice and were immediately transferred to storage at -20C 10#C. 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 -20*C 10C.
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Chemical Characterization
EtFOSE-OH CAS Number: 1691-99-2
Chemical Formula: C8F17S 0 2N(CH2CH3)CH2CH20H 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 Expiration Date
EtFOSE-OH
FM-3929 2(N-Ethylperfiuorooctane sul!bnamido)-ethanol
3M
05/2000
Storage Conditions
Ambient temperature
Chemical Lot #
30035, 30037, 30039
Physical Description
Purity
Waxy Solid To be determined*
* The purity of the test article determ ined nominally by N M R a n a ly s t. Subsequent chem ical characterization is occurring and this analytical report w il be am ended to indicate the purity when a certificata of analysis is issued.
Dose Confirmation Analyses
The dose confirmation data w ere 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 Milli-Q water into the linear range of the instrument. For each sample, a matrix spike was prepared (at approximately 50-100% 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).
3M Environmental Laboratory
Prepara tory Method
ETS-8-4.1, "Extraction of Potassium Perfluorooctanesulfonate or Other Fluorochemical 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 autovial.
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 fluorochemical using HPLC-ESMSMS. For example, molecular ion 499, selected as the primary-ion for PFOS (QF17S 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 Chromatograph: Hewlett-Packard* Series 1100 Liquid Chromatograph system Analytical column: Keystone* BetasilTM Ce 2x50 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 40%B over 0.5 minutes Hold at 40%B for 3 minutes
Mass Spectrometer: Micromass* API/Mass Spectrometer Quattro H" Triple Quadrupole system
Software: Mass Lynx'" 3.2 Cone Voltage: 20-60 V Collision Energy: 25-45 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 (a m u )
Product Ion (a m u)
PFOS
499.0
99.0
PFOSA PFOSAA
498.0 584.0
78.0 169.0
EtFOSE-OH
630.0
59.0
M556 THPFOS
556.0 427.0
78.0, 169.0 80.0
Deviations
Deviations from the original protocol and methods are documented in the table below.
Table 4. Deviation Summary for FACT TOX-013
Deviation
Pipettewas used instead Oxforddispenser
Date(s) of Occurrence 10/12/99
0.2--1.OmLof sample was used forextractioninsteadof 1.OmL.
10/12/99
Milk curd samples were not analyzed.
Entire study
Impact on Study
Standards andsampleswereprepared identically. Noadverseimpactonstudy.
Currantwork indicates that volumes 0.5 mLprovideresultsequivalentto1mL extractionvolumes. Resultsofsample volumes <0.5 mLhavenotbeenvalidated andwinbe markedinthedatatable. Nomilkcurddata isavailableforthefinal 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 (LOQ): 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.
Summary of Quality Control Analyses Results
Linearity: The coefficient of determination (r2) of the standard curves werekO.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. All 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).
Limits of Quantitation (LOQ): 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 of Serum Extracts
Analyte
Method LOQ
PFOS 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 MS/MSD and was reproducible to within
10% .
Matrix 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. THPFOS 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; M556 data is quantitated to 31%. The validity of this assumption has not been verified by other techniques.
Summary of Sample Results
Samples from Control Animals: Low levels of PFOS, PFOSA, PFOSAA, EtFOSE-OH, and M556 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.
Samples from Dosed Animals: 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 of 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 ExpirationDate 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 of the Control Matrices Used for Liver Analyses in Study FACT TOX-013
Location
Battelle Memorial Institute
Control Matrix
Rat Liver
Source ExpirationDate Storage Conditions Chemical Lot# Physical Description N/R--not recorded
Harlan N/R N/R N/R
Rat Liver
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Table 8. Characterization of the Analytical Reference Materials Used for Sera Analyses in Study FACT TOX-
013
Location
3M Lab
Materials
PFOS
C/trSOv
PFOSA
C.FjjSOjNH,
PFOSAA
CjF^SO/mCH^HJ
(CH|COOH))
EtFOSE-OH
CjF^OjNtCH^lHj)
CHiCHjOH
M556
CtFjjSO^HH)
(CH.CHJ)
THPFOS* CJVFJ*Ofi
Source
Expiration Date
Storage Condition Chemical Lot Number Physical Description
Purity
3M Specialty Chemicals
08/31/01
Ambient temperafcjre
N/R 01/01/2010 Ambient temperature
171 L-15700
Vit* aystallne
powder
86.4%
Light yeiow waxy soW TBD
N/R 01/01/2010 Ambient temperature N8 112999-09 Tan waxy toW
TBD
3M CP/PCP Division 01/01/2010
Ambient temperature 936
Amber waxy sofid TBD
3M 01/01/2010 Ambient temperatura N B 113047-80 White powder
TBD
ICN Blomedicals 01/2010
Ambient temperature 53406
Brown waxy solid NA
N/R-- not recorded TBD-- to be determined NA-- not applicable
Table 9. Characterization of the Analytical Reference Materials
Location
Materials
S ource E x p ira tio n D ate S tora ge C o n d itio n s C h e m ic a l L o t Num ber P h y s lc a l D e s c rip tio n
P u rity
Battello Memorial InBtitute
PFOS
3M
M5S6
3M
PFOSAA PFOSA THPFOS*
3M 3M ICN
08/31/01
01/01/2010
Ambient temperature
Ambient temperature
171 NB 113047-80
W hits crystalline powder
86.4%
ViMte powder TBD
2010 Amtent temperature
817
N/R
TBD
01/01/2010
Ambient temperature
L-15708
Light yellow waxy soid
TBD
N/R Ambient temperature
59000
N/R
NA
N /R -- not recorded TBD-- to be determined NA-- not applicable
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Table 10. Tween Dosing Confirmation for Study In-life #418-009
Group Do*
Sample Number
Expected Cone. MeasuredCone. EtFOSE (ng/mL) EtFOSE(ng/mL)
Group 1--Control 0 mg/mL Group2--0.2 mg/mL Group3--1.0 mg/mL Group4--2.0 mg/mL Group5--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-418-009-D, 06/08/98 B-418-009-0, 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 1of 6 T
B-418-009-A, 06/08/98 3of6 M
B-418-009-A, 06/08/98 5 of6 B
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. Measured Cone.
EtFOSE % MS
EtFOSE (ng/mL) EtFOSE (ng/mL) 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-MS 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 of 6 T-MS
B-418-009-A, 06/08/98 3of6 M-MS
1100 1100
949 1053
86 96
B-418-009-A, 06/08/98 5of6 B-MS
NA Notapplicable
1100
944
86
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Appendix B: Protocol
Analytical Report: FACT TOX-013 LRN-U2095
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' Analytical Repo^ ^ ? S f 9 l i - o ' *
A
3M Environmental Laboratory____________
Protocol - Analytical Study 2(N-Ethylperfluorooctanesulfonamido)-ethanol in
Two Generation Rat Reproduction
In-vivo study reference num ber: Argus 418-009
Study num ber: FACT 060998.1 Test substance: 2(N-EthyIperfIuorooctanesulfonamido)-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 1
St. Paul, MN 55106
Experimental start date: Expected term ination 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 HPLCElectrospray/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
jllilz+x-flzz------------ ----------------------------- t+ r-
Kris Hansen
Date
Study Director
Marvin Case Sponsor Representative
/ b e t'/fa r
Date
ft
3M^Environmental Laboratory
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3M Medical Department Study: T6316.5
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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 Reg ulatory 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 T est M a t e r ia l s ___________________ __ ____________________________________
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 m atrix: Rat liver and serum
3.13 Analytical control substance: None
3.1.4 Analytical control substance m atrix: 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 m atrix: Argus Research Laboratories; traceability information will be included in the final report
3.2.3 Analytical control m atrix:
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
3.2.3.2 Rat serum - Sigma Chemical Company; traceability information will be included in the final report
3 3 N um ber 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 sam ples: 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.
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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 m aterial: 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 1 0 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 Experim ental - Overview_________________________ I___________________________ 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 Experim ental - Analytical M ethods______________________ !______________________ 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 transform ations 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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7.0 M aintenance of Raw Data and Records________________________ _________ 7.1 The following raw data and records will be retained in the study folder in the archives
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 of data 7.2 Supporting records to be retained separately from the study folder in the archives according to AMDT-S-8 will include at least the following: 7.2.1 Training records 7.2.2 Calibration records 7.2.3 Instrument maintenance logs 7.2.4 Standard Operating Procedures, Equipment Procedures, and Methods 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
9.0 Attachments__________________________________________________________ 9.1 FACT-M-1.0, Extraction of Potassium Perfluorooctanesulfonate or Other Anionic
Surfactants from Liver for Analysis Using HPLC-Electrospray/Mass Spectrometry 9.2 FACT-M-2.0, Analysis of Fluorochemicals in Liver Extracts Using HPLC-
Electrospray/Mass Spectrometry 9.3 FACT-M-3.0, Extraction of Potassium Perfluorooctanesulfonate or Other Anionic
Surfactants from Serum for Analysis Using HPLC-Electrospray/Mass Spectrometry 9.4 FACT-M-4.0, Analysis of Fluorochemicals in Serum Extracts Using HPLC-
Electrospray/Mass Spectrometry
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Study Title Combined Oral (Gavage) Fertility Development and-Perinatal/Postnatal
Reproduction Toxicity Study o f N-EtFOSE in Rats
PROTOCOL AMENDMENT NO. 1
Amendment Date: July 28,1999
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 LERN U2095
3M Environmental Laboratory
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Analytical Report: FACT TOX-013 LRN-U2095
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.
AMEND 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 o f interest.
Amendment Approval
Marvin Case Ph.D., Sponsor Representative
J o <h k - Dat v
Kris J. ansen Ph.D., Study Director
Date
3M Environmental Laboratory
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Protocol FA C T 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 o f the sub-contract laboratory(s) final report. The specimens will be returned with the following documentation: the signed original chain of custody and records o f storage conditions while at the sub-contract facility.
Reaso n: 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
y Q de & U f fDate
T/L & ------- -------------------------------------------------
Kristen J. Hansen, Ph.D., Previous Study Director
Date
Dale L. Bacon, PinT 3M Environmental Laboratory Management
3M Environmental Laboratory
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Analytical Report: FACT TOX-013 LRN-U2095
Study Title Analytical Study o f 2(N-Ethylperfluorooctanesulf>namido)-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 Medical Department Study: T-6316.5
3M Environmental Laboratory
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Analytical Report: FACT TOX-013 LRN-U2095
Protocol LRN-U2095 Amendment Number 4
This amendment modifies the following portion(s) of the protocol:
1. P rotocol reads: The study director for the present study was identified in the protocol as James K. Lundburg, Ph.D. Amend 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. 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.
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Protocol LRN-U2095
Amendment Number 4
Amendment Approval
John L ButenhoffPhD., Sponsor Representative
Date
lA/V^n Marvin T. Case, D. V.M., Ph.D., Incoming Study Director
lo
Q -trtr Date &
3JVf Environmental Laboratory
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Analytical Report: FACT TOX-013 LRN-U2095
Study Title Analytical Study of 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
3M Environmental Laboratory
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Protocol F A C T TO X-013 Amendment No. 5
This amendment modifies the following portion(s) of the 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 of 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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Protocol F A C T TOX-013 Amendment No. 5
Amendment Approval
John L. Butenhoff, Ph.D., Sponsor Representative
/
Date
rc
M a h in T. Case, D.V.M., Ph.D,, Study Director
Date
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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 Environmental Laboratory
M ethod
E x tra ctio n ,of P otassium P erfluoro o cta n esu lfo n a te o r O t h e r
F l u o r o c h e m ic a l c o m po u n d s f r o m Seru m f o r Analysis U sin g HPLC-
E lectro spra y /M ass Spectrom etry
Method Number: ETS-8-4.1
Adoption Date: 03/01/99
Author: Lisa Clemen, Glenn Langenburg
Revision Date: ^ ^
Approved By: 01
-- F Laboratory Manager
-
Date
Ir k ----------Group Leader
Date
LAtjfc. A Technical Reviewer
______________ _____________________ Date
1.0 S c o p e a n d A p p l i c a t i o n 1.1 Scope: This method is for the extraction o f potassium perfluorooctanesulfonate (PFOS)
or other fluorochemical compounds from serum. 1.2 Applicable compounds: 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 3M Environmental Laboratory
ETS-8-4.1 Extraction of PFOS from Serum
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2.0 S u m m a r y o f M e t h o d
_____________ _______________________________________________
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-ieri-butyl ether (MtBE). In this method, seven fluorochemicals were extracted: PFOS, PFOSA, PFOSAA, EtFOSE-OH, PFOSEA, M556, and surrogate standard (see 3.0 Definitions). An ion pairing reagent is added to the sample and the analyte ion pair is partitioned into MtBE. The MtBE extract is removed and put onto a nitrogen evaporator until dry. Each extract is reconstituted in 1.0 mL o f methanol, then filtered through a 3 cc plastic syringe attached to a 0.2 |im nylon
filter into glass autovials.
2.2 These sample extracts are analyzed following method ETS-8-5.1 or other appropriate methods.
3.0 D e f i n i t i o n s ____________________________________________________________________________
3.1 PFOS: perfluorooctanesulfonate (anion o f potassium salt) C8FI7S 0 3' 3.2 PFOSA: perfluorooctane sulfonylamide 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 C8F 17S 0 2N(CH2CH3)CH2CH20H
3.5 PFOSEA: perfluorooctane sulfonyl ethylamide C8F I7S 0 2N(CH2CH3)H
3.6 M556: C8F17S 0 2N(H)(CH2C 00H ) 3.7 Surrogate standard: 1H-1H-2H-2H perfluorooctane sulfonic acid
4.0 W a r n i n g s a n d C a u t i o n s
________________ _____ _______________________________
4.1 Health and safety warnings
4.1.1 Use universal precautions, especially laboratory coats, goggles, and gloves when handling animal tissue, which may contain pathogens.
5.0 In t e r f e r e n c e s ___________ ____________________ ___ _____________________________________
5.1 There are no interferences known at this time.
6.0 E q u i p m e n t _________________
__________________ ___ _________________________________
6.1 The following equipment is used while performing this method. Equivalent equipment is acceptable.
6.1.1 Vortex mixer, VWR, Vortex Genie 2
6.1.2 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 S u p p l i e s a n d M a t e r i a l s _________________ ____________________________________________ 7.1 Gloves 7.2 Eppendorf or disposable pipettes 7.3 Nalgene bottles, capable of 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 times with methanol and 3 times with
Milli-QTM water. Rinse syringes a minimum o f 9 times with methanol, 3 rinses from 3 separate vials.
8.0 R e a g e n t s a n d S t a n d a r d s ___________ _____________________________________________ 8.1 Type I reagent grade water, Milli-QTM or equivalent; all water used in this method should
be Milli-QTM water and may be provided by a Milli-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 (Na2C 0 3), J.T. Baker or equivalent 8.5 Sodium bicarbonate (NaHCOj), J.T. Baker or equivalent 8.6 Methyl-T-Butyl Ether, Omnisolv, glass distilled or HPLC grade 8.7 Methanol, Omnisolv, glass distilled or HPLC grade 8.8 Serum or blood, frozen from supplier 8.9 Fluorochemical standards
8.9.1 PFOS (3M Specialty Chemical Division), molecular weight = 538 8.9.2 PFOSA (3M Specialty Chemical Division), molecular weight = 499
ETS-8-4.1 Extraction of PFOS from Serum
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8.9.3 PFOSAA (3M Specialty Chemical Division), molecular weight = 585
8.9.4 EtFOSE-OH (3M Specialty Chemical Division), molecular weight = 570
8.9.5 PFOSEA (3M Specialty Chemical Division), molecular weight = 527
8.9.6 M556 (3M Specialty Chemical Division), molecular weight = 557
8.9.7 Surrogate standard: 4-H, perfluorooctane sulfonic acid (l-H .l-H , 2-H, 2-H C8F,3S 0 3H) molecular weight = 428
8.9.8 Other fluorochemicals, as appropriate
8.10 Reagent preparation
NOTE: When preparing larger volumes than listed in reagent, standard, or surrogate preparation, adjust accordingly.
8.10.1 10 N sodium hydroxide (NaOH): Weigh approximately 200 g NaOH. Pour into a 1000 mL beaker containing 500 mL Milli-QTM water, mix until all solids are dissolved. Store in a 1 L Nalgene bottle.
8.10.2 1 N sodium hydroxide (NaOH): Dilute 10N NaOH 1:10. Measure 10 mL o f 10 N NaOH solution into a 100 mL volumetric flask and dilute to volume using Milli-QTM water. Store in a 125 mL Nalgene bottle.
8.10.3 0.5 M tetrabutylammonium hydrogen sulfate (TBA): Weigh approximately 169 g of TBA into a 1 L volumetric containing 500 mL Milli-QTM water. Adjust to pH 10 using approximately 44 to 54 mL of 10 N NaOH (While adding the last mL of NaOH, add slowly because the pH changes abruptly). Dilute to volume 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 (NajCO/NaHCOj): Weigh approximately 26.5 g of sodium carbonate (NsqCO^ and 21.0 g o f sodium bicarbonate (NaHC03) into a 1 L volumetric flask and bring to volume with MilliQTM 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 Weigh approximately 100 mg of PFOS into a 100 mL volumetric flask and record the actual weight.
8.11.4 Bring to volume with methanol for a stock standard of approximately 1000 ppm (pg/mL).
8.11.5 Dilute the stock solution with methanol for a working standard 1 solution of approximately 50 ppm.
8.11.6 Dilute working standard 1 with methanol for a working standard 2 solution of approx. 5.0 ppm.
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8.11.7 Dilute working standard 1 with methanol for a working standard 3 solution of approx. 0.50 ppm.
8.12 Surrogate stock standard preparation
8.12.1 Weigh approximately 50-60 mg of surrogate standard l-H .l-H , 2-H, 2-H, C8F13S 0 3H into a 50 mL volumetric flask and record the actual weight.
8.12.2 Bring to volume with methanol for a surrogate stock of approximately 1000-1200 ppm. '
8.12.3 Prepare a surrogate working standard. Transfer approximately 1 mL o f surrogate stock to a 10 mL volumetric flask and bring to volume with methanol for a working standard of 100 ppm. Record the actual volume transferred.
9.0 S a m p l e H a n d l i n g _________________ _____________________________________________________ 9.1 All samples are received frozen and must be kept frozen until the extraction is performed.
9.2 Allow samples to thaw to room temperature prior to extraction.
10.0 Qu a lity Co n t r o l _____________________________________________________
10.1 Solvent Blanks, M ethod blanks and matrix blanks 10.1.1 An aliquot o f 1.0 mL methanol is used as a solvent blank.
10.1.2 Extract two 1.0 mL aliquots of Milli-QTM water following this procedure and use as method blanks.
10.1.3 Extract two 1.0 mL aliquots o f the serum following this procedure and use as matrix blanks. See 11.1.4.
10.2 M atrix spikes 10.2.1 Prepare and analyze matrix spike and matrix spike duplicate samples to determine the accuracy of the extraction. 10.2.2 Prepare each spike using a sample chosen by the analyst, usually the control matrix received with each sample set.
10.2.3 Expected concentrations will fall in the mid-range of the initial calibration curve. Additional spikes may be included and may fall in the low-range of the initial calibration curve.
10.2.4 Prepare one matrix spike and matrix spike duplicate per 40 samples, with a minimum of 2 matrix spikes per batch.
10.3 Continuing calibration checks 10.3.1 Prepare continuing calibration check samples to ensure the accuracy of the initial calibration curve. 10.3.2 Prepare, at a minimum, one continuing check per group 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 will fall within the mid-range of the initial calibration curve. Additional spikes may be included that fall in the low-range of the initial calibration curve. This is necessary if the analyst must quantitate using only the low end o f the calibration curve (for example, 5 ppb - 100 ppb, rather than 5 ppb - 1000 ppb).
11.0 C a l i b r a t i o n a n d S t a n d a r d i z a t i o n _________________________________________________
11.1 Prepare matrix calibration standards
11.1.1 Transfer 1 mL o f serum to a 15 mL centrifuge tube.
11.1.2 If most sample volumes are less than 1.0 mL, extract standards with matrix volumes equal to the sample volumes. Do not extract less than 0.50 mL o f matrix. Record each sample volume on the extraction sheet.
11.1.3 While preparing a total of twenty aliquots in 15 mL centrifuge tubes, mix or shake between aliquots.
11.1.4 Two 1 mL aliquots, or other appropriate volume, 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 Use 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 of surrogate working standard for the concentration to fall within the calibration curve range 5 ppb 1000 ppb.
11.3 Extract spiked matrix standards following 12.6-12.16 of this method. Use these standards to establish each initial curve on the mass spectrometer.
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Table 1
Approximate spiking amounts for standards and spikes
Using 1.0 mL of matrix
Working standard
pL Approx, final cone, of
(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 50.0 ppm
20 0.100 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 P r o c e d u r e ____________________________________ _______________________________________
12.1 Obtain frozen samples and allow to thaw at room temperature or in a lukewarm waterbath.
12.2 Vortex mix for 15 seconds, then transfer 1.0 mL or other appropriate volume 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 samples, including blanks and standards, ready for extraction with 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 Table 1 in that section, for the calibration curve standards. Also prepare matrix spikes and continuing calibration standards.
12.8 Vortex mix the standard curve samples, matrix spike samples, and continuing calibration samples for 15 seconds.
12.9 Check to ensure the 0.5 M TBA reagent is at pH 10. If not, adjust accordingly.
12.10 To each sample, add 1 mL 0.5 M TBA and 2 mL o f 0.25M sodium carbonate/sodium bicarbonate buffer.
12.11 Using an Oxford Dispenser, add 5 mL methyl-ierr-butyl ether.
12.12 Cap each sample and put on the shaker at a setting of 300 rpm, for 20 minutes.
12.13 Centrifuge for 20 to 25 minutes at a setting of 3500 rpm, or until layers are well separated.
ETS-8-4.1 Extraction o f PFOS from Serum
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12.14 Label a fresh 15 mL centrifuge tube with the same information as in 12.5.
12.15 Remove 4.0 mL of the organic layer to this clean 15 mL centrifuge tube.
12.16 Put each sam ple on the analytical nitrogen evaporator until dry, approxim ately 1 to 2
hours. 12.17 Add 1.0 mL of methanol to each centrifuge tube using a graduated pipette.
12.18 Vortex mix 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-volume autovial when necessary.
12.20 Label the autovial with the study number, animal number and gender, sample timepoint, matrix, final solvent, extraction date, and analyst(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 D a t a A n a l y s i s a n d C a l c u l a t i o n s _______
_______________________________________
13.1 Calculations
13.1.1 Calculate actual concentrations of PFOS, or other applicable fluorochemical, in calibration standards using the following equation:
mL of standard x concentration o f standard fug /mL-)__________________ = mL o f standard + mL o f surrogate standard + initial matrix volume (mL)
Final Concentration (pg/mL) of PFOS in matrix
14.0 M e t h o d P e r f o r m a n c e _____________ ____________________ __________________________ 14.1 The method detection limit (MDL) is analyte and matrix specific. Refer to MDL report
for specific MDL and limit of quantitation (LOQ) values (see Attachm ents B and C).
14.2 The following quality control samples are extracted with each batch o f samples to evaluate the quality of the extraction and analysis.
14.2.1 Method blanks and matrix blanks. 14.2.2 Matrix spike and matrix spike duplicate samples to determine accuracy and
precision of the extraction.
14.2.3 Continuing calibration check samples to determine the continued accuracy o f the initial calibration curve.
14.3 Refer to section 14 of ETS-8-5.1 for method performance criteria.
15.0 P o l l u t i o n P r e v e n t i o n a n d W a s t e M a n a g e m e n t __________________________ _
15.1 Sample waste is disposed in biohazard containers, flammable solvent waste is disposed in high BTU containers, and used glass pipette waste is disposed in broken glass containers located in the laboratory.
ETS-8-4.1 Extraction of PFOS from Serum
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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 A t t a c h m e n t s
______________________ _________________________________
17.1 Attachment A, Extraction worksheet
17.2 Attachment B, MDL/LOQ values and summary
173 Attachment C, Calibration standard concentration worksheet
18.0 R e f e r e n c e s __________ ______________________ ______________________________________ 18.1 The validation report associated with this method is ETS-8-4.0 & 5.0-V -l.
18.2 FACT-M-3.1, "Analysis o f Serum or Other Fluid Extracts for Fluorochemicals using HPLC-Electrospray Mass Spectrometry"
19.0 a f f e c t e d D o c u m e n t s ----------------------------------------- -------------------------------------
19.1 ETS-8-5.1, "Analysis of Serum or Other Fluid Extracts for Fluorochemicals using HPLC-Electrospray Mass Spectrometry"
20.0 R e v i s i o n s ____________________ _________________________________________
Revision Number
1
Reason For Revision Section 12.21 Changed to include sample storage at room temperature
Section 12.13 Added the shaker speed. Section 12.17 Final volume is 1.0 mL; not adjusted for initial volumes
less than 1.0 mL.
Revision Date
04/02/99
3M Environmental Laboratory
ETS-8-4.1 Extraction of PFOS from Serum
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Extraction Worksheet ETS-8-4.1
Study # Matrix Box # Wk/Dav
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 =
"" -
mL
......
Serum Extraction Method
_______________ 1........................................... ........................................... ft Initials-----------
Vortex 15 sec. Pinette Matrix
.... ...... .....................................................................................................................
Volume
mL
Pipette 1 mL of 0.5 M TBA, pH 10. pH =
Std. #
. ..
Pipette 2 mL of 0.25 Na?COV0.25M NaHCOt 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 aliquot of organic layer
.
Put on Nitrogen Evaporator to dryness
Add methanol
Volume
Temperature: 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.
Attachment A 3M Environmental Laboratory
ETS-8-4.1 Extraction of PFOS from Serum
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MDL/LOQ values for rabbit serum
Compound
MDL (PPb)
LOQ Linear Calibration Range (LCR) (PPb) Approximate concentrations to be used for preparing the
Standard Calibration Curve
PFOS
1.74 5.55 5 ppb - 1000 ppb
PFOSA
1.51 4.79 5 ppb - 1000 ppb
PFOSAA EtFOSE-OH
3.46 11.4
20.5 5 ppb - 1000 ppb 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
ETS-8-4.1 Extraction of PFOS from Serum
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Compound: PFOS
Prepared range Rabbit Serum of 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 o f 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
LCR from curve (ppb)
(ng/mL) 4.93 - 976
4.93 - 97.6
24.8 - 978
4.93 - 976
LCR from curve (ppb)
(ng/mL) 24.7 - 974
9.74 - 247
97.4 - 974
9.74 - 974
% Recovery Range
83-108 85-104 85-106 94-111
% Recovery Range
88-103 87-105 93-102 94-103
% 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 3M Environmental Laboratory
ETS-8-4.1 Extraction o f PFOS from Serum
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Com pound: 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 (pph)
(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
Compound: 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/mL) 24.8 - 976
9.76 - 248
49.3 - 976
9.76 - 976
% Recovery Range
96-106 91-110 86-106 95-117
Com pound: MS56 Prepared range
Rabbit Serum of 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/mL) 24.8 - 976
9.76-97.6
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 3M Environmental Laboratory
ETS-8-4.1 Extraction of PFOS from Serum
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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:
Method/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 0.500
0.507 0.507
0.532 0.532
0.501 0.501
0.521 0.521
5.00 5.07 5.32 5.01 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
532
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 Am't 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
Calculated concentrations of standards in the sample matrix
PFOS Final cone
ng/mL
4.93 9.76 24.8 49.3 97.6 248 493 735 976
PFOSA Final cone
ng/mL
5.00 9.89 25.1 50.0 98.9 251 500 746
989
PFOSAA Final cone
ng/mL 5.24 10.4
26.3 52.4
104 263 524 782 1038
EtFOSE Final cone
ng/mL 4.94
9.78 24.8 49.4 97.8 248 494 737 978
PFOSEA M556
Final cone Final cone
ng/tnL
ng/mL
5.01 1 5.13
9.93 10.2
25.2 25.8
50.1 51.3
9 9 3 102
252 258
501 S13
749 766
993 1017
Surrogate Std cone ng/mL
100
Surrogate Final cone
ng/mL 500
All Am't spiked
mL 0.005
Validated ranges - approximate concentrations
Serum
PFOS
PFOSA
PFOSAA EtFOSE-OH PFOSEA
M556
Rabbit
5.00-1000 | 5.00-1000 1 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 of PFOS from Scrum
3M Environmental Laboratory
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3M Environmental Laboratory
M ethod
A n alysis q f P o ta ssiu m P erflu o ro o cta n esu lfo n a te o r O t h e r F l u o r o c h em ic a ls in Seru m E xtra cts U sin g H P L C -E lectro spr a y /M ass Spec tr o m etr y
M ethod N um ber: ETS-8-5.1
Author: Lisa Clemen, Robert Wynne
Approved By:
vM
Laboratory Manager
--
Group Leader
t j Z-*------------- -
Technical Reviewer
Adoption Date: 03/01/99 Revision Date: ^
`i / z c , Date 1 /U , Date oh I w Date
1.0 S c o p e a n d A p p l i c a t i o n __________ _______________________________________________________ 1.1 Scope: This method describes the analysis o f serum extracts for fluorochemical surfactants
using HPLC-electrospray/mass spectrometry.
1.2 Applicable Com 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.
Word 6/95
ETS-8-5.1 Analysis of Serum Extract Using ES/MS
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2.0 S u m m a r y o f M e t h o d _________________________________________________________________
2.1 This method describes the analysis of 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 of a particular fluorochemical, such as the perfluorooctanesulfonate (PFOS) anion, m/z= 499. Additionally, samples may be analyzed using a tandem mass spectrometer to further verify the identity of a compound by detecting daughter ions o f the parent ion.
3.0 D e f i n i t i o n s ___________ _________________________________________________________________
3.1 A tm ospheric Pressure Ionization (API): The Micromass Quattro II triple quadrupole systems allow for various methods of ionization by utilizing various sources, probes, and interfaces. These include but are not limited to: Electrospray Ionization (ESI), Atmospheric Pressure chemical Ionization (APcI), Thermospray, etc. The ionization process in these techniques occurs at atmospheric pressure (i.e., not under a vacuum).
3.2 Electrospray Ionization (ES, 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 of a strong electrical field.
3.3 Mass Spectrometry, Mass Spectrometer (MS), Tandem Mass Spectrometer (MS/MS): The API Quattro II triple quadrupole systems 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 (MS/MS) for more specific fragmentation information.
3.4 Conventional vs. Z-spray probe interface: The latest models 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 of operation, cleaning, and maintenance are the same. However, Z-spray components and conventional components are not compatible with one another, but only with similar systems (i.e., Z-spray components are compatible with some other Z-spray systems, etc.)
3.5 M ass Lynx Software: System software designed for the specific operation o f these Quattro II triple quadrupole systems. Currently MassLynx has Windows 95 and WindowsNT 4.0 versions. All versions are similar. For more details see the manual specific to the instrument (Micromass Quattro II triple quadrupole MassLynx or MassLynx NT User's Guide).
4.0 W a r n i n g s a n d C a u t i o n s ____________________ __________________________________________
4.1 Health and Safety W arnings:
4.1.1 Use caution with the voltage cables for the probe. When engaged, the probe employs a voltage of 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 of 400 bar (5800 psi) back pressure. If the back p ressu re exceeds 400 bar, the HP1100 w ill initiate au to m atic sh u td o w n .
4.2.2 Do not run solvent pumps to dryness.
5.0 In t e r f e r e n c e s _____________ ___________________________________________________________
5.1 To minimize interferences when analyzing samples, teflon should not be used for sample storage or any part of instrumentation that comes in contact with the sample or extract.
6.0 E q u i p m e n t __________________________ __________________________________________________
6.1 Equipment listed below may be modified in order to optimize the system. Document any modifications in the raw data as method deviations.
6.1.1 6.1.2
Micromass Quattro II triple quadrupole Mass Spectrometer equipped with an electrospray ionization source
HP 1100 low pulse solvent pumping system, solvent degasser, column compartment, and autosampler
7.0 S u p p l i e s a n d M a t e r i a l s __________________ _____________________________________________
7.1 Supplies 7.1.1 High purity grade nitrogen gas regulated to approximately 100 psi (House air system) 7.1.2 HPLC analytical column, specifics to be determined by the analyst and documented in the raw data. 7.1.3 Capped autovials or capped 15 mL centrifuge tubes
8.0 R e a g e n t s a n d S t a n d a r d s ____________________________ _________ ________________________ 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 Milli-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 S a m p l e H a n d l i n g
___________________________________________________________
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 If analysis will be delayed, extracted standards and samples can be refrigerated at approximately 4 C, or at room temperature, until analysis can be performed.
10.0 Q u a l i t y C o n t r o l ____________________________________________________________________ 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, with a minimum of 2 spikes per batch.
10.2.4 Matrix spike and matrix spike duplicate concentrations will fall in the mid-range o f the initial calibration curve. Additional spike concentrations may fall in the lowrange of the initial calibration curve.
103 Continuing Calibration Verifications
10.3.1 Continuing calibration verifications are analyzed to verify the continued accuracy of the calibration curve.
10.3.2 Analyze a mid-range calibration standard after every tenth sample, with a minimum of one per batch.
11.0 C a l i b r a t i o n a n d S t a n d a r d i z a t i o n
_______________________________________________
11.1 Analyze the extracted matrix standards prior to and following each set o f extracts. The average of two standard curves will be plotted by linear regression (y = my + b), weighted 1/x, not forced through zero, using MassLynx or other suitable software.
11.2 If the curve does not meet requirements, perform routine maintenance or reextract the standard curve (if necessary) and reanalyze.
11.3 For purposes of accuracy when quantitating low levels of analyte, it may be necessary to use the low end of the calibration curve rather than the full range of the standard curve. Example: when attempting to quantitate approximately 10 ppb of analyte, generate a calibration curve consisting of the standards from 5 ppb to 100 ppb rather than the full range of the curve (5 ppb to 1000 ppb). This will reduce inaccuracy attributed to linear regression weighting o f high concentration standards.
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12.0 P r o c e d u r e s ________________________________________ _____________________ ______________ __ 12.1 Acquisition Set up
12.1.1 Click on start button in the Acquisition Control Panel. Set up a sample list. Assign a filename using MO-DAY-last digit o f year-sample number, assign a method (MS) for acquiring, and type in sample descriptions.
12.1.2 To create a method click on scan button in the Acquisition control panel and select SIR (Single Ion Recording) or MRM. Set Ionization Mode as appropriate and mass to 499 or other appropriate masses. A full scan is usually collected along with the SIRs. Save acquisition method. If MS/MS instruments are employed, additional product ion fragmentation information may be collected. See Micromass MassLynx 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 of extracted matrix standards and ends with a set of 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 Using the Autosam 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 HP 1100/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 jiL injection
12.2.2.2 Inject/sample = 1
12.2.2.3 Cycle time = 13.5 minutes
12.2.2.4 Solvent ramp =
Time
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 Instrum ent Set-up
12.3.1 Refer to ETS-9-24.0 for more details. 123.2 Check the solvent level in reservoirs and refill if necessary.
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12.3.3 Check the stainless steel capillary at the end of the probe. Use an eyepiece to check the tip. The tip should be flat with no jagged edges. If the tip is found to be unsatisfactory, disassemble the probe and replace the stainless steel capillary.
12.3.4 Set HPLC pump to "On". Set the flow to 10 - 500 uL/min or as appropriate. Observe droplets coming out of the tip of the probe. Allow to equilibrate for approximately 10 minutes.
12.3.5 Turn on the nitrogen. A fine mist should be expelled with no nitrogen leaking around the tip o f the probe. Readjust the tip o f the probe if no mist is observed.
12.3.6 The instrument uses these parameters at the following settings. These settings may change in order to optimize the response:
12.3.6.1 Drying gas 250-400 liters/hour 12.3.6.2 ESI nebulizing gas 10-15 liters/hour 12.3.6.3 HPLC constant flow mode, flow rate 1 0 -5 0 0 pL/min 12.3.6.4 Pressure <400 bar (This parameter is not set, it is a guide to ensure the
HPLC is operating correctly.)
12.3.7 Carefully guide the probe into the opening. Insert probe until it will not go any further. Connect the voltage cables to the probe.
12.3.8 Print the tune page, with its parameters, and store it in the study binder with a copy taped into the instrument log.
12.3.9 Using the cross-flow counter electrode in the ES/MS source is recommended for the analysis of biological matrices.
12.3.10Click on start button in the Acquisition Control Panel (this may vary among MassLynx versions, see appropriate MassLynx USER'S GUIDE). Press the start button. Ensure start and end sample number includes all samples to be analyzed.
13.0 D ata Analysis and Calculations__________ __________________________________ 13.1 Calculations:
13.1.4 Calculate matrix spike percent recoveries using the following equation:
% Recovery = Observed Result - Background Result x 100 Expected Result
13.1.5 Calculate percent difference using the following equation:
% Difference = Expected Cone. - Calculated Cone, x 100 Expected Cone.
13.1.6 Calculate actual concentration o f PFOS, or other fluorochemical, in matrix (pg/mL):
fng o f PFOS calc, from std. Curve x Dilution Factor) x 1 u e (Initial Volume of matrix (mLl + mL o f Surrogate Standard) 1000 ng
Final Volume (mL)
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14.0 M e t h o d P e r f o r m a n c e __________________ ____________________________________________ 14.1 Method Detection Limit (MDL) and Limit of Quantitation (LOQ) are method, analyte, and
matrix specific. Please see ETS-8-4.1, Attachm ent B, for a listing of current validated MDL and LOQ values.
14.2 Solvent Blanks, Method Blanks, and Matrix Blanks
14.2.1 Solvent'blanks, method blanks, and matrix blanks values are must be below the lowest 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% of 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 If criteria listed in this method performance section isn't met, maintenance may be performed on the system and samples reanalyzed or other actions as determined by the analyst. Document all actions in die appropriate logbook.
14.7 If data are to be reported when performance criteria have not been met, the data must be footnoted on tables and discussed in the text o f the report.
15.0 P o l l u t i o n P r e v e n t i o n a n d W a s t e M a n a g e m e n t
_______________________________
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 following information included either in the header or hand written on the page: study or project number, acquisition method, integration method, sample name, extraction date, dilution factor (if applicable), and analyst.
16.2 Print the tune page, sample list, and acquisition method from MassLynx to include in the appropriate study folder. Copy these pages and tape into the instrument runlog.
16.3 Plot the calibration curve by linear regression, weighted 1/x, then print these graphs and store in the study folder.
16.4 Print data integration summary, integration method, and chromatograms, from MassLynx, and store in the study folder.
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ETS-8-5.1 Analysis of Serum Extract Using ES/MS
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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 of a summary spreadsheet.
16.6 Back up electronic data to appropriate medium. Record in study notebook the file name and location of backup electronic data.
17.0 T a b l e s .D i a g r a m s . F l o w c h a r t s , a n d V a l i d a t i o n D a t a ____________________________ 17.1 Attachment A: 'ETS-8-5.1 Data summary spreadsheet.
18.0 R e f e r e n c e s ___________________________________ _______________________________________ 18.1 FACT-M-4.1, "Extraction of Potassium Perfluorooctanesulfonate or Other Fluorochemical
compounds from Serum for Analysis Using HPLC-Electrospray/Mass Spectrometry
18.2 ETS-9-24.0, "Operation and Maintenance of the Micromass Atmospheric Pressure Ionization/Mass Spectrometer Quattro II triple quadrupole Systems"
18.3 The validation report associated with this method is ETS-8-4.0 & 5.0-V-l.
19.0 A f f e c t e d D o c u m e n t s ______________ _____________ ___________________________________ 19.1 ETS-8-4.1, "Extraction o f Potassium Perfluorooctanesulfonate or Other Fluorochemical
Compounds from Serum for Analysis Using HPLC-Electrospray/Mass Spectrometry"
20.0 R e v i s i o n s ------------------ -------------------------------------------
Revision _ Number.
Reason For Revision
1 Section 6.1.2 Clarification of 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 of the curve.
Section 12.2.2.4 Clarification o f solvent ramp.
Section 17.1 Changed from attachment B to A.
Revision Date
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 of Extraction/Analyst:
Date of 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
Analysis of Serum Extract Using ES/MS
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Appendix D: Data Sum m ary Tables
Table 12. Reported Fluorochemical Levels in Sera Analyses in Study FACT TOX-013
Dosage Group
Specimen 10
PFOS (pg/mL)
1 10097F
0.0394
1 10105F
0.0181
1 10106F
0.0258
1 10107F 1 10108F
0.0343 0.0253
1 9922M* 1 9930M*
0.0115 0.0134
1 9931M
0.00725
1 9932M
0.0162
1 9933M*
0.0156
II 10121F II 10126F
9.62 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 III 10164F
76.1 49.6
III 10172F
68.4
III 10177F
42.2
III 9997M
108
III 9999M*
178
III 10001M
94.9
III 10002M III 10004M
113 130
IV 10187F IV 10194F
89.5 73.4
IV 10203F
126
IV 10211F
99.7
IV 10214F
98.3
IV 10019M
302
IV 10024M*
477
IV 10029M* IV 10033M IV 10034M
296 272 249
* - Tentative values, initial volume was <0.5 mL
PFOSA (pg/mL)
<LOQ (4.79 ppb)
<LOQ (4.79 ppb) <LOQ (4.79 ppb)
<LOQ (4.79 ppb) <LOQ (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
.
0.481
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)
M666 (pg/mL)
<LOQ (38.2 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)
Doeage 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 10045M
326
V 10051M
162
V 100M M
182
NR - Sample not received or reported
* * Tentative velues, 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 (pg/mL)
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)
M556 (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
Doeage Group
I I I I I I I I I I I I 1 1 1 II II II II II II II II II II II II II II II
Specimen ID
10097F 10105F 10106F 10107F 10108F 9922M 9930M 9 9 3 1M 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 39.8 23.7 22.1 116 102 89.9 80.7 87.3 M .7 67.8 53.7 28.0 71.5
PFOSA (pg/g)
<LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ 0.514 0.708
1.40 0.601 0.508 4.49 4.10 2.88 3.68 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 <LOQ <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 14.8 9.44 2.82 6.55
M558(pg/g)
<LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ <L0Q <LOQ <LOQ <LOQ <LOQ <LOQ <LOQ
1.19 1.75 2.88 1.55 1.41 12.8 10.2 11.6 8.95 11.6 5.39 7.75 4.64 3.27 4.58
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Table 13. Reported Fluorochemlcal Levels In Liver Analyses in Study FACT TOX-013
(continued)
_____________________________
Dosage 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
Spscltnsn ID
10155F 10156F 10164F 10172F 10177F 9997M 9999M 10001M 10002M 10004M 1015SM 10156M 10184M 10172M 10177M 10187F 10194F 10203F 10211F 10214F 10019M 10024M 10029M 10033M 10034M 10187M 10194M 10203M 1 0 2 1 1M 10214M 10042M 10044M 10045M 10051M 10054M
PFOS (pg/g)
PFOSA (pg/g)
102 130 179 119 105 415 234 498 257 386 89.0 219 203 188 153 164 240 344 255 264 831 791 556 781 556 226 277 448 457 344 1218 1356 1132 1063 1054
~1
2.22 2.24 1.94 2.17 2.88 10.8 9.41 8.67 8.29 8.41 5.11 6.14 8.26 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 0.93 11.4 8.11 16.4 13.0 10.9 9.80 10.8
PFOSAA (pg/g)
15.6 20.2 22.7 11.9 20.0 73.5 28.6 85.2 34.2 64.9 12.0 27.3 294 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
**858 (pg/g)
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
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Appendix E: Data Spreadsheets
Analytical Report: FACT TOX-013 LRN-U2095
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8
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3M Environmencal Laboratory
g
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?*3
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MM vdutM below05 bL. LAC01/31/00
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3M Environmental Laboratory
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,1
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3M Environmental Laboratory
it l3
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A fp 411409. Two-GcacnAJGo RqrDdoctioB Study of EtTOSE-OH lo R*u EiFOSE-OH (T-Ali)
NuobofTctt SobfUncv):
3M Environmental Laboratory
i
A
9s
t ji
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8
Taudvevahiet.iAhUlvnigratbtlovO-5mL. L A C O t ft lA D
3M Environmental Laboratory
A
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Appendix F: Example Calculations
Formula Used for Sera Analyses in Study FACT TOX-013
AR (ng/mL) * DF x SC x FV (mL) x 1.0 ng x PC = Reported Concentration (jig/mL) EV (m L)' lOOO ng
Calculation Used for Group 4, Animal 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 mL 1000 ng
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 of sera extracted PC-- PFOS purity correction factor (86.4%)
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Appendix G: Contract Lab Report
This appendix includes the following contract laboratory report:
Battelle Memorial Institute, Study Number. N003604-D, 2 (N-Ethylfluorooctanesulfonamido)-ethanol in Two Generation Rat Reproduction, (59 pages)
3M Environmental Laboratory
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BIOLOGICAL SAMPLE ANALYSIS Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
. . . Putting Technology Ta Work
FINAL REPORT
2 (N-Ethylfluorooctanesulfonamido)-ethanoI in Two Generation Rat Reproduction
SPONSOR
3M Toxicology Services 3M Center
Building 220-2E-02 S t Paul, MN 55144
Study Initiation: September IS, 1998
Testing Facility
Battelle Memorial Institute SOS King Avenue
Columbus, Ohio 43201-2693
Prepared By
PatrickL. South, B.S.
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Batidle StudyNumber. N003604-D 3MEnvironmentalLaboratoryStudyNumber. FACT 060998.1
FINAL REPORT
2 (N-Ethylfluorooctanesulfonamido)-ethanol in Two Generation R at Reproduction
Jod C. Andre, Ph-D. Battelle Principal Investigator
RichardW. Slauter, PLD,, D .T. Battelle SeniorProgramDirector
3M Environmental, Laboratory
u
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Batidle StudyNumber. N003604-D 3MEnvironmentalLaboratory StudyNumber FACT 060998.1
2 (N-Ethylfluorooctanesulfonamido)-ethanol in Two Generation R at Reproduction
EXECUTIVE SUMMARY
Rat liver samples sent to Battelle by 3M Environmental Technology and Services were analyzedby the previously validated method "Method for Analysis of Potassium Pcrfluorooctanesulfonate (PFOS) in Rat Liver by LC/MS/MS". Samples were extracted and analyzed by High-Performance Liquid ChromatographyMass Spectroscopy (LC/MS/MS) for PFOS, M-556, PFOSAA, and PFOSA content only. Related flucrochemicals 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 (pg) per gram ofliver tissue extracted.
3M Environmental Laboratory
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Batidle StudyNumberN003604-D 3MEnvironmentalLaboratory StudyNumber FACT060998.1
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 Date Reported to
to Battelle Task Offiite Study
Phase Inspected
Inspection Date Leader/Battelle Director/
______________ ______________ __________ Management . Management_____
Sample weights Sample homogenization Extraction Sample analysis
10/12/1999 10/12/1999 10/13/1999 10/13/1999
Quality Assurance Unit Battelle Memorial Institute
Date
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Battelle StudyNumber. N003604-D 3MEnvironmentalLaboratoryStudyNumber. FACT060998.1
GOOD LABORATORY PRACTICES COMPLIANCE STATEMENT
Study Title: 2 (N-EthylfluorooctanesuIfonainido)-ethanol in Two Generation R at
R eproduction
This study was conducted in compliance with the Food and Drag 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.
Jon C. Andre, P h D .
.
Battelle Principal Investigator
Kris Hansen, P h D . Study Director
3M Environmental.Laboratory
V
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Battelle Study Number N003604-D 3M Environmental Laboratory Study Number FACT 060998.1
Table of Contents
Executive Summary.....,,.................................... Quality Assurance Statement.............................
Compliance Statement...................................... Table of Contents............................................. 1.0 Introduction............ ............................ 2.0 Reference Substances........................... 3.0 Receipt of Samples .......................... 4.0 Analysis of Samples ............................
4.1 Summary of Method...............
4.2 Results.................................... 4.2.1 Quality Control.......... 4.2.2 Sample Results..........
5.0 Conclusions......................................... 6.0 Acknowledgements.............................. 7.0 Specimen Storage andRecord Archives,
L ist of Tables
'
Table 1. Example of Instrument Parameters Used to Analyze Samples.........................
Appendix A (Results) Summary Results for Rat liver Sample Analysis.................. '........................................
Appendix B (Daily Acceptance Criteria Summary) Daily Acceptance Criteria Summary............................................................... ............
Appendix C (Sample Inventory List) Sample Inventory List................ ...............................................................................
Appendix D (Chromatograms) Representative Chromatograms....................................................................................
Appendix E (Protocol, Amendments, and Deviations) Protocol, Amendments, andDeviations..........................................................................
PFOS Purity Report
Appendix F (PFOS Purity Report)
Page iii iv
.V
vi ,,1 ..1 ..1 ..1 ..1 ..2 ..2
..3 ...3
...4 ...4
2
A -l
B-l
,C-1
D -l
.E-l
.F-l
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Bsitelie StudyNumber N003604-D 3MEnvironmentalLaboratoryStudyNumber. 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 StudyNumber FACT 060998.1 (TOX-013) and the results from this
analysis. See Appendix E for a copy of the study protocol, amendments, andprotocol deviation reports
(signed deviation reports were not available for inclusion here).
'
2.0 Reference Substances The analytical reference substances for this studywere 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 nam* appearing on the Material Safety Data Sheet andbottle label is potassium perfhioroalkyl yilfnnatff The name more commonly used by 3M in analytical methods and correspondence is potassium pCT-fl^t'rfyvtanrunlfnnuti The latter name will be used in this report. Sec Appendix F for purity data supplied by 3M to Battelle. The reference substances were stored atroom temperature.
The surrogate standard was 1H,lH^H,2H-Perfluorooctane sulfonic acid, lot number 59909, supplied by ICN. The surrogate standardwas stored at roomtemperature.
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 underprotocol 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 numberN003604-A). The current version of the method is attached to this report in Appendix E. Samples were analyzedby LG/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 /M S/M SSW cm
AutoNumptcr HPLC |uni|>s Mas* spectrometer Analytical column Mobile phase components Gradient prolile
Injection volume Flow Column temp HPLC pressure MS source Dcsnlvatioii .is Ncliuli/er as Source binds temp Dcsohation letup Cone voltaic
Collision encr" v Collision "as Multiplier Resolution Ions monitored
Total run time Approximate retention times:
Make: Gilson Make: Gilson Make: Micromasa
Model: 234 Models: 30S and 306 Model: Quattro LC with Z-spray source
Keystone Betasil Cl 8, S|im, 2 x 5 0 mm. Part No. 055-701-2
Component A: Ammonium acctatc(2mM):methanol, 60:40, vrv
Component B: Ammonium acetate(2mM)nnethanol, 5:95, vrv
p n je, min
%B Flow. mlAnin
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 c o lu m n flow at start split to 20 nL/min into the MS
Ambient
Approximately 840 psi at gradient start
Electrospray, Negative Ion
Nitrogen at ~575 L/hr
Nitrogen at -8 0 L/hr
140C 250*C
70 V for SS, PFOS 20 V for M-556, PFOSAA. PFOSA
40 eV
Argon, gas cell, a t--2.5x10 mb
650 V 12.0 for M SI; 10.0 for MS2
427>81 MEM transition for SS 499>99 MEM transition for PFOS 556>78 MRM transition for M-556 584>169 MRM transition for PFOSAA
49S>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 StudyNumber. N003604-D 3MEnvironmentalLaboratoryStudyNumber FACT060998.1
4.2.1 Quality Control
System suitability acceptance criteria were established during the method validation and are included in Appendix C, 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 undilutedhomogenates. After the data were reviewed, dilutions of the homogenates were performed in order to bring analyte concentrations within the calibration range. The first analysis-thatprovided 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 standardwhich meets acceptance criteria for accuracy (25% RE). 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 notationALOQ denotes "Above Limit of Quantitation" for samples thathad concentrations higher than the theoretical concentration for the 13 pg/g calibration standard. Samples that were initially ALOQ were diluted with blank liver homogenate andre extracted. Samples thatwere expected to be ALOQ were first dilutedwith blank liverhomogenate 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) ofPFOS was calculated to be 0.0173 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 ofthe 7 reps by their standard deviation. The method of MDL determinationwas providedby 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
T itle
Jon C. Andre, PLD. Richard W. Slauter, Ph.D., DA.B.T. PatrickL. South, B.S. Gerke H. van der Zwaag, MS. Bobby C. Braswell, B.A. Cynthia J. Ryan, B.S.
Battelle Principal Investigator Senior ProgramDirector Mass spectroscopist ' Sample preparation chemist Quality assurance auditor Lead quality assurance auditor
7.0 Specimen Storage and Record Archives
All original paper H as well as electronic copies of data, will be forwarded to 3M for archival. Copies ofboth the final report and all original paper data generated in conjunction with this studywill be maintained by Battelle. All residual liver samples, extracts, andunused test article will be disposed of or returned to the Sponsor as directedby the Sponsor.
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APPENDIX A -RESULTS
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' Battelle Study Number N003604-D 3M Environmental Laboratory Study Number: FACT 060993.1
rr o * . im m , m t M , m u
BOX STUDY; AOSMnrr SOATWAAK w r n is :
in r a t u v e a
N0099040
MANUALLY
CXCSLfT
Seelbio
Date Qrono
Animal Number
Sampln TYo
P fOS Cono,
1
2 3 4
9 7 9
10 11
12 13 14
15 1 17
1 1 20 21
22 29 24 29 20
27 2 29 30 91 32 99 94 35 99 97 99 99 40 41 42
43 44 * 49 49 47 49 49 so S1
S3 S3 94 99 99 57
99 SB fio
92 83 94
as
1 1 1
1
1 2 2 2 2
2 3 3 3 3 3 4 4 4 4 4 9 a
s8
9 1 1 1 1 1 2 2 2 *2 2 3 3 3 3 3 4 4 4 4 4
1 1 1 1 1 2 2 2 2 2 3 3 3 3 3
4 4 4 4 4
b lo o * seLCvy murr o f q uantttaticn
8822 0830 0831
8832
0093 88S1 0094 8888 0897
8870 0007 0000
io ao i 10002 10004 10019 10024
10029 10033 10034 10CVQ 10044 10049 10091 10094 10007 10109 10109 10107 10108 10139 10140 10142 10121 10128
10177 10155 10156 10104 10172 10157 10184 10203 10211
10214 10087 10106 10106 10107 10109 10139 10140
10142 10121 10128 10177 10195 10150 10164
10172
10167 10164 10203 10211 10214
Matama! M atan*
Mamma!
M eam al
Mctnel Mamma! Mamma! Mamma! Matern Matern Metern Metern Mamma! Mamma! Metern Metern Matern
Mamma! Mamma! Mamma! Mamma!
Mamma! Mamma! Matama! Matamal
Fat! Fata! Fata! Fata! Fata! Fatal FtCM Fatal Fata! Fata!
Fatal Fatal Fatal Fata! Fatal Fata! Fata! Fata1 Fata!
Fatal Matamal Mamma! Mamma! MammaJ Mamma! Matama! Mamma! Matama! Matama! Matama! Mamma! Mamma! Matama! Mamma! Mamma!
Matama! Mamma! Matama! Mamma!
Matama!
-77E-Q1 0.446-01 9.88E-01 106HM
1.176*00 1.346*02 1.196*02 146*02
9.346*01 1.016*02 4306*02 2.716*02 9.798*02 4976*02 4476*02 .526*02 9.196*02 4436*02 9.046*02 4436*02 1416*01 1.876*01 1 16*03 1 3 6 *0 3 1 2 6 *0 3 1.7SE-01
BUM 1.406*01
BLOQ BLOQ 4.11 EH
2.746*01 4506*01 4906*01 2.66EHH U 1M 1.166*02 1.506*02 4076*02 1 0 6 *0 2 1.906*02 2.796*02 3.906*02 266*02 3.096*02 3.206*01 2.606-01 2.816-01 n s s E -o i 2.006-01 1 8 *0 1 346*01 4298*01 4336*01 7.966*01 1.776*02 1.036*02 236*02 2.366*02 2.106*02 2.526*02 316*02
L253
Analysts dete key:
Normal tont October 13,1888 Undertine - Octobor 13 It M M d O c tet 18,1989
M S L U ttH M M " O d cb arX , 1888
Alt samples undiluted All samplaa undiluted
All samplaa diluted All samples diluted
M-3S0
C0IM p rt
P ro sa* Cene,
Ilfl/S
PPQSA Cene,
llfl/t
BLOQ BLOQ BLOQ BLOQ BLOQ 18E*01 1.036*01
U C E itt fi.966HM 1.166*01 5 6 6 *0 1 3*936*01 4946*01 4906*01 4496*01 4496*01 4786*01 7326*01 1.176*02 4226*01 1 5 6 *0 2 1 2 6 *0 2 1 3 6 *0 2 1.196*02 1.918*02
BLOQ BLOQ 8LOQ BLOQ BLOQ 4666*00
1 .H -09 m esa
4166*00
U TS *sa 7.see*00 441 EHM
.a 7 E *M 1 9 6 *0 1 4556*01 4556*01 4796*01 4336*01
BLOQ BLOQ BLOQ BLOQ BLOQ 4946*00 3.2TEU 0 |. W 0 5e*00 7.786*00 4146*01
1.136*01 4336*01 0 1 6 *0 1 4996*01 4996*01 4366*01 4716*01 4346*01 4456*01
BLOQ BLOQ BLOQ BLOQ BLOQ 1.106*01 1.506*01
in e - 4826*00
7.388*01
4526*01 i*a e o i 4496*01 ija e n a i* U 2M I 1js e n a 1 56 *0 2 ij o e - o* 4006*02 1.MCKJ3 1 7 6 *0 2 1.586*02
BLOQ BLOQ BLOa BLOQ BLOQ 4016*00
Z97Et<M Z 9 Z E -S 9 4906*00
4006*01 156*01 4026*01 4276*01
1.196*01 4116*01 4156*01 4366*91 4566*01 4146*01
BLOQ BLOQ BLOQ BLOQ BLOQ 4446*00 4826*00 8.3S E * 4576*00 1.406*01 1.716*01
1.H W 1
4736*01 4946*01 4376*01 4746*01 4366*01 7.006*01 4526*01 4006*01
BLOQ WLOQ BLOQ
BLOQ
BLOQ 4.496*00 4.106*00
Z flS ftS fl 3.506*00 6.426*00
1.096*01
ftJ lE iflQ AJZESfla 42S fl 4416*00 19C01 1.106*01 1.126*01 106*01
L106MM 1 .*< e *d 1 1306*01 U B E *fil 9.aoe*oo 1.M E-01
BLOQ
BLOQ BLOQ BLOQ BLOQ 1.406*00
8.016-01 4056-01 n ia l
Z&B&91 4886*00 46+O fl
2.24& 00 1.846M 4176*00 4906*00 4.066*00
H iE rflli 3.38&CQ 4506*00
BLOQ BLOQ BLOQ BLOQ BLOQ Z 3 S 6 -0 0
1 2 2 fc S B ZOSEN 1.S0EK zsa& oo 4916*00 5.116*00 4146*00 4296*00 5 206*00
S.3SEH 9.906*00 4996*00
w -E ta t 4116*00
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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 pg/g
Calculated Concentration of Replicate 1 Calculated Concentration of Replicate 2 Calculated Concentration of Replicate 3 Calculated Concentration of Replicate 4 Calculated Concentration of Replicate 5 Calculated Concentration of Replicate 6 Calculated Concentration of 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
iiiiiiiiiiiiiin g g n m
S/N
n
0.1331 7.88
^ il
is
LOQ (det from 10 x std.dev. "noise") LOQ (det from cal curve low std.)
Curve Coeff of Determination
Date analyzed . Method
i 0.17005 0.1331
0.9978
130ct99 LC/MS/MS
Kev 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 of Det of calibration curve unacceptable
PFOSAA
0.1484 0.1281 0.1484 0.1605 0.1661 0.1513 0.1385
PFOSA
0.1167 0.1325 0.1521 0.1441 0.1490 0.1382 0.1413
0.1488 0.0128
0.1391 0.0119
0.1334
0.1315
IlllflliillP J I
11.66
11.74
msm^SSMmm: M I S S
0.12763 0.1334
0.11853 0.1315
0.9937
0.9891
130ct99 LC/MS/MS
130ct99 LC/MS/MS
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APPENDIX B-DAILY ACCEPTANCE CRITERIA SUMMARY
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PFOS e t ai IN RAT UVER STUDY NUMBER: N003804-0
DATA ENTERED: MANUALLY
SOFTWARE:
EXCEL 97
REGRESSX3N PARAMETBtt
Anatvale Date OcU mt 13,1008
October 16,1808
October 1ft, 1808
October 30,1800
AnaM e
PFOS M 466 PFOSM PPOSA
PfO S UAt PFOSAA PFOSA
p ros M-596 PFOSAA PFOSA
PFOS PFOSA
x *c o r
-0.0164 4100640 0.00232
-156
4100368
000360 -250
a00383 a 0221 aoosTo -71.
aooeis -153
x c o *r
a ez7 0.0070 1.S0E+O4
1J2 0576 aoesi 1 .7 3 60 4
2.17 0.512 a06S3 1.236*04
2.07 1.666*04
Intercept
0.0772 410213 4100388
873
4100820 4100607 410Q321
-866
410805 4100268 41000603
722
410361 1.026*03
CoafTaf Determination
0864 0986 0984 0.988
0988 0986 0986 0980
0966 0964 0983 0.986
0987 0.988
Ceieiaantef Deviations
One n p <* Cel pt 1 dueled One reo of Cal p|1 duded One rap of eel pt7 eluded One rep of eel pt 5 duded
One rap of cal pt 7 oiduded One rep of pto 1 ,3 ,6 eluded
One rep of pta 4 ,7 eluded
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PFOS t al IN RAT LIVER
STUDY NUMBER: N003604-D
DATA ENTERED: MANUALLY
SOFTWARE:
EXCEL 97
QC Result A nalysis Oats
October 13,1969
AnM e PFOS
M-556
PF08AA
PFOSA
October 18,1989 ...
PFOS M-559 PFOSAA PFOSA
October 18,1999
PFOS M-556 PFOSAA PFOSA
October 20,1999
PFOS PFOSA
QC Level. no/m L
10 3.3 0.7 0.19 10 3.3 0.7 0.18 10 3.3 - 0.7 0.18
10 3.3 0.7 0.18
10 3.3 0.7 0.18 10 3.3 0.7 0.18 10 3.3 0.7 0.16
10 3.3 0.7 0.18
10 3.3 0.7 0.18 10 M 0.7 0.18 10 3.3 0.7 0.16
10 3.3 0.7 0.16
10 3.3 0.7 0.18 10 3.3 0.7 0.18
%RSD
%RE
6.6
3.8 7.9 3.1
4.7 11.7 3.0 11.5 8.3 5.1 8.7 14.5 16.9 9.2
5.8 4.6
-4 .0 4.8 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
5.5 4.5 8.3 9.7 3.4 2.7 8.0 17.7 4.3 2.1 7.4 17.7 11.8 8.1
8.0 8.8
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
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 11.3 12.6
I *....
2.4 2.0 3.7 5.3 2.3
4.0
2.3 3.4
4.5 -1 .7 -20.3 -6.1 2.9 23.4 11.8 13.4 0.8 1 .8 20.6 -18.5
0.0 13.7 0.0 18.0
*4.0 -12.0 -21.7 16.0 -1.8
U 1.9 11.3
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APPENDIX C-SAM PLE INVENTORY LIST
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.' Battelle Study Number. N003604-D 3M Environmental Laboratory Study Num ber FACT 060998.1
Study TOX-013, A rsu* 418-009. Sample Infemnagon fe r hum ant to H ltM la
Sam p i* 1 2 3 4 s 8
7 8 9 10 11 12 13 14 IS 16 17 18 10
20
21
22 23 24 25
2a 27 28 29 30 31 32 33 34 35 38 37 38 39 40 41 42 43 44 45 48
47 48 49 so 51 52 53 54 55 58 57 58 50 80 81 62 63 64 65
v! uJI
f oo
6u. u5.
S am e l* c rip tion
FO -9922-flrpl-M FO-9030-Ofpl-M
F3-Se31-arp<-M FO -9932-grpl-M P3-9933-grpl-M F O -9961-grpll-M FO -9664-orpll-M FO-9965-oipH-M FC-9987-Qrpll-M FO-9970-orpH-M F0-S097-flrpm -M F0-B 999-0fpm -M FO -10001-tjrpllFM F0-100Q2-grpHI-M FO -10004-crpllU it F 0 -1 0 0 1 9 -crp tV -M FO -10024-prplV -M F0-1002om lV-M FO -10033-grplV -M FO-10034-prptV-W F0-10042-grpV-M FO-10044-grpV-M FO-10045-grpV-M F 0-10051-g rp V-M FO-10054-grpV-M
FO-10097-grpl-F F0-10105-gtpl-F FO-10106-grpl-F F0-10107-grpl-F FO-10108-grpl-F F O -10138-orpll-F FO-10140-btpU-P FO -10142-grpll-F I F0-10121-orpll-F F0-10126-grpN-F FO-10177-prpm-P FO-10155-grpHt-F F O -l015& -grplU -F
FO -10184-grpm -f1 FO -10172-grpW -F F C -1018 7-g rplV -F
FO -10203-grplV -F FO-10 2 1 1 -g rp iV -F FO -10214-grplV -F FO-10007-OPpl-F FO-10105-grpl-F
FO-10106-grpl-F FO-10107-grpl-F F 0 -1 0 1 0 6 ^ rp t-F FO -10136^jtpll-F FC-1014O-gtpU-F FG-10142-grpH-F FO-10121-grpH-F FO-10128-grpH-F FO -10177-fliplll-F F 0 -10 155-ffplll-F
F0-10164-grplll-F FO -10172-grpM -F FO -10187-orplV -F F0-10194^rpfV -F i FO-10203-orpIV-F I F0-10211-qrplV-F i FO-10214-grplV-F
3 a m p l*T y p *
ttetam al R a tU w
Ktatem al R a tU w
Aatamal R atU var
lU tam al Rat LN *r
4atamai R a tU w
itatam al Rat U v*r
iatamai R a tU w
d a te ra i R atU var
datarm i R atU var
datarne! R atU var
da tarm i Rat U v*r
idatam al Rat Uvar
s ta rn a i R a tU w
Maternal R a tU w
Maternal R a tU w
Matam al R a tU w
Maternal R a tU w
Matamal R a tU w
Maternal R a tU w
Matamal Ral U w
Matamal Rat U w
Maternal R a tU w
Matamal R a tU w
Maternai Rat U var
Matamal R a tU w
Fatal U w
Fatal U w
Fatal U w
Fatal Uvar
Fatal U w
Fatal U w
Fatal Uvar
Fatal U w
Fatal U w
Fatal U w
Fatal U w
Fatal U w
Fatal U w
Fatal Uvar
Fatal U w
Fatal Uvar
Fatal Uvar
Fatal Uvar
Fatal U w
-
Fatal Uvar
Matamal R a tU w
Matamal R a tU w
Matamal R a tU w
Matamal R a tU w
Matom ai Rat U var
Maternal R a tU w
Maternal R a tU w
Matamal R a tU w
Maternal Rat U w
Maternal Rat U w
Matamal R a tU w
Matamal R a tU w
Matamal R a tU w
Matamal Rat U w
Matamal R a tU w
Matamal R a tU w
Matamal R a tU w
Matamal R a tU w
Maternal R a tU w
M aternal Rat U w
'
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APPENDIX D-KEPRESENTATIVE CHROMATOGRAMS
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.1
4
a
i
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APPENDIX E-PROTOCOL, AM ENDM ENTS, AND DEVIATIONS
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rfrrt.T - 7"<0/t - D/~i
3M E n v ir o n m e n t a l L a b o r a t o r y _________________________
Protocol - Analytical Study 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-EtFOSJB-OH)
Name and address of Sponsor: `
Marvin Case 3M Toxicology Services
3M Center Building 220-2E-02 S t Paul, MN 55144
-
Name and address of testing facility: 3M Environmental Technology and Services 935 Bush Avenue, Building 2-3E-09
. S t 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
'
/ . .
'j.rr'r
fc . ' '
:
Kris Hansen Study Director
_______ i f i s l v i .
Date Marvin Case
Date
Sponsor Representative
i
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Analytical Report: FACT TOX-013 _ LRN-U2095
Battelle Study Humber. N003604-D
3M Environmental Laboratory Study Number FACT 060998.1
The analytical portion of this dosing study is designed evaluate the levels of perfluorooctane
sulfrmte (PFOS), or another metabolite of 2(N-ethylperfluorooctanesulfonamido>ethanol (N-
EtFOSE-OH)
by the study director, in the liver of the parentand subsequent
generations of the test system, or in the serumas necessary.
The in life portion of this study was conducted at Argus ResearchLaboratories.
2.0 Regulatory Compliance_________________________________________________
This study is conducted in compliance with the Food andDrug Administration GoodLaboratory Practices regulation as stated in 21 CFR 58. Any exceptions will be noted in the final report.
3:0 Tk?t 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: Ratliver andserum
3.1.3 Analytical control substance: Hone
3.1.4 Analytical control substance matrix: Ratliver andserum
'
3.2 Source of materials
3.2.1 Analytical reference substance: 3M Specialty Chemical Division; traceability information will be included in the final report
3.23 Analytical reference substance matrix: Argus ResearchLaboratories; traceability information will be included in the final report
3.2-3 Analytical control matrix:
3JL3.1 .Rat liver-Argus Research Laboratories; traceability information will be included in the final report; or
Rabbit liver- Covance Laboratories; traceabilityinformationwill be included in the final report
VTt ?. Rat serum - Sigma ("hemlca! Company; traceability informationwill be included in the final report
33 Number of test and control samples. Liver samples for testing were received from40 test animal 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 aletterfollowedby the Argus project number, the animal number, the group designation, and the drawdate.2
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Analytical Report: FACT TOX-013 LRN-U2 095
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 die
responsibility of the Sponsor.
3.7 Storage conditions for test materials: Test materials are stored atroomtemperature. Samples are stored at-20 10 C.
3jj Disposition of test and/or control substances: Biological tissues andfluids are retained per GLPregulation.
2 3 Safety precautions: Refer to the material safety data sheets of chemicals used. Wear
appropriate laboratoryattire, andfollow adequate precautions forhandlingbiological
materials andpreparing samples for analysis.
-
4.0 Experimental - Overview
---------------------------------------------------------- ;--
Tissues fromanimals dosed as described in Argus Research Laboratories Protocol #418-009 are received for analysis of fluorine compounds. At the discretion of the StudyDirector, a series of
analytical tests will be performed on select tissues.
Initially, all liver samples will be analyzed forPFOS by electrospray/mass spectrometry (ES/MS). On the basis of findings fromthese 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 OtherAnionic 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
S 3 FACT-M-3.0, Extraction of PotassiumPerfluorooctanesulfonate or OtherAnionic Surfactants from Serum for Analysis Using HPLC-Electrospray/Mass Spectrometry
5j4 FACT-M-4.0, Analysis of Fluorochemicals In SerumExtractsUsing HPLCElectrospray/Mass Spectrometry
6.0 Data Analysis __________________
'__________________________
6.1 Data transformations and analysis: Data will be reported as the concentration (weigfat/weight) of fluoride per tissue or sample, or of PFOS per unit of tissue orfluid.
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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Battelle Study Number. N003604-D 3M Environmental Laboratory Study N um ber FACT 060998.1
7.0 Maintenance orRaw Data ajtoRecords ---------------------------------------------
7.1 Thefollowing raw dataandrecords will be retained in the studyfolder in die archives ' according to AMDT-S-8:
7X1 Approved protocol and amendments
'
7X2 Study correspondence
7X3 Shipping records
7X4 Raw data
-
7X5 Electronic copies of data
7.2 Supporting records tobe retainedseparately fromthe study folder in the archives according to AMDT-S-8 will include at least die following:
7X1 Training records
7X2 Calibrationrecords
7X3 Instrument maintenance logs
.
7X4 Standard OperatingProcedures, EquipmentProcedures, andMethods
7X5 Appropriate specimens.
8.0 References_____ __________________________________________________ 8.1 3MEnvironmental Laboratory Quality System Chapters 1,5 and 6
8.2 Otherapplicable 3MEnvironmental Laboratory Quality System Standard Operating Procedures
9.0 Attachments_________:--------------------- -- ---------------------------------------
9.1 FACT-M-1.0, Extraction of Potassium Perfluorooctanesulfonate or Other Anionic Surfactants fromLiver forAnalysis Using HPLC-Electrospray/Mass Spectrometry
9.2 FACT-M-2D, Analysis ofFluorochemicals inliver Extracts Using HPLC- '
' Electrospxay/Mass Spectrometry
'
93 FACT-M-3.0, Extraction of PotassiumPerfluorooctanesulfonate or OtherAnionic Surfactants from Serumfor Analysis Using HPLC-Electrospray/Mass Spectrometry
9.4 FACT-M-4.0, Analysis of Fluorochemicals in SerumExtracts Using HPLC-
Electrospray/Mass Spectrometry
.
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Analytical Report: FACT TOX-013 LRN-U2095
Battelle StudyNumber N003604-D
3M Environmental Laboratory Study N um ber FACT 060998.1
METHOD FOR ANALYSIS OF POTASSIUM PXSFL'UOROOCTANXSTXLFONATX (FFOS)1NJAT1IV3ERBY;LC/MS/MS
V a n io a L O
. ' SfadvWei AMheffiaB
Hervi&oaa to 6 e aethod
"W ritten by:
P a trick L South
.D a ta :
7 9 * ^ ______
Approved by; _
C Andre, Pb-D.
,Bionatydcal O vgnbtry
D ate G x ^ jJ r S I J H t f
3M Environmental Laboratory
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3M Medical Department Study: T6316.5
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Analytical Report;: FACT TOX-013 . . LRN-U2095
BatteUc StudyNumber. N003604-D 3M Environmental Laboratory Study Number. F A C T 060998.1
I
M E X H O P F O R A N A LY SIS O F PO TA SSIU M P IR F L U O R O O C T A N IS U L F O N A T I (PFO S) IN R A T U V X R B Y LC/M S/M S
V crrfaaU
. . StadiMaJ
A natjat/D eies________________________
L Summary
Bdacdo&vdBBlT^tofpotHtiiinpBdQonoctiBBnlfbfltfB&dnlttdfloBnchBUiii
a t liver ii pedbcaaed. Callbratiaa Laudani reprepared by q jrin g blank iivac hrTrwgm att wilti
sohret tealBtls 6mb w o h^$*odeaily-p*peed e x it. Tba cal&ntian Bated v e ta tte d
witt. m rA iri befferai. and gm acad with after! man. Tbi orpnlcpbavi c e
avspmtcdttidijim nd
ieiurttanolfaBMljiiUbyi r /MS/MSi
XL Pottos*
ToCXtfB! . .
Ibcnd in Spngna-Dawiey t Uvee.
HL Samplxs
See Chain afCuVDdjr record i f applicable.
< IV . G XN E 2A I. IHSEB.UCTIOMS
Calflaara all reqnfaedbalances accordinf to lbs SOP a t b ab n a mage.
Makei
- - ........................
Labd ill sandardand reagent solution ii^iecifled in inappropriate SOP. If jw t tattedts
n i a asiatica for Udore talks. ba wan tha label tadndes tbs jatpanrim Ada and da^r
nrunbertar which Ite solutlco was initially prepared.
. '_
Sign on Ite S n a lp ^ c f this w etted to dgnUy that yonbevo M owed the method S fritta .
,n meinula u reagent ara am o * , and all eqoipacothas been property eaHbrato*.Ifyen
ScvlasB fto m te method, d o ran e the change, n d obtain tha approval oft e w it avnagac,
andy director, or axk leader a* anon aipavibla.
.
Initial and d ra all data entries on the page on whid they ware made. V only ana parana
eatsa all data a a aingia dqr. Ite docomeaatlaa but ba aoada In a dngla loeadoo on dMt
p j IfjenbifUe aodf naks --***-*--,. tba iddtkoal astica ro w be inirtaled and datedby the
* i--Mh| Am BiOy*
T > cam nr M ft tVmr--t "^1-- 1 rT H" >'1*" The method taw itattita m eal daonologkalorder.brtteaaqnane of tt^ a w ^ h a ilte e d
Ir-K. .T^lvw to M Mafferm iate, galea tba a d e r te cenala ctMtke la tiarifleri, StodtairinbataedtarttedBialaaartteabahrvaleaaeattaiaedarnntattitttallbgria
considered aspect.
__
Ho conwsioawffl be nm delbrpttdty or O co n ee of any tatt ardetebat FFOSAA
tT.
[ f ia ta r repealer, or poridva-dh otartmans piatti ted& p m iH
w^rftm wng wahxam. a f -- with Tefloa by the teat article hoald be laleiertarrt.
'
V . M atzsuau
S T * le l t e i l l reqnired ctenrieali, reagenti, and tren ti. U Tibia 1t e ihxunicna tta . O xck all labell tantady co ananre tbat all materiali i n oct atpbred and tfett thqr aia th pepar
pnrbjr or giade.
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3M Medical Department Study: T6316.5
Analytical Report: FACT TOX-013 ' LRN-U2095
BattcUe Study Num ber N003604-D 3M Environmental Laboratory Study Number FACT 060998.1
. M E T H O D FO B. A NA LY SIS O F PO TA SSIU M
PE R FL U O K O O C TA N E SU LFO N A T I (PFO S) IN R A T LTVXR BY LC /M 3/M S
.
Vantaa LO
.
. StadvHea
A-- h /P e te
T aM eLM atarfab
Materials .
i:c
Xii>[lu:r
(al .ltli*ir Mm 1`j.c t .1 m 11
I'lltllv
IVitif
1 Pnrewhiie
Analytical Standard
3M
Room Tamp
1 eHbeete IPPOS)
S m ro(ita Standard
1CN
Room Temp
Sufahnnt Add
A-S36
Analytical Standard
3M
Room Temo
. MJ70
Analytical Standard
3M
Room Team
PFCSAA
Analytical Standard
3M
Room Temo
FFOSA
Analytical
3M
Room
Standard
Tamo
PFCSEA
A ialytical
3M
Room
i
Standard
Temp
Bat Liver
Matrix
Hartan
Spracoo- --20"C
Ammonium Aretain. M otile Phare
*****
RT
NH3CO,
Sodium Hydroxide, RcstcatPrep
XT
KaOH | n n tfitg
Extract Prep :
RT
OBA).
Srultiiwi CofaUMtte Extract Prep
RT
NaO,
Extract Prep
RT
NaHCOi
ESiyi Acetate
Extract Prep
RT
l
Mc&oool
Mobile Phase,
Stock*. W5
RT-
M1U-Q Wiser
Reagent Prep, MobDePhase
M niipon
ASTMTypel RT
pH I Baffler
pH octal
RT
calibration
pS 10 Buffer
pH meter
RT
RT menu Aetna Tempexamro.
_
V L E q u ip m e n t
See Table 2 Strali required natforpieces a t equipment. Ue the able to docuoent ectaet pie
(e.f. nake, model) a t eqalpmoit. Chech ralibrarion ofefl eqiriprner t a^ulilm caflfaarioa (4 .
baXizacei) to o s n it it wi|i,**rf
' P u e Jrfli
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Analytical Report:' FACT TOX-013 LRN-U2095
BatteUe StudyNumber N003604-D
3M Environmental Laboratory Study Num ber FACT 060998.1
M ETH O D F O R A NA LY SIS O F PO TASSIUM
PE K FL U O R O O C T A N ISU L FO N A T X (PFO S) IN RA T L IV ER BY L G /M S/M S V enina L0 Study 5ou A aalw t/D atc
Analytical Baiane Weighs Set
Table X la d g a o t
list* M:iT)tit:tctuicr
Weigh Standaidi or Reagente
rHKfrtii
MmicI
\m->N
PipcQ&r
ptpet Samples
Plprtmr *nip--ooornpessr
PtpetSample* .
PipetEtOAc extacdcii Plpet Reagenti, WIS
Eppeaderf
Repealer
Vortocer-
1 M x Samples
'
Frecar (-20*C)
Rdtigwatnr (1-9*0
CmtrtftHB
Store QCl, Blank Liver
Store Beffa-, Stocka
Phase reparaban
Test Tobes
Csatriflige Tobes T a t Tabea
Transport tabea
Magnetic cirirr Orticai Shakir
Uvcr ampia
Evaporate Extracts Store QCj Stir matrix
fvrw rt Sample*
StodcweU Sdentine Blue Falcon
Blue Palean
Ettny
Polypropylene, U taL
Pdypropyiore, 15 mL
Polypropylene, 12 x7Sasn ' 5 mL oolyproorlene
SWS599 2096 . 2002
127-T160-36P
E v ap o rar
Evaporate Excaca
Zytnatk TaibovapLV
Syringe ra te a
Filler Fm art
. .
. .
^nmfifwnin*
tR meter Electrode VolmzwCck G aaA
VobuneHlc Ptpea. C lin A
Toasier Pipeta, Plaatic
Grind ttw p^(i iiijfKi BtrflfarfH
DetenxdzM Buffer pH Maka v^Hwi^ifl
QOndoaa Make Volumetric . DOotfon T rm ifa Extracta to Cendfiipe FUten
and LC Inserts
HA HA Samoa
HA HA HA HA
1 -1
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. Battelie Study Number; N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
method for analysis of potassium
p rB F U JO R O O C T A N IS U L F O N A T I (P F O S ) IN R A T L IV E R BY L O M S/M 3
V enial U Study Nau
A m tnt/D etes
V IL B l o c w u u i
A . P re p a ra tio n o f 2 m M A m m onium A cetate
\pdgh 0.1500 + 0.0020 g ofammonhnn acetate ndtBBMfhrID a 1000-aLvolumatilB
flu k . Diuolvetho aolldhotteraidffim atovehm orttharater. Sdadccmejr banacd
tor ana month aimed attoon tempeteme.
.
l m u rfra n m fa m cattle:
Actual fla il votam * _ _ _ _ _ ,
Date of prependon:___________ \_______
Study K n : .
B . p re p a ra tio n o f --29 % S odium H y d ro a id e S olution
Weigh 200 a 2 f of toUarnbydnndde into abeaker. Add 300 aaL ofWnil-Qvnmrand
sdxtodaotv. Cool lud oauiS? to i polypropylene bank Jar conge. Sohtdonnay be
-- *rr I mtuirti at mem tm inriarare.
. Actual meat o f S um hydradde: _ _ _ _ _ Actual volume MEU-Quater: Date of preparation:
Study No: ______________
-
C . P rep aratio n o f-2 -9 % S odintn H ydroxide S olution
*
iaa 10 mL of--29% Sodium Hydroxide Solution to a lOO-taLvctanetrie Saak aad dOua to volume with M IB -<2 an a*. Tramfcr to apoiyprepyianeb o te ft* auoga. Soludoe maybe cored to r i mnntha a room m npcri Unn.
^rvwi volume of--2994 K tO E eohtdon: _ _ _ _ _ _
Acnai fls il votasw Date of prepuriorc __ _
------
fttiirfyNn;
D . P re p a ratio n o f T e tra b u ty la n u n o n lu m H ydrogensaH ate (l'B A )
M,. S o lution , 0J5 (p H 1 0)
'
pH Meter CaHhntintt
pH bettor 7 pHbof&r. 10
pH reading:_______ pH reading:_______
Add 169 a lgtfTB A to-S O O aiLofVi& B .-Q 'w aiariaabeakat.A dhteteajH ia 10.00
a 0.02 uaiug-33-60 mL of29% Sodium Hydroxide Seindea, dDuta to 1000 aoLadth
. and mix. Adjuat the pH tn 10.00 a 0 J 2 . ia g -2 J % 2 itO S m dm te " ta a iftr to a polypropylene bottle tor murage. Soindan nay be eaedtor ana monte
Kond * nxun teaapenttnm. h s U b U lH je a tito S is d e lJ riS tllS O d U H b . * * * *
pH 10.0 > 0.0 2 -with 2.9% SodiumHydroxide SohidonMntceamy.
-
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3M Medical Department -Study: T6316.5
' Analytical Report: FACT TOX-013 _ LRN-U2095
- Battelle Study Number: N003604-D 3M Environmental Laboratory Study Num ber FACT 060998.1
M ETH O D F O R A N A LY SIS O F PO TA SSIU M P X X F L rO RO O C TA N ESU LFO N A TE (P F O S )JN R A T L IV E R B Y L C /M S/M S
V enina U
Actual m as cfTBA: _ _ _ _ _ _ A ctndflsilW B ioe . Armai Anal pH: _ _ _ _ ^ _
Data ofprepaxaltac___________________
Study No: _ _ _ _ _ _ _ _ _ _ pH fhgm -hrrttnt and/oriqdhm in:
. -'
. .
L P re p a ra tio n o f 0.25 M C a rb o n a ta B u ffer
Weigh 26J a 0.1 gefjodiutn cartonate end11.0 a Oil gafoodhnaMiartnBelt and Baraka- a the lame 1000-mL vohnnctric flack. Diandre the gatnrtali falBM-Qitcr;
ifiloto to votame with MUB-Q -water, mb; aad tarata: to a polypropylene botila be Kongo. Solution may bo uoedibrl month orbai Bond reftigecxted.
'
Actualmaee of eodhum cartonate: _ _ _ _ _ _ w t i i / vflnw frtraHviwfa*
Actual final volume: _________ Dale ofpreparatine: ___________________ Study N o:______________
*
F . P re p a ra tio n o f M obile P h a je
CampanealA: M ix together 600 mL of ImMennenniinn acetatetad <00 niL of n a *m n i Solution may be ueedf i * 1 month'whanacred et mom Imepantera.
Aetna! volume of1 m M ammonium acetate:_______ e>L Actual votame of methanol: _ _ _ _ _ _ mL Dam ofpreparedopStudy No:______________
ComponentB: M ix together 30 mL of2 mM ammontata acetate md 930 mL of m e lim i Solution may be u aedfbrl monthwhoa acted et rocn temperatura.
Actual volume of 1 mM atrnnnnhim acetate________n L
f ^ --1
nrfmediaiml:
nL
Date cf prepamliw _ _ _ _ _ _ _ _ _ _ _ _
Study No:
G . P re p a ra tio n o f S tock S u rro g ate S tan d ard a n d W orking S u rro g ata
S ta n d a rd (W SS)
'
1. Stock Surrogate Standard (360,000 ng/mL):
.
Weigh 23 a 2 mg o f IH . IH . 2H. 2H.-p iflnnronctene phonic acid aad tram&r to a 100-mLvalnmetricflajk.DUaoiv In methanol Statata votone
wi.v and m ix Store rctigcaicd. protecteditem UV tight
Artnal W riaht; Actual DQudoa Yohnaoc
Date afPrcpararinn:_________________
Study No: _ _ _ _ _ _ _ _ _
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Battello StudyNumber. N003604-D
3M Environmental Laboratory Study Number. FA C T 060998.1
M E T H O D F O R ANALYSIS O F PO TA SSIU M
P IR F L U O R O O C T A N S U L F O N A T I (PFO S) IN R A T L IV ER B Y LC/M S/M S
V anina L0 ' 5 ta 7
A a a h n t/D a tg
2. WSS (1000 ngfoL):
Dflnm 100 >iLcfKock smagata Candan!B 23 mLwith raethaani rndndx-
Aetna! Votan of StockInternal Standard: _ _ _____
Acciai DOmlco Vaiamo:
'
Date afPiependen: '
H . P re p a ra tio n o f C aH bradon S olvent Stocka and W orW nf S tan d ard s
X.imf.u 1
Stock LA Stock 1B Stock 2A Stock ZB Stock 3A Stock 3B Stock 4A Stock 4B Stock 3A Stock 3B Stock SA
L Solvent Stocks
. For each analyta neigh Iheapedfladamoimt ofS*ndinl(!ad^ndeadr
weighed aa A aai B lepBotea) Hated la Tifala 3 andtxana&r into aepaate
volumetrie "* Diaaolve In methanol, (Blote to votame with mmhenni, aed
adxwalL Stata refrigerated, protected o n UV light.
'
2. Mixed Solvent Stock*:
.
P Y - fc
innm ur f n d malyfeal andari HryUrate A aa Hmadla
Tab lai and uaa& rbito a single volumetric Saak. Dlootva la mehmal, dData
to volmne with methanol, and mix wdL Sana icOigcnted. protected ftetaUV
light. Repeat die procea -withPepitene B so d a. V u m b d jahw sm adbara -
' 0 prepare tkm working andari* .
.
Data cf par.paiariog__________________
Study Ko:
.
3. ..
Working Standard! (WS):
Dilute the mixed Kochi andworking candara with methanol aa^pedfied la Table 3 and mix wefl.
. Pm ef ormaradon:
S hikl*
PFOS
pros
M-356 M370 M370 PROSAR PROSAR PROSA PROSA PROSEA
T ah leX C xH b radon Sabrent Stock ad W erkt S trad arti
V lii.it Am imi
t.irj.ee
Atti.il
N.niiii.il 1
\nmiiMt \ 11.1f\ik4t sili. t-iil.lIVnl I ll.lt \nl.
* "1* I
Sii.it. or \ \ s
.m i.)
Imi.)
`"'J -ni 1
30 a lm g ta*W BW s s m ____ 10 A M B 8 B 1 f f l M g - J
U a 0.3 mg li fa w n t M ____ ____ - m m m ^ 1
30 x 1 ma I 13 a 0.3 ma
m ____ ss____ ^ j W a i r **" m ____ ____ H i l f n
30 X 1 ma
10 i'll!lllll!!ll!lllll|[M 1000.000
1 23 X0-3 ma m m m
-10 alllgyinaifflnq 2JO0.000
1 93.1m 46 X0.3 ma
weaaraataSaSmaBSuma fmifxeibin
10 10
mrfial>wBl 3.00Q.000 H M U U lbOQ.000
30 X1 ma siM B s^ fig n es! 10 lllimipiffll |M 1000.000
23 XO J ma 6Siffi3agB5MgB
10
XJOQ.OOO
30 i 1 u t
10 M SHI 1000.000
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Battclle Study Num ber N003604-D
3M Environmental L aboratory S tudy N u m b e r F A C T 060998.1
M ETH O D T O R ANALYSIS O F PO TA SSIU M
.
PZ R FL D O R O O C T A N ISH L FO N A T C (PFO S) IN HAT LIVER. BY LC /M S/M S
Venioa L0
.
StndjNo-:_________'
Analnt/Date:
Stock SB Mixed
Stock B
WS l
WS2
WS 3 WS 4 WS 3 WS 6 WS 7
FFOSEA. 23 a 0-5 m * |3a S t3t!ftSllaSi||B8 |
Storta 1 thru
3 aiL !i 3 9 j S t eh M P W iiin
Stock 1 don <KeuB
3 a L ByWtfingEafctnai each** Sh S M 8 S0 W W |
Wftml Stock i m LM
A
Mfaced Stock 1 mL *
B
WS 1 WS 2 WS 3
i m L**
2mL l5fififtSS3MDdBa!
U mL*" iMiffiMlWtIffTM
WS 4 WS 3
2-3 mL*" tSHSSwiaicfcas 1 2 mL"
io so
30
13
23
io 10 io io io
w gnw nl pggggM l
|y ||||ff l
m ig lM a M
M M M BifflB a M M S a iti weanroMBa m a rn a
' Weigh all analytical Jtandardato at lent the acarea 0.01m *. U volumetricorpodttvw ifigilar rmrnf rtprK)-
Lsoaooo 300,000
250JW0
20 ,0 0 0
1 0 ,0 0 0
4000 2000 1000 300 200
i
1 P rep aratio n of C alib ratio n S tan d ard s and B lanlo
1. Liver homograna
Prepare blank liver homogenaa la bulk by ureigbb* appnwimaoeiy 40 g of kutiV Hvt hun m300 mL N ilrae bod omninfat 300 mL cfMEB-Q water. rtrW I to a hooaogeneoiia mpenrinn. Ahqucr into approx 30 mL portico! Ibr
fjwww (approx - 20*C ) e nrage.
Actual M an a fliv o K
raralvnlnmfrfwaten
Darn of prep:__________;_______
.
Study:_________________ --
p i*rmiTin densityofcalibrstioo/QC rnalibc
M IX HOMOGENA3B THOROUGHLY ad determiaa the m m fa wlfflgfame o f 10 lepllcna wdghinp o f 1 mL portion of the THOROUGHLY M IXED homogenate. M IX HDMDGENATE IMMEDIATELY TOOK.TO BAS ALIQUOT REMOVAL.
Rrpiicatr# M an
2, Liver CaHbodon Standards
Prepare each Over calibration aandard by adding 0.43 m Laf undHutodBrer
homogenate (STIRBOMOGEMA.TEWHILEA1IQUOTING)Intoa 13oL
,,oncQon tube and adding 30 >iL ofWS or MeCB. Prepare tripHcato cal Bgodards and 4 Mnin See Table 3 farveilmnea. Tin dUutadlivcr denaity la
rnhaapproximately130mafaiL. MExuelL
Fags Sof 16
3M Environmental Laboratory
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3M Medical Department Study: T6316.5
Analytical Report': FACT TOX-013 LRN-U2095
Baltelle StudyNumber N003604-D
3M Environmental Laboratory Study Number. F A C T 060998.1
m t t h o d f o r a n a l y s is o f p o t a s s iu m
..
ZRFLX JO ROO CTA NK STTLFON A TI (PFO S) D i R A T U V X R BY L C /M S/M S
Venia 1.9
Study Mod
' Analrrt/D ale:
.
Cal SCitUl.iuU
1 2 3 4 5 < 7 Blank
Nm ice
WS 1 WS 2 WS 3 WS 4 WSJ WS 6 WS 7 MeOH
Tables. C alib rato i Standard! Blanks
Tarnet Voi Actual Vol Target
l.-tL l
..L>
[ fin a l Vnl
n u l.)
Actual liii.il Vnl
n n l.l
Nominai tu lli.
(MlLHlIl
____ m m a r n ____ o j____ w a
2000
50 dto#5 titiW
OJ E M B iiR U 1000
- 50 E h tito B d -2*5
fe jw w g M 400
50 P
i oj
loSeWtoM 200
30 fes M S t B ti o j kahaHBCSsf 100
30 .
o j kaw s w a p 1 30
50 o j f l n U k 20
so to iS a S s ffii1 0.3
D ateafprepatadonofcalnds/blank:___________________________
e e
V illin i.il l ii'ii. Ml" V 13 A 2A U
0M
033 0.13
J . P re p a ra tio n of Q uality C o n tro l L iv e r Sam ples (Q C i)
1. Quality Control Woridnf Standards
.
' Dilute the Allowing jcunx volumes methanol la volumetricflasks a d m ix well. Prepare flesh wbca used. Actual vohunes are in parentheses.
s.itif n i
OC WS 1 OC WS 2 OC WS 3 OC WS 4
Mixed Stock A
< Mixed Stock B
OC WS1 OC WS 2
Tabla 4. OC WS pregaradoa Voi Source, m i. Fin.il Voi. mia t in a n iB s^ ^
tfoiiU w im cnaS a i230W HiinSIS|t
< one. lili-Mil .
13.000 3000 1123 230
1
2. Preparation of Quality Control liv e r Simple*
Prepare each QC In bulk by fiM nf die volumetric flask spproodmamljrhsirflill
with
Uvtx homogenate (STIR HOMOGENATE WHILE
ALIQUCmNGl. adding lbs appropriata QC WS. m bdnt and dflntini to vchnaa
with undiluted liver homosenate (STIR HOMOGENATE WHILE
ALIQUCmNG). M IX THOROUGHLY tad dipmee X3-mL aUqncta bao
polypropylene tubes and store at approximately -20*C.
Date of QC prop:___________________Study. --- ---------------------- --K . P re p a ra tio n of M S C heck S ta n d a rd fo r System S u itab ility .
Piper 130 jjL ofWS 2 a t--10.000 ngibnL and 2 J mL ofWSS at --1000 aa/mL la mm tbe ro* 50-mL volumeeric flask. Ufluta Covoluxas with MeOH and mfre.
Paie 9 of 16
3M Environmental Laboratory
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E-13
P a g e '10
3M Medical Department Study: T6316.5
Analytical Report: FACT TOX-013 LRN-U2095
Battdle Study Number. N003604-D
3M Environmental Laboratory Study Number FACT 060998.1
M ETH O D F O R A N A LY SIS O F PO TA SSIU M
.
FXRFLUOROOCTANESTJLFONATX (FFO S) IN RA T L IV E R B Y L C /M S/M S . V in io a U>
. ' Strut* Wo.; Anshrat/Dete;
L . P re p a ra tio n o f hom ogenizer recovery Bver sam ples
' *
To determine the recovo? from it homo|ealzricc prceu. enhornop u tted M ark llw r mil befhrtlfied la deplente at 3 cancentnclcn IcvtJa and honrogenteadaslbllow. TMa
rinneaverf day that homnyrrriTi lltxt ofawdr males la nerthnaert
W-r-
n<g
MnV guar tata aril a fA, 13 aT.
polypropylene j-utiM iy tabea. Record iwigbts ofOvar.
3. Add 100 |iL o fWS 1,3, b x 14 (aee WS perdupficara toba) to prepon . giprrYriTOtriy , 0 ., ad 0.4 |Ig/g.
3. Vfnltiply fhe Tnnmr f llvg- in f by2 5 and add this BBT mL o famar.
4. Homoscaizeeodtlharmnpic.aBdrinehoaaoieolzerprobe'wiAaaotbbr
'im M r fM tg m a t tnnep3. addingtfaueTnhtanoreafandanmla.
,
3. O ran borongudier with MOOH between sample.
4. Cap midvortex bomogeaateferuailn'extmctloi.
M . P re p a ra tio n o f D ilatio n C heck Sam ple
1_ Place 133 mL ofrmdllrimd tver homogenate (STIRBCMOGEtlA'IB W HILE
AUQ UO nNO ) bio a 13 mL exnacdcottbe a n iM d M jrL afSOxed Stodc A.
2. Dnnte30 pLefatep 1 eolation (VORTEX SOLUTION W HILE
ALIQUOTING) -with 0.45 mL ofundiluted liver homogenate (STIR
HOMOGENATE W HILE ALIQUOTING) in 3.13 mL extraction tribes.
3P T b ii sample ibrwiM be prepared 2br ertrurrioBonly oa days uhta iiudf smnplas
win be dtaed and extracted.
.'
N . H om ogenization o f stu d y am pies
.
i. Place approximately 0.5 f efoahemogcaiaed atady sample UverbsoaU mL polyprepykne tube. Record weights of liver.
' 2. ' Multiply the mam ofliver in gby3L5 and add this many m Lrfwotec y Homogenize each liver ample, andrinae bomogeninerprobe with aeotber volume of water used In atap 2, addingTinao to hetaogt ntrrd sample. 4. ' dean hemegenfaoerwith MeOH between simples. 5, Cap and vortex homogenate hrr use In cxtricrtra.
O. Analysis Standards,Blanks, QCs, andSamples
1.
.
2. 3.
. 4. 3!
'' 7_
MDC UVES. HOMOGENATES THOROUGHLYBETORB ALIQUOTING
and pipet 300 jrL c f each QC (4 irpllratre per level), aad otherample belag extracted hao 15-tnL polypropylene extraction tobes. Tbe cxl stria and blanka
are already aliquoted.
To the B lan ks-E 3 reps), add 100 >iL cfMeGH tad vertex. To the Blanks + IS (3 tepa) and to the remaining ample, add 100 uL WS3 sod
vortex
Add 05 m L rfO J M T B A (pH 10) loaQ tabee sod vertex bdefly.
Add lm L a f 0^3 M carbonate butter and vortex briefiy.
Add 15 mL of ethyl acetate. Piece the tnbea ddewqr* on fee oebital d o lo r Sta
aetdng of M O tbr-2 0 mimar
____
Centriflige tubes at a *,rr*Tit o f3300 ipm fbr *20 TTirmtra to b patata layers.
Transfer 2 mL at the top orpmic layer to a dean polypropylene aba.
Pago 10 of 16
3M Environmental Laboratory
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3M Medical Department Study: T6316.5
Analytical Report: FACT TOX-013 ' ' LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
method tor analysis of potassium P E R F L O R O O C T A N E S U L F O N A T I (FFOS) IN B A T LTVXB. B Y LC/MS/MS
V e n in L0 . S trirM e i
Aatijtt/Ottti-_________________________
9. Evapore lo drynesi under otonfeu * i iBrtm of30*C 1brSOmlieene.
10. Recandone (h* raidae* In 300 jLafBcdeaol wi&vortmdaf. U . Syrinte-fiter xn>ct fato BnekmpletvhlifecM elyriK. Storiviale teftitented
(up Id 1 month) IfLO M S/N O m illaotbapei&nadlhamma day. ignee 3 4 ; T~~" tn p m n n t i mhlHty WM dn n u nu tted M t j e l l i i l l i e , a
Ve x tn e s of the c il ih , bienio, cad QCi mejrbe naeed t e op *>3 thy* ifte r
t h r f r h r l H . 1 f r * " 1* * " " t r h e l d i t m n m i p n r i f t a c a p t h e M ie l t-- i n f l
Timm i4 eel addalenfr p a n e te r a :
.
D a o QC o m e t p trp :______________________________ .
P. L C / M S / M S Analyst* F0
Uselhe system condition qmdfied in TdblaJO?The candidanea rM d m deiiesued me be modified by the eoefcrstta produce accasatile peek A n e .
LCMSMSwem
T ib ie ! - DC/MS/MS CoedhSam
.Vifiiviiniitci*
m*i.t l'umpN
M.hs S|iccfi'iintivr
Aii.i1.vnc.il Aolimiii
Mollili*Phase Oimimttaus CiMilicnt(iriitif*
M ike-
Model:
ID :
M a* M ik e
Model: Model:
ID: ID :
KeystoneBeasti CIS, 5m - 2 X SOn o , P tn N a 005-701-2,
S/N: CoiTip'TT1"
... . tleOC * A: Ammonium imtfattrmrrtamnl.
60:40,
yy
Camponeat B; Ammonium acetarmerbnal. 3:95. ttv
T t a t min
0
1 ' .6
6-1 *-3
9
1 11
241 0
0
100 100 100 100
0
0
Flow. Ltarfn 03 03
03 03 06 06 03 03
*
*
litjcilton totum e l-loiv sp lit
10^ c
LC column flow split te *30 u L/ain f
idJvoni faro the MS M roa i
liillltllll Ivlup IIP LC P u -m c
A m b i e n t _________ 10 0 0 ta i * g a t o l a n (
P0
M> Siiiru*
B e u im m * - K e te d v e Io n
OCMlU.ltiiHl .ts N cltuli/cr "a*
Nitrogen t 373 L/hr (
Nltrorai at L/br (
Sourcelllml*lenti) 140Cf *Q
Uhrt Lthrt
OcMiU.iti ii funi 230* C (
loue
70 V ( _ *20 V (
V)PP O S,-iS - ' V i PFOSA. FTOSAA, PFOSEA, M J56.M 570
C oIIMMII t'iH 'l"?
eV) PFOS,TtP FO SA , PfOSAA. M-336, M370 eV> PFOSEA"
1`olltMmi .h M ultiplier Kcsoiliiioit
Argon it *13 x 10~*mb p e cell 7
W
i *650 V f
Vi
12.0 t e MSI (
>. 10.0IhrMar
(Dstout&u n
'
? V 11 r f 16
3M Environmental Laboratory
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3M Medical Department Study: T6316.5
Analytical Report: FACT TOX-013 LRN-U2095
Battelle StudyNumber N003604-D 3M Environmental Laboratory Study Number FACT 060998.1
METHODFORANALYSIS OFPOTASSIUM
PERFLUOROOCTANESULFONATX (PFOS) INRATLIVERBY LC/M&MS
.
VentoLO
'
StudyMeu
nalvm /Palc
It lit wIll'i'lifiK U tl
4 2 7 X 1 MRM transition tx Surrogate Standard (SS) 493>99 MRM transitino HasPFOS
336>71 MRM transidost o M-556
J7C>1S9 MRM transitionftrM 370
34>169 MRM transitionIbrPFCSAA '
-
49t>73 MRM transition 4 PFOSA
MRM Transition lhr PrOhldA
1Mi ll I lilt 'tills \|Hi MM.n.itv:
11 niluiires f
SS: 4 noia (
arin) aria)
-
alt ik im ii tme* ":
PFOS: 4J urin (_____ ma)
1 4 M : 43 d a ( aria)
M370:4.6 min (
min)
PFOSAA: 4.7 uria (_____ min)
*
PTOSA: 3.1 min f
min)
PFOSEA: 3.7 min f
min)
.
. .
* Parameters d ar may be cbanpd by the aimlytt. Actual veines in ( ).
i The above cnadlttom iboold be dtabla tbr the Mkromass Quattro LC (SW
9033), Modifications may be necessary if m otherMlcromoie Quadra Saties
spectrometer lam ed. Split the flow pcaKalam a via a Keystone BIO tee or
siinilar device.
3. C.ItVrm. iC im --tjw n w w fw u d s | a tlA l*
fw yrnw l CFYKify
that the caHbndion Is mitablo by visual httpm tnn (os the tnnopact) dot a
suitable mobile phase km !a sin accanttety determined. Reeoludon m qr Bead te
be b itte r them dim used fcr snalyzbg samples.
-'
4.
standard. Tbo resulti should be compatible Id a recent Injection It avaSafata
3. Use an
chromatography integration software system to m llert the
6 outputfrom the analysis.
'
.
. Loading Order: Sea the lnHhtg reportfrom (ha antnmatari chmtnstngiaphy
Integtatlon suftwara tyncm.
7. Make ringle tqjccdorm of each cal standard, QC, study temple, orblank. M dta
at least 4 injection of the Instrument chert standard.
.
a. Ran set rises should typically not exceed SOinjections (too to h tstnaari response roll-aff considerations. Longer tuna may be performed,but dmypoaaa
ride ofyielding nraacceptablo curve resulta
,
VUL CALCULATIONS
L Spreadsheet Software: ______________ _ _ Version _ _ 2. MS Analysis Software:,____________________ V errina_______ 3. "imi.re tbe average fa sn y of die Uvei homogenate (10 repe) In m gtaL. 4. Using the avenge density of the homogenate, calmimi la Over density
(mg of liver per niL of diluted homogenate):
UndUnted Bver density (zng/mL) (g ofliver x average density o fhom ot>& ay(g of
liv er-fg ofwater)
'
where g ofliver m d g o f w ear ate messes used to prepare bnHr homogenate;
density cf water Is assnmed to be 1 g/tnL
'
Diluted liver density (rog/rnL) - Undllnted density DUn Factor '
Page 12 of 16
3M Environmental Laboratory
C-12 E-16
Page 112
3M Medical Department Study: T6316.5
Analytical Report: FACT TOX-013 -- LRN-U2095
. . Battelle Study Number N003604-D
3M Environmental Laboratory Study Number: FACT 060998.1
. .
,
-
t 1 J . | ;,
' ''
*
.
. '
M ETH O D F O R ANA LY SIS O F POTASSIUM
P X R FL U O R .O O C T A N ISU L FO N A T I (PFO S) IN R A T LIV ER BY L C /M S/M S ' V erataaU 8tadv Wa.1 Aaahrat/Delg
W h e re d ila fiK ln r-2 /l.i" L i l l i to aceocntibr 10%<2Iii aflSverbornofeaeta
. In cel odaod QC matrices.
.
S. Calmhta the aftra! coocararadoa
of?P08 ad etherflanredia ntrr ii k the
apcnaioai of calltatkat aandarde end QC* by fa the area ataaalyt* a d dtoalaa
>cton anlyCno Bver denaiiy corracticn). Uaa parity emtcdoaftrlPOSAAeady.
4. Calculate the acnraleoocsntraticnoii'FOS and otherflootocbenrical* to liver S r dr
>nhr.Hiitaiidardi an d O C a a ith n o w c
_
- C m fe|AnL.1 DOntadLiver dcartor (msfaL)x1000 mtft x ltr1 aartra
7 . a--~*m bg|ratlnnaaf the peat artaarf the test article endaurrom a E n d ed Me
* etaioa. Fla* tnarmal ia c ja tio n i where petSumcd. Calculate Ac a c t coacsstiadecirfcnfc
: liv e standard.
'
' j , r . w i . i . the teaicaaicn agnation idarin the peekreeparaemto (tea artd a /S S )tfaadi . m m h n lfM ri ' in leg grida couciueii tian 1 ttver h -ed ri fcrPPO&.M-g<L.
M570, andPFCSAA. Calculate the retresriaa equation refedn* ihe peek an * of A
yndyrrl m tear rrida mm^muition inBvertbr PEOSA pdPTOSEA. CTOS.M-
3 3 8 ,M 5 7 7 .H fc ri< * * --
hy adng ifa. n ra qata m d anl man harmal
m ufarf- PFOSA end PFOSEA ire ntatrtiatrd withoot reference tn ihe rnrmrete fasdamel
. enUbmion crave). Use a qaadradc regression e d |h c d 3/z yarigfai auJaded* h e
a&aaabrtes.
'
.
9. r*>TMt> ^rrm inrA aw ntrvrtnn f o r each injection of eallbadoa standard. QC. i d - `
ausple using the regression parameterx end the peak respoeaa ratios or erne.
10. rvL-nfam As relative error, avenge relative error, tieretard deviation, and relative Mandanl
' deviation Ibr aU QCa. rlm lai the relative errorft each IniectioQ ft calihrttirei Baiutard.
iL r i W h v rtiviv m w recoveryibrthehom oecnizarrecoveryIhrtHlraHrma
12, rSivTviarive pairdard deviation ft tha CTOS to SS peakarea ratio atArcrepllratc
' bgectiona of the check aaodard.
'
, IX . A co eftancx Cbtixrxa.
A . M S C heck.S tandard (S y fte a S uitability)
At least 3 injurious o f the MS Chet* Standard e a a provide a W SD eflO S orlaaaftrth a PTOS to S3 peak area ad o .
' B.
' *
C a lib ra tio n S ta n d a rd i
The percent relative en o n ftrr the ujum itiarion-level avenger rfthe raUbrnfan gaadardl thjviM rpw* dto fallowing ttrntrv
3M Environmental Laboratory
Pasa 13 af 16
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Page 113
3M Medical Department Study: T6316.5
Analytical Report: FACT TOX-013 _ LRN-U2095
Battelle StudyNumber. N003604-D 3M Environmental Laboratory Study Number FACT 060998.1
method for analysis of potassium
PXRFLIJOROOCTANKSULFONATE (FFOS) IN RATLIVERBY LC/MS/M8
V c n lo a U - .
Stadie M ai
TtbU 9.
Arrnpnnre to it
PFOS__________ I
M -5 MJ70 PPQ6 AA PPOSA PPOSZA
2 0 O 3% ttL O O)
roqjscixicn joajscuxn ingjsitLocn
20 03% it LO O
2 3 0 0 * t LOO)
Us to 3 allbtadaa n nd ud iqjectioni saybe excluded float lb* ear, provided tfatfoM
yecdemremsin! per fa d . Itenovri of la eolie f a t i Bay be dee If ^ g ro v il Is * 6ih *d .
S b ottre level U-iam rod. the Mmpfa bracketedby the rentinlnt lib rarian reap afflb e
...-- m. --r
TliecdJbiariaaenrvathaoVllam cecfOctatafdetenaiaUioBpf .
-0 J 7 or better.
1 C. QCi
naocoocentratien-fatiiveiifo perseti relativo error and percent rdPhreJtm fati dsvfaiais of tbe'QCi faM meerthe fbHowin Hinht:
Tabi 10. QC Acceptance Umita
ANALYTE
pros
1
20
M-53d
1 20
MS70
20
"" PFOSAA
20
` PFOSA PFOSEA
__________ 2 _________ ! 23
Banov! of badMifati -?ahx fttsn the QC ealndadoni tmqrbe dose If accnopaniadlgr a
li -iiiiMn
( t * , bansneti nnhfhncrinn orDteon'l Q fa t remit).
H tbo rrerijo detBmJned oonceataion fbr any QC f a t i caestd tie m panetadL *
ta b leader sixty director tioold bo notified. The nm may be repeated or portion efthe
raoBaybecomidadececptabU. For example. If tbe tow QC M U the fated im if t w r t i,
Bcopla may bo accepted Ufa fave enocentadoB bxaducedby *
eHbrtloa
andati and a mid-Uvei QC coocczeiarioa.
D . H o m o gen izer R ecovery and M o tio n C h eck Sam ples '
T fa areale reenvwy crea the 3 fa ti of homoje n ia r recovery empie fa til A t ir f
(be an.*!.*.
*wtM &U -within the range of *76-130% hmhiaiva. P f a n t l of
may bn dona If w rnm partti by iratrmahU .
pip iliurifti
t S en sitivity (L O Q s )
- Tbe validated lim iti of quantitation re nomimlly O.D |i( f f dt tot5FOS, M-334, MS70,
' endPFCSAA.
.
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3M Environmental Laboratory
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3M Medical Department Study: T6316.5
Analytical Report: FACT TOX-013 LRN-U2095
B atteU e S tu d y N u m b e r N 0 0 3 6 0 4 -D 3M E n v iro n m en tal L aboratory S tudy N u m b er. F A C T 0 6 0 9 9 8 .1
METHODFORANALYSIS OFPOTASSIUM PEUrLTJOROOCTANXSTJLFONATX(TFOS) INRATLIVIBYLC/MSMS
Vante U
' StmhrlTau . ` AaatjatfOales _ _ _ _ _ _ _ _ _ _ _ _ _
FePTOSA talPTOSEA taviU dtadIX X aoniailly 033 F/staelL j tati
rfU i.
* t a T k I w m . aniiailcam ifm j& A .aad
ppn c p n i im. f^rrUtl itm ig h t a atnedoa. T h en lowar m n r m n a i f vilnM'wffl ba
-- -withe * ran let, and may ba brindad in t a rrfrm W a if t a y m n t iccaptanca
. i..Am y m w i niiwi
m p t a a M d i m a n iu lturd a t a r a cm rrnlntlnaa
W ow t a validated levai ^ n n ia aQ jO pgff) arts be appropriMatyfiagged.
F. Spedfidty
Tba
20% cfLO Q . T l bacnxpt r f t a
calfhrarinnanwytm8 dftroncorreetiontaiaq
eflfect on qn&dtuloBs.------, -- w
..
01 be ooniideted oe flldent evidence t a t b r a d a n t Body aampta n <|Bantxfledproperty.
G . G eneral
.
IT above acceptance criteria Indiata ta t dril m atad la capable ofproducing ocaaiooal KKSioatxtte t a nonnid acceptance o taria oa validated iwtbod (13% netmalty). Wham faafisanl. plicate asatyaca Icrea t a Impact c it a occasional codicia.
X . SJ3 LT3 hrd mpr of snrrvlthvgt ar ree flic onnetwcric drive.
XL commotri
3M Environmental Laboratory
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3M Medical Department Study: T6316.5
.'
Analytical Report: FAC^ R^ ^ 2 09.1
Battelk Study Number. N003604-D
3M E n v iro n m en tal L ab o rato ry S tudy N u m b e r F A C T 0609 9 8 .1
. M E T H O D F O R A N A LY SIS O F PO TA SSIU M
prR yLX JO R O O C IA N X SU LFO N A TX TFOS) D i R A T U V I S BY L C /M S/M S
V an taaU
S
`
_______________
X1L C onclu sion s
TTTT s n a u z rm x s
Anxfyzti
Techidcal B eriew Q C X anew
Data: D ate
D ate D ate
Date D ate
D ate ' Dass
3M Environmental Laboratory
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Battelle StudyNumber. N003604-D 3M Environmental Laboratory StudyNumber. FACT 060998.1
' Study Tide
'
Combined Oral (Gavage) Fertility Development and Perinatal/Poatnatal
Reproduction Toxicity Study ofN-EtFOSE in Rats
PROTOCOL AMENDMENT NO. 1.
Amendment Date: July 28,1999
. Performing Laboratory
3M Environmental Technology & Safety Services
3M Environmental Laboratory
933 Bush Avenue
.
St Paul. MN 55106
Laboratory.Project Identification ET&SS FACT-TOX-013 URNU2095
3M Environment*! Laboratory 3M Environmental Laboratory
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--
Battelle StudyNumber N003604-D
1 3M Environmental Laboratory Study Num ber FACT 060998.1
Protocol FACT-TOX-C13 . Amendment 1
This amendment modifies the following portion(s) of the protocol:
1. PROTOCOL read s: The proposed study completion date is listed as 12/31/98.
AMEND 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
Marvin Case PhDn Sponsor Representative Kris J. Hansen PhD., Study Director
Date
3M Environmental Laboratory 3M Environmental Laboratory
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Battelle Study Number. N003604-D
3M Environmental Laboratory Study Number: FACT 060998.1 '
Study Tide
-
Combined Oral (Gavage) Fertility Development and Pcrinatnl/Poatnatal
Reproduction Toxicity Study ofN-EtFOSE in Rata
PROTOCOL AMENDMENT NO. 2
Amendment Date:
September 10,1999
Performing Laboratory 3M Environmental Technology & Safety Services
3M Environmental Laboratory 935 Bush Avenue S t Paul, MN 55106
Laboratory Project Identification ET&SS FACT-TOX-013 LIRNU2095
l
3M Environmental Laboratory 3M Environmental Laboratory
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Battelle Study Number. N003604-D 3M Environmental Laboratory Study Num ber FACT 060998.1
Protocol FACT-TQX-013
. Amendment 2
This amendment modifies the following portion(s) of the protocol:
1. P ro to col READS: The protocol states that liverwill be extracted and analyzed at the 3M Environmental Laboratory.
AMEND to read : The liver specimens will be extracted and analyzed atBattelle Memorial Institute, 505 King Avenue, Columbus, Ohio 43201-2693.
REASON: The liver specimens will be sent to Battelle Memorial Institute for extraction and . analysis to rime constraints in the 3M Environmental Laboratory.
2. PROTOCOL READS: The protocol states that serum specimens w ill be extracted and analyzed . following methods:
FXCT-M-3.0, "Extraction ofPotassium Perfluorooctanesulfonate or OtherAnionic Surfactants from Serumfor Analysis Using HPLC-Electrospray/Mass Spectrometry" FACT-M-4.0, "Analysis ofFluorochemicals in SerumExtractsUsing HPLCElectrospray/Mass Spectrometry"
AMEND to read : The serum specimens will be extracted and analyzed following methods:
ETS-8-4.1, "Extraction ofPotassium Perfluorooctanesulfonate or OtherFluorochemical Compounds from Scrumfor Analysis Using HPLC-ElectrosprayMass Spectrometry" ETS-S-5J,."Analysis ofPotassiumPerfluorooctanesulfonate or OtherFluorochemical Compounds in SerumExtracts HPLC-ElectrosprayMass Spectrometry"
REASON: The extraction and analytical methods FACT-M-3.0 andFACT-M-4.0, respectively, were updated on 04/27/99 to ETS-8-4.1 and ETS-8-5.1.
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Battelle StudyNumber. N003604-D 3MEnvironmental Laboratory StudyNumber FACT 060998.1
Protocol FACT-TOX-013 Amendment 2
PROTOCOL r e a d s: The protocol states that liver specimens will be extracted and analyzed following methods:
FACT-M-1.0, "Extraction ofPotassiumPerfluorooctanesulfonate or OtherAnionic
surfactants fromLiver for analysis Using HPLC-Electrospray/Maa Spectrometry"
FACT-M-2.0, "Analysis ofFriuorochemicals in LiverExtractsUsing HPLC-
.
Electrospi&y/Mass Spectrometry"
AMEND TOread: The liver specimens will be extracted andanalyzed following method:
Method for Analysis ofPcrfluorooctane Sulfonate (PFOS) in Rat liverby LC/MS/MS, Version 1.0
Dma *rju` since die Ever extraction ar|d analysis was sub-contractedto Battelle Memorial Institute, this m vhnent was written to include their livermethods andtides.
Amendment Approval
A M PhD.-, Sponsor Representative
fo b hk
KristenJ. HansenPhD-, Study Director
3M Environmental Laboratory
3M Environmental Laboratory
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Battelle StudyNumber N003604-D 3ME nvironm ental Laboratory StudyNumber FACT 060998.1
Study Tide Analytical Study 2(N-Ethylperfluorooctanesulfbnamido>eilumol in
' Two GenerationRatReproduction
3 ! PROTOCOL AMENDMENT NO. 3
Amendment Date: October 4,1999
. Performing Laboratory 3MEnvironmentalTechnology & Safety Service!
3M Environmental Laboratory 935 BushAvenue St Paul, MN 55106
Laboratory Project Identification ET&SS FACT-TOX-013 LIKNU2095
3M Environmental Laboratory 3M Environmental Laboratory
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Battelle Study Number; N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
-
1
Protocol F A C T Tox-013 Am endm ent Num ber 3
This amendment modifies the following portlon(s) of the protocol:
1. Protocol Reads: Kristen J. Hansen, PLD. is the Study Director.
Amend to Read: James K. Lundberg, Ph-D. is die Study Director.
.
Reason:
Original study design bn changed due to availability of resources and James K. Lundberg
will begin serving as the study director for'FACJT-TOX-013 as of 4 October 1999.
2. Protocol R eads: 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 of data. Additionally, 1 Section 73. states that supporting records to be retained separately from foe 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.
Amend to Read:
t
Section 7 states: "The original data, or copies thereof; will be available at foe 3M Environmental Laboratory to facilitate audits of foe study during its progress and before
acceptance of foe final report. "When foe final report ia completed, all original paper data,'
including: approved protocol and amendments, study couespondence, shipping records, raw
data approved final report, and electronic copies of data will be retained in foe archives of
the 3M Environmental Laboratory. All corresponding training records, calibration records,
instrument maintenance logs, standard operating procedures, equipment procedures, and
methods will be retained in the archives of the facility performing each analysis.
Reason:
..
To direct subcontract laboratories in foe disposition of foe items listed above.
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Protoco/ FACT Tax-013 Amendment Number3
3. P r o t o c o l r e a d s ; Disposition of test andcontrol substances: Biological tissues and fluids are retainedper GLP regulation.
Am en d to read :
Specimens 'will be maintained in tire 3MEnvironmentalLaboratory specimenarchives. All specimens sent to sub-contract laboratories will be returnedto the 3MEnvironmental
Laboratory upon completion of analysis andsubmission ofthe sub-contract labontory(s) final report. The specimens will be returnedwiththe following documentation: tire original chain of custody andrecords of storage conditions while attire sub-contractfacility.
a
- Reason:
To define in detail the appropriate disposition ofspecimen^analyzed at subcontract ' '
laboratories.
Amendment Approval
T C to L . Marv Case, D.V.M., PhJD., SponsorRepresentative
y o d u . tv * * Date
_ L J L = __ ;______;---------------------------js ts m
Kristen J. Hansen, PhJD., Previous StudyDirector .
Date
! Dale L. Bacon,
3M Environmental Laboratory Management
3M Environmental Laboratory 3M Environmental Laboratory
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Battelle StudyNumber. N003604-D 3MEnvironmental Laboratory StudyNumber. FACT 060998.1
DEVIATION REPORT
Battelle Study Number. N0036Q4-D 3M Environmental Technology and Services Study Number: FACT 060998.1
2 (N-Ethylpcrfluorooctaflcsulfonamidoy-ethanol in Two Generation Bat Reproduction
TYPEOFDEVIATIONS: PROTOCOL
.
DATESOFDEVIATIONS: October18, 1999
NATUREOFDEVIATIONS: Someoftheanalytical methodacceptance criteriawerenotmetforthe LC/MS/MSanalyaiaconducted 180ct99atBattelle. Thesedeviationa(ate toprotocol-amendment2. Seebelowforaunmany. .
An;il\n-
FFOS M-556 M-556 M-556 M-556
PFOSAA PFOSAA
OC3 exceeded20%error(-20.3%actual) OC2 exceeded 20%error (23.4%actual) OC3 exceeded20%RSD(21.2%actual) OC4 exceeded20%RSD (28.8%actual) Dilutionrecoveryexceeded 130%(131.5%actual with21.6%RSD) OC3 exceeded 20%error (-20.6% actual) OC4 exceeded 20%RSD (21.3% actual)
CAUSEOFDEVIATIONS: Samplepreparationand/orLC/MS/MSvariabilitieaoverthecomaeofthe samplesetmayhave contributedtothedeviations. .
IMPACTOFDEVIATIONSONTHESTUDY: The errantQCvalueswerebracketedbyacceptable
QCconcentrationlevelswhichdemonstrate*that thecalibrationcurves generallyprovidedgoodaccuracy
overthetestedrange. The dilutionrecovery forM-556was not consideredtoboexceedinglyhigh
enough, at onlyapproximately 1.5%above thenormal acceptance level, to havesignificantlyimparted-
thedata.
'-
CORRECTIVEACTION:Thisprotocol deviationsummarywas preparedforInclusionbnfoefinal report
APPROVEDBY:
JonC. Andre, Ph-D. BattellePrincipal Investigator
Date
KristenJ. Hansen, Ph.D. StudyDirector
N003604-D Protocol Deviation. 1, Page 1 of 1
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DEVIATION REPORT
Ttattelle. Study Number N003604-D
'
3M Environmental Technology and Services Study Number FACT 060998.1
2 (N-Ethylperfluorooctanesulfcmamido)-ethanol in Two Generation Eat Reproduction
'
. T Y P E O F D E V IA T IO N S : PR O TO C O L
D A T E O F D E V IA T IO N S :
October 2 0 . 1999
N A T U R E O F D E V IA T IO N S : PFOS QC3 exceeded the 2 Q * R E method requirement (actual - 2 1 .7 * ) .
The
recovery
nandard did not meet the 7 0 -1 3 0 * recovery requirement (actual* 5 . 0 * fo r
PFOS and 4 .6 * fo r PFO SA ). Theae method deviation* relate to amendment 2 o f the atndy protocol.
C A U SE OF D E V IA T IO N S : Sample preparation and/or L C /M S /M S variabilities over the coarse at the
aample aet may have contributed to the QC deviation. Sample preparation error appear* to have been the
cauio fo r the dilution recovery results.
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 : Tho orrant Q C value level waa bracketed by acceptable
Q C level which demonatratea that (he calibration curvei generally provided good accuracy
fo r study sample over the teated range.
-
.
A comparison o f the reaulta obtained for the diluted study samples team 20O ct99 and previous reeulta
that were slightly A LO Q (130ct99 and 180ct99) demonatrated good agreement between foe 2
xhia would indicate that the dilution o f the study samples was performed correctly
200ct99 so that do impact on foe quantitations occurred.
C O R R E C TIV E A C T IO N :T hia protocol deviation aummaiy waa prepared for inclusion in the fin al report.
APPROVED BY:
Jon C . Andra, P h-D .
-
Battelle Principal Investigator
Kristen I . Hansen, P h .D . Study Director
N003604-D Protocol Deviation 2, Page 1 o f 1
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Battcllo StudyNumber N003604-D 3MEnvironmental Laboratory StudyNumber FACT 060998.1
DEVIATION REFQRX
Battelle Study Number N003604-D 3M Environmental Technology and Services Study Number FACT 060998.1
2 (N-Ethylpcrfluorooctanesulfonamido)-ethaflol la Two Generation Sat Reproduction
: TYPE OF DEVIATIONS: PROTOCOL
DATES OF DEVIATIONS: October 12, 1999 through October 20,1999
NATURE OF DEVIATIONS: The lot number of PFOS used was not 217 as per i section 3.1.1 of the protocoL The source of reference substance matrix was not Argus j Research Laboratories as specified in section 3.2.2 of the protocoL Initial analyses of \ liver did not exclusively target PFOS as per section 4.0 of protocol.
t
j CAUSE OF DEVIATIONS: Only PFOS lot number 171 was available at Battelle. I Marian was the supplier of control rat livers used to prepare blanks, standards, and QCs
for the analytical portion of the study. All 4 analytes of interest (PFOS, M-556, PFOSAA, and PFOSA) were monitored during each analysis.
IMPACT OF DEVIATIONS ON THE STUDY: PFOS lot number 171 and Harlansupplied liver were both used for Battelle's validation of the analytical method (Battelle : study number N003604-A). These materials allowed achievement of the reported method xr^itanr criteria so that there is no impact on the study. The concurrent analysis of PFOS and metabolites was an efficiency improvement.
CORRECTIVE ACTION: This protocol deviation report was prepared.
APPROVED BY:
Jon C. Andre, Ph.D. Battelle Principal Investigator
Date
Kristen J. Hansen, Ph.D. Study Director
N003604-D Protocol Deviation 3, Page 1 of 1
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APPENDIX F - PFOS PURITY REPORT
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ETSS 2 3W
Analytical Report: FACT TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number FACT 060998.1
S 651 778 4226
04/26/99 09:56 0 :02/03 N0:341
Tor From: Subject:
Date:
3MSPECIALTY ADHESIVES * CHEMICALS ANALYTICAL LABORATORY
Lisa Cernea (3-3368) - ET&5S- 2-03-09
Request # 5783 '
TomXestaer- (3-36331 - SA&C AnalyticalLab-236-2B-11
OuMiical CXxncUrizaan o f TOST-Baotd F luonxhtmlcah by 'H-t'&fR A Sputrotcayy
March 24,1999: Preliminary report for FC-95 (PFOS), lot 171
SAMPLE DESCRIPTION^
,
FC-95, lot 171 (PFOS), TN-A-0834;Nominal productC,FirS0j<-) K(+) (whitepowder)
INTRODUCTION
.
This sample v u xubjecred to *H-NMR and l,F-NMR spectral analyses to determine the purity of the nominal product and tn characterize aa many impurity components aa possible.
A portion of the sample was accurately weighed, spiked with a known amount of 1.4-bis(triflnorociethy0hen7are (p-HFX), and th^n totally dissolved in DMSO-d for subsequent analysis by NMR_ A 400 MHz 'H-NMR spectrum (# h57830.401) and a 376 MHz ''F-NMR spectrum (# Q7830.401) were acquired using a Varian UNITYplus 4C0 FT-NMR spectrometer. Use of the p-HFX internal standard was intended to permit the determination of the absolute weight percent concentrations of the assigned components without necessarily needing to Identify or quantify all the components in the sample mistum.
K gsrars;
The combined NMR spectral dTM were used to assign all of the major and most of the minor components in this
sample as received. The qualitative and quantitative compositional results that were derived from the single trial
NMR internal
analyses are summarized in TABLE-1 on the following page. I have reported both
relative and ihsolute weight p rr^n t concentrations. One possible reason that the absolute wt.% values add up to
more 1004b may be due to the fact that 1assumed all of the components contained 8 carbons. If there were
any shorter chain homologs present 7,6,5, etc. carbons), then the avenge compound molecular weights
would have tw it somewhat less than those used in the calculations. In general, the " F-NMR technique U not `
particularly well suited for Identifying or quantifying small amounts of various fluorochemical homolog Impurity
components
the chains a n very short. A more complete characterization of any other fluorochemical
homologs would require analysis by electrospray MS or a similar technique.
Additional work would be required in an effort to positively verify the tentatively assigned components Hated la . TABLE-1 (denoted by possible). Small mounts of other unidentified impurities are also detected In the'NMR spectra, but additional work would be required in an effort to identify or quantify these other materials.
Copies of the NMR spectra will be provided for you at a later date. If you have any questions about the results in this initial report for FC-93, lot 171. please let me know. I apologize for the delay In completing this initial work.
Tom Xestner
c W e k P a y te -JA * C A aly*aaU b- 234.11-11
KU&rac*:LCiJUtUXX/il
3M Environmental Laboratory
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.-
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3MEnvironmental Laboratory StudyNumber FACT060998.1
ETSS 2 3VI
651 77S 4226 . 04/26/59 09:56 0 :G3/03 N0;341
March 24,1999
.
SAACAnalytical LxbRequest# 57830 - Inlfol Krem far FC-M. tot i n
TABLE-1
Sample: FC-9S, lot 171 (FFOSXTN-A-0834
Overall Quantitative rnrnprnirma1 Results by vH/l,F-NMR Internal Standardizados Analyses
S tru c tu ra l A erip im e n ta
C Fj(C F j)-SOj(-) K<+) CNocmil chain; sanane z 7 tor ciUmlartoe purposes)
NVOt A bsoluta W alfh t* (lin d e tria] measurement)
703%
N M U K i IsIIt i W eight* . (sin tie trial measurement)
6 8 .6 *
C F ^ C F ^ C F C C F jH C F O rS C -) K +) Cntam al aioootneibyl b ra n d ;
assum a x+y 3, z a 0, A y * 0, for calculation purposes)
17 .7 *
173*
. .(C FjJsC IH C FsJ.-SO sC -) K M (Isopropylbranch;assum e x * i fa rcalculadoparpse*)
103*
103*
C J^ rC F IC F sF S C b i-) K M
(Alpfat branch;
x 6 for calcolitico purpotes)
P o sato la F -S F s-C A rS O iM K M (assum e x * t for calculados purposes)
C F K C F jJ^ C tC F jW C F Jj-S O , K M (Internal gem-dim ethyl branch: tssum e x+y 4 sad x * 0 for
cakuliktiaa purposes)
33% 031% a i6 *
33* 036* 0 .1 6 *
P o ssib le C F rS F rC ^ s rS O j K M (assum e z 7 for cslculsdon purposes)
P robable C *H i.rS O j(-) K M (H ydrocarbon sulfonate salt; assume x S tor calculation purposes)
(C F jJjC -C C F iJrS C -) K M (t-bw yi branch: assume z 4 tor calculation purpoass)
. 0 .1 1 * 0 .0 3 1 * 0X327*
0.10% 0X330* 0X326*
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Appendix H: Interim Certificate of Analysis
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INTERIM CERTIFICATE OF ANALYSIS
Revision 1(9/7/00)
Centre Analytical Laboratories COA Reference #: 023-018B 3M Product: PFOS, Lot 171
Reference #: SD-009
Test Name Purity1
Purity: 86.4%____________________ Specifications
Result 86.4%
Appearance
White Crystalline Powder
Conforms
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 Acids 3(IC)
1. TFA 2. PFPA 3. HFBA 4. NFPA Elemental Analysis4: 1. Carbon 2. Hydrogen 3. Nitrogen 4. Sulfur 5. Fluorine
1. Theoretical Value = 17.8% 2. Theoretical Value = 0% 3. Theoretical Value = 0% 4. Theoretical Value = 5.95% 5. Theoretical Value = 60%
Positive
1. 0.017 wt/wt.% 2. 0.007 wt/wt.% 3. 1.355 wtVwt.% 4. 6.552 wt7wt.% 5. 0.003 wt/wt.% 6. 0.004 wtJwt.% 7. <0.001 wt/wt.%
1.00 wt./wt.% 10.60 wtVwt.%
None Detected
0.30 wt./wt.% None Detected Not Applicable3
1. <0.015 wt./wt.% 2. 0.27 wtiwt.% 3. <0.040 wt./wt.% 4. <0.009 wt./wt.% 5. <0.006 wt./wt.% 6. <0.007 wt./wt.% 7. 8.82 wtVwt.%
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 Environmental Laboratory
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INTERIM CERTIFICATE OF ANALYSIS
Centre Analytical Laboratories COA Reference #: 023-018B
Date o f Last Analysis: 08/31/00
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. No endotherm was observed for this sample.
4Sulfur in the sample appears to be converted to SO4 and hence detected using the inorganic anion method conditions. The anion result agrees well with the sulfur determination in the elemental analysis, lending confidence to this interpretation. Based on the results, the S 04 is not considered an impurity.
5TFA HFBA NFPA PFPA
Trifluoroacetic acid Heptafluorobutyric acid Nonofluoropentanoic acid Pentafluoropropanoic acid
6Theoretical value calculations based on the empirical formula, C8F 17S03"K+ (MW=538)
This work was conducted under EPA Good Laboratory Practice Standards (40 CFR 160).
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INTERIM CERTIFICATE OF ANALYSIS
Centre Analytical Laboratories COA Reference #: 023-018B
LC/MS Purity Profile:
Im p u rity 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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A ppendix I: Report Signature Page
ia.u 'C lA A .'^ rx MarvinT. Case D.V.M., Ph.D,,Study Director
Date
John L. Butenhoff, Ph.D., Sponsor Representative
Date
Dale L. Bacon, Laboratory Manager
^ fj,------ I W O
fCrt'i
PA*-
o 3. Date
O
3M Environmental Laboratory
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