Document bBorGb1bgxLQOpkqZ6X41yQMO
3M Medical Department Study: T-6316.5
3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Analytical Report: FACT TOX-013 LRN-U2095
Study Title
Analytical Study 2(N-Ethylperfluorooctanesu1fonamido)-ethanol in Two Generation Rat Reproduction
Amended Analytical Laboratory Report
Determination of the Presence and Concentration of PFOS, M556, PFOSAA, and PFOSA in the Liver and PFOS, M556, PFOSAA, PFOSA, and EtFOSE-OH in the Sera of Crl:CD@BR VAF/PIUS@Rats Exposed to EtFOSE-OH
Data Requirement
Not Applicable
Author
3M Environmental Laboratory
Study Completion Date MAayt s3ig1n,in2g001
Performing Laboratories
Sera Analyses
Liver Analyses
3M Environmental Laboratory Building2-3E-09, 935 Bush Avenue
St. Paul, MN 55106
Battelle Memorial Institute 505 King Avenue
Columbus, OH 43201-2693
Project Identification
3M Medical Department Study: T-6316.5 Argus In-Life Study: 418-009
Analytical Report: FACT TOX-013 3M Laboratory Request No. U2095
Total Number of Pages
143
3M Environmental Laboratory
3M Environmental Laboratory
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3M Medical Department Study: T-6316.5
3M Medical
Department
Study: T6316.5
Analytical
Analytical Study: FACT-TOX-013
Report:
LRN-U2095
FACT TOX-013 LRN-u2095
This page has been reserved for specific country requirements.
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3M Environmental
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3M Environmental Laboratory
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3M Medical Department Study: T-63 16.5
Analytical Study: FACT-TOX-013 LRN-U2095
Analytical Study: 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:CD@BRVAF/Plus@ Rats Exposed to EtFOSE-OH
Study Identification Number: T-631 6.5, 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/l 6100utilized standards that had an expiration date of 2/00.
Liver values generated at contract laboratories were corrected by 3M Environmental Laboratory to reflect the official purity values from the COA. Revised final reports will be solicited from the contract laboratory and will be added as a report amendment at a later date.
Expiration dates on some reagents and solutions were missing.
The analytical report from Battelle is not signed or dated by the Principal Analytical Investigator or laboratory management.
The Quality Assurance Statement in the Battelle analytical report does not include the dates of the QA inspection activities or the dates reported to the Study Director and laboratory management. The Quality Assurance Statement is not signed.
The Argus and Battelle analytical reports do not include the names of all the contributing personnel.
Date
Sponsor Representative
Date
3M Environmental Labora tory
3M Environmental Laboratory
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Analytical Study: FACT-TOX-013 LRN-U2095
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Analytical Study: 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@'BRVAF/PIUS@Rats Exposedto 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
10112/99
6/5/00 - 6114/00 9/11100 - 9113/00
Extraction Data
Draft report
10/26/99 6116/00 911 4/00
10/26/99 6116/00 911 4/00
511 410 1
Amended report
511 410 1
511 410 1
QAU Repredntative
Date
3M Environmental Laboratory
3M Environmental Laboratory
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3M Medical Department Study: T-6316.5
Table of Contents
Analytical Study: FACT TOX-013 LRN-U2095
GLP Compliance Statement............................................................................................. 3
GLP Study-Quality Assurance Statement ...................................................................... 4 Study Personnel and Contributors.................................................................................... 7
Introduction and Purpose ................................................................................................. 8 Test System................................................................................................................. 8 Specimen Collection and Analysis ............................................................................... 9
Specimen Receipt and Maintenance ................................................................................ 9
Chemical Characterization................................................................................................ 10 Dose Confirmation Analyses ........................................................................................ 10
Method Summaries........................................................................................................... 1101 3M EnvironmentalLaboratory ...................................................................................... 11 PreparatoryMethod................................................................................................. 11 Analytical Method.................................................................................................... 11 Analytical Equipment............................................................................................... 11 Deviations .................................................................................................................... 12
Data Quality Objectives and Data Integrity....................................................................... 12 Data Summary. Analyses. and Results ............................................................................ 13
Summary of Quality Control Analyses Results............................................................. 13 Summary of Sample Results........................................................................................ 14
Statistical Methodsand Calculations................................................................................ 14
Statement of Conclusion.................................................................................................. 14
Appendix A: Chemical Characterization. Control Matrices and Dose Confirmation
Analyses........................................................................................................................... 15
Appendix B:Protocol........................................................................................................ 1198
Appendix C: Extraction and Analytical Methods ............................................................... 2307
ETS-8-4.1, Extraction of Potassium Perfluorooctanesulfonateor Other Fluorochemical
Compounds from Serum for Analysis Using HPLC-Electrospray/Mass Spectrometry.
(14 pages) ........................................................................................................................
2308
ETS-8-5.1, Analysis of Potassium Perfluorooctanesulfonate or Other Fluorochemicals
in Serum Extracts Using HPLC-ElectrospraylMass Spectrometry. (9 pages)...................2502
Appendix D: Data Summary Tables ................................................................................. 2611
Appendix E: Data Spreadsheets ...................................................................................... 2644
Appendix F: Example Calculations ................................................................................... 70
Appendix G: Contract Lab Report .................................................................................... 71
Appendix H: Interim Certificate of Analysis ....................................................................... 137
Appendix I: Report Signature Page .........................................................................
141
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Appendix J: Amendment 1 to FACT TOX-013 Final Report
14229
List of Tables
Table 1. Test System Population Demographicsand 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 ln-life #418-009 .................................... 17 Table 11.Tween Dosing Confirmation-Matrix Spikes for Study In-life #418-009 ........... 17
Table 12. Reported Fluorochemical Levels in Sera Analyses in Study FACT TOX-013 ...621 Table 12. Reported Fluorochemical Levels in Sera Analyses in Study FACT TOX-013
(continued) ......................................................................................................... 6222 Table 13. Reported Fluorochemical Levels in Liver Analyses in Study FACT TOX-013...6222
Table 13. Reported Fluorochemical Levels in Liver Analyses in Study FACT TOX-013
(continued) ......................................................................................................... 6233
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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
c
St. Paul, MN, 55144-1000
651-733-5180
P=
Sponsor
John L. Butenhoff, Ph.D., Sponsor Representative
3M Corporate Toxicology - Medical Department
p"
3M Center, Building 220-2E-02
St. Paul, MN 55144-1000
Analytical Chemistry Laboratories
Ser8 Analyses
3M Environmental Laboratory (3M Lab)
I
Kristen J. Hansen Ph.D., Analytical Investigator
Liver Analyses Battelle Memorial Institute Jon C. Andre, Ph.D., Analytical
investigator
3M Lab Contributing Personnel
c
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 0. Johnson Kelly J. Kuehlwein Sally A. Linda Joseph C. Pilon Scott R. Post Ian A. Smith Kathy M. Stock
Anh-Dao Vo Bob W. Wynne
Location of Archives
All original Laboratory. specimens Laboratory. substance.
raw data, protocol, and analytical report have been archived at the 3M Environmental The test substance and analytical reference standard reserve samples, as well as the pertaining to the analytical phase of this study, are archived at the 3M Environmental Control sera and liver will be maintained at the contract lab along with the test
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Introduction and Purpose
The purpose of the study is to determine the presence and concentration of PFOS, PFOSA,
rl
PFOSAA, and MS56 in liver samples and PFOS, PFOSA, PFOSAA, EtFOSEOH, and M556 in
sera samples collected from rats exposed to EtFOSEOH. This study was initiated on 1 October
1998.
P
Five groups of FO generation mate and female rats and 3 groups of Fl 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.
F"
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 Ill were selected for continued
evaluation. Fl generation male and female rats were given appropriate dosages of the test article
111
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:Cl?`BR VAF/Pius@ (Sprague-Dawley) rat
received from Charles River Laboratories, Inc., and assigned temporary numbers until assigned to
the study. Rats were permanently identified using MonePself-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 Fl generation rat
F"
selected for continued observation was identified with a MonePself-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 (418-099)
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Sample specimens were collected by Argus (study 418-009) and sent to the 3M Environmental
r"
Laboratory for analysis. Liver and sera specimens were collected from FO male rats at the
completion of the cohabitation period and FO female rats on day 21 postpartum. Liver specimens
were collected from FO generation litters, and stomach content specimens were collected from the
FO 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.
I""
Specimens Collected from Study Groups I through V (through 11130/98):
Serum Specimene-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 -70% 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.
p"
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 M558 levels were quantitated by external calibration. PFCSEA 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 84-98, lo-l-98 and I-29-99. All specimens were received frozen on dry ice and were immediately transferred to storage at -20C *IO%. 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 8 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% &IO%.
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Chemical Characterization
EffOSE-OH CAS Number: 1691-99-2
Chemical Formula: CBF,rS02N(CH2CH,)CH,CH,0H
Molecular Weight: 571 .O
Chemical characterization information Chemical characterization information presented in tabular form in Appendix Analysis available in Appendix I.
on the test article is presented in tabular form below. on the analytical reference materials used in this study is A (see Tables 8 and 9) and the interim Certificate of
Table 2. Characte&ation of the Test Article in Study FACT TOX-013
IChemkal Name
I
I Source
I
FM-3929 2(N-Etiylperftuorooctane sulfonamido)ethanol
3M
1 Exdration Date
05J2000
1 StoraaeConditions 1
Ambient temperature
Chemical Lot #
30035,30037,30039
Physical Description
waxy solii
l Tha purity of the test article
clwa&rtzauan
is oaming
crr~ofan~~kissued.
I To be determined' determined nominally by NMR analysisS. ubsequentchemical and thii analytical report wiPba amended to indicatethe putity whena
-
Do8econtinnatponAnaIyses
The dose confirmation data were collected according to a method that was not fully validated. Dose confirmation analyses were performed on test article samples taken at the start of dosage, at 6 weeks, and at the end of dosage during the in-life phase of the study.
Dose confirmation analyses were performed on 3 dose levels collected during the in-life phase of
the study: the resultsare presented in Appendix A (see Tables 10 and 1 I).
pa
Dose confirmation was performed by diluting the Tween dose samples with Mitli-Q water into the
linear range of the instrument. For each sample, a matrix spike was prepared (at approximately XI-tOO% 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).
3MtrvlmlLaboratory
.-
PREPARATORY METHOO
l ETS-84.1, "Extraction of Potassium Perfluorooctanesulfonate
or Other Fluorochemicat
Compounds from Serum for Analysis using HPLC-ElectrospraylMass
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 .O mL of methanol, then filtered through a 3cc plastic syringe attached to
a 0.2pm nylon filter into a glass autovial.
ANALWCAL METNOD
l ETS-8~8.1, "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 HPLCESMSMS. For example, molecular ion 499, selected as the primary-ion for PFOS (C,F,,S03-) analysis, was fragmented further to produce ion 99 (FSQ-). The characteristic product-ion 99 was monitored for quantitative analysis.
ANAL~~CAL EQWMENT
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' BetasilTW C,B 2x50 mm (5 pm)
p"
Column temperature: Ambient
Mobile phase components:
Component A: 2mM aqueous ammonium acetate
Component B: methanol
Flow rate: 300 j.rL/min
Injection volume: 10 uL
Ic" Solvent Gradient: 10 minutes
Start at 4O%B
Hold at 40WB for 1 minute
Increase to 95%B over 3.5 minutes
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Hold at 95Or6B for 2 minutes
Return to 40hB over 0.5 minutes
Hold at 40r6B for 3 minutes
Mass Spectrometer: Micromass@ API/Mass Spectrometer Quattro II"Triple Quadrupole system
Software: Mass Lynx" 3.2 Cone Voltage: 20-80 V Collision Energy: 2545 eV Mode: Electrospray Negative Source Block Temperature: 150C &I 0C c Z-spray source Analysis Type: Multiple Reaction Monitoring (MRM)
Table 3. Negative Ions Monitored in 3M Laboratory Analyses
R
EtFOSE-OH
630.0
M556
558.0
THPFOS
427.0
59.0 78.0, 169.0
80.0
I"r
Deviations from the original protocol and methods are documented in the table below:
Table 4. Deviation Summaw for FACT TOX-013
Deviation
Pie was usad instead
Oxforddiiser
I0.2-l .OmL of for extraction
sample instead
was used of 1.OmL.
Milk curd samples were not analyzed.
Date(s) of Occurrence
lOl12l99 Entire study
Impact on Study
I
Standards and samplesware preparad identically. No adversa impact on study.
Current work indicates that vdutnas 20.5 mL provide results equivalent to 1 mL extraction volumes. Resub of sample I volumes 46 mL have not been vaMat6U I andwilbemarkedinthedatatabk.
No milk curd data is available for the final
report
Data Quality Objectives and Data Integrity
prr
The following data quality objectives (DQOs) were indicated in the method performance section of
ETS-8-5.1 I `Analysis of Potassium Perfluorooctanesulfonate
or Other Fluorochemicals in Serum
Extracts Using HPLC-Electrospray/Mass
Spectrometry*:
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l Linearity: The coefficient of determination (rZ) equal to or greater than 0.980
l Limits of Quantitation (LOO): The LOCI 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.
l Acceptable Spike Recoveries: 70-I 30%
Data Summary, Analyses, and Results
With the exceptions noted in this report, data quality objectives for the analytical phase of this
la 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
*rr
included in this report. The data in this report reflect only that obtained from specimens extracted
on, or after October 11, 1999.
Summary of QuaMy Contml Anatyses Results
l Linearity: The coefficient of determination (r*) of the standard curves werer0.980.
l Calibration Standards: Quantitation of the target analytes was based on linear regression analysis (l/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).
l Limits of Quantitation (LOQ): The LOCI 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
I-- ~PFOSAA
1
20.5 ppb
I
1 EtFOSE-CH
1
36.2 ppb
I
I M556
I
24.9 ppb
I
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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: 10%.
Precision was determined
by analysis of MS/MSD and was reproducible
to within
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
prr
spikes were within i30% 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
surrogateresponse 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 quantiiative to f30% 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
l Samples from Control Animals: Low levels of PFOS, PFOSA, PFOSAA, EtFOS&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.
ila
l Samples from Dosed Animals: In general, PFOS, PFOSA, PFOSAA, EtFOSEOH, 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 0 and E.
Statistical Methods and Calculations
Statistical Appendix TOX-013.
methods were limited to the calculation of means and standard deviations. See F for example calculations used to generate the liver and serum sample data in FACT
Statement of Conclusion
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 EtFOS60H during the in-life phase of the study.
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Appendix A: Chemical Characterization, Confirmation Analyses
Control Matrices and Dose
Table 6. Characterization of the Control Matrices Used for Sera Analyses in Study FACT TOX-013
I Control Matrix
sowca
Expiration Date Storage Conditions Chernloal Lot # Physical Description N/R-not racorded
3M Lab
I
Rat Serum I (TN-A-2001 1
siirna
2010 Ambient 17HD308 Rat !3enrm
Rabbit Serum (TN-A-2573) I
Sigma 2010 Ambient 118H8418 Rabbit Serum
Table 7. Characterization of the Control Matrices
- Used for Liver Analyses in Study FACT TOX-013
Location
I Battelk Memorial Institute
I
I
Rat Liver
source
Expiration Date
Harlan N/R
Storage Condiins
N/R
Chemical Lot # Physical Description
N/R
Rat Liver
Nm-notracordad
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Table 8. Characterization of the Analytical Reference Materials Used for Sera Analyses in Study FACT TOX-013
Location
3M Lab
Source
3M Specially
N/R
NIR
Chemicals
Expiration Date
08/31/01
01/01/2010
01/01/2010
Storage Conditions
Ambient temperature
Ambient temperature
Ambient temperature
Chemical Lot
171
L-l 5709
NB 112999-99
Number
Physical Description
White crystalline powder
Light yellow waxy solii
Tan waxy solid
Puritv
86.4%
TBD
TBD
*Surrogate standard- 1H,l H,2H,2H-Tetrahydroperfluomctanesulfmic acid N/R-not recorded TBD-to be determined NA-not applicable
3M ICPiPCP Division 01/01/2010
Ambient temperature 936
Amber waxy solii TBD
3M 01/01/2010
NB 113047-80 White powder
TBD
Table 9. Characterization of the Analytical Reference Materials Used for Liver Analyses in Study FACT TOX-013
Battelle Memorial Institute
ICN Biomedicals 01/2010
53406 Brown waxy solid
NA
Chemical Lot
171
NB 113047-80
617
Number
L-l 5709
59909
PDheysscircipatlion Nhitapocvq@stadlliwnr Whk powder N/R Lwiaihxty yeslololiwd N/R
Puritv
I 86.4%
I
TBD
1 TBD
1 TBD
1
NA
*Surrogate standard- 1H,l H,2H,2H-Tetrahydropertluorcoctanesulfcmic acid N/R-not recorded TBD-to be determined NA-not applicable
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FACT TOX-013 LRN-u2095
Group Dose Group I-Control 0 m@mL
Sample Number
Expected cont. EtFOSE hslmL1
Measumd Cont.
EtFOSE
EtFOSE (na!mL) I Ye Recovwy Accuracy I
Group 2-0.2 m9imL
Group 3-l .O m@mL
Group 4-2.0 mglmL
Group ".O m@mL
Homogeneity Samples3.0 mghnL
NA = Not applicable
B418-009-E, 07/l!Y98
&416-009-A, 05iO6i96 1 of6T
B418-009-A, 06KW98
3of6M
I
&418-009-A, 06fw98 5ofSB
364oooo 32!5oooo
I
369oooo
3790000
121 108
123
126 I
Table 11. Tween Dosing Confirmation-Matrix
Spikes for Study In-life #418-809
I
Sample Number
Expected Cone. EtFOSE (nglml)
Measured Cont. EtFOSE (n@mL)
EtFOSE % MS Recovety Accuracy
.c6lowS-MS
I
1200
I
NA
I
NA
I
B418-009-B, 07115t98-Ms 1
1200
!
NA
I
NA
I
900
818
91
B-4184lO9-c. 07/15/9&Ms
900
826
92
B-416-009-D, 06/08&6-MS
B-418-OosD, 07/15/964s
&-418-009-E, -MS
I
I
B-416-009-E. 07115&8-MS !
1100
!
1089
99 I
B-418409-A, 0!5KW98
1100
GaA-Vn .3
I
RR
I
1 of6T-MS
I
-
I
B-418-009-A, OWOSl98
3of6M-MS
1100
1063
I B418-050o9f-6AB,-MS06KW98 1100 944 NA = Not appliiblt,
98 I
86 I
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Appendix B: Protocol
Analytical
Analytical Study: FACT-TOX-013
LRN-U2095
Report:
FACT TOX-013 LRN-U2095
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pr*
Analytical
Analytical Study: FACT-TOX-013
Re~~~~&~~~~
LRN-U2095
,9/3
"Ws-
3M ENVIRONMENTALLABORATORY
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: Z(N-Ethylperfluorooctanesulfonamido)-ethanol (N-EtFOSE-OH)
:Name and address of Sponsor:
Marvin Case 3M Toxicology Services 3M Center
Building 220-2E-02 St. Paul, MN 55144
Name and address of testing facility:
3M Environmental Technology and Serv@s
935 Bush Avenue, Building 2-33-09 1
St. Paul, MN 55106
/
Experimental start date: Expected termination date: December 31,1998 Method numbers and revisions:
FACT-M-1.0, Extraction of Potassium Peffluorooctanesulfonate or Other Anionic Surfactants from Liver for Analysis Using HPLC-Electrospray/Mass
Spectrometrj
FACT-M-2.0, Analysis of Fluorochemicals in Liver Extracts Using HPLCElectrospraybkss Spectrometry
F"
FACT-M-3.0, Extraction of Potassium Perfluorooctanesulfonate or Other Anionic
Surfactants from Serum for Analysis Using HPLC-Electrosprayhkss
Spectrometry
cs
FACT-M-4.0, Analysis of Fluorochemicals in Serum Extracts Using HPLC-
ElectrosprayIMass Spectrometry
Author: Lisa Clemen
FR -/la kl AZ Kris Hansen Study Director
4lrsl'rtl
Date
Marvin&e Sponsor Representative
/4k/fw
Date
4
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Laboratory
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LRN-U2095
1.0 PURPOSE
The analytical portion of this dosing study is designedevaluatethe levels of perfluorooctane sulfonate (PFOS), or anothermetabolite of 2(N-ethylpeffluorooctanesulfomunido)-ethanol (NFtFOSE-OH) designatedby 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 ResearchLaboratories.
2.0 REGuLAT~RYCOM~LI.~NCE
This study is conducted in compliance with the Food and Drug Administration Good Laboratory . Practices regulation as statedin 21 CFR 58. Any exceptions will be noted in the final report.
3.0 TESTMATERIALS
3.1 Test, control, and reference substances and matrices
p"
3.1.1 Anaiyticai reference substance: Potassium peffluorooctanesulfonate (PFOS), lot
# 217
3.1.2 Analytical reference substance matrix: Rat liver and serum
3.13 Analytical control substance: None
3.1.4 Analytical control substance matrk Rat liver and serum
3.2 Source of materials
3.2.1 Analytical reference substance: 3M Specialty Chemical Division; traceabihty information will be included in the final report
3.2.2 Analytical reference substance matrix: Argus ResearchLaboratories; traceability information will be included in the final report
3.2.3 Analytical contiol matrix:
3.23.1 Rat liver - Argus ResearchLaboratories; 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 Number of test and control samples. Liver samplesfor testing were received from 40 test animals and 10 control animals. Serum samples will be tested at the discretion of the Study Director.
c"
3.4 Identification of test and control samples: The samples are identified using the Argus ResearchLaboratories 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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LRN-u2095
3.5 Purity and strength of materMs: Characterization of the purity and identity of the referencematerial is the responsibility of the Sponsor.
3.6 Stability of test material: Characterization of the stability of the test material is the responsibility of the Sponsor.
3.7 Storage conditions for test materials: Test materials are stored at room temperature. Samples are storedat -20 f 10 OC.
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 sheetsof chemicals used. Wear appropriatelaboratory attire, and follow adequateprecautions for handling biological materials and preparing sampIesfor analysis.
4.0 EXPERIMENTAL - Overview
Tissues from animals dosedasdescribedin Argus ResearchLaboratories 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 selecttissues.
Initially, all liver sampleswill be analyzedfor PFOS by electrospray/massspectrometry (ES/MS). On the basis of findings from theseanalyses,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 - Anaivtical Methods
P
5.1 FACT-M-1.0, Extraction of Potassium Perfluorooctanesulfonateor Other Anionic
Surfactants from Liver for Analysis Using HPLC-ElectrosprayIMas Spectrometry
5.2 FACT-M-2.0, Analysid of Fluorochemicals in Liver Extracts Using HPLCElectrospray/Mass Spectrometry
5.3 FACT-M-3.0, Extraction of Potassium Peffluorooctanesulfonate or Other Anionic Surfactantsfrom Serum for Analysis Using HPLC-ElectrosprayIMass Spectrometry
5.4 FACT-M-4.0, Analysis of Fluorochemicals in Serum Extracts Using HPLCElectrosprayIMass Spectrometry
p"
6.0 DATA ANALYSIS
6.1 Data transformations and analysis: Data will be reported asthe concentration (weight/weight) of fluoride per tissue or sample, or of PFOS per unit of tissueor fluid.
6.2 Statistical analysis: Statistics usedmay include regressionanalysis of the serum concentrations over time, and standarddeviations calculated for the concentrations within each dosegroup. If necessary,simple statistical tests, such as Student's t test, may be applied to evaluate statistical difference.
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LRN-u2095
7.0 ~~~~~N~CEOFRA~DATAANDRECORD~
7.1 The following raw data and recordswill be retained in the study folder in the archives
R
according to AMDT-S-8:
7.1.1 Approved protocol and amendments
p" 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 separatelyfrom 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 maintenancelogs
p" 7.2.4 Standard Operating Procedures,Equipment Procedures,and Methods
7.2.5 Appropriate specimens.
8.1 3M Environmental Laboratory Quality System Chapters I,5 and 6
8.2 Other applicable 3M Environmental Laboratory Quality System StandardOperating Procedures
Fan
9.0 ATTACHMENTS
9.1 FACT-M-LO, Extraction of Potassium Perfluorooctanesulfonateor 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 HPLCElectrosprayhkss Spectrometry
9.3 FACT-M-3.0, Extraction of Potassium Perfluorooctanesulfonateor Other Anionic Surfactants from Serum for Analysis Using HPLC-Electrospray/hkss Spectrometry
9.4 FACT-M-4.0, Analysis of Pluorochemicals in Serum Extracts Using HPLCElectrospray/Mass Spectrometry
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FACT TOX-L01R3 N-U2095
LRN-u2095
w
Study Title Combined Oral (Gavage) Fertility Development an&PerinataL&ostnatal
Reproduction Toxicity Study of N-EtFOSE in Rats
PROTOCOL AMENDMENT NO. I
Amendment Date: July 28,1999
Performing Laboratory 3M Environmental Technology & Safety Services
3M Environmental Laboratory 935 Bush Avenue St. Paul, MN 55106
Laboratory Project Identlffcation ET&SS FACT-TOX-013 LJRN U2095
3/U Environmental Laboratory
3M Environmental
Laboratory
3M Environmental Laboratory
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Report:
FACT TOX-L01R3 N-U2095
LRN-u2095
Protocol FACT-TOX-073 Amendment I
This amendment modifies the following portion(s) of the protocol:
1. PROTOCOL READS: The proposed study completion date is listed as 12/3l/98. AMEND TO READ: The proposed study completion data is 6/30/00.
REASON: The proposed completion date was changedto allow time for analyzing all matrices of interest.
Amendment Approval
Marvin CasePh.D., SponsorRepresentative
Ibis J. Hknsen Ph.D., Study Director
Date
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Analytical
Report:
FACT TOXL-0R13N-U2095
LRN-u2095
Combined Oral (Gavage)Fertility Development andPekaWPostnatal Reproduction Toxicity Study of N-EtFOSE in Rats
PROTOCOL AMENDMENT NO. 2
Amendmenf Date: September lo,1999
Perfarming Laborafo# 3M Environmental `lk&nology & Safety Services
3M Environmental Laboratory 935 Bush Avenue St. Paul, MN 55106
Laboratory Project IdenfMcafion w ET&SS FACT-TOX-013
LIRN u2095
-
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LRN-u2095
Protocol FACT-7-0X-073 Amendment 2
This amendment modifies the following portlon(s) of the protocol:
I. PROTOCOL READS: The protocol statesthat liver will be extracted and analyzed at the 3M Environmental Laboratory.
AMEND 7'0 READ: The liver specimenswill be extracted and analyzed at Battelle Memo&l Institute, 505 King Avenue, Cohrmbus, Ohio 43201-2693.
f?EASON: The liver specimenswill be sent to Battelle Memorial Institute for extraction and analysis due to time constraints in the 3M Environmental Laboratory.
2. PROTOCOL READS: The protocol statesthat serum specimenswill be extracted and analyked following methods:
FACT-M-3.0, "Extraction of Potassium Petfluorooctanestionate or Other Anionic Suifactants fkom Serum for Analysis Using HPLC-Electrosprayhkss Spectrometry' FACT-M-4.0, `Analysis of Fluorochemicals in Serum Extracts Using HPLCElectrospray/Mass Spectrometry"
AMEND TO READ: The serum specimenswill be extracted and analyzed following methods:
ET&8-4.1, "Extraction of Potassium Pefluorooctanesulfonate or Other Fluorochemical Compounds from Serum for Analysis Using HPLC-Electrospray Mass Spectrometq? ETS-84.1, "Analysis of Potassium Perfluorooctanesulfonate or Other Fluorochemical Compounds in Serum Extracts HPLC-Electrospray Mass Spectrometry"
i?EASON; `The extraction and analytical methods FACT-M-3.0 and FACT-M-4.0, respectively, were updatedon 04/27/99 to ETS-8-4.1 and ETS-8-5.1.
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FACT TOX-013 LRN-u2095
Protocol FACT-TOX-013 Amendment 2
3. PROTOCOL READS: The protocol statesthat liver specimens will be extracted and analyzed following methods:
FACT-M-1.0, "Extraction of Potassium Perfluorooctanesulfonate or Other Anionic
surfactants from Liver for analysis Using HPLC-Electrospray/Ma Spectrometry"
FACT-M-2.0, "Analysis of Frluorochemicals in Liver Extracts Using HPLC-
.
Electrospray/Mass Spectrometry"
AMEND TOREAD; The liver specimens will be extracted and analyzed following m&od:
,
M&hod for Analysis of Perfluorooctane Sulfonate (PFOS) in Rat liver by LCAWMS, Version 1.0
REASON: Since the liver extraction and analysis was sub-contractedto BatteUe Memorial Institute, this amendment was written to include their liver methods and titles.
Amendment Approval
., Sponsor Representative
Kristen J. Hansen Ph.D., Study Director
P 3M Envirvtymmtel Laboratory
3M Environmental
Laboratory
3M Environmental Laboratory
sP9/g9
Date
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Analytical
Report:
FACT TOX-L01R3N-U2095
LRN-u2095
Study Title Analytical Study 2(N-Ethylperfluorooctauesulfomunido)-ethanol in
Two GenerationRat Reproduction
PROTOCOL AMENDMENT NO. 3
Amendment Date:
octoher 4,1999
Performing Laboratory 3M Environmental Technology & Safety Services
3M Environmental Laboratory 935 Bush Avenue St. Paul, MN 55106
Labora tory ProJect ldentification ET&SS FACT-TOX-013 LIRN U2095
3M Environmental
Laboratory
cri
3M Environmental Laboratory
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Report:
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FACT TOX-013 LRN-u2095
Protoco/ FACT Tax-013 Amendment Number 3
This amendment modifies the following portion(s) of the protocol:
I. i'ROTOCoL READS: Kristen J. Hansen, Ph.D. is the Study Director.
AME~VD TO READ:
F"
JamesK Lundberg, Ph.D. is the Study Director.
REASON:
Original study design has changed due to availability of resources and James K. Lundberg
will begin serving asthe study director for FACT-TOX-013 as of 4 October 1999.
2. PROTOCOL READS:
Section 7.1 statesthat the following ray data and records wilI 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, Section 7.2 statesthat supporting recordsto be retained separately from the study folder in the archives according to AMDT-S-8 will include at least the following: Training records, calibration records; instrument maintenance logs; StandardOperating Procedures,Equipment Procedures,and Methods; and appropriatespecimens.
AMEND TO READ:
. Section 7 states:"The original data, or copies thereof, will be available at the 3M Environmental Laboratory to facilitate audits of the study during its progress andbefore acceptanceof the final report. When the final report is completed, all original paper da@ including: approved protocol and amendments,study correspondence,shipping records, raw data, approved final report,`and electronic copies of datawill be retained in the archives of the 3M Environmental Laboratory. All corresponding training records, calibration records,. instrument maintenance logs, standardoperating procedures,equipment procedures, and methods will be retainedin the archives of the facility performing eachanalysis.
REASON:
CI To direct subcontract laboratories in the disposition of the items listed above.
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FACT TOX-013 LF!N-u2095
Pmfocol FACT Tax-013 Amendment Number 3
3. PROTOCOLREADS: Disposition of 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 of analysis and submission of the sub-contract laboratary(s)
final report. The specimens will be returned with the following documentation: the signed
m
original chain of custody and records of storageconditions while at the sub-contract facility.
REASON:
To define in detail the appropriate disposition of specimens analyzed at subcontract laboratories.
Amendment Approval
Marv Case,D.V.M., Ph.D., Sponsor Representative
Kristen J. Hansen, Ph.D., Previous Study Director
Dale L. Bacon, Ph&y 3M Environmental Laboratory Managekent
3h4 Envhnmental Laboratory
3M Environmental
Laboratory
3M Environmental Laboratory
Date
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Report:
FACT TOX-0L13RN-U2095
LRN-II2095
Study Title Analytical Study of 2(N-Ethylperfluorooctanesulfwxunido)-ethauol in
Two GenerationRat Reproduction
PROTOCOL AMENDMENT NO. 4
Amendment Date: 20 January2000
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 Labom tory
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LRx-u2095
Protocol lRN-U2095
AmendmentNumber 4
This amendment modifies the following portion(s) of the protocol:
1. PROTOCOL READS:
The study director for the present study was identified in the protocol as James K. Lundburg, Ph.D.
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 11(. Lundburg, has been reassigned to the role of Principle Analytical Investigator.
REASON:
The role of study director was reassigned in an effort to ensure compliance with Good Laboratory Practice Standards that outline study personnel requirements (refer to 21 CFR Part 58).
2. PROTOCOL READS: The sponsor for the present study was identified as Marvin T. Case, D.V.M., Ph.D.
AMEND TO READ:
Tlie 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 atid workload are more evenly balanced.
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FACT TOX-013
LRN-u2095 Prutocol LRl%U2095
Amendment Number 4
Amendment Approval
John L ButenAof Ph.D., Sponsor Representative
Marvin T. Case,D. KM, Ph.D., Incoming Study Director
Date fl
3M Environmental Laboratory
3M Environmental
Laboratory
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..-. _.- -- ._._.
__
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Report:
LRN-U2095
FACT TOX-013 LRN-u2095
Study Title Analytical Study of 2(N-Ethylpeffluorooctanesulfonamido)-ethanol in
Two Generation Rat Reproduction
PROTOCOL AMENDMENT NO. 5
Amendment Date: August 3I,2000
Performing Laboratory 3M Environmental Technology & Safety Services
3M Environmental Laboratory 935 Bush Avenue
St. Paul, MN 55106
Laboratory Project ldentificatlon FACT-TOX-0 13
ET&&S LRN U2095 Argus Study: 418409 3M Medical Department Study: T63 16.5
p"
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Report:
FACT TOX-0L13RN-U2095
LRN-u2095
Protocol FACT TOX-073 Amendmeni No. 5
This amendment modifies the following portion(s) of the protocol:
F-
7. PROTOCOL READS: The Principle Analytical Investigator for the present study was identified
asJames K. Lundberg, Ph.D.
2. AMEND TO READ: The role of Principle Analytical Investigator for the present study was reassignedto K.&ten J. HansenPh.D.
REASON: The role of Principle Analytical Investigator was reassigneddue to availability of resources.
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FACT TOX-013 LRN-u2095
Protocol FACT TOX-013 Amendment No. 5
Amendment Approval
John L. Butenhos Ph.D., Sponsor Representative
/
Date
TCG&L
M., Ph.D., Study Director
3M Environmental Laboratory
3M Environmental
Laboratory
Ca
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FACT TOX-013 LRN-u2095
Appendix C: Extraction and Analytical Methods
This appendix includes the following methods:
4
ETS-8-4.1, Extraction of Potassium Perfluorooctanesulfonate or Other Fluorochemical
Compounds from Serum for Analysis Using HPLC-ElectrosprayNlass Spectrometry,
-
(14 paws)
ETS-8-5.1, Analysis of Potassium Perfluorooctanesulfonate or Other Fluorochemicals in
Serum Extracts Using HPLC-ElectrosprayIMass Spectrometry, (9 pages)
C
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LRN-u2095
3M ENVIRONMENTALLABORATORY
METHOD
F"
EXTRACTIONOFPOTASSIUMPERFWOROOCTANESULFONATEOR OTEIZR
FLUOROCHEMICAL COMPOUNDS FROM SERUM FOR ANALYSIS USING HPLC-
ELECTROSPRAY/MASSSPECTROMETRY
Method Number: ETS-8-4.1
Adoption Date: 03/01/99
Author: Lisa Clemen, Glenn Langenburg
Revision Date: q[a-/lqff
Approved By:
Laboratory Manager Group Leader
R
Date
+W/YY
Date
&l/h/Y 4
Date
1.0 SCOPEANDAPPLICATION
L**
1.1 Scope: This method is for the extraction of potassium perfluorooctanesulfonate (PFOS) or other fluorochemical compounds f?om serum.
1.2 Applicable compounds: Fluorochemical surfactantsor other fluorinated compounds.
1.3 Matrices: Rabbit, rat, bovine, monkey, and human serum or other fluids asdesignated in the validation report.
Word6/95
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ETS-8-4.1 Extraction of PFOS from Serum
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2.0 SUMMARY OF METHOD
2.1 This method describesthe procedure for extracting potassium perfluorooctanesulfonate (PFOS) or other fluorochemical surfactants from serum, or other fluids, using an ion pairing reagentand methyl-tert-butyl ether @&BE). In this method, seven fluorochemicals were extracted: PFOS, PFOSA, PFOSAA, EtFOSE-OH, PFOSEA, M556, and surrogatestandard(see3.0 Definiiiorts). An ion pairing reagentis added to the sample and the analyte ion pair is partitioned into MtBE. The MtBE extract is removed and put onto a nitrogen evaporatoruntil dry. Each extract is reconstituted in 1.O mL of methanol, then filtered through a 3 cc plastic syringe attachedto a 0.2 pm nylon filter into glass autovials.
2.2 These sample extracts are analyzed following method ETS-8-5.1 or other appropriate methods.
3.0 DEFINITIONS
px"
3.1 PFOS: perfluorooctanesulfonate (anion of potassium salt) C,F,,SO,
3.2 PFOSA: perfluorooctane sulfonylamide C,F,,SO,NH,
PI
3.3 PFOSAA: perfluorooctane sulfonylamido (ethyl)acetate C,F,,SO,N(CH,CH,)CH,CO,'
3.4 EtFOSE-OH: Z(N-ethylperfluorooctane sulfonamide)-ethyl alcohol C,F,,SO,N(CH,CH,)CH,CH,OH
3.5 PFOSEA: perfluorooctane sulfonyl ethylamide C,F,,SO,N(CH,CH,)H
3.6 M556: C,F,,SOzN(H)(CH2COOH)
-
3.7 Surrogate standard: lH-lH-ZH-2H perfluorooctane sulfonic acid
p"
4.0 WARNINGS AND CAUTIONS
4.1 Health and safety warnings
4.1.1 Use universal precautions, especially laboratory coats, goggles, and gloves when
pa*
handling animal tissue, which may contain pathogens.
5.0 INTERFERENCES 5.1 There are no interferencesknown at this time.
6.0 EOUIPMENT
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 Centrifkge, Mistral 1000or IEC 6.1.3 Shaker, Eberbachor VWR
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6.1.4 Nitrogen evaporator,Organomation 6.1.5 Balance (+ 0.100 g)
7.0 SUPPLIES AND MATERIALS
7.1 Gloves
7.2 Eppendorf or disposable pipettes
7.3 Nalgene bottles, capableof 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
p4
7.7 Labels
7.8 Oxford Dispenser - 3.0 to 10.0mL
p*
7.9 Syringes, capableof measuring 5 PL.to 50 FL
7.10 Graduatedpipettes
7.11 Syringes, disposableplastic, 3 cc
7.12 Syringe filters, nylon, 0.2 l.trn,25 mm
7.13 Timer
P-.
7.14 Crimp cap autovials and caps
7.15 crimpers
Note: Prior to using glassware andbottles, rinse 3 times with methanol and 3 times with
Mini-Q'" water. Rinse syringes a minimum of 9 times with methanol, 3 rinses from 3 separatevials.
8.0 REAGENTS AND STANDARDS
8.1 Type I reaEnt grade water, Milli-QTM or equivalent; all water used in this method should
Pi%+
be Milli-Q water andmay be provided by a Milh-Q TOC PlusTMsystem
8.2 Sodium hydroxide (NaOH), J.T Baker or equivalent
8.3 Tetrabutylammonium hydrogen sulfate(TBA), Kodak or equivalent
8.4 Sodium carbonate(NqCOs), J.T. Baker or equivalent
8.5 Sodium bicarbonate (NaHCO,), J.T. Baker or equivalent
8.6 Methyl-T-Butyl Ether, Omnisolv, glass distilled or HPLC grade
8.7 Methanol, Omnisolv, glass distilled or HPLC grade
8.8 Serum or blood, frozen from supplier
8.9 Fluorocbemical 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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FIS
8.9.3 PFOSAA (3M Specialty Chemical Division), molecular weight = 585
89.4 EtFOSEOH (3M Specialty Chemical Division), molecular weight = 570
8.9.5 PFOSEA (3M Specialty Chemical Division), molecular weight = 527
89.6 M556 (3M Specialty Chemical Division), molecular weight = 557
89.7 Surrogate standard:4-H, perfluorooctane sulfonic acid (I-H,l-H, 2-H, 2-H C,F,,SO,H) molecular weight F 428
89.8 Other fluorochemicals, as appropriate
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 SO0mL Milli-QT" water, mix until all solids are dissolved. Store in a 1 L Nalgene bottle.
8.10.2 1 N sodium hydroxide (NaOH): Dilute 10 N NaOH 1:lO. Measure 10 mL of 10 N NaOH solution into a 100mL volumetric flask and dilute to volume using
Milli-Q'M water. Store in a 125mL Nalgene bottle.
8.10.3 0.5 M tetrabutylammoniurn hydrogen sulfate (TBA): Weigh approximately 169 g
of TBA into a 1 L volumetric containing 500 mL Milli-QTM water. Adjust to pH
lg using approximately 44 to 54 mL of 10 N NaOH (While adding the last mL of
NaOH, add slowly becausethe pH changesabruptly). Dilute to volume with Milli-QTM water. Store in a 1 L Nalgene bottle.
8.10.3.1 TBA requires a check prior to eachuse to ensurepH = IO. Adjust as neededusing 1 N NaOH solution.
8.10.4 0.25 M sodium carbonate/sodiumbicarbonatebuffer (Na&O,MaHCO,): Weigh approximately 26.5 g of sodium carbonate(Ha&O,) and 21.0 g of sodium
bicarbonate @JaHCO,)into a 1 L volumetric flask and bring to volume with Milli-
Q" water. Store in a 1 L Nalgene bottle.
ktandards preparation
8.11.1 PreparePFOS standardsfor the standardcurve.
8.11.2 Prepareother fluorochemical standards,as appropriate. Multicomponent
fluorochemical standardsareacceptable(for example, one working standard solution containing 1 .OOppm PFOS, 1.02ppm PFOSA, 0.987 ppm PFOSAA, and
1.10ppm EtFOSE-OH.)
8.11.3 Weigh approximately 100mg of PFOS into a 100 mL volumetric flask and record the actual weight.
8.11.4 Bring to volume with methanol for a stock standardof approximately 1000 ppm Q.&W.
8.11.5 Dilute the stock solution with methanol for a working standard 1 solution of approximately SOppm.
8.11.6 Dilute working standard 1with methanol for a working standard2 solution of approx. 5.0 ppm.
ETS-P-4.1 Extraction of PFOS from Serum
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8.11.7 Dilute working standard 1 with methanol for a working standard3 solution of approx. 0.50 ppm.
8.12 Surrogate stock standard preparation
8.12.1 Weigh approximately 50-60 mg of surrogatestandard 1-H,l-H, 2-H, 2-H, C,F,,SO,H into a 50 mL volumetric flask and record the actual weight.
8.12.2 Bring to volume with methanol for a surrogatestock of approximately 1000-l 200 PPm. *
8.12.3 Preparea surrogateworking standard. Transfer approximately 1 mL of surrogate stock to a 10 mL volumetric flask andbring to volume with methanol for a working standardof 100 ppm. Record the actual volume transferred.
9.0 SAMPLEHANDLING 9.1 All samples arereceived frozen and must be kept frozen until the extraction is performed. 9.2 Allow samples to thaw to room temperatureprior to extraction.
10.0 QUALITYCONTROL
10.1 Solvent Blanks, Method blanks and matrix blanks
_- - T
;.I -.A.. _nl;qrc+
10.1.2 Easxmtraectht otwdobl1a.n0kms.L aliquots of Milli-QTM water following this procedure and use F--
10.1.3 Extract two 1.OmL aliquots of the serum following this procedure and use as
matrix blanks. See11.1.4.
p4
D.2 Matrix spikes
10.2.1 Prepareand analyze matrix spike and matrix spike duplicate samples to determine the accuracy of the extraction.
10.2.2 Prepareeachspike u&g a sample chosenby the analyst, usually the control matrix received`with each sample set.
10.2.3 Expected concentrationswill fall in the mid-range of the initial calibration curve.
Additional spikes may be included and may fall in the low-range of the initial
calibration curve.
10.2.4 Prepareone matrix spike and matrix spike duplicate per 40 samples, with a
p-4
minimum of 2 matrix spikes per batch.
0.3 Continuing calibration checks
10.3.1 Preparecontinuing calibration check samplesto ensurethe accuracy of the initial calibration curve.
10.3.2 Prepare,at a minimum, one continuing check per group of 10 samples. For example, if a sample set = 34, four checks arepreparedand extracted.
10.3.3 Prepareeachcontinuing calibration check from the samematrix used to prepare the initial curve.
Fonmental Laboratory
ETS-8-4.1
Exfraction of PFOS fromSerum
3M Environmental Laboratory
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10.3.4 The expectedconcentrations 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 necessaryif the analyst must quantitate using only the low end of the calibration curve (for example, 5 ppb - 100ppb, rather than 5 ppb - 1000ppb).
11.0 CALIBRATIONANDSTANDARDIZATION
11.1 Prepare,matrix calibration standards
11.1.1 Transfer 1 mL of serum to a 15 mL centrifuge tube.
11.1.2 If most sample volumes are less than 1.OmL, extract standardswith matrix
volumes equal to the sample volumes, Do not extract less than 0.50 nil, of matrix. Record eachsample volume on the extraction sheet.
11.1.3 While preparing a total of twenty aliquots in 15mL centrifuge tubes, mix or shake between aliquots.
11.1.4 Two 1 mL aliquots, or other appropriatevolume, serve as matrix blanks. Typically use the standardconcentrations and spiking amounts listed in Table 1,
at the end of this section, to spike, in duplicate, two standardcurves, for a total of
eighteen standards,two matrix blanks, andtwo method blanks.
11.1.5 Refer to validation report ETS-8-4.0 & ETS-8-5.0-V-1, which lists the working rangesand the Linear Calibration Range (LCR) for calibration curves.
11.1.6 Use Attachment D as an iid in calculating the concentrationsof the working
standards. SeeSection 13.0 to calculate actual concentrations of PFOS in
calibration standards.
(14
11.2 To eachstandard,blank, or continuing check, add appropriate amount of surrogate
working standardfor the concentration to fall within the calibration curve range 5 ppb -
1000 ppb.
4
11.3 Extract spiked matrix standardsfollowing 12.6-12.16 of this method. Use these standards
to establish eachinitial curve on the mass spectrometer.
R
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Approximate spiking amoun r standards and spikes
50.0 ppm 50.0 ppm 50.0 ppm
10 15 20 *
0.500 ppm 0.750 ppm 1.OOppm
12.0 PROCEDURE
12.1 Obtain frozen samples and allow to thaw at room temperatureor 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 beenremoved.
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 standardas describedin 11.2.
12.7 Spike eachmatrix with the appropriateamount of standardas described in 11.1, or Table 1 in that section, for the calibration curve standards. Also preparematrix spikes and continuing calibration standards.
12.8 Vortex mix the standardcurve samples,matrix spike samples, and continuing calibration samples for 15 seconds.
12.9 Check to ensurethe 0.5 M TBA reagentis at pH 10. If not, adjust accordingly.
12.10 To each sample, add 1 ml; 0.5 M TBA and 2 mL of 0.25M sodium carbonate/sodium bicarbonate buffer.
12.11 Using an Oxford Dispenser, add 5 mL methyl-terl-butyl ether.
12.12 Cap eachsample 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 of PFOS from Serum
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12.14 12.15
12.16
12.17 12.18 12.19
12.20
12.21
12.22
Label a fresh 15 mL centritige tube with the same information as in 12.9.
Remove 4.0 mL of the organic layer to this clean 15 mL centrifuge tube.
Put each sample on the analytical nitrogen evaporatoruntil dry, approximately 1 to 2 hours.
Add 1.0 mL of methanol to eachcentrifuge tube using a graduatedpipette.
Vortex mix far 30 seconds.
Attach a 0.2 pm nylon mesh filter to a 3 cc syringe and transfer the sample to this syringe. Filter into a 1S mL glass autovial or low-volume autovial when necessary.
Label the autovial with the study number, animal number and gender, sample timepoint, matrix, final solvent, extraction date,and analyst(s)performing the extraction.
Cap and store extracts at room temperatureor at approximately 4 "C until analysis.
Complete the extraction worksheet, attachedto this document, and tape in the study notebook or include in study binder, asappropriate.
13.0 DATAANALYSISANDCALCULATIONS
*
13.1 Calculations
13.1.1 Calculate actual concentrations of PFOS, or other applicable fluorochemical, in
calibration standardsusing the following equation:
mL of standardx concentration of standard(un /mLI
=
mL of standard+ mL of surrogatestandard+ initial matrix volume (mL)
Final Concentration &&I&) of PFOS in matrix
14.0 METHODPERFORMANCE
14.1 The method detection limit. (MDL) is analyte and matrix specific. Refer to MDL report for specific MDL and limit of quantitation (LOQ) values (seeAttachments B and C).
14.2 The following quality control samples areextractedwith eachbatch of samples to evaluate the quality of the extraction and analysis.
14.2.1 Method blanks and matrix blanks.
14.2.2 Matrix spike and matrix spike duplicate samples to determine accuracy and precision of the extraction.
14.2.3 Continuing calibration check samples to determine the continued accuracy of the initial calibration curve.
14.3 Refer to section 14 of ETS-8-5.1 for method performance criteria.
15.0 POLL~TIONPREVENTIONANDWASTEMANAGEMENT
15.1 Sample waste is disposed in biohazard containers, flammable solvent waste is disposed in high BTU containers, and used glasspipette waste is disposedin broken glass containers located in the laboratory.
ETS-8-4. I Extraction of PFOS from Serum
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16.0 F&CORDS
16.1 Complete the extraction worksheet attachedto this method, and tape in the study notebook or include in the 3-ring study binder, asappropriate.
17.0 ATTACHMENTS 17.1 Attachment A, Extraction worksheet 17.2 Attachment B, MDL/LOQ values and summary 17.3 Attachment C, Calibration standardconcentration worksheet
18.0 REFERENCES
18.1 The validation report associatedwith this method is ETS-8-4.0 & 5.0-V-l.
18.2 FACT-M-3.1, "Analysis of Serum or Other Fluid Extracts for Fluorochemicals using HPLC-Electrospray,Mass Spectrometry"
19.0 AFFECTEDDOCUMENTS
19.1 ETS-8-5.1, "Analysis of Serum or Other Fluid Extracts for Fluorochemicals using HPLC-Electrospray Mass Spectrometry"
20.0 REVISIONS
Revision
Number 1
ReasonFor Revision
Section 12.21 Changedto include sample storageat room temperature.
Section 12.13 Added the shakerspeed. Section 12.17Final volume is 1.OmL; not adjusted for initial volumes
less than 1.OmL.
Revision
g&g 04/02/99
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ETS-S-4.1 Extraction of PFOS from Serum
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Extraction Worksheet ETS-84.1
.
Study # Matrix Box #
may
DateSpiked/Analyst ccv MS MSD
Surrogate Std
approx. mm actual pm #
FC-Mix approx. 0.5 pm actual ppm #
FC-Mix approx. 5 ppm actual wm #
FC-Mix approx. 50 ppm actual wm #
Comments
Blank Serum Extraction Method
I
Std #
I
-
:
I
-
amount =
I
I
mL
Date & Initials
Shake20 min. Centrifuge 20-25 min.
Shaker meed: Centrifuge speed:
Filter using a 3ccB-D svringewith a 0.2rtm filter into a 1.5mL autosamplevial Cont. Cal. Verifications used same matrix as for std curve.
Attachment A
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ETS-8-4.1 Extraction of PFOS fkom Serum
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.
pa*
MDL/LOQ values for rabbit serum
Compound
rPFOi3 L-- --
PFOSA
MDL (ppb)
1.74 1.51
LOQ (ppb)
5.55 4.79
Linear Calibration Range (LCR) Approximate concentrations to be used for preparing the Standard Calibration Curve
5 ppb - 1000 ppb
5 rmb - 1000 th
PFOSAA
ii.46
20.5 5 ;pb - 1000 ;pb
EtFOSE-OH
11.4
36.2 5 ppb - 1000 ppb
M556
6.03
19.2 5 ppb - 1000 ppb
PFOSEA
5.71
18.2 5 ppb - 1000 ppb
MDL/LOQ values in rat, bovine, monkey, and human serum, and monkey plasma were not statistically determined. Two curves in each of 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: MDLiLOQ Summary
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Extraction of PFOS from Serum
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Compound: *
PFOS
l/x
0.995 - 978
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Report:
LRN-U2095
FACT TOX-013 LRN-u2095
Compound: h
PFOSAA
l/X
0.991- 974
LCR from curve (Ppb)
O&W
24.7 - 974
9.74 - 247
97.4 - 974
9.74 - 974
% Recovery Raw9
81-111 97-107 85-108 95-115
RSD Range
4.18-10.6 6.38-21.8 4.33-12.5 4.11-23.2
Attachment B: MDULOQ Summary
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Compound: ti
EtFOSE-OH
IFull Range I 0.99r3 - 976
I Low Curve I 4.93 - 97.6
IHigh curve
49.3 - 976
I l/X
I 0.993 - 493
Compound: PFOSEA
Rabbit Serum
Prepared range of standards
@pW (n&W
Full Range
0.993 - 976
Low Curve I 4.93 - 248
High curve
49.3 - 976
l/X
0.993 - 976
Compound: M556 Rabbit Serum
LCR from curve (ppb)
6x/~) 49.3 - 976
9.76 - 97.6
97.6 - 976
9.76 - 976
% Recovery Range
77-110 97-107 go-109 86-111
LCR from curve (PPb)
(w/mL) 24.8 - 976
9.76 - 248
49.3 - 976
9.76 - 976
% Recovery Range
96-106 I 91-110
86-106 9.5-l 17
RSD Range
11.2-25s 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
Attachment B: MDL/LOQ Summary
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Ion Pair Standard Curves - Fluids
Prep date(s):
Standard number:
Analyte(s):
Equipment number:
Sample matrix:
Final solvent and TN:
Blank fluid/identifier:
Method/revision:
psi
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
Std cone
PFOSA
Std cone
PFOSAA Std cone
EtFOSE Std cone
PFOSEA Std cone
Wd 0.500
Ugly 0.507
Ug/mL 0.532
ug/mL 0.501
ug/mL 0.521
0.500
0.507
0.532
0.501
0.52i
5.00 -__I--5-.00
5.00 50.0 50.0
5.07 5.07 5.07 --- 50.1 50.1
5.32 5.32 5.32 53.2 1 53.2
5.01 _-- cil
5.01
5.21
5..-0' 1
---I5- .2--1-
50.1
52.1
50.1
52.1
50.0
50.1 1 53.2
50.1
32.1
50.0
50.1 1 53.2
50.1
52.1
M556 Std cone
VW0--.5.-0--1 0.501 5.01 -5.01 rs.ol---' 50.1 363 50.1 50.1
All AmY spiked mL 0.010 0.020 o.005 o.oio 0.020 0.005 0.010 0.015 0.020'
AI1 Final vol
mL 1.015 --- 1.025 1.010 1.015 - 1.025
1.-0-10 _1_.-015 1.020-1.025
Calculated concentrations of standards in the sample matrix
Validated ranges Serum -
Rabbit Bovine
Rat Monkey 6%Plasma
HWWl
- approximate concentrations
&OS
PFOSA
5.00-1000 1 5.00-1000 ]
Estimates only. Use values for rabbit.
Estimates only. Use values for rabbit.
Estimates only. Use values for rabbit.
Estimates only. Use values for rabbit.
PFOSAA 5.00-1000
EtFOSE-OH 1 5.00-1000
PFOSEA \ 5.00-1000
M556 1 5.00-1000
R
IJ
Attachment C: Ion Pair Standard Curves
3M Environmental
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CI
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Extraction
ETS-8-4.1 of PFOS from Serum
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3M ENVIRONMENTALLABORATORY
METHOD
ANALYSISQF POTASSIXJMPERFL~OROOCTANESIJLFONAOTREOTFIER
FLUOROCFIEMICALSIN SERUMEXTRACTSUSING
HPLC-ELECTROSPRAY/MASS SPECTROMETRY
Method Number: ETS-S-5.1
Author: Lisa Clemen, Robert Wyune Approved By: Laboratory Manager
Adoption Date: 03/01/99 Revision Date: "Ila&fl
4/x, Date
Group Leader
+yu!-,c.
TechnicaRl eviewer
1.0 SCOPEANDAPPLICATION
1.1 Scope: This method describes the analysis of serum extracts for fluorochemical surfactants using HPLC-electrospray/mas spectrometry.
1.2 Applicable Compounds: Fluorochemical surfactantsor other fluorinated compounds, or other ionizable compounds.
1.3 Matrices: Rabbit, rat, bovine, monkey, and human serum, or other fluids as designated in the validation report.
Word (795
ETS-8-5.1 Analysis of Serum Extract Using ES/MS
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2.0 SUMMARYOF METHOD
2.1 This method describesthe analysis of fluorochemical surfactantsextracted Tom 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 asthe perfluorooctanesulfonate (PFOS) anion, m/z= 499. Additionally, samples may be analyzed using a tandem mass spectrometerto further verify the identity of a compound by detecting daughter ions of the parent ion.
3.0 DEFINITIONS
3.1 Atmospheric Pressure Ionization (API): The Micromass Quattro II triple quadrupole systems allow for various methods of ionization by utilizing various sources,probes, and interfaces. These include but arenot limited to: Eleotrospray Ionization (ESI), Atmospheric Pressurechemical Ionization (APcI), Thermospray, etc. The ionization processin these techniques occurs at atmospheric pressure(i.e., not under a vacuum).
3.2 Electrospray Ionization (ES, ESI): a method of ionization performed at atmospheric pressure,whereby ions in solution aretransferredto the gasphasevia tiny chargeddroplets. These chargeddroplets areproduced 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 equippedwith quadrupole mass selective
detectors. Ions are selectively discriminated by mass to chargeratio (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 of 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 arethe 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
*a( compatible with some other Z-spray systems, etc.)
3.5 Mass Lynx Software: System software designed for the specific operation of these Quattro
II triple quadrupole systems. Currently MassLynx hasWindows 95 and WindowsNT 4.0
F
versions. All versions are similar. For more details seethe manual specific to the instrument
(Micromass Quattro II triple quadrupoleMassLynx or MassLynx NT User's Guide).
4.0 WARNINGSANDCAUTIONS 4.1 Health and Safety Warnings:
Ipl
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 appropriateprotective gloves, eyewear,
mm
and clothing.
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4.2 Cautions:
4.2.1 Do not operatesolvent pumps above capacity of 400 bar (5800 psi) back pressure. If the back pressureexceeds400 bar, the HP 1100will initiate automatic shutdown.
4.2.2 Do not run solvent pumps to dryness.
5.0 INTERFEWNCE~
5.1 To minimize interferenceswhen analyzing samples,teflon should not be used for sample storageor any part of instrumentation that comes in contact with the sample or extract.
6.0 EQUIPMENT
1"
6.1 Equipment listed below may be modified in order to optimize the system. Document any
modifications in the raw dataas method deviations.
6.1.1 6.1.2
Micromass Quattro IT triple quadrupole Mass Spectrometerequipped with an electrospray ionization source
HP1 100 low pulse solvent pumping system, solvent degasser,column compartment, and autosampler
7.0 SUPPLIESANDMATERIALS
7.1 Supplies 7.1.1 High purity grade nitrogen.gasregulated to approximately 100 psi (House air system)
7.1.2 HPLC analytical column, specifics to be.determinedby the analyst and documented in the raw data
7.1.3 Capped autovials or capped 15 mL centrifuge tubes
8.0 REAGENTSAND~TANDARDS 8.1 Reagents
8.1.1 Methanol, HPLC gradeor equivalent
8.1.2 Milli-QTM water, all water used in this method should be Milli-QTM water or equivalent, andmay be provided by a Mini-Q TOC Plus system or other vendor
8.1.3 Ammonium acetate,reagentgrade or equivalent
8.2 Standards
8.2.1 Typically two method blanks, two matrix blanks, and eighteenmatrix standardsare preparedduring the extraction procedure. SeeETS-8-4.1.
9.0 SAMPLEHANDLING
9.1 Fresh matrix standardsarepreparedwith each analysis. Extracted standardsand 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 standardsand samples can be refrigerated at approximately 4" C, or at room temperature,unti1 analysis can be performed.
10.0 OUALITYCONTROL 10.1 Solvent Blanks, Method Blanks and Matrix BIanks
10.1.1 Solvent-blanks, method blanks and matrix blanks arepreparedand analyzed with eachbatch to determine contamiriation or carryover.
10.1.2 Analyze a method blank and a matrix blank prior to eachcalibration curve.
10.2 Matrix Spikes
10.2.1 Matrix spikes arepreparedand analyzedto determine the matrix effect on the recovery efficiency.
10.2.2 Matrix spike duplicates are preparedand analyzed to measurethe precision and the recovery for eachanalyte.
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 andmatrix spike duplicate concentrationswill fall in the mid-range of the initial calibration curve. Additional spike concentrationsmay fall in the lowrange of the initial calibration curve.
10.3 Continuing Calibration Verifications
10.3.1 Continuing calibration verifications are analyzedto verify the continued accuracy of the calibration curve.
10.3.2 Analyze a mid-range calibration standardafter every tenth sample, with a minimum of one per batch.
11.0 CALIBRATIONANDSTANDARDIZATION 11.1 Analyze the extracted matrix standardsprior to and following each set of extracts. The
averageof two standardcurves will be plotted by linear regression(y = my + b), weighted l/x, not forced through zero, using MassLynx or other suitable software.
11.2 If the curve doesnot meet requirements, perform routine maintenance or reextract the standardcurve (if necessary)and reanalyze.
11.3 For purposesof accuracy when quantitating low levels of analyte, it may be necessaryto use the low end of the calibration curve rather than the full rangeof the standardcurve. Example: when attempting to quantitate approximately 10 ppb of analyte, generatea calibration curve consisting of the standardsfrom 5 ppb to 100 ppb rather than the full range of the curve (5 ppb to 1000ppb). This will reduceinaccuracy attributed to linear regressionweighting of high concentration standards.
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12.0 PROCEDURES
12.1 Acquisition Set up
12.1.1 Click on start button in the Acquisition Control Panel. Set up a sample list. Assign a filename using MO-DAY-last digit of year-samplenumber, assign a method (MS) for acquiring, and type in sample descriptions.
12.1.2
To createa method click on scanbutton 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 areemployed, additional product ion fragmentation information may be collected. SeeMicromass MassLynx GUIDE TO DATA ACQUISITION for additional information and
MRM (Multiple Reaction Monitoring),
12.1.3 Typically the analytical batch run sequencebegins with a set of extracted matrix standardsand endswith a set of extractedmatrix 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 arenot considered samplesbut may be included as such.
12.2 Using the Autosampler
12.2.1 Set up sample tray according to the sample list preparedin Section 12.1.1.
12.2.2 Set-up the HP 11OO/autosamplerat the following conditions or at conditions the
analyst considers appropriatefor optimal response.Record actual conditions in the instrument logbook:
Pa
12.2.2.1 Sample size = 10 PL injection
12.2.2.2 Inject/sample = 1
w
12.2.2.3 Cycle time = 13.5 minutes
12.2.2.4 Solvent ramp =
12.2.2.5 Pressthe "Start" button. 12.3 Instrument Set-up
12.3.1 Refer to ETS-9-24.0 for more details. 12.3.2 Check the solvent level in reservoirs and refill if necessary.
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12.3.3 Check the stainless steel capillary at the end of the probe. Use an eyepiece to check the tip. The tip should be flat with no jagged edges. If the tip is found to be
unsatisfactory, disassemble the probe and replacethe stainless steel capillary.
12.3.4 Set HPLC pump to "On". Set the flow to 10 - 500 uL/min or asappropriate. Observe droplets coming out of the tip of the probe. Allow to equilibrate for approximately 10 minutes.
12.3.5 Turn 0x1the nitrogen. A fine mist should be expelled with no nitrogen leaking around the tip of the probe. Readjust the tip of the probe if no mist is observed.
12.3.6 The instrument usestheseparametersat the following settings. These settings may changein order to optimize the response:
12.3.6.1 Drying gas 250-400 liters/hour
R
12.3.6.2 ES1nebulizing gas 1O-l 5 liters/hour
12.3.6.3 HPLC constant flow mode, flow rate 10 - 500 pL/.min
12.3.6.4 Pressure<400 bar (This parameter is not set, it is a guide to ensurethe HPLC is operating correctly.)
12.3.7 Carefully guide the probe into the opening. Insert probe until it will not go any further. Connect the voltage cablesto the probe.
12.3.8 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 electrodein the ES/MS sourceis recommended for the analysis of biological matrices.
12.3.1OClick on start button in the Acquisition Control Panel (this may vary among MassLynx versions, seeappropriate MassLynx USER'S GUIDE). Press the start
button. Ensure start and end sample number includes all samples to be analyzed.
13.0 DATAANALYSISANDCALCULATIONS 13.1 Calculations:
13.1.4 Calculate matrix spike percent recoveries using the following equation:
% Recovery =
ObservedResult - Background Result x 100 Expected Result
13.1.5 Calculate percent difference using the following equation:
% Difference = Expected Cont. - Calculated Cont. x 100 Expected Cone.
13.1.6 Calculate actual concentration of PFOS, or other fluorochemical, in matrix h&W
ln(nnof PFOS talc. from std. Curve x Dilution Factor) x 1 ug (Initial Volume of matrix (mL) + mL of SurrogateStandard) 1000 ng
Final Volume (mL)
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14.0 METHOD PERFORMANCE
14.1 Method Detection Limit (MDL) and Limit of Quantitation (LOQ) are method, analyte, and matrix specific. PleaseseeETS-8-4.1, Attachment B, for a listing of current validated MDL and LOQ values.
14.2 Solvent Blanks, Method Blanks, and Matrix Blanks
14.2.1 Solvent*blanks, method blanks, and matrix blanks values are must be below the lowest standardin the calibration curve
-
14.3 Calibration Curves
14.3.1 The ? value for the calibration curve must be 0.980 or better,
R
14.4 Matrix Spikes
14.4.1 Matrix spike percent recoveries aremust be within f 30% of the spiked concentration.
14.5 Continuing Calibration Verifications
(
14.5.1 Continuing calibration verification percent recoveries must be f 30% of the spiked
p"
concentration.
14.6 If criteria listed in this method performance section isn't met, maintenance may be performed on the system and samplesreanalyzed or other actions as determined by the analyst. Document all actions in the appropriate logbook.
14.7 If data areto be reported when performance criteria have not beenmet, the data must be footnoted on tables and discussedin the text of the report.
15.0 POLLUTIONPREVENTIONANDWASTEMANAGEMENT
15.1 Sample extract waste and flammable solvent is disposedin high BTU containers, and glass pipette waste is disposedin broken glass containers located in the laboratory.
16.0 RECORDS
16.1 Each page generatedfor a study must have the following information included either in the headeror 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
R1
appropriate study folder. Copy these pagesandtape into the instrument runlog.
16.3 Plot the calibration curve by linear regression,weighted l/x, then print these graphs and store in the study folder.
16.4 Print data integration summary, integration method, and chromatograms, from MassLynx, and store in the study folder.
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16.5 Summarize data using suitable software (Excel 5.0) and storein the study folder, see Attachment A for an example of a summary spreadsheet.
16.6 Back up electronic data to appropriate medium. Record in study notebook the file name and location of backup electronic data.
17.0 TABLES,DIACRAMS,FLOWCHARTS.ANDVALIDATIONDATA
F"
17.1 Attachment A: -ETS-8-5.1 Data surnrnaiy spreadsheet.
LII
18.0 REFERENCES
18.1 FACT-M-4.1, "Extraction of Potassium Perfluorooctanesulfonateor Other Fluorochemical compounds from Serum for Analysis Using HPLC-Electrosprayh4ass Spectrometry
p") 18.2 ETS-g-24.0, "Operation and Maintenance of the Micromass Atmospheric Pressure Ionization/Mass Spectrometer Quattro II triple quadrupole Systems"
F-
18.3 The validation report associatedwith this method is ET!+8-4.0 & 5.0-V-l.
19.0 AFFECTEDDOCUMENTS
19.1 ETS-84.1, "Extraction of Potassium Perfluorooctanesulfonate or Other Fluorochemical Compounds from Serum for Analysis Using HPLC-Electrospray/Mas Spectrometry"
c"
20.0 &CVISIONS
Revision Number.
1
ReasonFor Revision Section 6.1.2 Clarification of HP1 100 system components. Section 11.1 Average of two curves, not standardvalues, areused for plotting linear regressionand addedthe l/x weighting of the curve.
Section 12.2.2.4 Clarification of solvent ramp. Section 17.1 Changed from attachment B to A.
Revision pa&
04/02/99
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Laboratory Study #
Study:
Test Material:
Matrix/Final Solvent:
Method/Revision:
-
Analytical Equipment System Number:
Instrument SoftwarefVersion:
Filename:
R-Squared Value:
Slope:
Y Intercept:
Date of Extraction/Analyst:
Date of Analysis/Analyst:
slope: Taken from linear regression equauon. Group/Dose: Taken from the study folder. Sample#k Taken from the study folder. Concentration (ug/mL): Taken from the MassLynx integration Initial Volume (mt): Taken from the study folder. Dilution Factor: Taken from the study folder. Final Cow. (ug/mL): Calculated by dividing the initial volume
summruy. 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 Summary Tables
Table 12. Reported Fluorochemicai Levels in Sera Analyses in Study FACT TOX-013
l = Tentative values. hithl volume was 4.5 mL
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Table 12. Reported Fluorochemical Levels in Sera Analyses in Study FACT 10X-013 (continued)
* = Tmtative vakma, initial vobma was Co.5 ml
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Table 13. Reported Fluorochemical kantinuedl
Levels In Liver Analyses In Study FACT TOX-013
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Appendix E: Data Spreadsheets
Analytical
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FACT.TOX.013 Argud 418.009
Analytical Study: FACT-TOX-013 LRN-U2095
3M Environmental Laboratory
lOlRF
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Appendix F: Example Calculations Formula Used for Sera Analyses in Study FACT TOX-013
AR (ng/mL) x DF x SC x FV (mL) x 1.0 pg EVomao
x PC = Reported Concentration (&mL)
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 &mL -iYFGX 1OOOng
c
AR-Analytical result from MassLynx summary
DF-Dilution factor
SC-PFOS salt correction constant (0.9275)
R"
FV-Final extract volume (1.OmL unless otherwise noted)
EV-Volume of seraextracted
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-Ethylfluorooctanesu1fonamido)-ethanolin Two Generation Rat Reproduction, (65pages)
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BIOLOGICAL SAMPLE ANALYSIS Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
Analytical Study: FACT-TOX-013 LRN-U2095
qpBaltelle d& . . . Putting Technology To Work
FINAL REPORT
2 (N-Ethylfluorooctanesu1fonamido)-ethanolin Two Generation Rat Reproduction
SPONSOR
3M Toxicology Services 3M Center
Building 220-2E-02 St. Paul, MN 55144
TestinP FaciliQ
Battelle Memorial Institute 505 King Avenue
Columbus, Ohio 43201-2693
Prepared By Patrick L. South, B.S.
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
FINAL REPORT
2 (N-Ethylfluorooctanesu1fonamido)-ethanolin Two Generation Rat Reproduction
A
Bathhe Principal Investigator
Battelle Senior Program Director
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
2 (N-Ethy1fluorooctanesulfonamido)-ethanolin Two Generation Rat Reproduction
EXECUTIVE SUMMARY
Rat liver samples sent to Battelle by 3M Environmental Technology and Services were analyzed by the previously validated method "Method for Analysis of PotassiumPeriluorooctanesulfonate (PFOS) in Rat Liver by LC/MS/MS". Samples were extracted and analyzed by High-Performance Liquid Chromatography Mass Spectroscopy (LC/MS/MS) for PFOS, M-556, PFOSAA, and PFOSA content only. Related fluorochemicals mentioned in the analytical method were not investigated.
The results for the concentration determinations in the liver samples from this study are attached as appendices to this report. Concentrations are reported as mass of analyte (pg) per gram of liver tissue extracted.
...
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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:
Phase Inspected
Inspection Date
Date Reported to Battelle Task Leader/ Battelle Management
Date Reported to Offsite Study Director/ Management
Sample weights Sample homogenization Extraction Sample analysis Audit study file Audit final report Audit study file Audit final report
10/12/1999 10/12/1999 10/13/1999 10/13/1999 12/9/1999 12/9/1999 2/21/2001 2/21/2001
11/1/1999 11/1/1999 11/1/1999 11/1/1999 12/9/1999 12/9/1999 2/21/2001 2/21/2001
3/30/01 3/30/01 3/30/01 3/30/01 3/30/01 3/30/01 3/30/01 3/30101
Date kattelle Memorial Institute
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GOOD LABORATORY PRACTICES COMPLIANCE STATEMENT
Study Title:
2 (N-Ethylfluorooctanesu1fonamido)-ethanolin Two Generation Rat Reproduction
This study was conducted in compliance with the Food and Drug Administration's Good Laboratory Practice Regulations (21 CFR 58)' with the exception that the mass spectrometry data for the liver samples was collected and processed with the MassLynx software system (version 3.1)' which was not h l l y validated. The study was listed on Battelle's Master List of regulated studies.
-.-
n
%c &eL,
Jon C./q(ndre, Ph.D. Battellg Principal Investigator
Marvin T. Case, DVM, Ph.D. Study Director
i/
Date
I,?
Date
h/
.
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
Table of Contents
Executive Summary.............................................................................................................................................
P..a. ge
111
QualityAssurance Statement............................................................................................................................... iv
Compliance Statement.......................................................................................................................................... v
Table of Contents................................................................................................................................................ vi
1.0 Introduction............................................................................................................................................. 1
2.0 Reference Substances ............................................................................................................................. 1
3.0 Receipt ofSamples................................................................................................................................. 1
4.0 Analysis of Samples ............................................................................................................................... 1
4.1 Summary ofMethod ................................................................................................................. 1
4.2 Results ....................................................................................................................................... 3
4.2.1 Quality Control ............................................................................................................ 3
4.2.2 Sample Results ............................................................................................................ 3
5.0 Conclusions............................................................................................................................................. 3
6.0 Acknowledgements................................................................................................................................. 4
7.0 Specimen Storage and Record Archives................................................................................................. 4
List of Tables Table 1. Example of InstrumentParameters Used to Analyze Samples............................................................. 2
Appendix A (Results) Summary Results for Rat liver SampleAnalysis......................................................................... A-1
Appendix B (Daily Acceptance Criteria Summary) Daily Acceptance Criteria Summary ...................................................................................... B-1
Appendix C (Sample Inventory List) Sample Inventory List........................................................................................................ C-1
Appendix D (Chromatograms) Representative Chromatograms ............................................................................................. D. 1
Appendix E (Protocol. Amendments. and Deviations) Protocol. Amendments. and Deviations...................................................................................... E-1
Appendix F (PFOS Purity Report) PFOS Purity Report ...................................................................................................................... F-1
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Battelle Study Number: NOO3604-D 3M Environmental Laboratory Study Number: FACT 060998.1
1.O Introduction This report presents a description of the method used to analyze PFOS, M-556, PFOSAA, and
PFOSA in rat liver samples from 3M Study Number FACT 060998.1 (TOX-0 13) and the results from this analysis. See Appendix E for a copy of the study protocol, amendments, and protocol deviation reports).
2.0 Reference Substances The analytical reference substances for this study were supplied by 3M. The following lot number or
tracking number designations apply: PFOS (lot 171), M-556 (TN-A-2203), PFOSAA (TN-A-1283) and PFOSA 0.-15709). Note that based on information supplied to Battelle from 3M, PFOS has two equivalent names. The name appearing on the Material Safety Data Sheet and bottle label is potassium perfluoroalkyl sulfonate. The name more commonly used by 3M in analytical methods and correspondence is potassium perfluorooctanesulfonate. The latter name will be used in this report. See Appendix F for purity data supplied by 3M to Battelle. The reference substances were stored at room temperature.
The surrogate standard was lH,lH,2H,2H-Perfluorooctanesulfonic acid, lot number 59909, supplied by ICN. The surrogate standard was stored at room temperature.
3.0 Receipt of Samples Samples were received frozen and intact at Battelle, from 3M Environmental Technology and
Services, in one batch on October 6, 1999. Samples were generated by Argus Research under protocol number 418-009. See Appendix C for a copy of the inventory list. The samples were stored at approximately -20C.
4.0 Analysis of Samples
4.1 Summary of Method
Samples were analyzed by a previously validated method (Battellestudy number N003604-A). The current version of the method is attached to this report in Appendix E. Samples were analyzed by LC/MS/MS, and an example of the instrument parameters is listed in Table 1. Note that only PFOS, M-556, PFOSAA, and PFOSA (and the surrogate) were quantitated. The other related fluorochemicals, although present in the stock solutions, were not monitored. Quadratic regressions weighted l/x were used to construct the calibration curves.
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Table 1. Example of InstrumentParametersUsed to Analyze Samples
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4.2 Results
Battelle Study Number: N003604-D 3M EnvironmentalLaboratory Study Number: FACT 060998.1
4.2.1 Quality Control
System suitability acceptance criteria were established during the method validation and are included in Appendix E, Section IX Acceptance Criteria. Relevant statistics from each sample set are provided in Appendix B. Representative chromatograms are given in Appendix D.
4.2.2 Sample Results
The results of the sample analyses as well as a method detection limit determination are presented in Appendix A. All liver samples were initially extracted as undiluted homogenates. After the data were reviewed, dilutions of the homogenates were performed in order to bring analyte concentrations within the calibration range. The first analysis that provided acceptable data for an analyte was used in reporting. Four extraction sets were required to provide data for each analyte.
The limit of quantitation is defined as the Concentration of the lowest standard which meets acceptance criteria for accuracy (25% RE; see Appendix E for definition). The notation BLOQ denotes "Below Limit of Quantitation" for samples that had concentrations lower than the theoretical concentration for the 0.13 pg/g calibration standard. The notation ALOQ denotes "Above Limit of Quantitation" for samples that had concentrations higher than the theoretical concentration for the 13
pg/g calibration standard. Samples that were initially ALOQ were diluted with blank liver homogenate and re-extracted. Samples that were expected to be ALOQ were first diluted with blank
liver homogenate before extraction. The "Corrected PFOS Conc" presented in the results tables is the concentration found for the diluted sample multiplied by its dilution factor (final volume + sample homogenate volume).
The method detection limit (MDL) of PFOS was calculated in Battelle study N003296Fto be 0.0173 pg/g fiom 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(SN)ratio was calculated by dividing the mean found concentration of the 7 reps by their standard deviation. The method of MDL determination was provided by the Sponsor.
5.0 Conclusions
All analyses met acceptance criteria unless otherwise noted.
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6.0 Acknowledgements
Acknowledgement of principal contributors participating in the performance of this study at Battelle is presented in the following list.
Participant
Title
Jon C. Andre, Ph.D. Richard W. Slauter, Ph.D., D.A.B.T. Patrick L. South, B.S. Gerke H. van der Zwaag, M.S.
Battelle Principal Investigator Senior Program Director Mass spectroscopist Samplepreparation chemist
7.0 Specimen Storage and Record Archives
See Appendix E, protocol amendment 3 for records archival information. All residual liver samples, extracts, and unused test article will be disposed of or returned to the Sponsor as directed by the Sponsor.
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APPENDIX A -RESULTS
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PFOS, M456, PFOSAA, PFOSA IN RAT LIVER
EARELLE STUDY:
N0036W-D
SPREADSHEET SOFTWARE
DATA ENTERED:
MANUALLY
Sample
Dose
GrOUL
Animal Number
1
1
2
1
3
1
4
1
5
1
6
2
7
2
8
2
9
2
10
2
11
3
12
3
13
3
14
3
15
3
16
4
17
4
18
4
19
4
M
4
21
5
22
5
23
5
24
5
25
5
28
1
27
1
28
1
29
1
30
1
31
2
32
2
33
2
34
2
35
2
35
3
37
3
38
3
39
3
40
3
41
4
42
4
43
4
44
4
45
4
46
1
47
1
48
1
49
1
50
1
51
2
52
2
53
2
54
2
55
2
5.6
3
57
3
!%
3
59
3
60
3
61
4
62
4
63
4
84
4
65
4
BLOQ = BELOW LIMIT OF QUANllTATlON
9g22 9930 0931 9932 9933 9961 9gS4 9965 9967 9970 9997 9999 low1 10002 10004 10019 10024 10029 10033 10034 10042 10044 10045 10051 10054 10097 10105 10106 10107 10108 10136 10140 10142 10121 10126 10177 10155 10156 10164 10172 10167 10194 10203 10211 10214 10097 10105 10106
10107
10108
10138 10140 10142 10121 10126 10177 10155 10156 10184 10172 10187 10194 10203 10211 10214
Analysis data key:
Normalfont = October 13,1999 Underline = October 16,1999 Bold = October 18,1999
Bold Underllne = October 20,1999
EXCEL 97
SampleType
Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal
Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Fetal Maternal Maternal Maternal
Maternal
Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal Maternal
PFOS Conc, p gIg
M356 Conc,
pg 1g
6.n~oi 9.44E-01 9.68E-01 1.2OE+00 ).17E+00 1.34E+02 1.I8E+02 l.C4E+O2 9.34EW1 1.01 E+OZ 4.80E+02 2.71 E+02 5.76E+02 2.97E+02 4.47E+02 9.62E+02 9.15E+02 6.43E+02 S.C4E+02 6.43+02 1.41 E+03 I.57E+03 I.31 E+03 I.23E+03 1.228+03 1.72E-01
BLOQ 1.40E-01
BLOQ BLOQ 4.61+01 2.74EMI 2.56EW1 2.90E+01 2.65E+01 12 1EM2 1.18E+02 1.5OEWZ 2.07E+02 1.38E+02 1.90E+02 2.78E+02 3.98+02 2.95E+02 3.068+02 3.25E-01 2.8OE-01 2.61E-01 2.56E-01
2.90E-01 6.21 E W I 3.24E+01 8.2BEWI 6.33E+01 7.85E+01 1.77E+O2 1.03E+02 2.531+02 2.35EW2 2.18E+02 2.62E+02 3.21 EM2 5.19EWZ 5.29E+02 3.98E+02
BLOQ BLOQ BLOQ
moa
BLOQ 1.28E+Ol l.OZE+Ol 1.16E+01 8.95E+00 l.lBE+Ol 6.35E+OI 3.93+01 6.64E+01 3.8OE+Ol 5.46+01 8.45E+01 9.75E+01 7.82+01 1.17E+02 8.228+01 1.28EW2 I.52E+02 1.33E+02 1.18E+02 1.61 E+OZ
BLOQ BLoa BLOQ BLOQ BLOQ 2.66E+OO 1.55E+OO 1.41E+OO `1.1 9E+00 1.75POO 8.1 6E+OO 7.17E+00 7.64E+00 8.41E+00 5.87E+00 1.98E+01 2.68E+O1 2.66E+OI 2.75E+01 2.93E+01
BLOQ BLOQ BLOQ BLOQ
BLOQ 4.64E+00 3.27E+00 4.56E+OO 5.39E+OO 7.75E+00 3.14E+01 1.15E+01 3.33E+01 4.31 E+01 2.99E+01 3.99E+01 3,95E+OI 6.78E+OI 6.54E+01 6.45E+OI
All samples undiluted All samples undiluted All samples diluted All samples diluted
PFOSAA Conc, pg1g
moa
BLOQ BLOQ BLOQ BLOQ 1,10E+01 1.56E+01 9.79E+00 6.62+00 1.04E+01 7.351+01 2.86E+01 8.52E+01 3.42E+OI 6.49E+01 I.Z2E+02 I.48E+02 8.62E+01 1.29E+02 1.35E+02 1.881+02 2.06E+02 1.50E+02 1.57E+02 1.65E+02 BLOQ BLOQ BLOQ BLOQ BLOQ 5.01E+00 2.67+00 2.67+00 2.68E+00 4.34E+00 Z.OOE+Ol 1.56E+01 2.02EW1 227E+01 1.19E+01 3.1 1E+OI 5.15E+01 4.958+01 4.66EWl 5.14E+OI BLOQ BLOQ BLOQ BLOQ
BLOQ 9.44E+00 2.82E+OO 6.55+00 5.87E+00 I.46E+01 1.71 E+01 1.20+01 2.73+01 2.94E+01 3.37E+OI 2.74E+01 4.55E+01 7.60E+01 5.6ZE+01 6.00E+01
PFOSA Conc, pg1g
moa
BLOQ
moa
BLOQ BLOQ 4.49E+00 4.10E+00 2.88E+OO 3.86E+00 5.42E+00 1.06+01 9.41E+00 8.67E+00 8.29E+OO 8.41 E+00 1.26E+01 1.1 OE+01 1.12E+01 1.26E+O1 l.lOE+Ol 1.64E+01 1.30E+01 1.09+01 9.8OE+OO 1 .O8E+O1 BLOQ BLoa BLOQ BLOQ BLOQ 1.4OE+00 6.01E-01 5.06E-01 5.14E-01 7.08E-01 2.88E+00 2.22+00 2.24E+M) 1.94+00 2.17+00 2.80E+M) 4.06E+00 3.14E+00 3.398+00 4.56E+M)
BLOQ BLOQ BLOQ BLOQ
BLOQ 2.35E+OO 1.22E+00 2.DBE+00 1.90+00 2.65+00 6.91+00 5.11 E+OO 6.14E+00 6.26E+00 6.20E+OO 6.36E+00 9.96E+OO 9.93E+00 1.14E+01 8.11E+OQ
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METHOD DETECTION LIMIT (MDL) RESULTS STUDY: N003604-D ANALYSIS DATE AND INSTRUMENT ID: DATA ENTERED: SPREADSHEET SOFTWARE:
All concs in pglg
130ct99; 9053 Electronically and manually Excel 97
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.
Spike Level
M-556
0.1269 0.1220 0.1433 0.1368 0.1670 0.1225 0.1190
0.1339 0.0170
0.133 1
PFOSAA
0.1484 0.1281 0.1484 0.1605 0.1661 0.1513 0.1385
0.1488 0.0128
0.1334
SM
PFOSA
0.1 167 0.1325 0.1521 0.1441 0.1490 0.1382 0.1413
0.1391 0.0119
0.13 15
LOQ (det. from 10 x std.dev. "noise") LOQ (det. from cal curve low std.)
Curve Coeff of Determination
Date analyzed Method
Kev
-1 Spike Level too high; Spike Level must be < lox MDL
2 - Spike Level too low; Spike Level must be > MDL 3 - SM too low; SM must be > 5
-4 Coeff of Det of calibration curve unacceptable
0.17005 0.133 1
0.9978
130ct99 LC/MS/MS
0.12763 0.1334
0.9937
130ct99 LC/MS/MS
0.11853 0.13 15
0.9891
13Oct99 LC/MS/MS
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APPENDIX B-DAILY ACCEPTANCE CRITERIA SUMMARY
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PFOS et al IN RAT LIVER
STUDY NUMBER: N003604-D
DATA ENTERED: MANUALLY
SOFTWARE:
EXCEL 97
REGRESSION PARAMETERS
October13,1999
One rep of Cal pt 1 excluded
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PFOS et al IN RAT LIVER
STUDY NUMBER: N003604-D
DATA ENTERED: MANUALLY
SOFTWARE:
EXCEL 97
Analysis Date October 13,1999
October 16,1999
October 18,1999
Analyte PFOS M-556 PFOSAA PFOSA PFOS M-556 PFOSAA PFOSA PFOS M-556 PFOSAA PFOSA
PFOSA
QC Level, nglmL
10 3.3 0.7 0.16 10 3.3 0.7 0.16 10 3.3 0.7 0.16 10 3.3 0.7 0.16
10 3.3 0.7 0.16 10 3.3 0.7 0.16 10 3.3 0.7 0.16 10 3.3 0.7 0.16
10 3.3 0.7 0.16 10 3.3 0.7 0.16 10 3.3 0.7 0.16 10 3.3 0.7
0.16
3.3
I 0.7 0.16
6.6 3.8 7.9 3.1 4.7 11.7 3.0 11.5 6.5 5.1 8.7 14.5 16.9 9.2 5.8 4.6
5.5 4.5 8.3 9.7 3.4 2.7 8.0 17.7 4.3 2.1 7.4 17.7 11.6 6.1 8.0 8.6
8.7 11.7 7.0 15.1 14.7 17.0 21.2 28.8 14.7 11.4 15.1 21.3 16.7 11.5 12.6
2.3 4.0 2.3
-4.0 -4.6 -6.4 -12.2 -2.4 2.5 -6.6 -5.1 -1.7 -10.4 -13.0 8.2 -4.3 -2.1 1.3 3.9
14.8 15.5 8.8 -2.7 -2.8 5.7 -3.7 4.5 -0.8 -2.9 -7.0 15.8 -3.9 5.4 -4.4 13.7
-4.5 -1.7 -20.3 -6.1 -2.9 23.4 11.6 15.4 0.8 -1.8 -20.6 -1 8.5 0.0 13.7 0.0 16.0
-12.0 -21.7 -16.0 -1.6 6.5
1.9
11.5
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APPENDIX C-SAMPLE INVENTORY LIST
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Study TOX-013, Argus 418009. Sample Informtion for shipment to Battelle
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APPENDIX D-REPRESENTATIVE CHROMATOGRAMS
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--
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& BQaLtCte9ll0e53
10 uL; N003684-D
16-0ct- 99! 10:55:3i
ESI160ctO6 Srn (Mn, 1x2)
Operator: PLI 2: MRM of 2 Channels ES-
427.00 > 81.O(
18'
SURROGATE
4.43
0 ,,., ,.,, ,,,,I..,,,,.l,l,,,,l,,,,l,,,,I,,,, 160ct06 SmI(Mn, 1x2)
100-
4.20
PFOS
%-
,,,, I,,,, ,,
2: MkM of 2 'ChannelsES-
499.00 > 99.0( I.79e:
0-,
~, , , , , , , I , ,
1601306 SmI(Mn, l h )
%
5.28
5.87
, , , , , , , 1 , , , , 1 , , ~ , , 1 , , , , ~ , , , ,, ,, ,
I 3: MkM of 3lChannels ES556.00 > 78.0C 317
M-556
0: , , 16OctO6
, ,
Sm
(Mn,
Ih)
'"4
PFOSAA
5.07
5.56 5.86 6.16
3:MkM of 3 Channels ES584.00 > 169.0C
0 ,,,, I60ct06 S
4.69 m 5.07
3: M M of 3 Channsels ES498.00 > 78.0C 43:
3M Environmental Laboratory
rm , , , I , , , , , , 5.bO
5.77
6.bO
6.28
Time
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%%-
,
%-
SURROGATE PFOS M-556
5.84er 1.08er 3.90e:
4.54
%- PFOSAA
100-
PFOSA
%-
1.06&
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D-3 3M Environmental Laboratory
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3attelle
2LC 9053 31-
30ct20 Sm (Mn, 1x2)
100-
3.94
%-
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
Sample 3 10 uL; N003684-D SURROGATE
13-Oct-I 99! 16:01:4I
Operator: PLI 2: MRM of 2 Channels ES-
427.00 > 81.O(
3.66s
0 ,I,,
,,.
30ct20 SmI(Mn,
Ih) , , ,
.
.
(
.
,
100-
4.22
%-
PFOS
499.00 > 99.0( 6.02ed
0 I 1 II
1I I I
, , ,3:,M M,of3,channels I I I I
1 II I 1I I I I 11 I I I 1 I II I 1 I I II 1 I I I I 19
I I 1
30ct20 SmI(Mn, I&)
100-
4.44
ES556.00 > 78.0(
34;
%-
3.83
0 I S , . >,-, 30ct20 SmI(Mn, I&) 100-
%-
PFOSAA
4.63 3.65
PFOSA
%
584.00 > 169.0( 87t
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%- 3.39
%-
%-
%-
!
%-
SURROGATE PFOS M-556 PFOSAA
PFOSA
5.94el 6.53el 1.86e! 1.18e! 2.85e!
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APPENDIX E-PROTOCOL, AMENDMENTS, AND DEVIATIONS
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- - &x 3M Environmental Laboratory Study Number: FACT 060998.1 fh-c f T'A
bl =-??.-
3M ENVIRONMENTLAALBORATORY
- PROTOCOLANALYTICASLTUDY
2(N-Ethylperfluorooctanesdfonamido)-ethanol in Two Generation Rat Reproduction
In-vivostudy referencenumber: Argus 418-009 Study number: FACT 060998.1 Test substance: 2(N-Ethylpeffluorooctanesulfonamido)-ethanol (N-EtFOSE-OH)
Name and address of Sponsor:
Marvin Case
3M Toxicology Services
3M Center Building 220-2E-02 St. Paul, MN 55144
Name and address of testing facility:
3M Environmental Technology and Services
935 Bush Avenue, Building 2-3E-09
St. Paul, MN 55106
Experimental start date: Expectedterminationdate: December 31,1998 Method numbers and revisions:
FACT-M-1.0, Extraction of Potassium Peffluorooctanesulfonateor Other Anionic
Surfactants from Liver for Analysis Using HPLC-ElectrosprayMas
Spectrometry
FACT-M-2.0, Analysis of Fluorochemicals in Liver Extracts Using HPLC-
i
Electrospray/Mass Spectrometry
' FACT-M-3.0, Extraction of Potassium Peffluorooctanesulfonateor Other Anionic Surfactants from Serum for Analysis Using HPLC-Electrospray/h'lass Spectrometry
FACT-M-4.0, Analysis of Fluorochemicals in Serum Extracts Using HPLC-
ElectrosprayMass Spectrometry
Author: Lisa Clemen
IhLA Kris Hansen
Study Director
q/l5/78
Date
Marvin Case
Sponsor Representative
/O?/&Y Date
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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)designatedby 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 REGULATORCYOMPLIANCE This study is conducted in compliance with the Food and Drug Administration Good Laboratory
Practices regulation as stated in 21 CFR 58. Any exceptionswill be noted in the final report.
3.0 TESTMATERIALS
3.1 Test,control, and reference substancesand matrices
3.1.1 Analytical reference substance:Potassium perfluorooctanesulfonate (PFOS),lot # 217
3.1.2 Analytical reference substance matrix: Rat liver and serum
3.1.3 Analytical control substance: None
3.1.4 Analytical control substance matrix: Rat liver and serum
3.2 Source of materials
3.2.1 Analytical reference substance: 3M Specialty Chemical Division; traceability informationwill be included in the final report
3.2.2 Analytical referencesubstance matrix: Argus Research Laboratories; traceability information will be included in the final report
3.2.3 Analytical control matrix:
3.2.3.1 Rat liver -Argus Research Laboratories:traceabilityinfomation will be
included in the frnal report; or
Rabbit liver - Covance Laboratories; traceability information will be
included in the final report
3.23.2 Rat serum - Sigma Chemical Company; traceability information will be
included in the final report
33 Number of test and control samples. Liver samples for testing were received from 40 test animals and 10 control animals. Serum samples will be tested at the discretion of the Study Director.
3.4 Identificationof test and control samples: The samplesare 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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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
3.5 Purity and strength of materials: Characterizationof the purity and identity of the reference material is the responsibility of the Sponsor.
3.6 Stability of test material: Characterization of the stability of the test material is the responsibility of the Sponsor.
3.7 Storage conditions for test materials: Test materials are stored at room temperature. Samples are stored at -20 f 10 "C.
3.8 Dispositionof 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 - EXPERIMENTAOLverview
Tissues from animals dosed as described in Argus Research LaboratoriesProtocol #418-009are
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/massspectrometry
( E S M S ) . On the basis of findings from these analyses, additionalsample matrices may be evaluated or other metabolites may be targeted. If additional analysis is performed, a protocol amendment will be written.
5.0 - EXPERIMENTALnalvticalMethods
5.1 FACT-M-1.0, Extraction of Potassium Perfluorooctanesulfonateor Other Anionic Surfactantsfrom Liver for Analysis Using HPLC-Electrosprayhlass Spectrometry
5.2 FACT-M-2.0,Analysis of Fluorochemicalsin Liver Extracts Using HPLCElectrosprayMass Spectrometry
5.3 FACT-M-3.0, Extraction of Potassium Perfluorooctanesulfonateor Other Anionic
Surfactantsfrom Serum for Analysis Using HPLC-Electrospray/Mass Spectrometry 5.4 FACT-M-4.0, Analysis of Fluorochemicalsin SerumExtracts Using HPLC-
ElectrosprayMass Spectrometry
6.0 DATAANALYSIS
6.1 Data transformationsand analysis: Data will be reported as the concentration (weighvweight)of fluorideper 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 concentrationswithin each dose group. If necessary, simple statistical tests, such as Student's t test, may be applied to evaluate statistical difference.
3
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
7.0 MAINTENANCEOFRAW DATAAND RECORDS 7.1 The followingraw 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 7.15 Electronic copies of data 7.2 Supporting records to be retained separately from the study folder in the archives
accordingto AMDT-S-8will include at least the following:
7.2.1 Training records 7.2.2 Calibration records 72.3 Instrumentmaintenance logs 7.2.4 Standard Operating Procedures, Equipment Procedures, and Methods 7.25 Appropriate specimens.
8.0 REFERENCES 8.1 3M Environmental Laboratory Quality System Chapters 1,5and 6 8.2 Other applicable 3M Environmental Laboratory Quality System Standard Operating
Procedures
9.0 ATTACHMENTS 9.1 FACT-M-1.0, Extraction of PotassiumPerfluorooctanesulfonateor Other Anionic
Surfactantsfrom Liver for Analysis Using HPLC-Electrospray/MasssSpectrometry 9.2 FACT-M-2.0, Analysis of Fluorochemicals in Liver Extracts Using HPLC-
ElectrosprayA4ass Spectrometry 9.3 FACT-M3.0, Extraction of Potassium Peffluorooctanesulfonateor Other Anionic
Surfactantsfrom Serum for Analysis Using HPLC-Electrospray/Mas Spectrometry
9.4 FACT-M-4.0,Analysis of Fluorochemicals in SerumExtracts Using HPLC-
Electrosprayh4ass Spectrometry
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3M Environmental Laboratory
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M EnvironmentalLaboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASST[TM
PERFLUOROOCTANESULFONATE(PFOS) IN RATLIVERBY LC/MS/MS
Vaaion LO
3M Environmental Laboratory
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3M Medical Department Study: T-6316.5
..
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
?
METHOD FOR ANALYSXS OF POTASSNM P E R F L U O R O O C T A N E S ~ O N A(P~FOS)IN RAT LIVERBYLc/Ms/116s
Verrion LO Study No.:
Annlyst/D.dc:
L SUMMARY
n.
IIL
N.
._
V. 3M Environmental Laboratory
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASsmM PTCRFLUOROOCTANESULFONATE(PFOS) IN RAT LIVER BY LC/MS/MS
version 1.0 Study N u
AndyJt/Jl.tc:
,
i i
Peauomoctane Sulphonic Acid
M-556
, I4570
PFOSAA
PFOSA
msEA
RatLiw
Methanol
- I
I
vt EQUIPMENT
SaTable 2 for all rquhdmajorpieces Ofcquipmcnt Usc the table to doaunenttpeachralpiax
(e.& mak~m, odel) of equipment Check calibrarion ofall apipmcntnquiringcalibrarimtion(eg. babccs) to amre it is cumnt
Page3 of16
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
\-
METEOD FOR ANALYSIS OF POTASSIUM
PERFLUOROOCTANESU.L.FONAveTrsEio(PnF1.O0 S) IN RAT LIVER BY LC/MS/MS
. Stndr NC
TCStTUbCS
Transport*
h&gIUtiCsrimr
Orbital SbnLer
Evaporate Extrac*l
Store QCs
Stir maaix
Exmu Sampla
Blue FaIan
. l5mL Polypmwlcnc,
12 x75 mm SmL
polypromilcnt
2002 127-Tl60-56F'
HDmogmizer
Griadliver
PHmeter
DaamineBII&rpH
Electrode
lktermbBII&rpH
Vol~cFlaskS, MalreVOl~C
QassA
I
Dilutions
I
J
NA
NA
I
I
NA
NA
I NA
NA
I
1
i
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E-8
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Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M EnvironmentalLaboratory Study Number: FACT 060998.1
ME'&OD FOR ANALYSIS OF POTASSIUM PJCR,FLTJOROOCTANESULFONAT(EPFOS) IN RAT LIVERBY Lc/Ms/Ms
version LO Study No.:
A4y#/Dote:
va PROCEDURE
A. Prepnration of 2 mMAmmonium Acetate
Weigh0.1500_+0.0020gafammonium~andtraasfi?rtolaooOsrCvDhrmstric flask. Dissolve solid in water and dilute to volume with water. Solution may be used for onemonth stonxiatmom tcmpcrabac
~lnszsofrmmnnitrmacctate:
AchlaldnalVOlLUE Dateofprepadon: Study No:
B. Prep.ration of -29% Sodium Hydroxide Solution
Weigh200 i 2 g of sodium hydmidc into abcalrer. Add 500 mL dMilliQwateraad mix to difsolvc Cool d trans6arn a polypropylene bottle ixnorngc Solutionmay bs stored for 6 months at room temperature.
Actu?llmass ofsodium llyciroxide: AaualVOlumCMilli-Qwattr: Datc0fprrp;nntion: Study No:
C. Preparation of -2.9% Sodium Hydroxide Solution
Add 10 mL of-29% SodiumHydroxide Solutionto a lOO-mL wlumetricfksk and dilute to volumewith W-Qwater. Transfuto a polypropyk bottk for stomp. Solution may be s t o dfor6 monthsatmorntcmptlature.
Actual volume of-29% NaOH solution: Actual final volume:
Date ofprepamion:
Study No:
D. Preparation of TetrabutyhmmoniumHydrogensulfate(TBA)
Solution, 0.5 M, @H 10)
pHMttuCaliion
pRbufher:7 pHbufher: 10
PHreading:@eradnig..
. Add 169 I1 gofTBA to-SO0 mL OfAGIli-QwaDxiuabeaker. AdjmttbcpHta 10.00
t 0.02 using4 5 - 6 0 mL d 2 9 % Sodim H y M & sol^^ dilute to lo00I& witb Milli-Qwata,andmixM~thapHm10.M)10.02using-z.9./o~oHaodmix
Tmsfer to a polypmpylme boule for storage. Solution may k used for one month
storedat room tempem- but the DEmust be checked urior to aeh use Adjustto
pH 10.0 t 0.02 with 29% sodiumH-de
Solution as masaxy.
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3M Environmental Laboratory
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METEOD FOR ANALYSIS OF POTASSIUM PERFLUOROOCTANESULFONA~(PFOS) IN RAT LIVERBY LC/MS/MS
vurion LO
Study No.: '
AJlai~Itc
ActoalmsssafTBA: ActnalfinaIvolUmC:
. ActnalfhmlpH:
Date ofprcpatioxt
Study No: ~IHafter rrchcddng andlorreadjusting
E. Preparation o f 0.25 M Carbonate Buffer
Weigh 26.5 i 0.1gofsodium carbonateand 21.0 t 0.1 g ofsodium bicarbonateaod em&rtothcsame 1000-mLvolumehicflask.DkohrethematerinlsinMilli-qwtcr, dilateto vo1umewithMilli-Qwntcr. mix.aad himsf& to a polypropylenebottle for soorage. Soludon may be used for 1monthwhen s t o d r&igmtcd.
Actualmassdsodiumcaltlonate: Actualmass ofsodiumbicarbonate: . ActuaIfinaIvol~: Date afprcpamioxt Study No:
F. Preparation of MobiIe Phase
&mponcnt A: Mix together 600 mL of2mMammo&m acetate aod 400 mL of mtthaaol Solution may be usedfor 1month whm StORd at room twpaahac
Actualvolume afz mMsmmoniumaa$tc:
mL
. . Actualvolnmeofmethaool:
mL
Date ofprepamion:
Study No:
ComponentB: Mix to@cr 50 mL of2 mMammoniumacetateaud950 mL d metbaa01Solution may be used for 1monthwhea stored at mom tanpaatwe.
Actual W l ~ n f ID2A4 ammopiumacetate:
mL
Actualvolumeofmcthanol:
mL
Date afprqmaiion:
Study No:
G. Prepamtion of Stock Surrogate Standard and Working Surrogate standard (WSS)
3M Environmental Laboratory
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASSIUM
PERFLUORO0CM"LFONATE (PFOS) IN RAT UNER BY LC/MS/MS
Vvsion 1.0 Study No.:
AndYSUDptc
2. wss (lo00ngImL.1:
DilatelOOIJ.cbstocknmogatestandardto25mI.withmcthpnoland~.
Actnal Volume afstock htunal standard: Ac~aulDilution ValDatedPnparation:
E. Preparation of CalibrationSolvent Stock and Working Standards
I.
SolvultStDckr:
. F o r d analytewdghthc specifitd a m & t o f s t a n d a r d ( i i
weighedas A aad B I@-)
ltted in Table 3 andtransftrintD scparare .
volamctric flasks Dissolve in methanol, dilute to wlume with mcthanoi, a d
mtcwdl. Sto~rcfiigaatcd,pmtcdedfiomWlight
2. Mixedsol~stocks:
Pipet the specified amount of each analyficalStandardRqlicate A as listedin Table 5 a d tmnsfkr into a single volumetricflask Dissolve in rndmol, dilute to volume with methanol. andmix mil. Store re6ig.n;ue4 protectedfromW
light Rcputtheprocsswith~licatcBstoclc; Themtecdsofventstockscac
vscd toprrparetha workingstnndorplr
Date ofpreparaton:
Study No:
3.
working StandardJ0:
Dilutethe mised stocks andworkingstandnrdswith Wthaool assptcifitd in Table 3 and mix well.
DaOe Cbpl'CpatiOS
3M Environmental Laboratory
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASSIUM
PERnUOROOCTANESULFONATE(PFOS) IN RAT LIVERBY Lc/Ms/Ms
Venion 1.0 Study No.:
Aml~atc:
Weigh allanalyticalstandardsto at least the nearest 0.01 mg.
** Use volumuricorppsitive-displaamentpipct(s). I. Prepantion of Calibration Standards and Blanks
1. Livahomogenate
Pnpanblank liwrhomogenate in bulk by weighingapproximntely40gof blankliverinto a 500 mL Nalgcncbottle containing200 mL 0fMilli-Q water.
Grindto a homogeneous suspension. Aliquot into approx 30 mLportionsfor
h z u l (approx -20C) storagt.
AcamlMarsafliver: Achral wiume ofwotp: Date ofprcp:
Study:
Ddaminedalsi~ofealibrat~maDik
MJXHOMOG~NATETHOROUGHLY and dtvrminethe in of 10 repiicatewcighings of 1mL partions afthcTHOROUGHLY MDED hom0genatL MIXHOMOGENATE IMMEDIATELY PRIOR TO EACH
ALIQUOT REMOVAL.
I
I
I
I
I
I
I
I
1
I
LivacalibEatianStandards
pnparr each livacalibrationstambud by adding 0.45 mL of undilutedlivcr
homogenate (STIR HOMOGENATE WHILE ALIQUOTING) into a 15 mI. d o n tube pnd adding 50 &of WS or MeOK Prrparetriplicate cal standardsand6blankrSceTable5forMiumes. Thedilutedliwdensiryis
a s n r m t d t o b e ~ y 1 5 0 m g l m tMixwell
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3M Environmental Laboratory
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASSIUM
PERFLuoRoocTANESULFONATE (PFOS) IN RATLIVER BY LC/MS/MS v&M LO
Study No.:
\
An.lyStlDatc
Table5. C d b d o a Standvdr andBl&
Date ofpreparation of d ads/bk&
J. Preparation of Quality Control Liver Samples (QCC)
1.
Quality Contml Working Standards
DiIutethefollowing sour^^ volumes methanol in volumceicflasksand mix d.Pnpankshwhenused Actualvolumessreinpareotheses.
2. -on
of Quality ControlLiva Samples
ReparreachQci n b u l k b y f i l l i n g t h e w l m ~ c f l a & a pW p ~kIl
with undilutedliver homogcnac (STIR HOMOGENATEWHILE
ALIQUOTING), adding the appropriateQC WS.mixing and dilutingtovolums
withd u t d liver homgcoate (STIRHOMOGENATEWRILE ALJQUOTING). MIX THOROUGHLYand disptnse 2 . 5 4 . aliquotsinto polypropyltnetubes and store at approximately-2OOC
Table 7. OC Prcnfirntinn
Date ofQC pnp:
study:
K. Preparationof MS Check Standard for System Suitability
Pipet 250 of WS 2 at-10.000 nglmL and2 5 mL of WSS at -IO00 n g h L in methim01 into thesame 5 0 - d volumCaicflask Dilute to volume withMdlH andmix
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FOR aALY!SE OF POTASSIUM PERFLUOROOCTANESULFONATE (PFOS) JN RAT LKVERBY u=IMsIMs
L. Preparation of homogenizerrecovery liver samples
Todetarmincthc~~~thehomogenization~~nnhomogenizcdblankliva w i l l k ~ m ~ t i c y c a t 3 ~ ~ c m I ~ a n d h o m o g c n i z t d a s f o Tlhlios w s n d s t o k done every day thathomogtnizationofsaudysampla is pcrfonnta
1. piaa appradmatdy0 3 gofunhomopepizedblank liverinto mchof6.15 mL
polyplupybanh-ifagehlba. Rccordweightsafliva.
2. .
Addl00~afwS1.3,aad4(onewSpaduplicatetubes)toprrpare fordfications a t w y 4, 0.8. and 0.4 pg/g
3. Multiply themass ofliverin g by 2 5 and addthis many mL ofwater.
4. Homogenizeeachliwsamplq andrinsehomogenizerpube with snotha
VolUmeofwaterustd in stcp3. addingrinseto homogenized sample.
5.
Clcanbomo~withMeoHbetwetnsamples
6.
CapandVoltrxhomogermtefOrusein~aa
M. Preparation of Dilution Check Sample
1. plaa 2.95 mL o f d u t e d liver homogenate (STIRHOMOGENATE WHILE ALIQUOTJNG) into a 15 mLcxmctiontubeandadd50pL ofMixui Stodc A
2. Dilute 50 pL ofstep 1 solution (VORTEX SOLunON WHILE ALIQUOTING) with 0.45 mL of undiluted liver homogenate (STIR HOMOGENATE WHILE ALIQUOTING) in 3.U mL extradontubes
3. This sample should be prepandfor OmacfiOnonly on days when study samples willkdilutcdandcxtraad
. . N. Homogenization of study samples
1. Placeappxr~ximatdy0.5 g ofnnhomogmizcdsi,udy sample liverinto a 15 mL
polypropylentt u k Recordweights ofliva.
2
Multiply tile mass of liver ingby 2.5 andaddtbismany mt ofwale?.
3. HomogmizC tach h e r sample.and bhomogenizCrprobe with another
volume ofwater wed in step 2. addingrime to homogenized sample.
4.
Clamhomog~with~H~rampla.
5. Capandvortcxhomogmtcforuseinaeactioa.
0. Analysis Standards, Blanks, QCs,and Spmplu
1. MIXLIVERHOMOGE"ESTRoROUGHLY BEFORE ALIQUOTING andpipet 500 pL of each QC (4 replicatesper Iml). and other samples being
pmaaed into 15-mLp01~pmpylcncomactiontubes The cal stds and blanks an alrcady aliquotd
2 TOthe B W - I S (3 npSh add 100& U L a f H a n d v m 3. To t h e B W + I S (3 andtothe Rmaiaingsamples, add 100& WSS and
Vortff
4. Add 0.5 mL af0.5 MTBA ($3 10) to all tubesandvoncx briefly.
56. Add 1mLof0.2SMMbufkriindvowrtabrictly. Add 25 mL of ethyl accmtc. FYatx the tubes sidcways on the orbital shaker at a stting of300for-20 mimrta.
7. cmhifuge tubaat a settingof3500 rprnfor-u)mirmts to scpmatc layas 8. Transfer2 mL dthctop 0rganiClaytrto a cleanpolypmpylcnetllk
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M EnvironmentalLaboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASSIUM PERFLUOROOCTANESULFONATE(PFOS) IN RATLNERBY Lc/Ms/Ms
Version 1.0
Study No.:
Adystmpte: '
E-1.5
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASSIUM
PERFLUOROOCTANESULFONATE(PFOS) IN RAT LIVER BY LC/MS/MS
versiou LO Study Na:
AO.lYSt/Dnte:
427>81 MRM masitionfor S m g a k Standard
499>99 MRM tnnsitionfor PFOS
55078 MRM &ansitionforM-556
-570>169 MRM hansitionfor M570 *
5&1>169MRM transitionforF'FOSAA
498>78 MRM transitionfor PFOSA
528169 MRM d t i o n forPFOSEA
*11 minutes (
mia)
ss: 4 min L m i n )
PFOS 4.3 min L m i n )
M-SS6: 4 5 d L d )
M570 4.6 min
min)
PFOSAA. 4.7 min L m i n )
PFOSAklmin(mia)
PFOSEA: 5.7 min (
min)
+PmmetasthatmnybechaugedbytheanalystActualvaluesin( ).
2 The above conditions should be suitablefor theMicmmass QunmoLC (SM
9053). Modifications may bc ncmsBlyifanothuh4icromassQuaam Series
rpectrometeris uscd Splitthe flow postcolumn via a Keystone BIo-tceor
similardevice.
3.
Caliimtc themass spectmmeterusinga suitable nfumce compound,orveriij.
that the calibrationis suitable by visual inspection(onthetunepage) that a
suitablemobile phase ion is still acNTJtctydttermincd&solution may needto
be higher than that used for analyzing samples.
4.
To check the properperformance ofthe insenUnud,inject the instnmmt c h d
standarbThe d t s should be comparableto a recent injection if availablt
5. U s e ~ s a u t o m a t t d c h m m a t o g r a p h y ~ ~ o n ~ s y s t r m t o c o ~ t h s
outputtmm the analysis.
6.
Logding orda:See the loading rrporthn the automated chromatD&
in~onsoftwsrr~
7. Makesingleinjcctionsdtachcalst&ard,QC. Jtuctysampl~orblankMake
at least 4 irjectioruofthe
cheek srandard
8.
Run set- should typically not exceed80 injections dae to. e
t
response m l l d c o n s i ~ o n s .Laager nmsmay be performed, but thypose a risk ofyicldingnnacccp~lecurve rcsIll?s.
Wa CALCULATIONS
1. sprradsh&tsoftwan:
Version
2. MsAnalysissoftware:
Version
3. Cakulatethcavuagedtnsitydthe liwhomogcnatc( l o w ) in mgimL
4. Using the avenge density of the homogenate. calculateia livadensity
(mg ofliverpcrmLofdilutedhamogenate):
Undiluted liwdensity (mdmL)= (gaflivaxaveragc densityofhamogenate)/(gof liw+gdwatet)
when g ofliver and gofwater an masseswd to prrparebulkhomogcaatt; density of water isassumedtobe 1g/mL
Dilutui liver density (mglmL)= Undiluteddensity + Diln Factor
Page 12of16
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASSIUM PERFLuOROOCTANESULFONATE(PFOS) IN RAT LIVER BY LC/Ms/Ms
V d o n LO Study No.:
AariyruDuc
whvcdiInEKxor-211.8= 1.1111toeccormtfor lo%& dliwhomoganme incalndandQCmarrim
5. c a l c u l a o t t h e i l c h l a l c o-~on(n&lL) afmand othernnorochemicalsin tbe auspauions ofcalibrationstand;lrdsand-by usiagthem a ~ o f a d y t easnd dilution factors ody (no liver density correction). Use purity cormxionfor W O W only.
..
A. Ms Check Standard (System Suitablity)
ss At least 3 injectionsofthe MS CheEk Stilndardmust pmvide a o/oRsD of lo./. or lessfor the
PFOS to peak arca d o .
B. CaIibration Standards
The percentdative ~ m rfsor the concmtrdiion-level ay~agcsofthe caliimion standardc Jhouldmatthtfollowbg~ts:
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASSIUM
PERFLUOROOCI`ANESULFONATE (PFOS) IN RAT LXVER BY LC/MS/MS
Version LO Study No.:
AnnlydDlltc:
Table 10. OC Accmblnoc limits
M-556
PFOSAA
PFOSA PFOSEA
Removal o f i n d i v i d d m h e h t h e QC Qlculationsfnaybe done ifacwmpaniedbya rrasonableexplanation(e.& instnanentmalfunctionor Dixon's Q test results).
wmcavcragc dctaminedmnccnhationforanyQC lcvcl rrrrcQs thcacccpraacclimit, the
taslcleadaastudydirectorshouldbe notified Them may k repeated or apanimofthe
nm mgyk co&dmdocccpt?blc For -plq ifthe low QC Eailsthe stated reqr `
\
samplamaybePcceptedthathavem~tratonsbradretcdbythehighest~~ration
smndard and a mid-lcvtl QC c0ncuWUion.
D. Homogenizer Recovery and Dilution Chedt SampIes '
Thc ayu~gcrccovuyacrossthe 3 levels ofhomogenizerrsovuysamples as well that of
. . the dilution check samples should EalIwithinthe rangeof70-130% inclusive. Rrmovpl of
mdivuid outliersbmm thecalculations maybe done ifacmmpanicdby a reasonable
aplanetiaa
E. Sensitivity (LOQs)
' Thevalidatedlimits d#on andFFosAA
are nominally0.13 vg/g each for PFOS, M-556,W O ,
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3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASSIUM PERFLUOROOCTANESULFONATE(PFOS)IN RATLlVER BY Lc/Ms/Ms
Yenion LO Stady No.:
Ady#DabC:
ForPFOSA andPFOSEA,thevalidatedLoQsare nominally 0.33 @ g d Dnc to the natnnattheheprrporationcbthe~onstandards,lowrrconcmatiaasdPFOSA8nd
G.
x
M.
3M Environmental Laboratory
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E-I9
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
METHOD FOR ANALYSIS OF POTASSIUM PERnUOR00CX'A"ULFNATE (PFOS) IN RAT LNER BY LC/M!YMS
Version LO . Siudy Nar '
CONCLUSIONS
QC RNim
Date
. Daa:
Datr Datr
Date: Date
Daor Date:
3M Environmental Laboratory
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
Study Title CombinedOral (Gavage) FertilityDevelopmentand PerinataVPostnatal
ReproductionToxicity Study ofN-EtFOSE in Rats
PROTOCOL AMENDMENT NO. I
Amendment Date: July 28,1999
Performing Laboratory 3M EnvironmentalTechnology & SafetyServices
3M Environmental Laboratory 935 Bush Avenue
St.Paul, MN 55106
Laboratory Project Identification ET&SS FACT-TOX-013 LIRN U2095
3M Environmental Laboratory
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
PrOtOCOl FACT-TOX-Of 3 Amendment 1
This amendment modifies the following portion(s) of the protocol: 1. PROTOCORLEADS: The proposed study completion date is listed as 12131/98.
AMENDToREAD: The proposed study completiondata is 6/30/00.
REASONT: he proposed completiondate was changed to allowtime for analyzingall matrices of interest.
Amendment Approval
h m V & 776- A
0
Marvin Case Ph.D., SponsorRepresentative
JO&d 1+%G Datd
Kris J. Hhsen PhD.,'Study Director
g IZ/55
Date
3M Environmental Laboratory 3M Environmental Laboratory E-22
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
Study Title Combined Oral (Gavage)FertilityDevelopment and PerinataVPostnatal
Reproduction Toxicity Study of N-EtFOSE in Rats
PROTOCOL AMENDMENT NO. 2
Amendment Date: September 10,1999
Performing Laboratory 3M EnvironmentalTechnology & Safety Services
3M Environmental Laboratory 935 Bush Avenue St. Paul, MN 55106
Laboratory praject /dentincation ET&% FACT-TOX-013
LIRN U2095
I
3M Environmental Laborafoty
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
PrOtOCOl FACT-TOX-013 Amendment 2
This amendment modifies the following pottion(s) of the protocol:
I. PROTOCORLEADS: The protocol statesthat liver willbe extracted and analyzedat the 3M Environmental Laboratory.
AMENDTo READ: The liver specimenswill be extracted and analyzed at Battelle Memorial
Institute, 505 King Avenue, Columbus, Ohio 43201-2693.
REASON:The liver specimenswill be sent to Battelle Memorial Institute for extractionand analysis due to time constraints in the 3M Environmental Laboratory.
2. PROTOCORLEADS: The protocol statesthat serum specimens will be extracted and anal*ed following methods:
FACT-M-3.0, "Extractionof PotassiumPerfluorooctanesulfonateor Other Anionic Surfactantsh m Serum for AnalysisUsing HPLC-ElectrosprayMass Spectrometry" FACT-M-4.0, "Analysis of Fluorochemicalsin Serum Extracts Using HPLCElectrosprayMass Spectrometry"
AMENDTOREAD: The serum specimenswill be extracted and analyzed followingmethods:
ETS-&;Q.l'%, xtraction of Potassium Perfluorooctanesulfonate or Other Fluorochemical Compounds h m Serumfor AnalysisUsing HPLC-ElectrosprayMass Spectrometry" ETS-8-5.1, "Analysis of Potassium Perfluorooctanesulfonateor Other Fluorochemical Compounds in Serum Extracts HPLC-ElectrosprayMass Spectrometry"
REASON: The extraction and analyticalmethods FACT-M3.0 and FACT-M-4.0,
respectively,were updated on 04/27/99 to ETS-84.1 and ETS-8-5.1.
3M Environmental Laboratory E-24
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
PrOtOCOl FACT-TOX-013 Amendment 2
3. PROTOCOL READS: The protocol states that liver specimens will be extracted and analyzed following methods:
FACT-M-1.0, "Extraction of Potassium Perfluorooctanesulfonateor Other Anionic surfactants fiom Liver for analysis Using HPLC-ElectrosprayMasSpectrometry"
FACT-M-2.0, "Analysis of Frluorochemicalsin Liver ExtractsUsing HPLC-
ElectrosprayMas Spectrometry"
AMENDtoREAD: The liver specimenswill be extracted and analyzed followingmethod:
Method for Analysis of PerfluomoctaneSulfonate(PFOS)in Rat liverby LC/MS/MS, Version 1.0
REASON: Sincethe liver extraction and analysiswas sub-contractedto Battelle Memorial
Institute, this amendment was written to include their liver methods and titles.
Amendment Approval
Kristen J. Hansen Ph.D., Study Director
3M EnvirOnmental Laboratory
E-25 3M Environmental Laboratory
3/2f7/99
Date
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
.
1
Study Title Analytical Study 2(N-Ethylperfluorooctanesulfoddo)-ethal in
Two GenerationRat Repduction
PROTOCOL AMENDMENT NO. 3
Amendment Date: October 4, 1999
Perfbnning Laboratory 3M Environmental Technology & Safety Services
3M Environmental Laboratory
935 Bush Avenue St. Paul, MN 55106
Laboratory Project ldentiffcaffon ET&SS FACT-TOX-013
LIRN U2095
3M Environmental Laboratory
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Battelle Study Number: N003604-D 3M EnvironmentalLaboratory Study Number: FACT 060998.1
.
2
Protocol FACT Tox-013 Amendment Number 3
This amendment modifiesthe following portion(s) of the protocol:
1. PROTOCORLEADS: Kristen J. Hansen, Ph.D. is the Study Director.
AMENDTO READ: James K. Lundberg, Ph.D. is the Study Director.
REASON: Original study design has changed due to availability of resources and James K. Lundberg will begin servingas the study director for'FACT-TOX-013as of 4 October 1999,
2. PROTOCORL EADS:
Section 7.1 statesthat the followingray data and recordswill be retained in the study folder
in the archives according to AMDT-S-8: Approved protocol and amendments; study correspondence;shippingrecords; raw data; and electroniccopies of data. Additionally, Section 7.2statesthat supportingrecords to be retained separatelyh m the study folder in the archives accordingto AMDT-S-8 will include at least the following: Trainingrecords; calibration records; instrument maintenance logs; Standard Operating Procedures, Equipment Procedures, and Methods; and appropriate specimens.
AMENDTO READ: . Section 7 states: "The original data, or copies thereof, will be available at the 3M
EnvironmentalLaboratory to facilitateaudits of the study during its progress and before acceptance of the final report. When the final report is completed, all original paper data, including: approved protocol and amendments, study correspondence, shipping records, raw data, approved final report, and electronic copies of data will be retained in the archives of the 3M EnvironmentalLaboratory. All corresponding trainingrecords, calibrationrecords,
btnunent maintenance logs,standard operating procedures, equipment procedures, and
methods will be retained in the archives of the facilityperforming each analysis.
REASON: To direct subcontract laboratories in the disposition of the items listed above.
3M Envirvnmental Laboratory 3M Environmental Laboratory E-27
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Battelle Study Number: N003604-D 3M EnvironmentalLaboratory Study Number: FACT 060998.1
.
1
PIVtOCd FACT TOX-013 Amendment Number 3
3. PROTOCOL READS: Disposition of test and control substances: Biological tissues and fluids are retained per GLP
regulation.
AMENDTO READ: Specimenswill be maintainedin the 3M EnvironmentalLaboratoryspecimen archives. All specimens sent to sub-contractlaboratorieswillbe returnedto the 3M Environmental Laboratory upon completion of analysis and submissionof the sub-contractlaboratory(s) final report. The specimenswill be returned with the followingdocumentation: the signed
original chain of custody and records of storage conditionswhile at the sub-contractfacility.
REASON:
To define in detail the appropriatedispositionof specimens analyzed at subcontract
laboratories.
Amendment Approval
T L Marv Case, D.V.M., Ph.D., SponsorRepresentative
v o u * [qqq Date '
&O /99?
, Date
Kristen J. Hansen, PhD., Previous Study Director
Dale 'L. q f J & Bacon,M.3, M Environmental LaboratoryManagement
1015 / 9 9
Date
Dke
3M EnvironmentalLaboratory E-28
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Study Tifle Analytical Study of 2(N-Ethylperfluorooctanesulfonamido)-ethanol in
Two Generation Rat Reproduction
PROTOCOL AMENDMENT NO. 4
Amendment Date: 20 January 2000
Performing Laboratory
3 M 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: 4 18-009
3M Medical Department Study: T-63 16.5
3M EnvironmentalLaboratory
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LRN-U2095
-
APmrOetnOdCmOlenLtRNNum42b0e9r 54
This amendment modifies the following portion(s) of the protocol:
I. PROTOCORLEADS:
The study director for the present study was identified in the protocol as James K.
Lundburg, Ph.D. AMENDTO 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 Maivin T. Case, D.V.M., Ph.D. AMENDTO 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.
E-30 3M Environmental Laboratory
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-
APmreontodcmoel nLtRNNu-mUb2e0r945
Amendment Approval
John L ButenhofPh.D., Sponsor Representative
Date
t A Wr
Marvin T. Case, D. KM., Ph.D., Incoming Study Director
l o F A , &-a
Date 6
E-3 1
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. 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 Laboratory935 Bush Avenue St. Paul, MN 55106
Laboratory Project Identification FACT-TOX-0 13
ET&SS LRN U2095 Argus Study: 418-009 3M Medical Department Study: T6316.5
3M Environ3mMeEntnavlirLoanbmoernattaolrLyaboratory
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-
Protocol FACT TOX-013
Amendment No. 5
This amendment modifies the following portion(s) of the protocol:
7. PROTOCOL READS: The Principle Analytical Investigator for the present study was identified as James K. Lundberg, Ph.D.
2. AMENDTO 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.
E-33
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Amendment Approval
Analytical Study: FACT-TOX-013 LRN-U2095
Protocol FACT TOX-013 Amendment No. 5
(5
John L. ButenhoB Ph.D.,Sponsor Representative
Date
M h i n T.Case, D.V.M., Ph.D., Study Director
W
Date
E-34
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
DEVIATION REPORT
Battelle Study Number: N003604-D 3M Environmental Technology and Services Study Number: FACT 060998.1
2 (N-Ethy1perfluorowtanesulfonamido)-ethanol in Two Generation Rat Reproduction
TYPE OF DEVIATIONS: PROTOCOL
DATES OF DEVIATIONS: October 18, 1999
NATlJRE OF DEVIATIONS: Some of the analytical method acceptance criteria were not met for the
LC/MS/MS analysis conducted 180ct99 at BatteIle. These deviations d a t e to protocol amendment 2.
See below for summary.
r
PPOS M-556 M-556 M-556 M-556
PFOSAA PFOSAA
I
1
QC3 exceeded 20%error (-20.3 % actual) QC2 exceeded 20%error (23.4%actual) QC3 exceeded 20%RSD (21.2%actual) QC4 exceeded 20%RSD (28.8% actual) Dilution recovery exceeded 130%(131.5%actual with 21.6%RSD) QC3 exceeded 20% error (-20.6%actual) QC4 exceeded 20%RSD (21.3 % actual)
CAUSE OF DEVIATIONS: Sample preparation andor LC/MS/MS variabilities over the course of the sample set may have contributed to the deviations.
IMPACT OF DEWATIONS ON THE STUDY: The errant QC values were bracketed by acceptable
QC concentration levels which demonstrates that the calibration curves generally provided good accuracy over the twted range. The dilution recovery for M-556Was not considered to be exceedingly high enough,at only approximately 1.5% above the normal acceptance level, to have significantlyimpacted the data.
CORRECTIVE ACTI0N:lXs protocol deviation summary was prepared for inclusion in the final report.
APPROVED B Y
-; r L Date
I
, Battile Principal investigator
Study Director
h 4 V # I k I: e 4 *
bwhJpI,p Ivlcc avo/
l w w L . 2441
Date
N003604-DProtocol Deviation 1, Page 1 of 1
E-35
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Battelle Study Number: N003604-D 3M EnvironmentarLaboratoryStudy Number: FACT 060998.1
DEVIATION REPORT
Battelle Study Number: N003604-D 3M Environmental Technology and Services Study Number: FACT 060998.1
2 (N-E!thylperfluorooctanesulfomnido)-ethanol in Two Generation Rat Reproduction
TYPE OF DEVIATIONS: PROTOCOL
DATE OF DEVIATIONS:
October20,1999
NATURE OF DEVIATIONS PFOS QC3 exceeded the 20% RE method requirement (actual -21.7%). The dilution recovery check standard did not meet the 70-130% recovery requirement (actuals 5.0% for PFOS and 4.6% for PFOSA). These method deviations relate to amendment 2 of the study protocol.
CAUSE OF DEVIATIONS: Sample preparation andor LC/MS/MS variabilitiesover the course of the sample set may have contributed to the QC deviation. Sample preparation error appears to have been the cause for the dilution recovery results.
IMPACT OF DEVIATIONS ON THE STUDY: The errant QC value level was bracketed by acceptable
QC concentration levels which demonstrates that the calibration curves generally provided good accuracy for study samples over the tested range.
A comparison of the results obtained for the diluted study samples from 200ct99 and previous results that were slightly-ALOQ (13Oct99 and 18Oct99) demonstrated good agreement between the 2 determinations. This would indicate that the dilution of the study samples was performed correctly 20Oct99 so that no impact on the quantitationsoccurred.
CORREclTvE ACTI0N:This protocol deviation summary was prepared for inclusion in the final report.
APPROVED BY:
L c Gv& JofJC. Andre, Ph.D.
Date
Baitelle Principal Investigator
A
N003604-DProtocol Deviation 2,Page 1 of 1 E-36
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-
Battelle Study Number: N003604-D
3M Environmental Laboratory Study Number: FACT 060998.1
DEVIATION REPORT
Battelle Study Number: N003604-D 3M Environmental Technology and Services Study Number: FACT 060998.1
2 (N-Ethy1perfluorooctanesulfonamido)-ethanolin Two Generation Rat Reproduction
TYPE OF DEMATIONS: PROTOCOL
DATES OF DEVIATIONS: October 12, 1999through October 20,1999
N A m OF DEVIATIONS: The lot number of PFOS used was not 217 as per section 3.1.1 of the protocol. The source of reference substance matrix was not Argus 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.
CAUSE OF DEVIATIONS: Only PFOS lot number 171 was available at Battelle. Harlan 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 hterest (PFOS,M-556,
PFOSAA, and PFOSA) were monitored during each analysis.
IMPACT OF DEVIATIONS ON THE STUDY: PFOS lot number 171 and Harlan-
supplied liver were both used for Battelle's validation of the analytical method (Battelle study number NOO3604-A). These materials allowed achievement of the reported method acceptance 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:
LCGik-dq
Jon@. Andre,Ph.D. Batt&e Principal Investigator
2- 2-74
Date
Study Director
N003604-DProtocol Deviation 3, Page 1 of 1 E-37
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
APPENDIX F - PFOS PURITY REPORT
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Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
8 651 778 4226 ~
04/26/99 09:56 @1 :02/03 N0:341
Ta; blnG
s&iGc
parr;.
~,~
3M 3PECMLT.Y ADHESXVZS & CHEMICALSANALYTXCU, LABORATORY
- Lisa Ckmn (8-5568) -ETUS- 24349 - - - Tom kstner (34633) SA&C Analytical Lab 236-2B-1I
Rcquest # 57830
CIURIicd Chtaci2-n
of POSF-Baed FtuorochrrmLaLv 8y 'R-NHRdi "F-NM.
SpeCtTOSCan
Match 24,1999 Retiminary report for FC-95 (PFOS), lot 171
.
~ ~ ~ ~ ~ hGom- indAprod-uct =OGFd8O,(-3) K(4+) (whitepowder)
ODUCTIOY;
'Ibis sample was subjecrcd-to'H-NMR and '%NMR specaal analyses to determine the purity of the nominal product and to chanrcrerue aa many impuritycomponcnbM possible.
A portion of the sample was accurately weighed, spiked with a known mount of 1,4-bis(trifluoromcthyhyl)bmzl?ne (pHFX),and then totally dissolved in D M S M for subsequent analysis by NMR A 400 MHz 'H-NMR Spectrum(b N7830.401)and a 376 h4Hz "F-NMR spectrum(# fS7830.401)were acquired using a Vdan UNITYpIus 400Fr-NMR sptctromcter. Use of the pHFX internal standard was intended LOpermit the derennination of the absolute weight percent concentrationsof the assignedcomponentswithout necessarily needing to identify or quanti6 all the components in the sample mixture.
RzuYLm
The combinedNMR spccrral dam were used to assign 311 of he major and most of the minor componentsin thi8 sample received. The qualitative and quantitalivc compositional r e s u l ~that w e n derived from the single Vial NMR internal sfandnrdization analyses are summarized in TABLE-1on the followingpage. I have reported both reiative and absalute weight percent concentrations. One possible rewon that the absoIuce wt.46 values add up to mom than 100% may be due to the fjcr that I assumed all of the components conrained 8 carbons. If thcre were
any shorterchain homologs present (i-e.. 7.6.5, tcc. carbons). then the average coToudd molecular weights
would have been samewhat less than those used in the calculations. In general, the ?-NMR technique is not
POrticularly well suited for identifyingor quantifyingsmall amounts of various fluorochtmid homolog impurity components unless the chainr are very short. A more complete characterization of any other fluorochemical homologs woutd roquire analysis by elcctrospray MS or a similar technique.
Additional work would be required in an effort LO positively verify the tentatively assigned components listed in TABLE- 1 (denoted by possible). Small amounts of other unidentified impurities ilfe also detected in the NMR SppetWa but additional work would be required in an effort to identify or qumriQ these other mrrids.
Copies of the NMR spectra will be provided for you at a later date. If you have any questionsabout the ruultt in
this initial report for FC-95,lot 171. piease let me know. I apologize for the delay in cnmpleting this initial work.
3M Environmental Laboratory
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ETSS 2 3U Mdnh 24 1999
Analytical Study: FACT-TOX-013
-
LRN-U2095
Battelle Study Number: N003604-D 3M Environmental Laboratory Study Number: FACT 060998.1
651 ?78 4226
04/26/99 09:56 # :03/03 N0:341
S A X AnalyticalLab R e p s t f 37830 tlal Rebort for FC-H. lot 174
,
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R
Analytical
Analytical Study: FACT-TOX-013
Report:
LRN-U2095
FACT TOX-013 LRN-u2095
Appendix H: Interim Certificate of Analysis
3
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Report:
LRN-U2095
FACT TOX-013 LRN-u2095
Purity' Test Name
Qpearance :dentification
VIetals. (IQ/MS)
1. Calcium
2. Magnesium
3. Sodium
4. Potassium'
5. Nickel
6. Iron
7. Manganese
Iota1 % 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. Nitxate
5. Nitrite
6. Phosphate
7. Sulfate4
Organic Acids ' (IC)
1. TFA
2. PFPA
3. HFBA
4. NFPA
Elemental Analysis?
1. Carbon
2. Hydrogen
3. Nitrogen
4. Sulfur
5. Fluorine
COA023-018B
3M Environmental
Laboratory
3M Environmental Laboratory
mererence *: DU-UVY
Purity: 86.4%
Specifications White Crystalline Powder
1. Theoretical Value = 17.8% 2. Theoretical Value = 0% 3. Theoretical Value = 0% 4. Theoretical Value = 5.95% 5. Theoretical Value = 60%
Result 86.4%
Conforms
Positive
1. 0.017 wt./wt.% 2. 0.007 wt./wt.% 3. 1.355 wt.hvt.% 4. 6.552 wt.lwt.`%o 5. 0.003 wt.lwt.% 6. 0.004 wt./wt.% 7. <O.OOl wt./wi.%
1.oo wt./wt.% 10.60 wt./wt.%
I
None Detected
0.30 wt.hvt.% None Detected Not Applicable3
1. co.015 wt./wt.% 2. 0.27 wt.lwt.% 3. co.040 wt./wt.% 4. <0.009 wt.lwt.% 5. -=0.006 wt.fwt.% 6. <0.007 wt./wt.?h 7. 8.82 wt.lwt.%
1. co.1 wt./wt.% 2. co.1 wt./wt.% 3. co.1 wt./wt.% 4. <0.25 wt./wt.%
1. 12.08 wt./wt.% 2. 0.794wt./wt.% 3. 1.61 wt./wt.% 4. 10.1 wtJwt.% 5. 50.4 wt./wt.%
Page 1 of 3
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FACT TOX-013 LRN-u2095
INTERIM CERTIFICATE OF ANALYSIS
Centre Analytical Laboratories COA Reference #: 023-018B Date of Last Analysis: 08/31/OO Expiration Date: OS/3I/O1
Storage Conditions: Frozen I-10C
Re-assessmentDate: 08/31/01
`Purity = 100% - (sum of metal impurities, 1.39% +LC/MS impurities, 1O.CiO%+InorganicFluoride, 0.27%+NMR impurities, 1.OO%+PO&X, .0.30%)
Total impurity from all tests = I3.56% Purity = 100% - 13.56% = 86.4%
2Potassiumis expectedin this salt form and is thereforenot considered an impurity.
3Purity by DSC is generalIy not applicable to materials of low purity. No endotherm was observed for this sample.
`Sulfur in the sample appearsto be converted to SO, and hencedetectedusing the inorganic anion method conditions. The anion result agreeswell with the sulfur determination in the elemetital analysis, lending confidence to this interpretation. Based on the results, the SO4is not consideredan impurity.
`TFA HFBA NFPA PFPA
Trifluoroacetic acid Heptafluorobutyric acid Nonofluoropentanoic acid Pentafluoropropanoic acid
`Theoretical value calculations baaedon the empirical formula, C~FI~SOJX+ (MW=538)
This work was conducted under EPA Good Laboratory Practice Standards(40 CFR 160).
COA023-018B
3M Environmental
Laboratory
c
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Report:
LRN-U2095
FACT TOX-013 LRN-u2095
INTERIM CERTIFICATE OF ANALYSIS
Centre Analytical Laboratories COA Reference #: 023-018B
LCYMS Purity Profile:
Impurity c4 CS C6
Total
wt./wt. O/o 1.03 1.56
6.38
10.60
1
m Note: The C4 and C6 values were calculated using the C4 and C6 standardcalibration
curves, respectively. The C5 value was calculated using the averageresponsefactors
from the C4 and C6 standardcurves. Likewise, the C7 value was calculated using the
*r
averageresponsefactors from the C6 and C8 standardcurves.
PreparedBy:
David S. Bell
Date
Scientist, Centre Analytical Laboratories
Reviewed By:
pl
John Flaherty
Date
Laboratory Manager, Centre Analytical Laboratories
m
COA023-018B
3M Environmental
Laboratory
3M Environmental Laboratory
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3M Medical Department Study: T-6316.5
3M Medical
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Study: T6316.5
Appendix I: Report Signature Page
Analytical
Analytical Study: FACT-TOX-013
Report:
LRN-U2095
FACT TOX-013 LRN-u2095
A
7-L
., Ph.D., Study Director
John L. Butenhoff, Ph.D., Sponsor Representative
Dale L.
Date Date , Date
a
3M Environmental
Laboratory
F-
3M Environmental Laboratory
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3M Medical Department Study: T-6316.5
3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Analytical Study: FACT TOX-013 LRN-U2095
Appendix J: Amendment 1 to FACT TOX-013 Final Report
TOX-013 Final Study Report Amendment 1
Study number: TOX 013
Study title: Analytical Study 2(N-Ethylperfluorooctane sulfonamid0)-ethanolin Two Generation Rat Reproduction
Study Director: Marvin T. Case, D.V.M., Ph.D. Amendment date: May 7,2001
Amendment number: 1
This amendment modifies the following portion of the final report:
A final signed report from Battelle Memorial Institute, presenting the results for PFOS, PFOSAA, PFOSA, and M-556 levels in rat liver specimens, replaces the draft Battelle report in Appendix G.
Liver results in this report are identical to those presented in the original TOX-013 report (Table 13, pages 22-23). As in the original liver data, the PFOS values reported in the Battelle report were corrected by 3M for purity of the reference standard material.
The final Battelle report differs from the draft report in the following ways: All signature pages are signed and dated. The Quality Assurance Statement page has four additional audit dates added.
0 Table of Contents page numbers were corrected. 0 Two Battelle participants were eliminated from page 4, `Acknowledgements.' 0 The storage and archive instructions (page 4) are now found in the 3M TOX-013
protocol amendment 3. 0 Inclusion of 3M TOX-013 protocol amendments 4 and 5, thus changing the total
number of pages. Minor wording changes.
Other changes to the TOX-013 report include: The cover page was updated to reflect the total number of pages and the title was changed to say "Amended Final Report." The Table of Contents was updated to reflect the added amendment. The additional audit date of the Amended Analytical Laboratory Report TOXO13 was added to the Quality Assurance Statement.
3M Environmental Laboratory
3M Environmental Laboratory
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3M Medical Department Study: T-6316.5
3M Medical Department Study: T-6316.5
Analytical Study: FACT-TOX-013 LRN-U2095
Analytical Study: FACT TOX-013 LRN-U2095
Approved by:
Kristen H. Hansen, Ph.D., Principal Analytical Investigator OS/!!O 10 1 Date
6
I
Marvin T. Case, D.V.M., Ph.D., Study Director
Date
Bill Reagan, Ph.D., Environmental Laboratory Manager
OJ+,/O,
Date
3M Environmental Laboratory
3M Environmental Laboratory
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