Document zQbRD7mdE0gNpkrdRG0nGwkJz
M & A 6 - 37*7
INTERIM REPORT #23 Analysis of Sediment Samples
STUDY TITLE Analysis o f Perfluorooctanoic Acid (PFOA) in Water, Soil, Sediment, Fish, Clams, Vegetation, Small Mammal Liver and Small Mammal Serum Using LC/MS/MS for the
3M Decatur Monitoring Program
DATA REQUIREMENTS EPA TSCA Good Laboratory Practice Standards 40 CFR 792
STUDY DIRECTOR Jaisimha Kesari P.E., DEE
Weston Solutions, Inc. 1400 Weston Way
West Chester, PA 19380 Phone:610-701-3761
INTERIM REPORT COMPLETION DATE May 2,2006
PERFORMING LABORATORY Exygen Research
3058 Research Drive State College, PA 16801
Phone: 814-272-1039
STUDY SPONSOR 3M Company
3M Building 0236-01-B-10 St. Paul, MN 55144 Phone: 651-733-6374
C:
CO O to
PROJECT . Protocol Number: P0000760
Exygen Study Number P0000760
Total Pages: 110
BEST COPY AVAILABLE
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GOOD LABORATORY PRACTICE COMPLIANCE STATEMENT
Exygen Study Number P0000760, entitled "Analysis o f Perfluorooctanoic Acid (PFOA) in Water, Soil, Sediment, Fish, Clams, Vegetation, Small Mammal Liver and Small Mammal Serum Using LC/MS/MS for the 3M Decatur Monitoring Program," conducted for 3M Company, is being performed in compliance with EPA TSCA Good Laboratory Practice Standards 40 CFR 792 by Exygen Research, with one exception. The laboratory control and control spikes for the direct injection and alternate SPE methods and the spiking procedures for the surrogate were not recorded promptly at the time of extraction.
John Flaherty ' Principnal Investigator
Exygen Research
Jaisimha Kesari P.E., DEE Study Director Weston Solutions, Inc.
Date
Exygen Research
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Jfci Exygen Study No,: F0000760
QUALITY ASSURANCE STATEMENT
Exygen Research's Quality Assurance Unit reviewed Exygen Study Number P0000760, entitled, "Analysis of Perfluorooetanoic Acid (PFOA) in Water, Soil, Sediment, Fish, Clams, Vegetation, Small Mammal Liver and Small Mammal Serum Using LC/MS/MS for the 3M Decatur Monitoring Program". All reviewed phases1 were inspected for conduct according to Exygen Research's Standard Operating Procedures, the Study Protocol, and all applicable Good Laboratory Practice Standards. All findings were reported to the Exygen Principal Investigator and Management and to the Study Director.
Phase
. Final Raw Data Review and Interim Analytical Report Review
Date Insnected
5/2/06
Date Reported to Date Reported to
Principal
Exygen Date Reported to
Investiaator Management Studv Director
5/2/06
5/2/06
5/2/06
after Lead, Quality Assurance Unit
s /toe / , Date
lNote: All in-lab inspections will be documented in the QA statement for the final
analytical report at the conclusion of the study. This QA statement involves only the review of the interim report and associated raw data.
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CERTIFICATION OF AUTHENTICITY
This interim report, for Exygen Study Number P0000760, is a true and complete representation of the raw data. .
Submitted by:
Exygen Research 3058 Research Drive State College, PA 16801 (814) 272*1039
Principal Investigator, Exygen:
ilm f k lj/
; Flaherty Vice President Exygen Research
s A /fiDate
Exygen Research Facility Management:
{I L , , ,__
Richard y<Mzzini President Exygen Research
A) K tdurJ
Date
Study Director, Weston Solutions, Inc.
gM tA /i/
JaisimhaTvesari P.E., DEE Weston Solutions, Inc.
m
Date
Sponsor Representative, 3M Company:
%2k
Date
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....... ...................................------------------------H-5.
Interim Report #23 - Analysis of Sediment Samples
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STUDY IDENTIFICATION
Analysis of Perfluorooctanoic Acid (PFOA) in Water, Soil, Sediment, Fish, Clams, Vegetation, Small Mammal Liver and Small Mammal Seram Using LC/MS/MS for the
3M Decatur Monitoring Program
PROTOCOL NUMBER:
P0000760
EXYGEN STUDY NUMBER: P0000760
TYPE OF STUDY:
Residue
SAMPLE MATRIX:
Sediment
TEST SUBSTANCE:
Perfluorooctanoic acid (PFOA)
SPONSOR:
3M Company 3M Building 0236-01-B-I0 St. Paul, MN 55144
STUDY DIRECTOR:
Jaisimha Kesari P.E., DEE Weston Solutions, Inc. 1400 Weston Way West Chester, PA 19380
STUDY MONITOR:
Michael A. Santoro 3M Company 3M Building 0236-01-B-10 St. Paul, MN 55144
PERFORMING LABORATORY: Exygen Research 3058 Research Drive State College, PA 16801
ANALYTICAL PHASE TIMETABLE:
Study Initiation Date:
11/05/04
Interim Analytical Start Date:
04/27/06
Interim Analytical Termination Date: 04/30/06
Interim Report Completion Date: 05/02/06
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PROJECT PERSONNEL
The Study Director for this project is Jaisimha Kesari at Weston Solutions, Inc. The following personnel from Exygen Research were associated with various phases of this interim portion of the study:
Name John Flaherty Karen Risha Paul Connolly Christine Edwards Mark Ammerman Amy Sheehan Brittany Kravets
Scott Crain Frances Crespi Devon Ingram Christa Gallant
Title Vice President
Scientist Technical Lead-LC/MS
Technician Sample Custodian Associate Scientist
Technician Technician Technician Technician Technician
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TABLE OF CONTENTS
Page
TITLE PAGE.......................................................................................................................... 1 GOOD LABORATORY PRACTICE COMPLIANCE STATEMENT.............................. 2 QUALITY ASSURANCE STATEMENT............................................................................3 CERTIFICATION OF AUTHENTICITY............................................................................ 4
STUDY IDENTIFICATION.................................................................................................. 5
PROJECT PERSONNEL....................................................................................................... 6
TABLE OF CONTENTS....................................................................................................... 7
LIST OF TABLES..................................................................................................................8
LIST OF FIGURES........ ....................................................................................................... 9
LIST OF APPENDICES...................................................................................................... 10
1.0 SUMMARY......................................................................
11
2.0 OBJECTIVE.................................................................................................................. 11
3.0 INTRODUCTION........... ............................................................................................. 12
4.0 ANALYTICAL TEST SAMPLES................................................................................12
5.0 REFERENCE MATERIAL.......................................................................................... 12
6.0 DESCRIPTION OF ANALYTICAL METHOD......................................................... 13
6.1 Extraction Procedure For Sediment............................................................................13
6.2 Direct Inject Extraction Procedure For Sediment...................................................... 14
6.3 Additional SPE Extraction Procedure For Sediment................................................. 14
6.4 Percent Solids Procedure For Sediment.....................................................................14
6.5 Preparation of Standards and Fortification Solutions.............................
14
6.6 Chromatography......................................................................................................... 16
6.7 Instrument Sensitivity................................................................................................. 16
6.8 Description of LC/MS/MS Instrument and Operating Conditions........................... 16
6.9 Quantitation and Example Calculation................................................................ 17
7.0 EXPERIMENTAL DESIGN........................................................................................ 19
8.0 RESULTS......................
19
9.0 CONCLUSIONS........................................................................................................20
10.0 RETENTION OF DATA AND SAMPLES............ ................................................. 20
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LIST OF TABLES
Table L Summary of PFOA in Sediment Samples................
Page 22
Table n. Summary of PFOA in Direct Injection Sediment Samples.............................23
Table III. Summary of PFOA in SPE Extracted Sediment Samples...............................24
Table IV. Matrix Spike Recovery of PFOA in Sediment Samples................................. 25
Table V. Matrix Spike Recovery of PFOA in Direct Injection Sediment Samples.......26
Table VI, Matrix Spike Recovery of PFOA in SPE Extracted Sediment Samples......... 27
Table VE. Surrogate Spike Recovery of 13C PFOA in Sediment Samples..................... 28
Table VE3. Surrogate Spike Recovery o f 13C PFOA in Direct Injection Sediment Samples.......................... ...... ....... ................................................................. 29
Table IX. Surrogate Spike Recovery o f ,3C PFOA in SPE Extracted Sediment Samples................................................................... ............. ...........................30
Table X. Total Percent Solids in Sediment Samples................................ .....................31
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Figure 1.
LIST OF FIGURES
Page Typical Calibration Curve for PFOA in Methanol......................................... 33
Figure 2. Extracted Standards o f PFOA in Methanol, 25 ng/L and 50 ng/L, Respectively.... ................................... .............................................................. 34
Figure 3. PFOA in Reagent Blank, 0.4 ng/mL Fortified Reagent Spk A, and 4.0 ng/mL Fortified Reagent Spk B, Respectively................................... 35
Figure 4. Chromatogram Representing a Sediment Sample Analyzed for PFOA (Exygen ID: C0172892, Data Set: 042806D).................................................36
Figure 5. Typical Calibration Curve for l3C PFOA in Methanol................................... 37
Figure 6. Extracted Standards of 13C PFOA in Methanol, 25 ng/L and 50 ng/L, Respectively............ ......................... ............................................................... 38
Figure 7. ,3C PFOA in Reagent Blank, 0.4 ng/mL Fortified Reagent Spk A, and 4.0 ng/mL Fortified Reagent Spk B, Respectively................................... 39
Figure 8. Chromatogram Representing a Sediment Sample Analyzed for l3C PFOA (Exygen ID: C0172892, Data Set: 042806D)...............................40
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LIST OF APPENDICES
Appendix A Study Protocol F0OOO76O (Exygen Study No. P0000760) with Analytical Method V0001782: "Method o f Analysis for the Determination o f Perfluorooctanoic Acid (PFOA) in Sediment by LC/MS/MS", and Protocol Amendments.............................................41
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1.0 SUMMARY
Exygen Research extracted and analyzed sediment samples for the determination of perfluorooctanoic acid (PFOA) according to Exygen Method V0001782 (Appendix A).
The limit of quantitation for PFOA in sediment was 2.0 ng/g.
The standard sediment method (V0001782) was originally used to extract all of the samples. Use of this method yielded poor spiking recoveries for PFOA. Because o f this, a direct injection method (Section 6.2) was used, which also yielded poor recoveries. Finally, an alternative SPE column extraction (Section 6.3) was used to analyze for PFOA and ,3C PFOA.
Analytical results for the analysis o f PFOA in sediment samples extracted according to the method based on dry weight are summarized in Table I. Analytical results for the analysis o f PFOA in sediment samples by direct injection, based on dry weight, are summarized in Table II. Analytical results for the analysis of PFOA in sediment samples by alternative SPE extraction, based on dry weight, are summarized in Table III. The overall average percent recovery standard deviation for PFOA in sediment samples based on wet weight was 73 16%. Fortification recoveries for the analysis o f PFOA in sediment samples are summarized in Table IV. Fortification recoveries for the analysis o f PFOA in direct injection sediment samples are summarized in Table V. Fortification recoveries for the analysis o f PFOA in SPE extracted sediment samples are summarized in Table VI. The average percent recovery standard deviation for 13C PFOA in sediment samples based on wet weight was 97 27%. Fortification recoveries for l3C PFOA in sediment samples based on wet weight are summarized in Table VII. Fortification recoveries for 13C PFOA in direct injection sediment samples based on wet weight are summarized in Table VIII. Fortification recoveries for 13C PFOA in SPE extracted sediment samples based on wet weight are summarized in Table IX.
The total percent solids for sediment samples are detailed in Table X.
2.0 OBJECTIVE
The objective of the analytical part o f this study was to determine levels of perfluorooctanoic acid (PFOA) in sediment according to Protocol P0000760 (Appendix A).
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3.0 INTRODUCTION
This report details the results o f the analysis for the determination o f PFOA in sediment using the analytical methods entitled, "V0001782: Method o f Analysis for the Determination o f Perfluorooctanoic Acid (PFOA) in Sediment by LC/MS/MS."
The study was initiated on November 05,2004, when the study director signed protocol number P0000760. The analytical start date for this interim report was April 27, 2006 and the analytical termination date for this interim report was April 30,2006.
4.0 ANALYTICAL TEST SAMPLES
Three sediment samples (Exygen ID: C0172892-C0172894) were received on wet ice on April 22, 2006 from Tim Frinak at Weston Solutions, Inc. The samples were logged in by Exygen personnel and placed in refrigerated storage.
Sample login and chain of custody information is located in the raw data package associated with this interim report. Storage records will be kept at Exygen Research.
5.0 REFERENCE MATERIAL
The analytical standard, PFOA, was purchased from Oakwood Products, Inc. and was received at Exygen on March 17, 2005. The surrogate spiking standard, 13C labeled perfluorooctanoic acid (13C PFOA SP0004184), was received at Exygen on April 15, 2004 from the 3M Company.
The available information for the reference materials is listed below. PFOA was stored ambient and I3C PFOA was stored frozen.
Compound PFOA
!3CPFOA
Exveen Inventory No. SP0005444 SP0004184
Lot# 203 3507-195
Purity (%) Expiration Date 99 03/31/07 97 03/29/09
The molecular structure o f PFOA is given below:
PFOA Chemical Name: Perfluorooctanoic acid Molecular Weight: 414 Transitions Monitored: 413 ->369 (for quantification) and
413 - 219 (for confirmation) Structure:
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,3C PFOA Chemical Name: 1,2-13C perfluorooctanoic acid Molecular Weight: 416 Transition Monitored: 415 --> 370 Structure:
6.0 DESCRIPTION OF ANALYTICAL METHOD
The analytical method "V0001782: Method of Analysis for the Determination of Perfluorooctanoic Acid (PFOA) in Sediment by LC/MS/MS" was used for the sediment samples in this study.
6.1 Extraction Procedure For Sediment
Before the samples were weighed for the extraction, they were mixed thoroughly by vigorously shaking the container. A 5 gram portion o f sediment was weighed into a fifty milliliter centrifuge tube for the extraction. After fortification o f appropriate samples, 35 mL o f 1% acetic acid in water was added to the samples. The samples were vortexed and allowed to shake on a wrist action shaker for -6 0 minutes. The samples were centrifuged for ~20 minutes at -3000 rpm. The supernatant was then loaded onto a Ci8 SPE cartridge conditioned with 10 mL of methanol and 20 mL of water. The eluate was discarded. Twenty milliliters of methanol was added to the sediment samples left in the centrifuge tube. The samples were vortexed and allowed to shake on a wrist action shaker for another 30 minutes. The samples were centrifuged again for -20 minutes at -3000 rpm. The supernatant was then loaded onto the same Ci8 SPE cartridge. The eluate was collected into a 500 mL Nalgene Bottle. The column was washed with 4 mL of methanol. The wash was collected in the same bottle as the eluate. Approximately two
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hundred milliliters o f water was added to the bottles. The samples were mixed by shaking and loaded onto another Ci8 SPE cartridge conditioned with 10 mL of methanol and 20 mL of water. The eluate was discarded. Approximately five milliliters of methanol was added to the cartridge. Five milliliters o f eluate was collected into a graduated 15 mL polypropylene centrifuge tube. Each sample was analyzed by LC/MS/MS electrospray.
6.2 Direct Inject Extraction Procedure For Sediment
Before the samples were weighed for the extraction, they were mixed thoroughly by vigorously shaking the container. A one-gram portion of sediment was weighed into a 15-milliliter centrifuge tube for the extraction. Ten milliliters o f 1% acetic acid in methanol was added to each sample. The samples were then shaken by hand, vortexed, and sonicated for thirty minutes. The samples were then centrifuged for -10 minutes at -3000 rpm. Each sample was analyzed by LC/MS/MS electrospray,
6 3 Additional SPE Extraction Procedure For Sediment
The samples that were prepared in 1% acetic acid for the direct injection method were used for this extraction. Five milliliters o f each sample was aliquoted into a 50-mL polypropylene centrifuge tube and the volume was taken to 40 mL with water. The samples were then centrifuged for -1 0 minutes at -3000 rpm. The supernatant was then loaded onto a Cir SPE cartridge conditioned with 10 mL of methanol and 5 mL of water. The eluate was discarded. Approximately five milliliters of methanol was added to the cartridge. Five milliliters o f eluate was collected into a graduated 15 mL polypropylene centrifuge tube. Each sample was analyzed by LC/MS/MS electrospray.
6.4 Percent Solids Procedure For Sediment
Percent solids were determined using the procedure indicated in Exygen method V0000427. Approximately 20 grams of sample was weighed into a pan. The weight of the sample plus the pan was recorded. The samples were then dried in an oven overnight at 104 2 C. Then the samples were transferred to a dessicator and allowed to cool for -15 minutes. Each sample was then weighed again, including the weight o f the pan. The percent solid for each sample was then calculated. See Table X for percent solids results.
6.5 Preparation of Standards and Fortification Solations
A mixed stock standard solution of PFOA and 13C PFOA was prepared at a concentration of 1000 jig/mL by dissolving 100 mg of each of the standards (corrected for purity and
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salt content) in 100 mL o f methanol. From this solution, the following fortification standards were prepared:
Cone, of
Fort
Stock or Fort. Volume
Solution
(mL)
(pg/mL)1
1000
10
100 10
10 10
1.0 10
0.1 10
1o f PFOA and 13C PFOA
Final Volume
(mL)
100 100 100 100 100
Final Cone, of Fortification Std.
(pg/mL)
100 10 1.0 0.1 0.01
A stock solution o f only 13C PFOA was also prepared at a concentration of 100 pg/mL by dissolving 10 mg the standard (corrected for purity and salt content) in 100 mL of methanol. From this solution, the following fortification standards were prepared:
Cone, o f Stock or Fort.
Solution (pg/mL)1
100 10 1.0 1o f 13C PFOA
Fort Volume
(mL)
10 10 10
Final Volume
(mL)
100 100 100
Final Cone, of Fortification Std.
(pg/mL)
10 1.0 0.1
A set of non-extracted calibration standards containing PFOA and l3C PFOA was prepared in methanol, as specified in Exygen method V0001782. The following
concentrations were prepared
Cone, of Fort Fort
or Calibration Volume
Solution
(mL)
(ng/mL)1
100 1.0
100 0.5
100 0.2
10 1.0
5.0 1.0
2.0 1.0
1o f PFOA and 13C PFOA
Final Volume
(mL)
10 10 10 10 10 10
Final Cone, o f Calibration Std.
(ng/mL)
10 5.0 2.0 1.0 0.5 0.2
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The standards at final concentrations of 10, 5.0,2.0,1.0, 0.5 and 0.2 ng/mL were used for calibration. Extracted calibration standards were prepared following method V0001780. The stock standard solution and all fortification and calibration standard solutions were stored in a refrigerator (4 2C) when not in use. Documentation of standard preparation is located in the raw data package associated with this interim report.
6.6 Chromatography
Quantification of PFOA was accomplished by LC/MS/MS electrospray. The retention time o f PFOA was -11.1 min. Peaks above the LOD were not detected in any of the reagent blank samples corresponding to the analyte retention time.
6.7 Instrument Sensitivity
The smallest standard amount injected during the chromatographic run had a concentration of 0.2 ng/mL of PFOA.
6.8 Description of LC/MS/MS Instrument and Operating Conditions Instrument: API 4000 Biomolecular Mass Analyzer Interface: Turbo Ion Spray Liquid Introduction Interface Computer: DELL OptiPlex GX400 Software: Windows NT, Analyst 1.4.1
HPLC:
Hewlett Packard (HP) Series 1100 HP Quat Pump HP Vacuum Degasser HP Autosampler HP Column Oven
HPLC Column: Thermo Fluophase RP, 50 rara x 2.1 mm Column Temp.: -30 C Injection Voi.: 15 pL Mobile Phase (A): 2 mM Ammonium Acetate in water Mobile Phase (B): Methanol
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Time fmin) 0.0 1.0 8.0 10.0 11.0 18.0
%A 65 65 25 25 65 65
%B 35 35 75 75 35 35
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Total run time: ~18 min Flow Rate: 0.3 mL/min
Ions monitored:
Analvte
PFOA PFOA Confirm Ion
13C PFOA
Mode
negative negative negative
Transition Monitored 413 -> 369 413 -> 219 415->370
Approximate Retention Time
(min) ~11.1 min.
-11.1 min. -11.1 min.
6.9 Quantitation and Example Calculation
PFOA concentrations are quantitated in nanpgram o f PFOA per milliliter o f extract and then converted to nanogram per gram. The PFOA concentrations were quantitated in nanogram o f PFOA per liter for Set #3 (Set 042806D). Fifteen microliters o f sample or calibration standard were injected into the LC/MS/MS. The peak area was measured and the standard curve was generated (using 1/x fit weighted linear regression) by Analyst software using seven concentrations of standards. The concentration was determined from the equations below.
Please note that the equations in this section are presented in a different order than the equations in the method (V0001782), but this has no effect on the final calculations.
Equation 1 calculated the amount of analyte found (in ng/L, based on peak area) using the standard curve (linear regression parameters) generated by the Analyst software program.
Equation 1:
Analyte found (ng/L) = fPeak area - intercept! x DF Slope
Where: DF = Dilution Factor, factor by which the final volume was diluted, if necessary.
For samples fortified with known amounts of PFOA and 13C PFOA prior to extraction, Equation 2 was used to convert the amount o f PFOA found in ng/L to ng/g (ppb).
Equation 2:
PFOA found (ppb) fPFOA found (ng/L) x SPE volume extracted!
[sample aliquot volume x (sample weight / direct inject sample volume)]
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Equation 3 was used to calculate the percent recovery.
Equation 3:
Recovery (%) =
.
(analyte found (ng/g. wet weight) - analvte in control (ng/g, wet weight)') xl00% amount added (ng/g, wet weight)
Note: For the PFOA recovery calculation, the "control" is the unspiked aliquot of the primary field sample.
Equation 4 was then used to calculate the amount o f PFOA found in ppb based on dry weight.
Equation 4:
PFOA found (ppb) dry weight = PFOA found (ppb) x [100% / total solids(%)]
An example of a calculation using an actual sample follows:
Sediment sample Exygen ID C0172892 Spk D (Set: 042806D), fortified at 4 ng/mL
with PFOA where: peak area
= 236588
intercept
4630
slope dilution factor
= 420 = 100
ng/g PFOA added (fort level) amt in corresponding sample (ng/g) SPE volume extracted (L)
= =s =
4000 586 0.04
sample aliquot volume (mL)
= 5
sample weight (g)
=" 1
direct inject sample volume (mL)
= 10
total solids (%)
= 66.54
From equation 1: Analyte found (ng/L)
From equation 3: PFOA found (ppb)
= r236588 - 46301 x 100 420
~ 55200 ng/L
~ (55200 ne/L x 0.04 L) [5 mL x (1 g / 10 mL)]
= 4420 ppb
From equation 3: % Recovery
= (4420 ng/g - 586 ng/g) x 100% 4000 ng/g
= 96%
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From equation 4: PFOA found (ppb) dry weight - 4416 ppb x (100% / 66.54%)
= 6640 ppb
NOTE: This value may be slightly different than that o f the raw data due to rounding.
7.0 EXPERIMENTAL DESIGN
13C PFOA was used as a surrogate for all the samples. 13C PFOA was added to the sediment samples in the laboratory after the samples were weighed for extraction. For sediment samples designated as laboratory matrix spikes, PFOA was also added at a known concentration to the samples in the laboratory after the samples were weighed for extraction.
The sediment samples were extracted in one set. The set included one reagent blank and two reagent blanks fortified at known concentrations. The set contained three sediment samples. For each sample, two laboratory matrix spikes and a duplicate were extracted.
8.0 RESULTS
Analytical results for the analysis o f PFOA in sediment samples based on dry weight are summarized in Table I. Analytical results for the analysis of PFOA in sediment samples by direct injection, based on dry weight, are summarized in Table II. Analytical results for the analysis o f PFOA in sediment samples by alternative SPE extraction, based on dry weight, are summarized in Table III. The overall average percent recovery standard deviation for PFOA in sediment samples based on w et weight was 73 16%. Fortification recoveries for the analysis of PFOA in sediment samples are summarized in Table IV. Fortification recoveries for the analysis o f PFOA in direct injection sediment samptes are summarized in Table V. Fortification recoveries for the analysis of PFOA in SPE extracted sediment samples are summarized in Table VI. The average percent recovery standard deviation for C PFOA m sediment samples based on wet weight was 97 27%. Fortification recoveries for 13C PFOA in sediment samples based on wet weight are summarized in Table VII. Fortification recoveries for 13C PFOA in direct injection sediment samples based on wet weight are summarized in Table VIII. Fortification recoveries for 13C PFOA in SPE extracted sediment samples based on wet weight are summarized in Table IX,
The total percent solids for sediment samples are detailed in Table X.
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9.0 CONCLUSIONS
The sediment samples were successfully extracted and analyzed for PFOA using an alternative SPE method, which yielded acceptable QC data.
10.0 RETENTION OF DATA AND SAMPLES
All original paper data generated by Exygen Research that pertains to this interim report will be shipped to the study director. This does not include facility-specific raw data such as instrument or temperature logs. Exact copies of all raw data, as well as a signed copy of the interim analytical report and all original facility-specific raw data, will be retained in the Exygen Research archives for the period of time specified in EPA TSCA Good Laboratory Practice Standards 40 CFR 792.
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TABLES
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Table I. Summary of PFOA in Sediment Samples
Exygen ID
C0172892 C0172892 Rap
C0172883 C0172893 Rep
C0172894 C0172894 Rep
C lient Sam ple ID
OAL-SO-BPPC1-0-QQOO D A L-S D -B P P 01-0 -0 0 0 0 *
DAL-S D-BPP02-0-0000 D A L -S D -B P P 02 -0-0 000 *
D A L -S D -B P P 03-<H )000 D A L -S D -B P P 03 -0-0 000 *
A n alyte Found (ppb, n g/g) Dry W eight C 8 Acid PFOA
P erfluorooctanoic Acid
NR NR
NR NR
NR NR
Assessed A c cu ra cy
< * *
NR NR
NR NR
NR NR
` Laboratory Duplicate NR = Not reported due to quality control result failures. See Table II for re-anatysis results.
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Table II. Summary of PFOA in Direct Injection Sediment Samples
Exvasn ID
C0172892 C0172892 Rep
C0172893 C0172893 Rep
C0172894 C0172894 Rep
C lient Sam ple ID
D A L -S D -B P P 0 1 -0 -0 0 0 0 D A L -S D -B P P 01-0 -0 0 0 0 *
D A L -S D -B P P 0 2 -0 -0 0 0 0 D A L -S D -B P P 0 2 -0 -0 0 0 0 *
D A L -S D -B P P 0 3 -0 -0 0 0 0 DAL-SD-B PP03-0-0000*
A nalyte Found (ppb, ng/g) D ry W eight C8 A cid PFO A
P erfluorooctanolc A cid
NR NR
NR NR
NR NR
Assessed A cc u ra c y
[+ /-% )
NR NR
NR NR
NR NR
"Laboratory Duplicate NR * Not reported due to quality control result failures. See Table III for re-analysis results.
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Table III. Summary of PFOA in SPE Extracted Sediment Samples
E x v a a n ID
C0172892 C0172892 Rep
C01728S3 C0172893 Rep
C0172894 00172694 Rep
Laboratory Duplicate
C lien t S em ple ID
A n a lyte Found {p p b , n g /g ) D ry W eig h t C 8 A cid PFO A
P erflu o ro o c tan o lc A d d
D A L-SD -B PP01-0-0000 QAL-SD-BPPOi-O-OOOO*
D A L-SD -B PP02-0-0000 D A L-SD -B P P 02-0-0000'
881 945
927 823
D A L-SD -B PP03-0-0000 D A L-SD -B PP03-0-0000*
2390 2380
A tte s te d A ccuracy
30 30
30 30
30 30
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Table IV. Matrix Spike Recovery o f PFOA in Sediment Samples
Sample Description
DAL-SCFBPP01-0-0000 (C0172BM Spk D,400 ppb Spike)
DAL-SD-BPP01-0-0000 (C0172892 Spk E, 4000 ppb Spike)
DAL-SD-BPP02-0-0000 (C01S*S Spk G,400 ppb Spike)
DAL-SD-BPP02-0-0000 (C0172M3 Spk H, 4000 ppb Spike)
DAL-SD-BPP03-CM)000 (C0172S04spk j , 400 ppb Spike)
D A L-SD -B PP03-0-0000 [C0172804 Spk K, 4000 ppb Spike)
Amount Spiked fng/a)
Amt Found in Sample <ng/g) wet weight
C8 Add PFOA
Amount Recovered fno/p) wet weight
400 4000
NR NR
NR NR
40 4000
NR NR
NR NR
400 4000
NR NR
NR NR
Recovery <%>
NR NR
NR NR
NR NR
Average: Standard Daviation:
NR NR
'Sample residua exceeds Ihe spiking level significantly <3* spiking level); therefore, an accurate recovery value cannot be calculated.
NR * Not reported due to quality control result failures. See Tatte V for re-analysis results. Note: Since this summary table shown rounded result*, recovery values may vary slightly from the values In the raw data.
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Table V. Matrix Spike Recovery of PFOA in Direct Injection Sediment Samples
Sara pie Descrtptlon
DAL-SD-BPP01-0-0000 (com an spk d, too ppb spike)
DAL-SD-BPP01 -0-0000 (00172192 8pk E,40000 ppb Spike)
DAL-SD-BPP02-0-0000 (W17SS9S Spk G, 4000 ppb Spike)
DAL-SD-B PP02-0-0000 (C0172SM Spk H.40000 ppb Spike)
DAL-SD-BPP03-0-0000 (C0172BP4spk J, 4000 ppbSpike)
D A L-SD -B PP03-0-0000 (C0172S94 Spk K, 40000 ppb 8 pite)
Amount Spiked -W
4000 40000
4000 40000
4000 40000
Amt Found in Sample (ng/g) wet weight
C8 Arid PFOA
Amount Recovered (ng/g) wet weight
NR NR NR NR
NR NR NR NR
NR NR , NR NR
Recovery (% )
NR NR
NR NR
NR NR
Average: Standard Deviation:
NR NR
` Sample residue exceeds the spiking level significantly (3x spiking level); therefore, an accurate recovery value cannot be calculated.
NR Not reported due to quality control result failures. See Table VI for re-analysis results. Note: SIrice th Is summary table shows rounded results, recovery values may vary slightly from the values In the raw data.
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Table VI. Matrix Spike Recovery of PFOA in SPE Extracted Sediment Samples
Sample Description
DAL-SD-BPP01-0-0000 (C0172SS2 Spk D,4000 nfl/g Spike)
DAL-SD-BPP01-0-0000 (COI7WB2Spk E, 40000 n M Spike)
DAL-SD-BFP02-0-0000 <CW?2*S Spk e , 4000 ng/g Spike)
DAL-SD-BPP02-0-0000 (C0172003 Spk H.40000 np4oSpike)
DAL-SD-BPP03-0-0000 |C0172094 Spk J, 4000 ne'0 Spike)
DAL-SD-BPP03-0-0000 (C0172034 Spk K. 40000 ngfg Spike)
Amount Spiked (nate)
4000 40000
4000 40000
4000 40000
Amt Found in Sample (ng/g) wet weigh
585 586
504 504
1060 1060
CB Acid PFQA Amount Recovered (no/o) wet weight
4420 25600
3860 25100
4140 23200
Average: Standard Deviation:
Reoovery {%)
96 83
84 61
77 55
73 16
Note: Since this summary table shows rounded results, recovery values may vary slightly from the values In the raw data.
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Table VII. Surrogate Spike Recovery of 13C PFOA in Sediment Samples
Exygen ID
Sem ple Description
C0172892 C 0172892 Rep C0172892SpkC C0172892 Spk D C0172892 Spk E
C0172893 C0172893 Rep C 0172893 Spk F C O t72893 Spk G CD172893 Spk H
CO172894 C0172894 Rep C 0172894 Spk 1 C 0172894 Spk J C0172894 Spk K
D A L -S D -B P P 0 1 -0 -0 0 0 0 D A L-SD -B PP01-0-0000 D A L -S D -B P P 0 1 -0 -0 0 0 0 DAL-SD-BPP01-0-DQOO D A L -S D -B P P 0 1 -0 -0 0 0 0
D A L-SD -B PP02-0-0000 D A L-S D -B PP02-0-0000 D A L-SD -B PP02-0-0000 D A L-SD -B PP02-0-0000 DAL-S D -B PP 02-0-0000
D A L-SD -B PP03-0-0000 DAL-S D -B PP 03-0-0000 DAL-S D -B PP 03-0-0000 DAL-S D -B PP 03-0-0000 D A L-SD -B PP03-0-0000
Amount Spiked (n g /p )
4 4 4 400 4000
4 4 4 40,0' 4000
4 4 4 400 4000
,!>c - p f o a A m ount R e c o v e red W e t W eight
(ng/g>
NR NR NR NR NR
NR NR NR ' NR NR
NR NR NR NR NR
Recovery (% )
NR NR NR NR NR
NR NR NR NR NR
NR NR NR NR NR
Average: Standard Deviation:
NR - Not reported due to quality control result failures. See Table VIII for re-analysis results. Note: Since this summary table shows rounded results, recovery values may vary slightly from the values in Ihe raw data.
NR NR
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Table VIII. Surrogate Spike Recovery of 13C PFOA in Direct Injection Sediment Samples
Sam ple Description .
C0172892 C 0172892 Rep C O I72892 Spk C C0172892 Spk D C0172892 SpkE
00172893 C0172893 Rep C0172893 Spk F COI72893 Spk G C O I72893 Spk H
C0172894 C 0172894 Rep C 0172894 Spk I C0172894 Spk J C0172894 Spk K
D A L-S D -B PP01-O-OQOO D A L-SD -B PP01-0-0000 DAL-SD-BPP01 -0-0000 DAL-SD-BPP01 -0-0000 D A L-SD -B PP01-0-0000
D A L-S D -B PP02-0-0000 D A L-S D -B P P 02-0-0000 D A L-S D -B PP02-0-0000 D A L-S D -B PP02-0-0000 D A L-S D -B PP02-0-0000
D A L-S D -B PP03-0-0000 D A L-S D -B PP03-0-0000 D A L-S D -B PP03-0-0000 D A L-S D -B PP03-0-0000 D A L-SD -B PP03-0-0000
Amount Spiked
(ng/g)
40 40 40 4000 40000
40 40 40 4000 40000
40 40 40 4000 40000
1sC -PFO A A m ount R eco vered W e t W eight
_____ _________
NR NR NR NR NR
NR NR NR NR NR
NR NR . NR NR NR
R eco very (% )
NR NR NR NR NR
NR NR NR NR NR
NR NR NR ' NR NR
Average: Standard Deviation:
NR = Not reported due to quality control result failures. See Table IX for re-analys)s results. Note: Slrtce this summary table shows rounded results, recovery values may vary slightly from the values In the raw data.
NR NR
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Table IX. Surrogate Spike Recovery of 13C PFOA in SPE Extracted Sediment Samples
Exygen ID
COI72892 C0172892 Rep C0172892 SpkD C0172892 Spk E
C0172893 C0172893 Rep C0172893 Spk C0172893 Spk H
C0172894 C0172894 Rep C0172894 Spk J C0172894 Spk K
Sample Description
D At-S D-BPP01-O-ODOO DAL-SD-BPPOt-0-0000 OAL-SD-BPP01-0-0000 DAL-SD-BPP01-0-0000
DAL-SD-BPPQ2-0-0000 DAL-SD-8PP02-0-0000 DAL-SD-BPP02-0-0000 DAL-SD-BPP02-tK)000
OAL-SD-BPP03*<M)000 DAL-SD-BPP03-0-0000 DAL-SD-BPP03-0-0000 DAL-SD-BPP03-0-0000
Amount Spiked (ng/g)
40 40 4000 40000
40 40 4000 40000
40 40 4000 40000
13c -p f o a Amount Recovered Wet Weight (note)
52.0 51.0 3750 26800
47.8 51.8 3500 25200
45.2 40.3 3050 22100
Note: Sines this summary table shews rounded results, recovery values may vary slighUy from the values In Ihe raw date.
Average Standard Deviation:
Recovery (*)
130 128 94 65
120 129 88 63
113 101 77 55
97 27
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Table X. Total Percent Solids in Sediment Samples
Exygen ID
CO172892 C0172893 CO172894
Sample Description
DL-SD-BPP01-0-0000 DAL-SD-BPP02-0-0000 DAL-SD-BPP03-0-0000
Total Solids (%) 66.54 54.37 44.46
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FIGURES
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Figure 1. Typical Calibration Curve for PFOA in Methanol
042 9 0 0 0 5 SPE.rdfc. (PFOA) " U n jr R giin p > * wnigM ing) y - 420 *-* 4.03**003 O'- o a s e s )
Area, counts
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Figure 2. Extracted Standards of PFOA in Methanol, 25 ng/L and 50 ng/L, Respectively
I X CM ZSM -f-PFOA (5taArd)4W.miS. mm* -tampt* 2 o f 4 t from M 2 M c n irfir A n*: fJZM coart* HUgMl 1.W*M3tpo KT; rt.tm h t 11.01
11D6
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Figure 3. PFOA in Reagent Blank, 0.4 ng/mL Fortified Reagent Spk A, and 4.0 ng/mL Fortified Reagent Spk B, Respectively
I R MtnfaMtat cCtfoormtrtaiiS-)PFOA ( U n t m n ^ ^ n K K M m -tampli i fFt from HUXMfff
EcU0>> I A m : 30296 unir Height 2 5 7 rK)03 op* RT: 11.0 min
11.00
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Figure 4. Chromatogram Representing a Sediment Sample Analyzed for PFOA (Exygen ID: C0172892, Data Set: 042806D)
CM 722 -PFOA (itoJl*o\rr)-tllteiii.*amu-aampt* 19ef4*fromMZMEOMflr Ana:3S421ccuata HeJffkt: ZTtnOOScps R7t 11.0min
1103
Intensity, cp s
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Figure 5. Typical Calibration Curve for 13C PFOA in Methanol
04200608*4. 8PE.rib?13CPFOAfc"Unaar"R*0ruil6ftf l wtlghting);y40Bx+D.D010(f*OAOGO)
Area, counts
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Figure 6. Extracted Standards of 13C PFOA in Methanol, 25 ng/L and 50 ng/L, Respectively
I XCMMM+f 13CPFOA & sm f* * * )4 1 tW 7 ft*mu
A n * : 1td01 c * * * t* H tigA ti ftffe+MQcp R 7 :11.$ m /*
Z o f4 ttr o 1M2$MXw!Tr
11.02
11.00
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Figure 7. 13C PFOA in Reagent Blank, 0.4 ng/mL Fortified Reagent Spk A, and 4.0 ng/mL Fortified Reagent Spk B, Respectively
I Hongont Control - 13CPFOA fimtnown) m .0/m .9nmn -*amph t o f4tfrom UQWKOMtff t* n t nottonne')
(A 10.0-1
Tima, min
I Raagarrl Spk A - 130 PFOA (00)415.0/370.0 im u u m pla 10 of 40 from 0428000 w tlf Ar*a:2729Q oounte H*ight2.C2+C3 cps RT: H U min
11-01
Tima, min
I Raigafti Spk B - 13C PFOA(00)415.0/370.0 jm u * u m p l 11 of 48 from 042806&-*ff A ra i: 270001 oounfc Haight 22a+004 opr RT: 11.1 min
o> a. 2j0a4
11.07
1.0*4
i
7 Tima, min
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Figure 8. Chromatogram Representing a Sediment Sample Analyzed for 13C PFOA (Exygen ID: C0172892, Data Set: 042806D)
C*72*2 ttC P raA (tMt*OW*)415.V3Tt.e m u MKtfih 21o f Arm: 3149S7 coi/tts HUgJit; 2.9U*094tpt KT; 11.1milt
from 042MtDMfT
11i>7
Intensity, cps
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APPENDIX A
Study Protocol P0000760
(Exygen Study No. P0000760) with Analytical Method and
Protocol Amendments
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ExygesProtocolNumber:P0000760
STUDY PROTOCOL
Study Title: Analysis of Perfluorooctanoic Acid (PFOA) in Water, Soil, Sediment, Fish, Clams, Vegetation, Small Mammal Liver and Small Mammal Serum Using LC/MS/MS for the 3M Decatur
Monitoring Program
Exygen Protocol Number: P0OO0760
Performing Laboratory: Exygen Research 3058 Research Drive State College, PA 16801 Phone: (814)272-1039
Sponsor Representative: Michael A. Santoro Director o f Regulatory A ffairs 3M Building 0236-01-B-10 St. Paul, MN 55144 Phone:(651)733-6374
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DISTRIBUTION:
1) Jaisimha K m i, Study Director, Weston Solutions 2) John M . Flaherty, Principal Investigator, Exygen Research 3) Michael A. Santoro, Sponsor Representative, 3M Company 4) Exygen Research Quality Assurance Unit
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Exygen Protocol Numbei: P000076Q
PROTOCOLAPPROVAL
Study Tide: Analysis o f Perfluorooctanoic Acid (PFOA) in Water, Soil, Sediment, Fish. Clams, Vegetation, Small Mammal Livers and Small Mammal Serum Using LCAiS/MS for the 3M Decatur Monitoring Program
Exygen Protocol Number: P0000760
APPROVALS
Jaisimwi Kcsari, Study Director Weston Solutions
Michael A. Si 3M Company
Date
a? -a x 'l
D ata
QualityAssurance Unit
P u f s o fts
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Exygen Protocol NumbT: P00CQ7W
TABLE OF CONTENTS
TITLE PAGE.................... ...... ...... ... ........................... DISTRIBUTION........... ......... ...... ..... ............ ............... PROTOCOL APPROVAL.......... .................................... . . ...................... 3 TABLE OF CONTENTS.................................. ..... ...................................... . ... ......... ........ 4 INTRODUCTION........................ ................ .................... .................................... ........................5 TEST MATERIAL.......... ................................. ................ .................... ...5 SURROGATE FIELD SPIKE COMPOUND........................... ....... ...I................. ...5 OBJECTIVE................................. ...................... ............. ......... ........... ...6 TESTING FACILITY..... ................................ ................ . ........ ............ ...6 STUDY DIRECTOR........ ................................... _............. SPONSOR REPRESENTATIVE................. ............................. PRINCIPAL INVESTIGATOR.... ............... ............................ PROPOSED EXPERIMENTAL START AND TERMINATION DATES........ ......................7 IDENTIFICATION AND JUSTIFICATION OF THE TEST SYSTEM....... ... ..................... 7 ^ SAMPLE PROCUREMENT, RECEIPT AND RETENTION...'......................
SAMPLE IDENTIFICATION....... ..............................................................................
.ANALYTICAL PROCEDURE SUMMARY.... ........................................................
VERIFICATION OF ANALYTICAL PROCEDURE.................................................
. .METHOD FOR CONTROL OF BIAS......... ..... .................................. !................. STATISTICAL METHODS....................... .................................... . GLP STATEMENT................... .............. ........................ REPORT....... ................... ...................... ................... SAFETY AND HEALTH.... ...................... ...................... ... _;.................. 12 AMENDMENTS TO PROTOCOL.____ ________ _____ .._ :... ............ .....13 DATA RECORD KEEPING.... ....... .. .................................. ............. ... .... 13 QUALITY ASSURANCE................. ......... .................. ...... .......................................14
RETENTION OF DATA AND ARCHIVING......... ........................................ ....................... ............ ...................... ......14
APPENDIXLANALYTICALMETHODS....... _ ............... .................................... ... 5......... .........................*.....................
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INTRODUCTION
The purpose of this study is to perform analysts for perfluorooctanoic acid (PFOA) in water, soil, sediment, fish, clams, vegetation, small mammal livers and small mammal serum using LC/MS/MS for the 3M Decatur Monitoring Program.
The study w ill be audited for compliance with EPA TSCA Good Laboratory Practice Standards 40 CFR 792 by the Quality Assurance Unit of Exygen Research.
TEST MATERIAL
The test material is perfluorooctanoic acid (PFOA) end was purchased from Sigms-Aldrich.
PFOA Chemical Name: Perfluorooctanoic add Molecular Weight: 414 Lot Number 23116HB
Purity: 97.64% Transitions Monitored: 413 --> 369 (for quantification) and
413 ->-219 (for confirmation) Structure:
F, F F
'OH
SURROGATE FIELDSPIKE COMPOUND
The surrogate field spiking compound is 1>C labeled perfluorooctanoic acid (1}C PFOA) andwas purchasedby 3M from Peririn-Ehner Life and Analytical
Sciences.
UC PFOA Chemical Name: 1,2-130 perfluorooctanoic add Molecular Weight: 416 Lot Number: 3507-195 Purity. 97% Transition Monitored: 4 1 5 - -3 7 0
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OBJECTIVE
The purpose o f thi* study i t to perform analysis for perfluorooctanoic acid (PFOA) in water, soil, sediment, fish, clams, vegetation, small mammal livers and small mammal scrum for the 3M Decatur Monitoring Program using the current versions o fthe following Exygen analytical methods:
VO0O178O: "Method o f Analysis for the Determination of Perfluorooctanoic Acid (PFOA) in Water by LC/MS/MS"
V 0001781: "Method o f Analysis for the Determination o f Perfluorooctanoic Acid (PFOA) to Soil by LC/MS/MS"
V0001782: 'Method o f Analysis Sot the Determination o f Perfluorooctanoic Acid (PFOA) in Sedimentby LC/MS/MS"
V 0001783: "Method o f Analysis for the Determination o f Perfluorooctanoic Acid (PFOA) in Fish and Clams by LC/MS/MS"
V00017S4: " Method o f Analysis for the Determination o f Perfluorooctanoic Acid (PFOA) in Vegetation by LC/MS/MS"
V 0001785: "Method o f Analysis for the Determination o f Perfluorooctanoic Acid (PFOA) in Small Mammal Liver by LC/MS/MS"
VOOOI786: "Method o f Analysis for tbe Determination o f Perfluorooctanoic Acid (PFOA) in Small Mammal Serum by LC/MS/MS"
TESTING FACILITY
Exygen Research 3058 Research Drive State College, PA 16801 Phone:(814)272-1039
STUDY DIRECTOR
JaisimhaKesari P.E., DEE Weston Solutions, hie. 1400 W eiton W ay
W est Chester, P A 19380
Phone: (610) 701-3761 Fax: (610) 701-7401
j.kesari@ w eBtonsolutions.com
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fixygDQProtocolNumberPOO00760
SPONSORREPRESENTATIVE
Michael A. Santoro 3M Company Director o fRegulatoryAffairs 3M Building 0236-01-B-10 St. Paul. MN 55144 Phone:(651)733-6374
PRINCIPALINVESTIGATOR
John M. Flaherty Exygen Research 3058 Research Drive StateCollege, PA 16801 Phone:(814)2724039 jolm.flaherty@cxygcn.com
PROPOSED EXPERIMENTAL START AND TERMINATION DATES
It is proposed that the analytical portion o f this study he conducted from October 01, 2004 to December 31, 2005. The actual experimental start and termination dates w ill be included in the fatal rtjtort.
IDENTIFICATION AND JUSTIFICATION OF THE TEST SYSTEM
The following arethe test systems for tfaiastudy: Water (groundwater and surface water) Soil a Sediment
Fish
Clams Vegetation Small Mammal Liver Small Mammal Serum
The samples w ill be collected by Weston Solutions. The control samples will be purchased and prepared by the testing facility. Purchase and processing
Fegt 7v/6S
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details for the control samples w ill be included in the final report associated with this study.
The test systems were chosen to access the environmental impact o f PFOA in the Decatur, Alabama area.
SAMPLE PROCUREMENT, RECEIPTAND RETENTION
Wales, soil, sediment, fish, clam, vegetation, small mammal liver and small mammal serum samples w ill be received at Exygen directly from Weiton Solutions. The detail* o fsample procurement for this study are outlined in the 3M work plan entitled " Phase 2 Work Plan for Sampling Environmental Media." The number and types o f samples collected w ill vary depending availability in the field. The total number o f samples received and analyzed for each matrix w ill be documented in the final report associated with this study.
Water, soil, and sediment samples w ill be used as received without further processing at Exygen. These samples w ill be stored refrigerated at 2C-8C. Fish, clam, vegetation and small mammal liver samples w ill be processed according to the appropriate analytical method (fee Appendix I). These samples w ill be stored frozen at -UPC. Small mammal whole blood samples w ill be centrifuged in the field at the time o f collection and the serum fraction w ill be used for the study. Small mammal serum w ill be stored frozen at -HPC.
The receipt and processing o f the samples w ill be documented in the final report and raw data associated with the study.
SAMPLE IDENTIFICATION
Prior to analysis, each sample w ill be assigned a laboratory sample reference number. The reference number w ill be unique and w ill distinguish each laboratory sample that is processed throughout the analytical procedure. Chromatographic data w ill be identified by the laboratory sample reference number.
Sample storage conditions and locations w ill be documented throughout the study.
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ANALYTICALPROCEDURE SUMMARY
Reference*: V000178Q: "Method o f Analysis for the Determination of Perfluorooctanoic
Add (PFOA) in Water by LC/MS/MS" V00017B1: " Method o f Analysis for the Determination o f Perfluorooctanoic
Add (PFOA) in Soil by LC/MS/MS" VOOOt782: "Method o f Analysis for the Determination o f Perfluorooctanoic
Acid (PFOA)in Sediment by LC/MS/MS" V0001783: "Method o f Analysis for the Determination o f Perfluorooctanoic
Add (PFOA) in Fish and Clams by LC/MS/MS" V0001734: " Method o f Analysis for the Determination o f Perfluorooctanoic
> Acid (PFOA) in Vegetation by LC/MS/MS" VOOOl73$: "Method o f Analysis for the Determination o f Perfluorooctanoic . Acid (PFOA) in Small Mammal Liver by LC/MS/MS" VOOOl786: "Method o f Analysis for the Determination o f Perfluorooctanoic
Acid (PFOA) in Small Mammal Serum by LC/MS/MS"
The above methods use analytical conditions capable o f separating the isomers o f PFOA. The final report w ill include the isomers summed into total PFOA found.
VERIFICATIONOFANALYTICALPROCEDURE
A laboratory control sample w ill be used for the preparation of fortified control samples. The test substance w ill be made into solutions as per the method, and added to the matrices via a miciopipettc.
For water sampling, Exygen w ill supply one bottle persample collected. The bottles w ill be 500 mL precleaned Sci/Spec Premier wide mouth HDPE bottles. These bottles have been routinely used for PFOA sample collection at the testing facility and have been shown to be free o f PFOA. A ll containers used for water sample collection w ill be shipped to the sample location containing 160 ng o f 15C PFOA (equivalent to 500 ng/L in the final sample). Samples will be added to each container to a volumetric fill line at 200 m L A field duplicate, a low field spike and a high field spike o f each sample w ill be collected. The low and high field spikes w ill contain PFOA as well as perfluorobiitanesulfbnate (PFSS), perfluorohexanestitfonate (PFHS), and perfhioicoctanesulfonatc (PFOS). These compounds are included in the solutions used to spike the samples. The results for PFBS, PFHS and PFOS w ill not bereported in this study. Exygen w ill supply one field blank (control water) and two field blank spikes (control water fortified wilh PFOA at a low
Page 9 q f6 J
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Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
ExygftnProtocolNumber:P0760
and high level) for every twenty sample collected. At the testing facility, each water sample (excluding field duplicates and field spikes) w ill be extracted in duplicate and w ill also be fortified at a low and high concentration with PFOA and processed through the described procedure to determinemethod accuracy and to check for bias.
For soil, sediment, clems, and vegetation, Exygen w ill supply one 500 mL precleanedSci/Spcc Premier wide mouth HDFE bottle per sample collected or a zip-seal bag. A ll containers/bags used for sample collection w ill be shipped to the sample location. Samples w ill be added to each container or bag in the field.' A t th testing facility, each sample w ill be extracted in duplicate and w ill also be fortified at a known concentration with PFOA at both a low and high level and procesaed through the described procedure to determine method accuracy and to cheek for bias. u C-PFOA w ill also be added to each sample in the laboratory prior to extraction at the level specified below.
' For small mammal liver, Exygen win supply a $0 mL polypropylene contrifoge tube. Forsmall mammal serum, Exygen w ill supply acollection kit for each sample contaming serum separator tubes (red top), vacutainers. needle holders and needles, transfer pipettes, and polypropylene tubes. At the testing facility, each Hverand serum sample w ill he extracted in duplicate and w ill also be fortified at a known concentration with PFOA at both a low and high level id processed through the described procedure to determine method accuracy and to check for bias. n C-PFOA w ill also be added to each sample in the laboratory prior to extraction at the level specified below.
Low and high spiking levels for each matrix aredefined below:
M atrix
Low PFOA High PFOA
"C-PFOA
Sulking Level Spiking Level Spiking Level
Water
SOOng/L
5000 nsn .
500 n tfL
Soil
4 ngte
40ng/g
40ng/g
Sediment
4 nate
40 ngte
40 ng/g
Fish
10 nate
lOOngte
lOOng/g
Clams
10 nate
lOOnste
lOOngte
Vegetation
10 nute
lOOng/g
lOOngte
Small Mammal Liver
lOng/g
lOOng/g
lOOngte
Small M ammaliSerum
lng/g
100 ng/mL
100 ng/mL
Recoveries am anticipated to -b e between 7CW4 an d 130% o f the fortified
levels; however, the exact precision and accuracy w ill be determined by the analysis o f the quality control samples described above. A statement of accuracy w ill be included in the final report.
Prior to sample analysis, a laboratory control spike study w ill be conducted in water to justify the use o f l3C PFOA results to establish precision and accuracy o f PFOA samples. The following samplesare Id be prepared:
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000074
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Exygen Protocol Number P0000760
Two control water blanks Two control water samples fortified at 250 ng/L with 1JC PFOA Two control watercamples fortified at 250 ng/L with !1C PFOA and at
250ng/L with PFOA. Two control water samples fortified at 5000 ng/L with ,3C PFOA and
at 5000 ng/L with PFOA. The above samples are to be extracted and analyzed according to method Y0001780 entitled " Method o f Analysis for the Determination of Perfluorooctanoic Acid (PFQA) in Water by LGMS/MS."
METHODFOR CONTROL OF BIAS
Control o f bias w ill be addressedby taking representative sob-samples from a homogeneous mixture of each matrix from untreated control samples, and by analyzing at least two levels o f fortifications.
STATISTICAL METHODS
Statistics w ill be limited to (hose specified in the subject methods and to the calculation of averagerecoveries, a* applicable.
GLP STATEMENT
A ll aspects o f this study shall be performed and reported in compliance with EPA TSCA Good Laboratory Practice Standards 40 CFR 792. The final report or data package (supplied to the Sponsor) shall contain a statement that the study was conducted in compliance with current and applicable GLP standards and w ill outline any deviations in the study from those standards. This statement w ill be signed by the Study Director and Sponsor Representative.
REPORT
A final report w ill be prepared by the principal investigator or their designee at the conclusion of the itudy. The report w ill include, but w ill not be limited to, the following:
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Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Exygen Protocol Number: P0000760
. The name and address of the Study Director, Sponsor Representative, and o fdie testing facility.
A statement o f GLP compliance {any related documentation, such as chain-of-custodyrecords, most he in the study records).
.. The signed and dated statement by the Exygen Research Quality Assurance Unit regarding dates o f study inspections and dates Sndings were reposted to the Study Director and Management.
A description o f the exact analytical conditions employed in the study. If the subject method was followed exactly, it is necessary to include only a copy o f the analytical method. Any modifications to tins method w ill be incorporated into the report. I f the method is photo-reduced, the project number and page number mustbe included on each page.
Description o f the instrumentation used andoperatingconditions.
e A ll results from all sets analyzed. Control and fortified samples w ill be
identified and the data table w ill include sample number and fortification level.
Representative chromatograms for each analyte in each matrix, including chromatograms o fa standard and acontrol sample, and a chromatogram at a fortification level. The location o f the analyte peaks w ilt be clearly identified in all chromatograms.
A ll circumstances that may have affected the quality or integrity o f the data w ill be documented in the report.
Locations where raw data and the final report are to bo archived.
Additions or corrections to the final report shall he in the form of an amendment signed by the Study Director. The amendment shall clearly identify that part o f the report that is being altered and the reasons for the alterotions. The amendment w ill be signed and dated by the Study Director andthe SponsorRepresentative.
SAFETY AND HEALTH
Laboratory personnel w ill practice goad sanitation and health habits.
Every reasonable precaution shall be taken to prevent inadvertent exposure of personnel and the environment to the test or reference substancefs).
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#076
Interim Report #23 - Analysis of Sediment Samples
f*"64 Exygen Study No.; P0000760
Exygen Protocol 'Number: P00007&0
/-* ameendments to protocol
A il significant change* to the analytical protocol outlined here w ill be expressed in writing, signed and dated by the Study Director and Sponsor Representative. Amendments usually w ill be issuedprior to initiation o f study plan change. However, when a change is required without sufficient time for the issue o f a written amendment, that change may be effected verbally with supporting documentation signed and dated by the Study Director and followed with a written amendment aa soon aa possible. In this case, the effective date o f the written amendment w ill be foe dale o f the documented change. Copies o fthe signed amendments w ill be appended to ail distributed study plan copies, the original amendment w ill be maintained with the original studyplan. Any deviations from the study plan or from the analytical method asprovided w ill be documented and reported promptly to foe Sponsor Representative.
DATARECORD KEEPING
Records to bemaintained include the following (as appropriate):
Sample tracking sheet(s) Sample receipt records, storage history, and chains o fcustody History andpreparation o fstandards (stock, fortification, calibration) Description o fany modifications to the method Instrument run sheets, bench-sheets or logs f Analytical datatables A ll chromatographic and instrumental conditions Sample extraction and analysis dates A complete listing o f study personnel, signatures and initials Chronological presentation of all study correspondence Any otherdocumentation necessary for the reconstruction o f the study
C hrom atogram s- A il chromatograms w ill contain the following:
Sample identification, injection date, arrow or other indication o f the area of interest, and injectionnumber corresponding to the run.
Additionally, fortifications w ill include foe amount o f analyte added and the sample number o ffoe samplethat was fortified.
Analytical standard chromatograms w ill additionally include foe concentration (e.g., ggfaiL).
Page 13 o f 63
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000077
Interim Report #23 - Analysis of Sediment Samples
p. 55 Exygen Study No.: P0000760
ExygenProtocolNumber:P000760
As part o f the documentation the following sheets w ill be included in each analytical set; a run sheet liltin g the samples to be run in the set. and an instrument conditions sheet describing the instrument type and operating conditions.
A ll applicable requirements for reporting o f study results as per 40 CFR 792.185.
QUALITY ASSURANCE
The QA Unit o f Exygen Research w ill inspect the study at intervals adequate to asaure compliance with GLP's, and w ill report the findings o f audits to the Study Director, Exygen Management, andthe Sponsor Representative.
RETENTION OFDATAANDARCHIVING
A ll hard copy raw data, including, but not limited to, the original chromatograma, worksheets, correspondence, and results shall be included with the data package submitted to the StudyDirector. These w ill be archived with the original study plan, amendments, final report, and all pertinent information from the Sponsor.
The testing facility shall keep all electronic raw data and any instrument, equipment, and storage logs for the period o f time specified in 40 CFR 792.195. An exact copy o f the materials submitted to the study director w ill also be kept at Exygen Research.
Exygen w ill obtain permission from the study director before discarding or returning samples.
Exygen Research
Arg Ho/6}
Page 55 of 110
000078
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Exygen Protocol Number: P0000760
APPENDIX I
ANALYTICAL METHODS
VOOOl780; `'Method o f Analysi* for the Determination o f Perfluorooctanoic Acid (PFOA) in Water by LC/MS/MS"
V0001781: " Method o f Analysis for the Determination o f Perfluorooctanoic Acid (PFOA) in Soil by LC/MS/MS"
V0001782: "Method o f Analysis for the Determination o f Perfluorooctanoic Acid (PFOA) in Sediment by LC7MS/MS"
V000178J: "Method o f Analysis for the Determination o f Perfluorooctanoic Acid (PFOA) in Fish andClams by LC/MS/MS"
V0001784: "Method of Analysis for the Determination o f Perfluorooctanoic Acid (PFOA) in Vegetationby LC/MS/MS"
VQO01785: " Method o f Analysis for the Determination o f Perfluorooctanoic Acid (PFOA) in Small Mammal Liver by LC/MS/MS"
V0001786: "Method o f Analysis for the Deicmunation of Perfluorooctanoic Acid (PFOA) in Small Mammal Serum by LC/MS/MS"
Exygen Research
Pag* 15 o f 65
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000079
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Exygen Protocol Number: FOOOQ760
AMNfAtWLNYwTInCbAenL MVOEWTH17O*0D
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Page 57 of 110
000080
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P000760
ExygenProtocolNumberPODD0760
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Pag* i 7 o f t t
Exygen Research
Page 58 o f 110
000061
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Exygen Protocol Number: P000076
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Page 59 of 110
000082
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Exygen Protocol Number: P0000760
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Page t9 o f 65
Exygen Research
Page 60 of 110
000083
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Exygsa Protocol Numhtr P00007W
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Exygen Research
Page 61 of 110
000084
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Bxygcn Protocol Number. P0000760
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Exygen Research
Page 62 of 110 O O O 08S
Interim Report #23 - Analysis of Sediment Samples
p. 63
Exygen Study No.: P0000760
Exygen Protocol Number P0000760
- loiiihttittfc
IfilW itVl-- v- VGD017I
adofAwfoiufcftoPifcAwNpAinLoHYwTIiCaAfPLorMflu1cTroHoOctOaaclcAdd(?P0A)inWwrby
LOMS/MS
1 4 2 f t r i w f l i t ftrtU ad with known imounta o f PFOA prior to unction. vie tb* feOowlnj oy wrioo lo c a la ik*c tb* percent rc c o v a y .
fumlMilyOfcjafldEmil)*mlytofaintmcongoj{pg/L)|^^ ui))tciddod(iiL)
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Exygen Research
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Page 22 c/65
Page 63 of 110
000086
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Exygcp Protocol N um ber P0000760
ANALYTICAL METHOD Uctiud Number V00017II
M ette* e fA mbriblbr tbe Detonalittloa of Ferfiupfoectuctc Acid (PFOA) m sou by LCM3/M
AnalyticalTaatinfFacility:
B3S0tce5lye6fRCoedAelie--coaaerea,*PrcDAhriv1e6101
ApprovedBy PTaaeuThlCnkoUealuLwel.yvider,LCC-ldSJ,tBLxy*imRteeerch
.
Dale
/ JV6ihcuePFliaehaeurltaytt,QpmtwfM,EayyaRe-- rob
z s .
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Total?** 7
P a g * 23 o f 65
Page 64 of 110
000087
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Exygen Protocol Number: P0000760
AiyiMkMMnfl
MaftodNiHfcfV0QQI7I
I
analyticalmethod
..
NedwdofAnatyaltfortoDManuaLrOiMWSfN/MfiSlumooctaitofeAaid(PPOA)inSoilby
Ilia maJfcod a to to p toyad v tto iaalitka awl quantitation of perfloorooetMoic acid by Higb NifouuiuM Liquid Onpgiuofnpby coupto} to undos M ut Spotto metric Dilirtcr (LC/M&WS) is ta il
2.0 totay
22..12 ACproetonccaiyuuiittaiottono*earpvptraofpiriiaiitetoMraStIo33rybpenfoeretohtat.iidtinfanycbermralforpropersafay
1 0 SwvloJIaqmvaawnt
.
333..J12 33..54
NSI8AArUonemtlMeymyiplurnmleiatpptcIMfiSaeoaUaiptl|.omcrreeefteedwMwtonttoipniMturhgoopfiatlrndongtuefomegtdrdhiedlydwtowoIrittlailxkttaooddonaibltaope.mafocrapieflloleobdw*e.iienndgtNotocnpaaiemqdupifUlbiabtgreepxitiretcofiooetno.iohmo
pwf
4.0 KmgftiUtodtontatts
4444.3341 MAPWmgafiltmtatoro-onHiodcuodPmc-HLtuACoPocLfnfoCdtAiftrocai-ddA-.CS4tg.aRuo-Al<AoicihtGrt*
10 Indnumst and Equipment
3.1 A Ugh jwfonnaoce liquid bmoatognipb capable o f jHuuping up to 2 orfveBti equipped with * variable VoUmt injector ci^tble ot injecting 5000 pL onwiertod to a tooduaM* Spcc>octtr (LOM&MS).
5.2 A devito tooDeoi raw dtta t o peak integration and quantitation 5.3 Analytical *'***capable ofreading to 0.00001 g. M 50 mL dilpmd>La polypropylene mWfuge lube* 5.3 15 b L dUpotablt polyrepylm eetttrifoga tube* 3.6 Ditpoaabk micropipets (MOOvL, 100200uL). 5.7 llS'tnL LDPS a*m>w-muthtofUre. 5.8 2 mL daw HPIC vial tai $.9 DitpNtbkpipMH.
535...111120 SWAPuatCotmvpatSpae^nt)moPaam(HkaKVnHiafoGcldd0.0op6L(]agn>d)ClflrtSlO?OBpcLa)rt.rwidgiteh*t.opcaabk tipi.
5.13 Ultrasonic tu b .
P*r2Pf>
Page 24 o f 63
Exygen Research
Page 65 of 110 0000S8
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Exygen Protocol Number: P0000760
BayyMKaMKfc
womi
f ANALYTICALMITHOP ~
MflhodofAm'lydltoritoflmnniriniileoBmesf/tmefshurtoctinoicAcid(PFOA) in Soilby
5.W Wria-ictitinkir. S.15 CtblrUUieafwbWofipuunc50roLpolypropylenetuba 5000rpm,
6.0 araMftfnpblctyfMm 61 .AwdytiwIOoImbmkFtoophtHR>flCeyrtca$oiitito)2-1roiax3Qmm.? 1116,225 MMTO(BobenNbmttMil:leepEUoFSmntOtiwPT-:t(atA3imI0)i*J:CQ)iMweMtnAaroi ttOwinAnhtinWmr
fin2201t121i.44.0v05nl
26622t5555A H
55 55775555
nfnotwLtoRwulel O000...33J5 W
6 4 tyeftttV o lm K L3 jiL (eie be taremed to as and) u 50 y U 6-7 Quaadliti: FeikAm-cMcnidtodaricdihntioacrr>. 6.1 RudTime -1 3 mfmtti,
Uteatev* ecmtftiMi tr* intmded et * g&ida cod may Wclun^ad in order to optimise (heKFLCtyvfeoi.
7.0 MS/MSSyitam 7.1 ModrBlieboepeayNegativeidBMmode,monilotin|413-t369 nVz for
?FOA.
Tto aboveecodmoee bo ktended u i fuide *od may be chuged in order to optimiM1bMSMS system
10 Fn^rtiefSliM
3.1 M oKl'tt*
1-1.1 2unsmaMesuiBnnmKaBoeimuiaomaceItDatOe CinmwLaotefrwI*p.epired by adding 0.15* | of
Ataoute wlaroee m*rbeptepued.
P|<2of?
Page 25 o f 65
Exygen Research
Page 66 o f l l O
000089
Interim Report #23 - Analysis of Sediment Samples
p. 67 Exygen Study No.: P0000760
ExygenProtocolNumber: P0000760
Nwtorvoeoi 1
ANALYTICALMETHOD MfdwdofAnalyiiiIbrtbDetanninLtGliiMo3f/hMeSfleoroomeekAcid(?P0A)inSoilby
9.0 SU BtO fdfnp
9.1 fmndmdftek/FactlfleatcBSolution 9.1.1 VKpnftodeMinteof-100pffmLofPFOAbywegkitg10mg u<4ifttaannnlplKinila1a2n3d'attLriLfoDomMc!tbeodtftia*rpurty)andtatolo100mLviih 9 .2 amAlL&tltotMarottifLnL1L0Dfb0PiitgiEfirctnbtiLfoctailooirhiiittfio>nM<jfMfinKti)vAolfuempecoipfiflOdObwyitbbrnif*tgdaifttolfll A1.0iiftal. fortifintiooaniutfonofPPOAli preparaibyhrfl|in| IO nLof0 1 0 jigtaLMbiliMiofintivolumeof100 withmrinnelin
9AA
9.1.5
AloAIOU1LO0S2aXo5ailHLfLm|fio|jLfLieoftdDfLaiLLFDfOoLf&eofpBrfni(ctfbiokoffktoiltiLfqitiCjcatiaig*eo.k.thtekitLniiaollntiooiiltuhootitiaitno(aaobefurloffiVFvotFAluOlfmiipAmenjioiMvpfo1iNcl0up0mdtrwbeediytbotbefmymiaDbdOrinaiemewfinii1ihgn0
9.1. mTheetetemclklaaid1f2c5rtmiftcLeLtDioPcanbtauitotoaerotobertortd!rtrefcgeretoiu SppurncxtittBdMao*fro4f"pCreupdarat0i,tubkfi1 maadawmjmMof6 rotai
9.2 ftudeniCeJilsitkenSoluti
9J.I LeGaliWbitSiteMDStUcandlibmralsionprdtcaarndiatsiatirparetfpbartaitiIneoHtoPteLtCion*apireocr.edTuTreie.
9X1
TIdheeaftbimBio1f0tinvagmptli.lypicalxmnpie;additimi coocentntioasmtybe pipantitneeded.
_TeXSC_foLCFetenm*t"uOac1iiiono11IrrM0S5aa00fr*nu2etMr_fenaaudbrtet_aroaettaotiitiddeaacPeatetVlriabmtff424e2w1riuot1a0000r0tu1ti000tt0wtinioeanteie.eKteoaFonfoSctdirVrmeataifornidenclun4444444.dAami0000000*Clfiemboerrflaft.t)rimttil itaCSanbntdCisDdewaadrFilrid2rrbiil5tartni50iimdmir00dI0aotiuttniiioaroinqnlreioa*trfiirtauXXXXXXXSC*CCQCCtdCfrteanmanmmuiHuonuilmBiam&bdutaniirdardidoddondnardddddddldtfiaiyt)yyotwni7dEya^y)n(**D-OSfO^44ltPEL
tra*'*
Pag* 26 a fte
*>*"* v+!
Exygen Research
Page 67 of 110
000090
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Exygen Protocol Number: P0000760
AKALYnCALMETHOD MethodofA-ailpsfelheDflunma*LipCo/MafPSMflc3fiiefMQtaaolcAddfPFOA)inSoilby
]
92.1 AMt--a/staMndairldr)ilxofkrMtSosDd.fretaswbbafl amhe preparedwithwh
WJ U
AgiSthdto2elw*unCLw1to1te<av*obChid.ipveadtoemtawiltoeaawtnioscanekaast.rtaadnodnasrdcsfiae1n3d-medL*pm<Jyypbraeppyriepiwaretudbes
lOdk BitchS*Up
]0.1 tto
pocRiEnfoaweentceoqfhtreeewodqMelruanrnaaebflowtmlietrycateeiOfoiiifeioaMtvodmaruerSmyplllt0teieodMekrrntpohfotla6deWwndblnaafbtebtlrccaodhotnrh.aDki(tsotouyrpaspyetitnidnctygwdaeodl$clynitcmae3cL0o(lsoabrarnIsdcamosl)bnptrirataoiodlnjstwpiniiidklclelbut)wedioesepaevicaleiefirae^ilsdyit
HjO Sapbtoriin
1 1 ,1
J11l..23
TnAYenddedadg5eabdfdt,^rlnLtph|otoiorleuafberstelhaisdmaleaapnlouedlutomlattendixsi9wbo9eUunl)ctL.obopaoithtwyapnirdnopaaeycnlstiioMcaniescebfoniirao-1riff5loifsrm-m1tob5ueteaasm-(feitfreityi as
1(4 Bornintgrifiihinetvuobleu.me19 la40mLwithwaisrm the50eil polypropylene
l)i CwxlriAifflEor^lminute*st-3000rpsxi.
11.5 CfooloawdJettdaabyti5tmCtl*omfHPLCrtwfiditwf(-(12gd.ro5jrntel*c)).bDyopcnsoatiAlegtIoDJmmtmLrmunedthryinol
U? U.I
11,9
ELA1o5hlnuaumafdoibyLws(dpeeoistclhayamp-m5rop)pkm(sybaleLesns1lfeti0mgc0ecpHlcoleetmifce0oeg0^&opdmftaiueoybtLce.CosnC{/MfdinoiStaliioc^lnMwS$l)u.CrmonLa-oS5PfmolucUaa.lretriidngtoe.graDdiuscaaterdd
1 2 .1
InfectthsaaccauuztouKorcacbstudied,strap!andfortifiedsampl*lowift uLCdyMae8/dMsSaispyrltiaim. Aeabbcilknstandstri must praeedeandfolowal
123 SiMtaflnthdtiB*ioilisPdPaOdAiaouoktfeinaipiyetoiuitalgi*tot athastfiveormorsconoerruadonlevel!
123 Ablaetnegnohpuowttrutetdibt1ae0dCWoaftMothaoeenveaefnordyd3o-e1f0a*tfatmlammlpeplamt*sstAaenit.duardEdMxtrmancuiatseejvdebs,etiaaInndscaalurbddr*eedismeaitaottfthbe*
ftp*')
Page 27 o f5
Exygen Research
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000091
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
ExygmProtooolNumberP0000760
DntiiNwcb-
MethodNinberUMWSi
A N A LY TICA L M E T H O D
MetedcfAnafymfartbDetecmmeutJoznhoiftPmNflimtwGtaooieAcidfPFOA^inSoilby
eJ(lboxDtraaeccwctaeoddunbctyfatertxfttioraafceateciodncdtaotnotfdbtarodaeftkaamttrSaytcatnebddoasridnta*fneincdttaeerdrdtps)e.tnIdeoedeUbvemegtriynna5ain-e1g.0ooxftwnic^Ukwdst
12.4 Uh Kbmt(antedtwvflt ft quantitation. UnearMatedcurvesik rstomonftuwraatcroedaslytbsetnettmeia.nntityetnetebdyeImenocawnKnagtieFaVuiradnu|sMingseIfeeLwyntexf3b3rin(goroefqpueivaatlaerneta|
)ZS te w p ti t e -- d m ld m l exceed e n te il o f . A ny sm ptes th *
t u t e ittafcrdT C ipeaec* should b e fio te rd ih itc d an d reanalyzed.
13j0 AcccpUix*Criteria
13.1 13.2
mbodCMalfutieuna4stthr1ktfaobStDadeeianoobwntbnleautiapn.imikn(ia3HseiPuddmiFNPauOo4iistw1daAt3nhtuueoem)ttwI^sccuuvouaawopttpeeaismerieeaoamkPttotmcFeofoOlu*aOtrsAtedhtHsbaaapeuntoognl3nehfh0dcvteuae*nrurltgboiso^oigcU(nnhmtodoteditoPee3.xPnridOtaheaAan.mnemwuthofberoolaLm,nOwkaQhspailemtrIstpfhaleei
' 133 RacewnteoreoiteleptkMandmatrixspikesmustbebetween70-130%of
taenatreberoewtonfvitaoluyeles.sIsfhaocuoldnbtreolrqo-ekx*tnftclttetdo.utAridneydmeaterioxcatppitkeeblaoulimtsiudae.7th0e
w13a0rr%antsehdo.uldbeeviJuajsdbytheanalyst todotermineif re-otbaotianis
13.4 AnycalibrationltandodfemdtobeastalLitlCftieulBerbyuctngdeHuge
* EHorrwoervTeor*dmetyotbaelneuxmclubdeerdofAoctnraothtaedceaafckubUraitMiouoitfuddeucntiKtbhmatiocnoucladrvbee
Ienxjcelcutdeed.dtaut bmexceed20%of(hefoal rusherofextnewdstandards
133 Theoooela&ucoefficient R)fttr taUbrttkmcurvesfederatedmuit be
3KfpXi.oWy2ak(Rte2 2na&p9eK5n).unJfbecatJajtkeetaniatuoraedsjuulst*t finosiltruomutesnidteo(pheoreastiolnim, iaun,dthtehne
ettndaidtorIheidBvmtsetofsimptoiteutdbeleenilyaed.
IZ6 iR4e%tenwtionftttiiimtaentabneatwlyeticeanlreann.tIefrdvtsanntdtoadmmptcderimfturoondostfdtUrifttemfotrswitthhainn
nSMlytUeJrunthenheictmustherasrulyaed
TffttoT?
Paft 26of65
Exygen Research
Page 69 of 110
000092
interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: PQ000760
ExygenProtocolNumber: P0000760
IinnltMuiEb
StatedMinionVOOOI711
I
ANALYTICAL M17BOP
.....
MethodefAoibwfi*IbePfatweLriOnMoSf/PMe9rilucioocttnoicAltd(PFOA)inSoilby
(4.6 Cikuladooa 14.1 bfUtaomtead6lMmfepbBeyeotkbwmelnlAfo)uqunLafyilnknfot(uftaoStCmwTnkinduvbptdomApwcvnfoc:a(cKunnelwofrFeFjrDs*A*kfwinepdtm(uinnenlatrfL),
PFOAfound(naff.)'
xOF
DPbcMrbywhichIbefinelvolumewe(filmed,Lfneotttiiy.
14.2 feFeorfomlonwpinligtAiqrnteiJifIntdnwtoiefeekbnuoltwfentoim*poeiurcneinotrfePcoFvOeAry.priortocxtncion,um lmvoy(K)a
[jotilwiliyfefamadtna/L)- mtyttfbuadipcontrol(ayT*)] ioafyteadded(ptfL)
144 thelbfalowingoquniontoconvert\benoun*afPFOAfoundinng/Lic
P^iiPPbX
FFOAfoundfppb>*IPPQAfoundfart,)g ntradediQ-MU) aojp!wtoghi(5f)
W.4 bUamteddOienffeeBytVwfjtnaggfaelquationwcilotlMdieameustofPFOAfoundinppb PFOAfound<ppi)dbyweight-PPOAfound(ppb)x[160%l wildeofideftl]
foe*7r?
Pag* 2? o f 65
Exygen Research
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000095
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
ExygenProtocolNumber P000076Q
AINMAhiLxYlHTuIBCbAL;MVOEOTMHTOOD
MHImlif rtI)itilii i>i tMiiitiaiBMfctbyilLmO..M....S...M............. m in i 1'1lil (T r m ) ln
AaslytjtaJ TWingFacility.
B3gt(^UgtCwP4iRwl>wwgr>b,PdDAiriv1e6901'
Apffovgd By.
C--iL1_____ PTttucltmCoc&iloioMydcrtLC'MBiBxyjai ofaeewtb a /m / b l / f/VhfkeDe-PFrluihid"detym;Optntkm,fttyg*Jtieeereh
_Dm*titiuJaL
D*t*
TcftlPite* t
Exygen Research
Page 71 of 110
000094
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: PQ000760
Exygen Protocol Number: P0000760
MatedNietervrooiHi | WALVTtCAUIBMQP ] MethodofAwlyjiifeethepf minmignofPoflwinwwtin ioAoid(PFQA)inSedimentby
LUM3!M3
1.0 Stop*
aSIVdpdreibmteyoMuHtirgichitDMPettiberibectneoamre(LpnlCocye/MedLSiCqMburSitdV)emClahroorodfcmttaioaetBoangLrdapqhyuincotituspbleodaotofpaertloaoncdoeoineuMnoaic
2 .0 Safely
.
122.1 CAikhwnUytohbewipnFreCepamfetlibMorSeDtoSytaptraarcaticbeu*r.odbieanychemdcitbrproperlefely
3j0 Simple Xequnaueut
333.11} 33..54
NAMAdpSoirwUmiowleerjaieeppaemctmliceKnteppiJuctleorOetesplek.ojremeeiefoidtiutoeiRlnwMrbatpaMeroiiigchtpeofnkldrertufaeeerveddrserodNwithibryaioirlmleucbeliidiMeadiBbubpeee.ataocAtiedfileebodrweaimenpdiegdie.iteoasinaepmqleupdilliinbfograreplevlatnrluoftoiMrro.tobmi*
4.D ReaganrodSroodMda
444...123
AA
AAWMmceeitmthteiac-anAHroclP-idHLA-P*C'dRLgdeCraiagtgtereroa-tdAge.rCa.dge>ReagMtfOnde
4.5 RorftuwooetiatrfcAdd*Sigrae-Akirich
iJO lotrwronwdquqHiMm
5.1 AhighperforarneHqddetamategrapbeapeblaof pumpingupto2
rpoLtocrcenneeaqcudipptoed>tawnidthemvMaraiaebBlepvobhewaueieti^ie(dLCo/rMcaSp/MabSle).ofinjecting5*200
5921 S5AJ 5S.A7
AA50admeevlyilcddectpiolVOceMoliblaefocdepnotteplywpiNdroaepdoyiflfreoenreepdeeiaurokgtiratioftoe0gg,0rlie0a0tit6fa1*r.go.d quantitalioil 1Dtd1iam5p-emLetLefi^bLolDeamPitlEeoefloaocppripoocwlye-pemCrooJnOurt-htiQrotaOeticaLr,oi.i0nCft-i2ieOt0uubLc)e..
9.1 2mLcbeKPLCvialkiL
55..010 DAinpettpefeobelettwjip(1d0c0tm*1.000gLid 10*100ptXwithdhpoeebfodpi.
55..1112 W$?atenre*uSuipmNnkroViebcU6.ec(lfl)lClt$P8 cartridge*.
fee*}n
P a g * J o f 65
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000095
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: POOOO760
Exygen Protocol Number' P0000760
i
ANALYTICALMETBOB ~
J
MethodofAwlyihibiAtDtfcmiMfaLiOoMfMSb/MtoSrooctmicAdd(PPOA)irtSedifrwnt>y
555..J11J34 WVCwrwirtiHmiriwfbr.yMtoibpotohrl-tofipuuof50Lpolyptspylgtubwi300Qepa.
W Q w k y p h i c Syrtam
6.1 AniljliciJColumn:Fluopbu*RP(XayitoeeScienpfcl 2.1 nun1 50mm,Su 64LU..234 t<TMMhMaoofboMcbilpe2ninlFi5t1tfaMuthntmet4*f8<9i1Aw*)3>C:;[:Q3MmrthMmAomlmoniumAeetiUiowee
FlowRete
0Ij.0D 22902Jt.O50
26U5 63 22555
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00000.....33333
44W..7$ QbRwyuwmnTiMmiiiueV:ito.-luyPnmeook:aAuliilimLe*tu-.aexbteermnalcitraMadevddlPc*aXflrm*tkuucAh*ir*v3Q>nL).
Thethtveeooditkiittiebundedletguideandnwybechangedidonfcvto
iTilibiiTe Itii ITTI T ijiiiim
7,0 M&MS3ytfca
7.1 FMFoOdAe.SltttM^yNifriveMJOdmade,noeiftoritig413-t 369m/zfer
loiwptaibtoow<meoM3dMhkSelyieertecmia.toidedti sguideandmaybtdwgedlnder
1 0 fnpmttooofSeltiHaiii 9.1 Mobilita
. 6.U w2wmMMaiuemaaloeaettaaqtttoKe1uQaC0eminiweiiiwiraJteirp.rependbyadding0.154gof
Exygen Research
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000096
Interim Report #23 --Analysis of Sediment Samples
Exygen Study No.: P0000760
Exygen Protocol Number; POOQ07SO
1 . - ' ANALYTICALMXTHOD tfttbodofAnlyciibrOrwuroinctlimLOorMP9dMAim9oocuioicAcid(WOA)inMimratOy
1-3 Bund!Mde U>1 l1OHOcDmeniLIbelafwidrt(wA.nuticps^mdbyedding10 ml.oiaceticKidm
Aleresvotemaybaprepand.
9.1 SaadariSlBckffatSiMfSdulioc
9.1.1 9.1.2 9.13
mAmPAtftMa]fgrla0Oouaa>1rbfa*i5oihj*faIlm^ntcaifnaaLe1LoiL0arfdt0Ditu1Mtkia(P2ciHftNBhLnannllbiinCLLoslwtf*nLtMk4hW.oonadfaw-mtuIOiftbtcthiiOaidttltotlottAalp*aie.PoihfpfinPPnuaFOLrlitoOyvAo)fAPltuainfldQpiapnArotpHpbfvAuy1*r*0dtwdt0obibwgyHyhbithBhtrrmiiomnimtginlIOi,Qrituwgfai)nmIh1De>
mal2L9omfthLtLiODPpBtfmboLtt)cfo.totimtoaAnalvolumtofICCwithmeth*miin
9.1.4 amA]02L,51onfntXii^.gU1L>.0f?cyBrgtbiffaoitaitLt]iaiao.oohattwoototokaiitfciaf&PifvOoluAmiaeimofy1a0i0fwlVityhtranwtthinutgol1in0
9.1.3 9.1.5
fTA1ab0MeMefkbloLalcnikiooftwfian1aLb4)ot2afe05t.vmi1ftieULpiLklifoarOtatitfLaBiobsiLootalifatlUitokia.io*ti*voteofFtoaFbEeAsMnislovproarelulipnmaaerere)obfrfyigIbWerxinwgwirnitihgt
aItpwpowtabU*imdaistotyo4fp*CnpumdtaaonaattbkBbrimaiawnperiodgf0 month
92 StredariCalibrationgototient . 9.7.1 LCM&i'McalflKtiUitiededae-ptaparelinmethanolviadilution 922 HefwttwfoOloJwingit typicaliwplaiadditionaloowtotniioiumyb*
WoQfFnuoiMroiAtlUcnitiuiWka
1wto0oo0 510
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031.0
0 .2
Page 33 o f 65
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000097
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
ExygcnProtocolNumber.P0000760
MvlMiNu^w VOMIm
ANAUrnCAlMETHOD MethodofAmdytfitytb*PWnnlnsrimofPoffluoroocwtoicAdd(FFOA)inSedimentby
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000098
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: F0000760
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Exygen Research
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Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Exygen Protocol Number: P0000760
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Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
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Interim Report #23 - Analysis o f Sediment Samples
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Interim Report #23 - Analysis of Sediment Samples
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Page 40 o f65
Exygen Research
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000104
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Bxygca Protocol N um ber P0000760
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Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
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Exygen Research
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000106
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
ExygenProtocolNumber:P0076
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Interim Report #23 - Analysis of Sediment Samples
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Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
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9.0 itmdirtPrmamte 9.1 StandardStocOTortiflcatiooSolution 9.U o*nfepaanlytatedae*cmkuataotteodtio(ofteonfw-1ta0d0tueprptoutLritoyfPmPdOdAilubtyevtotifh10m0geL10wmithg nadUBOlinal23mLU2F6bottle. >U AmtnaILJlZopStfttmabLlL1tLe0D0rtPipfigEMtabtlioLDManaoa.XpdilottoNtoeofffUFuOlvAoJifutpmttrpoaff1e0d0bwjrithbrminegfitnigw!l 9.1.3 aaAL102o.51fmte{ifl*/.iniQ1L.0fPe|iiBgtifttteaoLattlttu-oaluafoiMlultoioiafoinfpaplvtMoluiampereopf1v0M0lwbyithbrmtAetghainaogli1n0 9.M TbeatockutaIbrtUScrtiuapotationarttobtitcredinarefrigeratorli afaputMntMhhnudaaMlelyo4f*pCepanmdaatimn.atebteforamaximumperiodof6 month
97 StandardCalibrateSoteteea
97.1 9.27
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000119
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Bxygen Protocol Number P0000760
BVPMMM
V00OI7U
I
ANALYTICALMBTHOP
'
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11.1 111UJ
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12.1 tycctbeaameamountofeachkmrtrdtsaapfeandfortifiedsampleintoto
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112 12-.
geaaUitiAnnhaemtmjnekemntoicepaclpptrranhleUaeaddodtaertmiu.iooedasmetaeftd.Ao,eeteetaohAtvamumeefUslerepyJaabmlauUo5efl-ilbttlte1gycncr0eattMnuonlaarfutovbtmatSsoieyvnsisfpeedLtl.naeainoidhaoceftnddroa(sadrtaqironrssmdugateituricRttecutsciolubetoMnartubfiotbunneobletucoelotoLuuhwtsifeorleeicntcdaafgLsplmlleiieneblbc/rerdoxeyaanaetwaridnodctedniaettbaihgelielnbtealhitadrwostbaiitanKeeftisngieogntua)ninojnoedfeendccpvmiatenieeormgmadvrnynkat*asnd)ay5i.andrare.db)Irainelafest
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Page 56 of 65
Exygen Research i %s
pagc 97 of 110
000120
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
fcxygProtoco)Number:PQD00760
rnk HteaJ HinterVQOQJ713 I ANALYTICAL JHETHOP
MethodcfAiutalafafaDMetaommmkaxlltilvetarbryPLsOrihMmSw4cuofaAold(PFOA)in Smal
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US
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13.2 133
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14J UtjeasneeeafdmaoendfbpbfeayafakafaaMrefaau)ttueLaiyioxnfxtfolaecAaiwtlcanudrlaestpeidrfoagsruaarmmra:o(ulinnteoafrPrifjOrcAwibiounndp(inrainMgUtonL> PFOAfami(nfteL) dnlundmeseti.xDP<fareifalor
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000121
Interim Report #23 - Analysis of Sediment Samples
n. 99 Exygen Study No.: P0000760
Exygen Protocol Number: P0000760
VOM)
I A H M Y nC M , METHOD
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Exygen Research , ;*- V x T ' *
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000122
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Exygen Protocol Number: P0000760
ANALYTICAL METHOD M edndNm ter Vexol?
Mrked g/Aeetnli b ribe PtferaBeaee ef Perilpuniecleeele AcM(PPOA)li sm u M em el ( e r r a t? LCMB/M8
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Pttge 59 o f61
Page 100 of 110
000123
Interim Report #23 - Analysis of Sediment Samples
n . 101
Exygen Study No.: P0000760
Bxygen Protocol M usber: P000076D
b^nkiM M ih
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1.0 Scop
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33..12 3.3
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tetventiquippedwith*friablereturn*Iqfoctorc?aMeofvertrag3*200
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Page 60of6$
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000124
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
ExyjenProtocolNumberP000076
Muto*Nur*VQOOirib I A>i,U.ynCAtMSTUOD
MettpdafAadyuiefrtimPMatemnmiHeolSneiorunmbftayLftmC'MoMi/MteSrerieArid(PFOA)in5mn
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repli"
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Exygen Research
Page 102 of 110
000125
Interim Report #23 - Analysis of Sediment Samples
p. 103 Exygen Study No.: P0000760
Exygen Protocol Number: P0000760
SwmRamftb
MtoodMwibNVWOmA
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Page 62 o f 65
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Interim Report #23 - Analysis o f Sediment Samples
11.101 Exygen Study No.: P0000760
ExygenProtocolNumber.P00007W
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djPage 65 o f
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000127
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
SxyRbo Protocol Number: P0000160
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000128
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Exygc Protocol Number: P0000750
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Page 106 of 110
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Interim Report #23 - Analysis o f Sediment Samples
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Exygen Study No. : P0000760
n
RESEARCH
3058 Research Drive
Phone: 014*272-1039
State College, PA 16801 Tax: 814-231-1580
PROTOCOL AMENDMENT
Amendment Number 1
Effective Date: 01/19/05
Exygen Study Number: P0001131 Cileni Study N u m b er. Pegel of 1
Npffl
DESCRIPTION OF AMENDED SECTION 1) Analytical Procedure Summary V 0001780;Section . 1 2 ) Verification o f Analytical Procedure
AMENDEDTO 1) Add to Section 8 .): Section 9.1.8, Alternale weight of standards may be used to
prepare alternale concentrations of stock solutions as necessary. Alternate levels of fortification solutions may also be prepared. 2 ) Low and high spiking levels of the analytes for each matrix may be altered depending on sample sb e available for extraction and/or to cover analyte concentrations expected In the samples.
RATIONALE 1) H g h er concentrations of standards need to be prepared In order to spike the sample bottiee at higher levels.
2) The sample sure avaleW e for small mammal 8ver and serum was sm aler than expected. SpHdng at the pre-dstermlned levels In the protocol puts the spliced concentration lower than the detection Until Also, the analyte levels in the ground water samples are expected to greatly exceed the predetermined spiking levels listed in the protocol. W hen ths levels In the samples greatly exceed the pfldng levels, an accurate neawery value cannot be calculated for the Q C sample. Higher spiking levels In the bottle* will cover the analyte concentrations expected In ihe w ater samples.
_ IMPACT ON STUPY T heL O Q is 100 ng/g far a 0.1 g sample o f small mammal lhm ran d ts1000n g /tn L fara 0.01 mL sample of small mammal serum.
Higher levels of spiking for Ihs water samples will ensure that more Q C recovery data can be used.
LIBRARY ID: W0001226-8
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Exvaen QAU Review 1 .11 o r ili I f
ADMINISTRATIVE FORM
Exygen Research
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Interim Report #23 - Analysis o f Sediment Samples
Ti. <100
Exygen Study No.: P0000760
3058 Research Drive Phone: 814-272-1039 State Coltese, PA 16KM Fax: 814-231-1580
Amendment Number Effective Date: Exygen Study Number
PROTOCOL AMENDMENT 2
03/07/05 P0001131 Client Study Number:
^ ia1 Nona
DESCRIPTION OF AMENDED SECTION
1) Report, page 11 o f 65 2 ) Teel Matriels, page 8 o f 85: P F 0 8 transition monitored 489 -> 99.
AMENDED TO 1) Instead o fo r final report, interim port will be Issued. 2) PFOSbansWon monitored may also be 4 9 9 -> 80.
RATIONALE 1} Due to Iheexoesaivs sizes o f ihe data sate, Interim reports w ll be Issued to allow the ctont to receive data in a timelier manan '' >*<*' l* r W 2 ) The API 4000 LC/MS/MS systems detect toe 499 > 80 PFOS transition with greater sensitivity than the 499 -> 99 transition.
IMPACT O N STUDY 1) The d e n t wtil be able to receive and review the data more qutokfy. 2} The 499 -> 80 transition can be detected with greater sensitivity; therefore, giving better chromatography.
LBRARV IO: V000123M -
Exygen QAU Rsvtew. L u a h s f a ADUtNISTRTiyE FORM
Exygen Research
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Interim Report #23 - Analysis of Sediment Samples
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Exygen Study No.: P0000760
t d m *
RESEARCH
3058 Research Drive
Phone: 814-272-1039
State College, PA 16801 Fax: 814-231 *1580
DEVIATION FORM
_______________________ . -________________________________________ Pag 1 of 2
Sanaa!;
X Project Specific Deviation ____ Facility Deviation
Date of Occurrence: 04/26/06
Exygen Prefect # : P78WP1131
Deviation # :
5
Client P ro je c t# : _______ NA_______
R eference#: 06-076
Regulatory D river:
X _____
_____
GMP
GLP Other None
Sam ple DeecrloUon:
Deviation Type: (Inctude VH fa r m ethods and SOPs)
X Protocol
_____ Method
_____ SO P
W : NA Notebook reference: NA
L o g in # :
L0DP8191
C ontainer#: _______ NA_______ L o t# : __________ NA
Sum m ary Of Deviation: The three sediment samples In L8191 (C0172892 - C 0172894) were originally extracted using the sediment method V 0001762: Poor recoveries were obtained for PFOS, PFO A and t5C PFOA. Because of this, the study sponsor requested the u3e of an alternative extraction for these compounds, as follows:
D irect Infection M ethod; Before the samples were weighed for the extraction, they were mixed thoroughly by vigorously shaking the container. A one-gram portion of sediment was weighed into a 15-miffifrter centrifuge tube for the extraction. Ten milliliters o f 1% acetic acid in methanol was added to each sample. The samples were then shaken by hand, vortexed, and sonicated for thirty minutes. The samples were then centrifuged for -1 0 minutes at -3 0 0 0 rpm. Each sample was analyzed by LC/M SiM S elactroapray.
Using this method acceptable data was obtained for PFO S. but the recoveries for PFOA and 15C PFOA w ere s ill poor. Another alternative method was then used for PFOA and ,3C PFOA, as follows;
A lternative SPE M ethod: The samples that w ere prepared In 1% acetic acid tor the direct injection method w ere used for this extraction. Five milliliters of Bach sample was aliquoled into a 50-rnL polypropylene centrifuge tube and the volume was taken to 40 mL with water. The samples were then ' centrifuged for -1 0 minutes at -3 0 0 0 rpm. The supernatant was then loaded onto a C ig SPE cartridge conditioned with ID mL of methanol and 5 mL of water. The eluate was discarded. Approximately five mlSillters o f methanol was added to the cartridge. Five milliliters o f eluate was collected into a graduated 15 mL polypropylene centrifuge tube. Each sample was analyzed by LC/MS/MS electrospray.
Cause: ____ Preparation____ A nalysis_____ Instrum ent____ Client Request X Other
Im tii& b
More usable data was obtained.
:
LIBRARY ID: V0001B40-6
fcxygen Research
ADMINISTRATIVE FORM
Rage lUy ol liU
0001.12
Interim Report #23 - Analysis of Sediment Samples
Exygcn Study No.: P0000760
CHEH EHSR 236 1B
651 733 1955
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