Document k96EXza3kjoxLabXnKLw6gJbn
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Study Title
ANALYTICAL PHASE REPORTFOR PFOS: A REPRODUCTIOSNTUDYWITH THENORTHERBNOBWHITE
Data Requirement
FIFRA Subdivision E, Section 71-4 OECD Guideline 206
Author
Lisa A. Stevenson
Analytical Phase Initiation Date
January 31,2002
Analytical Phase Completion Date
April 18, 2003
Performing Laboratory
3M Environmental Laboratoly Building 2-3E-09 935 Bush Avenue
St. Paul, MN 55106
Project Identification
3M Environmental Laboratory Study # E01-1245 Wildlife International Ltd: 454-108
Total Number of Pages 226
No part of this report should be reproduced, except in full, without written approval of the 3M
Environmental Laboratory.
3M Environmental Laboratory
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PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northern Bobwhite
GLP COMPLIANCSETATEMENT
Study Title:
Analytical Phase Report for PFOS: A Reproduction Study with The Northern Bobwhite
Study Identification Number: E01-1245
This analytical phase was conducted in compliance with Toxic Substances Control Act (TSCA) Good Laboratory Practice (GLP) Standards with the exceptions listed below:
Exceptionsto GLP compliance:
0 Automated data collection systems are not validated. The hardcopy printouts are considered as the original raw data.
0 The stability of the reference substances and samples has not been determined.
0 Not all data generated were recorded directly or promptly, or initiated and dated on date of entry.
Lisa A. Stevenson, Principal Analytical Investigator
Date
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PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northern Bobwhite
QUALITYASSURANCSETATEMENT
Study Title:
Analytical Phase Report for PFOS: A Reproduction Study with The Northern Bobwhite
Study Identification Number: E01-1245
The analytical phase was audited 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.
10/08/01-10/09/01
02/01 I02 o41o31o2-o41o~1o2,o4t7i /02
05/20/02-05/21to2
Protocol In-phase
Data Final Report
10/09/01
10/09/01
02/04/02
02/04/02
04/08/02, 05116/02 04/08/02, 05116/02
05121I02
05/21 I02
Quality Assurance Representaf6e
Date
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TABLEOF CONTENTS
GLP Compliance Statement ............................................................................................................... 2 Quality Assurance Statement ............................................................................................................. 3 List of Tables ...................................................................................................................................... 5 Study Information ............................................................................................................................... 6 Summary ............................................................................................................................................ 7 Purpose .............................................................................................................................................. 8 Reference Substances ....................................................................................................................... 8 Specimen Receipt and Storage.......................................................................................................... 9 Method Summary ............................................................................................................................... 9 PreparatoryMethod............................................................................................................................ 9 Sample Collection and Analysis ......................................................................................................... 10 Analytical Method ............................................................................................................................... 11 Analytical Results............................................................................................................................... 12 Data Summary.................................................................................................................................... 14 Statement of Conclusion .................................................................................................................... 23 Statistical Methods ............................................................................................................................. 25 Statement of Data Quality .................................................................................................................. 25 References......................................................................................................................................... 26 List of Attachments............................................................................................................................. 26 Signature Page................................................................................................................................... 27
Attachment A: Extraction and Analytical Method, ETS-8-231.l,"Solid Phase Extraction and
Analysis of FluorochemicalCompounds from Biological Matrices"................................................... 28
Attachment B: Data Summary Tables ................................................................................................ 48 Attachment C: Sample Chromatograms, Calibration Information, and Instrument Information.........62 Attachment D: Sample PreparationSheets ....................................................................................... 155 Attachment E: Study Protocol, ProtocolAmendments, and Deviations............................................. 187 Attachment F: Example Calculations ................................................................................................. 226
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LISTOF TABLES
Table 1. Summary Table. CBFl7S0; Concentration in Sera and Liver............................................. 7 Table 2. Summary Table. C8Fl7S03 Concentration in Sera and Liver with Outliers Removed .......8 Table 3. Reference Substances ........................................................................................................ 8 Table 4. SPE Extraction Summary.................................................................................................... 9 Table 5. Sample Analysis .................................................................................................................. 10 Table 6. Serum QC Summary Table................................................................................................. 13 Table 7. Serum Matrix Spike Summary Table .................................................................................. 13 Table 8. Liver QC Summary Table.................................................................................................... 13 Table 9. Liver Matrix Spike Summary Table ..................................................................................... 13 Table 10. C8F17S0, Data Summary. Female Quail Sera (Adult and Offspring)............................... 15 Table 11. C8Fl7S09 Data Summary. Male Quail Sera (Adult and Offspring)................................... 17 Table 12. C8F17S03D- ata Summary. Female Quail Liver (Adult and Offspring) .............................. 20 Table 13. C8Fl7S0i Data Summary. Male Quail Liver (Adult and Offspring)................................... 22 Table 14. Summary Table. C8Fl7S0; Concentration in Sera and Liver........................................... 24 Table 15. Summary Table. C8Fl7S0; Concentration in Sera and Liver with Outliers Removed .....25
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PFOS: A Reproduction Study with the Northern Bobwhite
STUDYINFORMATION
Study Director
Sponsor
Sean P. Gallagher Wildlife International, Ltd. 8598 Commerce Drive Easton, Maryland 21601
Analytical Chemistry Laboratory
3M Environmental Technology and Safety Services 3M Environmental Laboratory Building 2-3E-09 St. Paul, MN 55106 Susan A. Beach, Sponsor Representative
3M EnvironmentalTechnology and Safety Services (ET&SS) 3M Environmental Laboratory (3M Lab) Building 2-3E-09 935 Bush Avenue St. Paul, MN 55106 Lisa Stevenson, Principal Analytical Investigator
Study Personnel
Sean P. Gallagher, Wildlife International LTD., Study Director Joann B. Beavers, Wildlife International LTD., Laboratory Management William K. Reagen, 3M Environmental Laboratory Management Susan A. Beach, Sponsor Representative Harold 0.Johnson, Ill, Principal Analytical Investigator Lisa A. Stevenson, Principal Analytical Investigator Kent R. Lindstrom, Senior Research Chemist Ognjenka Krupljanin, Analytical Chemist Marlene Heying, Analytical Chemist
Experimental Dates
Sample Analysis Initiation: 31 January 2002
Sample Analysis Completion: 15 April 2002
Archives
All original raw data, protocol, and analytical report have been archived at the 3M Environmental Laboratory according to 40 CFR Part 792. The analytical reference standard reserve samples, as well as the samples pertainingto the analytical phase of this study, are archived at the 3M Environmental Laboratory according to 40 CFR Part 792.
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SUMMARY
The concentration of the C8Fl7S0i anion of perfluorooctane sulfonate, potassium salt (PFOS, C8FI7SOiK+) was determined in the liver and sera of adult bobwhite quail and their offspring in both a control group and a 10 ppm, dosed group from Wildlife feeding study #454-108. The following tables summarize the C8Fl7S03 concentrations found in the liver and sera of study samples. These results only relate to the samples tested. Matrix-extracted PFOS standards were used to establish the HPLC-MS/MS instrument calibration curve for C8Fl7S0i. Concentrations of C8F17SOiare reported after correction for the purity and the potassium contribution to the mass of the PFOS reference substance.
Table 1 summarizes all study sample data. Table 2 summarizes study data after removing certain results that have been statistically determined to be outliers utilizing the Dixon Q-Test.
Table 1. Summary Table, CSF~~SOCoSncentration in Sera and Liver
1 1 1 1 1 1 FemaleControl
17
Group
NA
<400ng/mL(16of 17)
20
<50.2ng/g'
<50.2 ng/g (20 of 20)'
21 10 ng/mL (1 of 17)
1 Male 1Oppm Group
20
I 141000ng/mL I 94400-226000ng/rnL I
2o
I 88500 ng/g*
50100 - 147000ng/g*
Female
Offspring
4
NA
<400 ng/mL (4 of 4)
4
<20.0 ng/g"
<20.0 ng/g (4 of 4)*
Control Group
1 1 1 M10aplepmmsGprroinugp
5
12600ng/mL ~ 8220- 19200ng/mL ~ 5
7350ng/g* ~
4940 - 13700 ng/g"
1 Female
7640-18500ng/mL
5 ~ 7180ng/g* ~ 4590 - 13900 ng/g*
1
Group
For individual sample values see Tables 10 to 13 and Attachment B.
Accuracy: Sample results are accurate to 100% +I-30%.
Sera QC samples met the acceptance criteria Liver QC samples did not meet the '/2 of QC
for at
the method. each level must
be
within
75%
-
125% criteria for
the
method.
All
liver
QC samples (3) spiked at 10 ppb were >125% recovery. All other liver QC samples (6) were within criteria, therefore the
second QC criteria was met in that 2/3 of all QC were within 75% - 125%.
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Table 2. Summary Table, CaF17S03' Concentration in Sera and Liver with Outliers Removed
Male Control Group
19"
FemGalreoCuoontrol 16
19
<400 ng/mL <400 ng/mL (16 of 16)
20'
<50.2 ng/g** <50.2 ng/g (19 of 19)**
Male 1Oppm Group
20*
20*
Female 1Oppm Group
17
8700 ng/mL
4710 - 14700ng/mL
20'
MCoanletrOolffGsproriunpg 6' 6' FeCmonatleroOlGffsropuripng 4' 4'
1 5 * 1 1 MaleOffspring
5*
lOppmGroup
Female Offspring
1Oppm Group
* I
4
5760 ng/g'*
4940 - 6520 ng/g**
I 4 1 5490ng/g** 1 4590-7030ng/g**
No outliers from this data set. Refer to Table 1 for results. For individualsample values see Tables 10 to 13 and
Attachment B. Accuracy: Sample results are accurate to 100% +/- 30%. Sera QC samples met the acceptance criteria for the method.
** Liver QC samples did not meet the Yz of QC at each level must be within 75% - 125% criteria for the method. All liver
QC samples (3) spiked at 10 ppb were >125% recovery. All other liver QC samples (6) were within criteria, therefore the
second QC criteria was met in that 2/3 of all QC were within 75% - 125%.
PURPOSE
The purpose of this analytical phase of the study is to quantify C8FI7SO9 in the liver and sera of
both control and dosed Northern Bobwhite Quail and their offspring.
REFERENCESUBSTANCES
Table 3. Reference Substances
Source Expiration Date Storage Conditions 3M Laboratory Identification Number Physical Description Puritv
3M Internal 08/3112006 Frozen -20C +/- 10C
SD-018, Lot # 217
White Crystalline Powder 86.9%
Oakwood Products, Inc. 12/01/2010
Frozen -20C +/- 10C
SD-036
White Solid 98%
PFDA is nonadecafluorodecanoic acid, or Perfluorodecanoic acid, C10FI9O2H and is used solely to monitor for gross instrument failure and not as an internal standard for quantitation.
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SPECIMEN RECEIPTAND STORAGE
Northern Bobwhite serum and liver samples were obtained from the sacrifice of the test animals upon the conclusion of the in-life phase of the study (#454-108) conducted at Wildlife International, Ltd. and sent to 3M Environmental Laboratory for analysis. The specimens were received at 3M Environmental Laboratory on 09/05/01, 09/25/01, and 09/27/01; assigned a laboratory tracking (LIMS) number (E01-1245, E01-1342, and E01-1365, respectively), and were stored at -20C +/- 10C until extraction and analysis.
METHODSUMMARY
The determination of C8FI7SO9 concentration in the liver and sera was performed according to 3M Environmental Laboratory method ETS-8-231.1, "Solid Phase Extraction and Analysis of FluorochemicalCompounds from Biological Matrices". The sera samples were prepared by measuring a volume of serum and diluting with water in a 1/20 ratio. The liver samples were prepared by measuring a weight of liver and diluting with water to a 1/10 ratio prior to homogenizing. Five mL of acetonitrile was added to 1.OmL of the diluted sera or 1.OmL of the homogenate of liver and was shaken for 20 minutes. These samples were then centrifuged for 10 minutes; the supernatant was decanted into 40 mL of water and passed through a conditioned solid phase extraction (SPE) column. Upon drying the column 2.0mL of methanol was passed through the column to elute the analyte. The samples were analyzed for C8FI7SO3- using HPLC-ES/MS/MS.
PREPARATOMREYTHOD
0 ETS-8-231.1 "Solid Phase Extraction and Analysis of Fluorochemical Components from Biological matrices." This method describes the extraction of target analytes from biological matrices, such as sera and liver, using solid phase extraction (SPE). Sera samples were diluted with Kandiyohi (commercially bottled) water 1/20, before extraction. Liver samples were diluted 1/10, approximately l g of liver and 9ml of Kandiyohi water, and then
homogenized. A 1.0 mL aliquot of the diluted sera or homogenate of liver was extracted by
adding 5mL of acetonitrile, shaking for 20 minutes, and centrifuging for 10 minutes. The supernatant was transferred to a clean tube, diluted with 40 ml of Kandiyohi water, and filtered through a conditioned C18 (SPE) column. Analytes were eluted off the column, and analyzed by high performance liquid chromatography-electrospray tandem mass spectrometry (HPLC-ES/MS/MS).
Table 4. SPE Extraction Summary
I 1 I Measure out volume of sera or weigh portion of liver
I
Dilute sera (1/20) or liver (1/10) with water
or homogenize livedwater
4
Aliquot 1.Om1of diluted/homogenizedsample and add 5.0ml of ACN. Spike samples
accordingly. Shake for 20 minutes, centrifuge for 10 minutes.
5
Dilute supematant with 40 ml of water
I 6 1 Filter sample through conditioned SPE C18 column.
I
I 7 I Elute target analytes from the column with 2.0 mL methanol (MeOH).
I
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SAMPLE COLLECTION AND ANALYSIS
All sera and liver samples were received frozen and remained frozen until thawed prior to preparing samples for analysis. After dilution or homogenization steps, unused samples and diluted sera or homogenized liver were frozen again if extractions were not immediately performed.
On each day of extraction, a water blank, a sera or liver blank, and a matrix spike and matrix spike duplicate were prepared along with each set of samples. Frozen diluted serdhomogenized liver samples were allowed to thaw prior to transferring a representative sample for extraction. Samples were prepared and analyzed according to ETS-8-231.1.
The following table describes the sample collection and preparation regimen. For clarity, a reference to "Day 1" refers only to the group of samples associated with the first batch of samples extracted.
Table 5. Sample Analysis
I 2
Preparation of method blanks and spikes,
calibration curve, qc samples, and sera samples,
control group, adults (day 1 sera samples), see
1
Attachment D for samdes Dretmed Analysis of day 1 sera samples
I
Preparation of method blanks and spikes, and sera samples, control and 10 ppm adults, control offspring, and IOppm offspring (day 2 sera
Analysis of day 2 sera samples
31 January 2002
31 January2002 01 February2002
01 February 2002
Analysis of control, 10 ppm and offspring,from day 1 and dav 2 sera samDles 7 Weighing out of liver samples
8 Preparation of method blanks and spikes, calibration curve, qc samples, and samples, control group (day 1 liver samples), see Attachment D for samples prepped
9 Analysis of day 1 liver samples
10 Preparationof method blanks and spikes, and liver 1 samples, control group (day 2 liver samples), see Attachment D for samples prepped
11 Analysis of day 2 liver samples
12 Preparationof method blanks and spikes, and liver
samples, 1Oppm group (day 3 liver samples) ,see Attachment D for samples prepped 13 Preparation of method blanks and qc samples at 5
and 200 m b 14 Analysis of qc samples
15 Analysis of day 3 liver samples
07,08 February 2002 11 February 2002
11 February 2002 12 February 2002
12 February 2002 13 February 2002
13 February 2002 13 February 2002 14 February 2002
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samples, loppm group, control offspring, 1Oppm offspring (day 4 liver samples), see Attachment D for samples prepped 17 Analysis of day 4 liver samples
18 Re-analysis of day 3 liver samples
19 Re-analysis of QC samples
20 Re-analysisof QC samples
18 Februaly2002 01 March 2002 05 April 2002 10April 2002
ANALYTICALMETHOD
0 Samples were analyzed using HPLC-ES/MS/MS. C8Fl7S0; concentrations were determined
using matrix-extracted calibration standards ranging in concentration from 0.25-1000 ng
C8FI7SO3*/mL methanol. This result was then used to back calculate the ng C8FI7SO3-/mL
sera or ng C8F17SO;/gram liver as appropriate.
An internal standard,
Nonadecafluorodecanoicacid (PFDA), was used to monitor instrument performance for gross
malfunction, but was not used to quantitate results. HPLC-EC/MS/MS analytical conditions
are summarized as follows:
0 The HPLC used for the study was a Hewlett-Packard 1100. The system consists of a vacuum degasser, binary pump, autosampler and temperature controlled column compartment. The run time is 10 minutes per sample. HPLC conditions include the use of a Keystone Scientific, Betasil C18 HPLC analytical column (2.lmm x 50mm, 5pm particle size), a 40C column compartment temperature, a 1OpL injection volume and a 0.300mUmin pump flow rate. The HPLC gradient is listed below:
0
90
10
1 .o
90
10
5.5
5
95
I 7.5 I
5
95
181
90
10
I 10 I
90
I
10
I
0 The mass spectrometer used for the study was a Micromass Ultima. The system consists of Z-Spray interface equipped with an electrospray probe operated in negative mode. The instrument was setup to operate in MS/MS mode, passing the c8F17sOi molecular anion (m/z 499) into the collision cell, where it is collided with inert gas to further fragment to the characteristic ion m/z 99, FSO;. Similarly the PFDA transition from m/z 513 to m/z 299 was monitored. The collision gas, 95% Argon / 5% Methane, was maintainedat a pressure of approximately 3 . 0 ~ 1 0m~Bar.
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ANALYTICALRESULTS
Data quality objectives outlined in the 3M Environmental Laboratory method and protocol were met, except as noted and discussed below (see Attachment A, ETS-8-231.1, "Solid Phase Extraction and Analysis of FluorochemicalCompounds from Biological Matrices" and Attachment E, Study Protocol, Protocol Amendments, and Deviations).
0 Regressions. Quadratic curve fit, weighted l/x, was applied to calibration standards and sample data. Each calibration curve had a coefficient of determinationof 2 0.985.
Calibration Standards. Instrument response was calibrated daily prior to sample analysis using matrix-extractedstandards ranging in concentration in the final solvent extract from 0.20 to 1000 ng C8Fl7S09/mL methanol, correspondingto a concentration of 201 to 40160 ng/mL of sera or 3.99 to 19953 ng/g liver. The calibration curve analyzed consisted of nine sera-extracted standards and fourteen liver-extracted standards bracketing a wide concentration of analyte. The accuracy of each level was evaluated. Any level outside 75%125% of nominal was deactivated with the exception of the lowest curve point, which needed to meet 70%-130% of nominal. In some cases the lowest concentration curve point, although outside the 30% nominal requirement, was included when constructing the calibration curve, but it was not used to determine the limit of quantitation. The limit of quantitation was then the next point on the curve meeting the 30% nominal requirement. Due to the quadratic response of matrix-extractedstandards using LC/MS/MS instrumentation, the calculated concentration of higher-levelstandards was often indeterminate, that is a single result could not be calculated using the quadratic equation. The accepted upper concentration range for study samples was determined by the highest calibration standard meeting the 75%-125% accuracy criteria when back calculated to the original concentration spiked into the matrixextracted standards. All analytical results that are reported are within the accepted calibration range of the instrument.
System Suitability Samples. System suitability was demonstrated prior to the start and at the end of each analytical run. Prior to the calibration curve and after the last sample, three mid-level unextracted calibration standards were analyzed. The peak area precision and retention time precision was monitored at the beginning and end of the run separately. The peak area precision was equal to or less than 5.0% RSD, the precision of the retention time was equal to or less than 2.5% RSD, meeting the stated quality objectives to show that the instrumentationwas providing suitable results throughout each analytical sequence.
Continuing Calibration Verification (CCV). A mid-level matrix calibration check was analyzed every ten samples or less to monitor instrumental drift, with a limit of +25%
deviation of the target concentrations. Only d a t a bracketed by passing CCV's were reported.
Samples bracketed by one or more failing CCV's were reanalyzed.
Limit of Quantitation (LOQ). The lower limit of quantitation (LLOQ) was defined in liver
(ng/g) and in serum (ng/mL) as the lowest acceptable extracted calibration curve point that is within the 70-130% nominal criteria and with an analyte peak area at least 2 times the blank. The upper limit of quantitation (ULOQ) was defined as the concentration of the highest acceptable curve point used to calibrate the response of the instrument.
Blanks. Method blanks (purchased Kandiyohi drinking water, sera and/or liver taken through the entire sample preparation and analysis process) provided a measure of background contamination.
Quality Control (QC) and Matrix Spikes. One set of nine QC samples in each matrix was extracted and analyzed and consisted of three levels of analyte in triplicate. Additionally, two matrix spike samples at the lowest concentration were prepared with each extraction set. Results are as follows:
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1 Table 6. Serum QC Summary Table
I
MS-~DD~*
75.2%
I
3.0%
I
I I I I I QC-25ppb* I I I I -0Ppb
1000ng/mL 8030nglmL
115% 90.5%
8.3% 2.5%
I I I I I QC-40ppm I I I I I QC-80ppm*
1610000 ng1mL 3230000nglmL
76.2% 114%
2.8% 5.7%
Sera samples labeled as MS and QC were prepared following the same procedure on a different day and at different concentrations. These MS samples were inadvertently not labeled as QC.
`QC samples were reanalyzed to confirm original results. Data from reanalysis were not included in calculating these results.
[Table 7. Serum Matrix Spike Summary Table
1 Three Matrix Spikes 1
10000 ng/mL
I
Three Matrix Spikes Duplicates
10000 ng1mL
93.9% 91.8%
I Table 8. Liver QC Summary Table
I
QC-1Oppb*
~~
QC-75ppb*
200 nglg
1500 nglg
138%
I
2.9%
I
115%
2.9%
QC-l50ppb*
-
2990 nglg
104%
2.0%
*QC samples were reanalyzed to confirm original results. Data from reanalysis were not included in calculating
these results.
=Liver
Matrix Spike Summary Table
Four Matrix Spikes
Four Matrix Spikes Duplicates
499 ng/g
I
499 nglg
110% 112%
The protocol and method state that 213 of all QC and a minimum of YZ of QC at each level
must be within 75% - 125% criteria. All three of the liver "QC-1Oppb" spikes exceeded the
stated criteria, therefore the liver data reported in the low range of the curve (Day 0 samples)
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may be biased high. Since all study samples that were not "Day 0" show analyte levels significantly above the low range of the curve, the overall impact (or bias) on data is minimal or none at all. 0 Absolute Recoveries. The absolute recovery of the QC samples is determined by comparing the results of the extracted quality control spikes quantitated versus an matrixextracted curve and a solvent curve. The sera spikes quantitate higher using a solvent curve than when using a matrix-extracted curve. The low spikes are 37.8% higher, the medium spikes 31.7% higher, and the high spikes 28.6% higher. The 32.5% average higher quantitation of the three levels of spikes using a solvent curve versus a matrix-extracted curve demonstrates that it is appropriate to use matrix-extractedstandards. The same trend is observed for liver samples. The liver spikes quantitate at 4.8% lower, 6.4% higher, and
8.4% higher respectively for the low, medium and high spikes of the liver matrix with an average of 3.0% higher using a solvent curve versus an extracted liver matrix curve, again
demonstratingthat it is appropriate to use matrix-extractedstandards.
0 Internal Standard: The internal standard (PFDA) was added to all samples and standards. PFDA was not used for quantitation, but was used to monitor for gross instrument failure.
0 Instrument Response Calibration. HPLC-ES/MS/MS instrument response was calibrated using the concentration of the C8FI7SO3 anion of perfluorooctane sulfonate, potassium salt (PFOS) that was adjusted for purity and the potassium ion contribution to the mass of PFOS used to prepare stock solutions. Any future calculations requiring concentrations to be expressed as a percentage of dietary in-take must adjust the dosed amounts as well.
DATASUMMARY
Tables 10 through 13 summarize individual sample data. Representative chromatograms are presented in Attachment C. The tables display C8FI7SO9 concentrations for individual injections. All data are corrected for purity of the PFOS reference substance used for the matrix-extracted calibration curve. All results relate only to the samples tested.
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Table 10. CsF17SO; Data Summary, Female Quail Sera (Adult and Offspring)
E01-1245-28444 454-108-330, Oppm female, adult, 01-31-02 E01-1245-28446 454-108-332, Oppm female, adult, 01-31-02
I
0.4 0.4
<400 <400
E01-1245-28449 454-108-336, Oppm female, adult, 01-31-02 E01-1245-28451454-108-338, Oppm female, adult, 01-31-02 E01-1245-28453 454-108-340, Oppm female, adult, 01-31-02 E01-1245-28456 454-108-344, Oppm female, adult, 01-31-02 E01-1245-28458 454-108-346, Oppm female, adult, 02-01-02
I
E01-1245-28460 454-108-348, Oppm female, adult, 02-01-02 E01-1245-28462 454-108-350, Oppm female, adult, 02-01-02 E01-1245-28464 454-108-352, Oppm female, adult, 02-01-02 E01-1245-28466 454-108-354, Oppm female, adult, 02-01-02 E01-1245-28468 454-108-356, Oppm female, adult, 02-01-02 EOI-1245-28470 454-108-358, Oppm female, adult, 02-01-02 E01-1245-28472 454-108-360, Oppm female, adult, 02-01-02
0.3
1
<400
<400
0.3
1
<400
0.3 1 <400 <400
0.3
1
<400
0.2 1 <400 <400
0.2
1
<400
0.2
0.2
I I 1I I I O0..1l I
I 0.3
0.3
1 1 1 1 I 1 1
<400 <400 <400 <400 <400 <400
<400
<400
1
<400
1 0.4
1
<400
<400
0.4
1
<400
1 c400
<400
I I I 0.44
1
<400
I 0.3
I
0.3
1 0.3 1 <400 <400
0.3
1
<400
0.3
,
0.3
~ 0.3
1
1
I
c400
<400
2050 2180
<400
I 2110.
E01-1245-28474 454-108-362, Oppm female, adult, 02-01-02
0.2 1 <400 <400
0.2
1
<400
E01-1245-28477 454-108-366, Oppm female, adult, 02-01-02
0.2 1 <400 <400
0.2
1
<400
E01-1245-28479 454-108-368, Oppm female, adult, 02-01-02
0.3 0.3
1 1
1
<400 <400
<400
E01-1245-284811454-108-370, 1Oppm female, adult, 02-01-02
0.3
I
9170
EO1-1245-284831454-108-372.lOmm female. adult. 02-01-02
0.4
1
9140
E01-1245-28485 454-108-374, 1Oppm female, adult, 02-01-02
0.2
1
8400
E01-1245-28487 454-108-376, 1ODum female, adult, 02-01-02
0.3
1
9280
E01-1245-284891454-108-378.lOmm female. adult. 02-01-02
1
0.1
I
1 I
4980
I
E0l-1245-284911454-108-380,10ppm female, adult, 02-01-02
0.1
1
5790
3M Environmental Laboratory
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* E01-1245-28518 454-108-246, Oppm female, offspring, 02-01-02
0.1
1
<400
<400
0.1
1
<400
I* E01-1245-28521 454-108-259, Oppm female, offspring,02-01-02 !
0.1
EO,-1245-285241454-1 08-273, Oppm female, offspring,02-01-02 0.08
0.08
c400 <400
<400
I <400
<400
I* I I I E01-1245-28525!454-108-2E',Oppmfemale, offspring,02-01-02
o0.2
1
<400
I I I * E01-1245-28528 454-108-517, 1Oppmfemale, offspring,02-01-02
18500 16600
17600
E01-1245-28530 454-108-525, 10ppmfemale, offspring,02-01-02
0.03
1
12800
12500
0.03
1
12100
E01-1245-28532 454-108-538, 1Oppmfemale, offspring,02-01-02 0.08 1 14600 13400
0.08
1
12200
E01-1245-28535 454-108-557, 10ppmfemale, offspring,02-01-02 0.06 1
0.06
1
8330 7460
7900
0.05
1
11500
E01-1245-28536 454-108-561, 10ppmfemale, offspring,02-01-02
10800
0.05
1
10100
* There are two results reported for these samples. Both values are included and averaged in the "Average of Dup Sample" column.
These values were rejected based on the results of the Dixon's Q-Test, 90% confidence interval, for the rejection of outliers.
Accuracy: Sample results are accurate to 100% +/- 30%.
Sera QC samples met the acceptance criteria for the method.
3M EnvironmentalLaboratory
3M Environmental Laboratory
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PFOS: A Reproduction Study with the Northern Bobwhite
Table 11. CsF17SOBData Summary, Male Quail Sera (Adult and Offspring)
I E01-1245-28443 r454-108-329, Oppm male, adult, 01-31-02
* E01-1245-28445 454-108-331, Oppm male, adult, 01-31-02 E01-1245-28447 454-108-333, Oppm male, adult, 01-31-02 E01-1245-28448 454-108-335, Oppm male, adult, 01-31-02 E01-1245-28450 454-108-337, Oppm male, adult, 01-31-02 E01-1245-28452 454-108-339, Oppm male, adult, 01-31-02
* E01-1245-28454 454-108-341, Oppm male, adult, 01-31-02
E01-1245-28455 454-108-343, Oppm male, adult, 01-31-02 E01-1245-28457 454-108-345, Oppm male, adult, 01-31-02
I E01-1245-28459 454-108-347, Oppm male, adult, 02-01-02
, E01-1245-28461 454-108-349, Oppm male, adult, 02-01-02
E01-1245-28465 454-108-353, Oppm male, adult, 02-01-02 * E01-1245-28467 454-108-355, Oppm male, adult, 02-01-02 * E01-1245-28469 454-108-357, Oppm male, adult, 02-01-02
E01-1245-28471 454-108-359, Oppm male, adult, 02-01-02
1, E01-1245-28473 454-108-361, Oppm male, adult, 02-01-02
I* E01-1245-28475 1454-108-363, Oppm male, adult, 02-01-02
* E01-1245-28476 454-108-365, Oppm male, adult, 02-01-02
E01-1245-28478 454-108-367, Oppm male, adult, 02-01-02
0.4
1
0.4
1
0.4
1
0.4
1
0.2
1
0.2
1
0.1
1
0.1
1
0.2
1
0.2
1
0.2
1
0.2
1
0.1
1
0.1
1
0.2
1
0.2
1
I 0.2
' 0.02
1
0.02
1
0.3
1
0.3
1
0.2
1
0.2
1
0.07
1
0.07
1
0.2
1
0.2
1
i 0.2
I 0.1
0.4
I
1
0.4
1
0.1
1
0.1
1
<400 <400 <400 c400 <400 <400 <400 e400 c400 <400 <400 <400 <400 <400 <400 <400 <400 <400
<400 <400 <400 <400 <400 c400 <400 c400 <400
c400 <400 <400 <400
~400
<400 <400 <400 <400 c400
<400 <400 c400 <400 1400
c400 <400 c400 .e400
<400 <400
3M Environmental Laboratory
3M Environmental Laboratory
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PFOS: A Reproduction Study with the Northern Bobwhite
I E01-1245-28480 1454-108-369, 1Oppm male, adult, d l 00,02-01-02 I
o0.22
I
I l10o 0 o
107000 117000
I 112000
0.2 E01-1245-28482 454-108-371, 1Oppm male, adult, d l 00,02-01-02
0.2
100
181000
180000
100
179000
0.1 E01-1245-28484 454-108-373, 1Oppm male, adult, d l 00,02-01-02
0.1
100
144000
150000
100
156000
0.3 * E01-1245-28486 454-108-375, 1Oppm male, adult, d100,02-01-02
0.3
100
138000
138000
100
138000
0.07
100
94400
E01-1245-28488 454-108-377, 1Oppm male, adult, d l 00,02-01-02
95300
0.07
100
96100
0.1 * E01-1245-28490 454-108-379, 1Oppm male, adult, d l 00,02-01-02
0.1
100
150000
158000
100
166000
0.1 * E01-1245-28492 454-108-381, lOppm male, adult, d100,02-01-02
0.1
100
141000
145000
100
149000
0.3
E01-1245-28494 454-108-383, lOppm male, adult, d100,02-01-02 0.3
100
147000
151000
100
156000
0.1 E0l-1245-28495 454-108-385, 10ppm male, adult, d100,02-01-02
0.1
100
119000
121000
100
123000
, E01-1245-28497 454-108-387, 10ppm male, adult, d l 00,02-01-02
0.3
0.3
100
174000
185000
100
196000
E01-1245-28499 454-108-389, 1Oppm male, adult, d100,02-01-02
0.1
0.1
1 00
129000
132000
100
136000
1. I 1 1 1 0.06
* E01-1245-28501 454-108-391, 1Oppm male, adult, d l 00,02-01-02 0.06
E0l-1245-28503 /454-108-393,10ppmmale, adult, d100,02-01-02 o0.'2
100
141000
144000
100
147000
160000 165000
162000
0.2 * E01-1245-28505 454-108-395, IOppm male, adult, d l00,02-01-02
0.2
100 127000 131000
100
136000
I I 1 :l I I 0.3 E01-1245-28507 454-108-397, IOppm male, adult, d100,02-01-02 0.3 E01-1245-28509 454-108-399, 1Oppm male, adult, d100,02-01-02 0.1
100 ' 100
99600 107000
138000 159000
103000 148000
0.1 E01-1245-28510 454-108-401, lOppm male, adult, d100,02-01-02
0.1
100
203000
215000
100
226000
0.2 E01-1245-28512 454-108-403, 1Oppm male, adult, d i 00,02-01-02
0.2
100
127000
132000
100
138000
1. I I ;:: i 1 0.1 E01-1245-28514 454-108-405, 1Oppm male, adult, d l 00,02-01-02 0.1 E01-1245-28516 1454-108-407, 10ppm male, adult, d100,02-01-02 0.1
100
108000
112000
100
1 17000
99200 112000
105000
I
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3M Environmental Laboratory
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, E01-1245-28519 454-108-253, Oppm male, offspring, 02-01-02 I
0.02
I E01-1245-28520 454-108-256, Oppm male, offspring, 02-01-02
, E01-1245-28522 454-108-266, Oppm male, offspring, 02-01-02 0.07
0.07
, E01-1245-28523 454-108-270, Oppm male, offspring,02-01-02
0.2
0.2
, E01-1245-28526 454-108-283, Oppm male, offspring, 02-01-02
, E01-1245-28527 454-108-291, Oppm male, offspring, 02-01-02 0.05
0.05
E01-1245-28529 1454-108-522, 10ppm male, offspring, 02-01-02 1
0.07
I
, E01-1245-28531 454-108-533, 1Oppm male, offspring, 02-01-02
, E01-1245-28533 454-108-545, 1Oppm male, offspring, 02-01-02
0.04
0.04
1
1
1
1
1
1
1
10 I
I
1
1
<400 c400 <400
I <400
<400 c400 c400 <400
I 19300
I 9310
8220 15500 13600
, E01-1245-28534 454-108-552, 10ppm male, offspring, 02-01-02
0.07
1
13600
0.07
1
11500
EO1-1245-28537 454-108-568, lOppm male, offspring, 02-01-02 I
0.1 0.1
1
1 1
1
10400
* There are two results reported for these samples. Both values are included and averaged in the
"Average of Dup Sample" column.
Accuracy: Sample results are accurate to 100% +/- 30%.
Sera QC samples met the acceptance criteria for the method.
c400 c400 <400 <400 19300 8760 14600 12500
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3M Environmental Laboratory
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PFOS: A Reproduction Study with the Northern Bobwhite
Table 12. CsFl7SOBData Summary, Female Quail Liver (Adult and Offspring)
I E01-1342-30321 10 DDm a.i. 330 F Liver
E01-1342-30339 0 ppm a.i. 332 F Liver E01-1342-30357 0 ppm a.i. 334 F Liver E01-1342-30375 0 m m a.i. 336 F Liver E01-1342-30393 0 ppm a.i. 338 F Liver E01-1342-30411 0 ppm a.i. 340 F Liver E01-1342-30429 0 rmm a.i. 342 F Liver
I E01-1342-30447 IODDm a.i. 344 F Liver
E01-1342-30465 0 pprn a.i. 346 F Liver E01-1342-30483 0 ppm a.i. 348 F Liver E01-1342-30501 0 ppm a.i. 350 F Liver E01-1342-30519 0 ppm a.i. 352 F Liver E01-1342-30537 0 DDm a.i. 354 F Liver E01-1342-30555 0 ppm a.i. 356 F Liver E01-1342-30573 0 ppm a.i. 358 F Liver E01-1342-30591 0 pDm a.i. 360 F Liver
E01-1342-30609 0 ppm a.i. 362 F Liver
E01-1342-30627 0 ppm a.i. 364 F Liver E01-1342-30645 0 ppm a.i. 366 F Liver E01-1342-30663 0 ppm a.i. 368 F Liver
E01-1342-30681 1E01-1342-30699 E01-1342-30717 E01-1342-30735 E01-1342-30753
10 DDm a.i. 370 F Liver 110m m a.i. 372 F Liver 10 ppm a.i. 374 F Liver
10 ppm a.i. 376 F Liver
10 o m a.i. 378 F Liver
rn a.i. 380 F Liver
1.0469
1
1.0232
1
1.0188
1
1.0543
1
1.0182
1
1.0904
1
I 1.0087 I 1 I
1.0998
I
1.1036
1
1.0237
1
1.1509
1
1.0578
1
1.0312
1
1.1031
1
1.0586
1
1.0424
1
1.0364
1
1.0577
1
1.0920
1
1.0868
I 1.0748 I
1.0790
1.1036 1.0021
1
1 1
1
1
1
<50.2* c50.2' <50.2* <50.2* ~50.2' c50.2* <50.2* <50.2* ~50.2' <50.2' c50.2* ~50.2' ~50.2' <50.2* <50.2* <50.2* c50.2* c50.2* <50.2* c50.2*
5920* 4430* 543w 3980* 3750*
IE01-1342-30982
E01-1342-31000 E01-1342-31018 E0l-1342-31036
I 10 DDm a.i. 402 F Liver 10 ppm a.i. 404 F Liver
10 ppm a.i. 406 F Liver 10 DDm a.i. 408 F Liver
3M Environmental Laboratory
3M Environmental Laboratory
1
1.0876
1
1
1.0173
'
1
1.0047
1
1.0044
1
5900* 5420* 587W 4560*
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These values were rejected based on the results of the Dixon's Q-Test, 90% confidence interval, for the rejection of outliers.
Accuracy: Sample results are accurate to 100% +/- 30%.
* Liver QC samples did not meet the Yi of QC at each level must be within 75% - 125% criteria
for the method. All liver QC samples (3) spiked at 10 ppb were >125% recovery. All other liver QC samples (6) were within criteria, therefore the second QC criteria was met in that 2/3 of all QC
were within 75% - 125%.
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3M Environmental Laboratory
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PFOS:A ReproductionStudy with the Northern Bobwhite
Table 13. C a F 1 7 S O 3 Data Summary, Male Quail Liver (Adult and Offspring)
E01-1342-30312 10 ppm a.i. 329 M Liver
E01-1342-30330 10 DDm a.i. 331 M Liver
E01-1342-30348 10 ppm a.i. 333 M Liver E01-1342-30366 0 ppm a.i. 335 M Liver E01-1342-30384 0 m m a.i. 337 M Liver E01-1342-30402 0 ppm a.i. 339 M Liver E01-1342-30420 0 ppm a.i. 341 M Liver E01-1342-30438 0 ppm a.i. 343 M Liver
E01-1342-30456 10 mrn a.i. 345 M Liver
E0l-1342-30474 10 tmm a.i. 347 M Liver E01-1342-30492 0 ppm a.i. 349 M Liver E0l-1342-30510 0 ppm a.i. 351 M Liver E01-1342-30528 0 ppm a.i. 353 M Liver
E01-1342-30546 IO DDm a.i. 355 M Liver
E01-1342-30564 0 ppm a.i. 357 M Liver E01-1342-30582 0 pprn a.i. 359 M Liver
E01-1342-30600 IO mrn a.i. 361 M Liver
E01-1342-30618 0 ppm a.i. 363 M Liver E01-1342-30636 0 ppm a.i. 365 M Liver E01-1342-30654 0 DDm a.i. 367 M Liver
E01-1342-30672 I10 ppm a.i. 369 M Liver
E01-1342-30708 I1o DDm a.i. 373 M Liver
E01-1342-30726 10 ppm a.i. 375 M Liver E01-1342-30744 10 ppm a.i. 377 M Liver E01-1342-30762 10 pprn a.i. 379 M Liver E01-1342-30780 10 ppm a.i. 381 M Liver E01-1342-30798 10 ppm a.i. 383 M Liver E0l-1342-30829 110 m m a.i. 385 M Liver E01-1342-30847 10 ppm a.i. 387 M Liver E01-1342-30865 10 ppm a.i. 389 M Liver E01-1342-30883 10 ppm a.i. 391 M Liver E01-1342-30901 10 mrn a.i. 393 M Liver E01-1342-30919 10 ppm a.i. 395 M Liver E01-1342-30937 10 ppm a.i. 397 M Liver E01-1342-30955 10 ppm a.i. 399 M Liver E01-1342-30973 10 tmm a.i. 401 M Liver E01-1342-30991 10 ppm a.i. 403 M Liver E01-1342-31009 10 ppm a.i. 405 M Liver E01-1342-31027 10 Dprn a.i. 407 M Liver
3M Environmental Laboratory
3M Environmental Laboratory
I I I 1.0530 I 1.0338
1.0062 1.0269 0.0886 1.0235 1.0090
I 1.1046 1 I 1.0586 I
1.0358 1.0583 1.0183
I 1.0899 1
1.0382 1.0941
1 1.0084 I
1.0818 1.0916 1.0327
I 1 I
1
1 1 1 1 1
1 I 1 I
1 1 1
1 I
1 1
1 I
1 1 1
1.0010
10
I 1.0276 I 10 I
1.1008
10
1.0236
10
1.0312
10
1.0501
10
1.0110
10
' I
1.0678 I
1.0315
10 I
10
1.0310
10
1.0947
10
1.0834
10
1.0489
10
1.0309
I
10
1.0276
10
1.0361
100
1.0019
100
1.0336
100
1.0956
100
<50.2*
I
<50.2*
I
209 e*
I
<50.2*
<50.2*
40.2'
<50.2*
<50.2*
<50.2*
I
<50.2*
I
<50.2*
<50.2*
<50.2*
<50.2'
I
<50.2*
<50.2*
<50.2*
I
<50.2*
<50.2*
~50.2'
78600*
86300*
I
70000*
8030V
90700*
80000*
735w
834W
I
79300*
70300*
70400'
86800'
65100*
50100*
63000*
147000*
146000*
138000*
132000*
Page 22 of 226
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PFOS: A ReproductionStudy with the Northern Bobwhite
E01-1365-31194 0 ppm a.i. 253 M Liver, Offspring
0.3806
1
<20.0*
E01-1365-31199 0 ppm a.i. 256 M Liver, Offspring
0.5947
1
<20.0*
E01-1365-31209 0 pprn a.i. 266 M Liver, Offsprinu
0.2673
1
<20.0*
lE01-1365-31214 10m m a.i. 270 M Liver. OffsDrina I 0.5900 I
1
I
<20.0*
I
E01-1365-31229 0 ppm a.i. 283 M Liver, Offspring
0.6666
1
<20.0*
E01-1365-31234 0 ppm a.i. 291 M Liver, Offsprinu
0.6072
1
<20.0*
E01-1365-31245 10 ppm a.i. 522 M Liver, Offspring
0.7325
10
E01-1365-31255 10 ppm a.i. 533 M Liver, Offspring
0.6903
1
E01-1365-31265 10 ppm a.i. 545 M Liver, Offspring
0.4624
1
E01-1365-31270 10 ppm a.i. 552 M Liver, Offspring
0.5353
1
E0l-1365-31285 10 ppm a.i. 568 M Liver, Offsprinu
0.7581
1
13700 **
4940* 5580' 5990* 6520*
0 These values were rejected based on the results of the Dixon's Q-Test, 90% confidence interval, for the rejection of outliers.
Attachment B contains data summary tables.
Accuracy: Sample results are accurate to 100% +/- 30%.
* Liver QC samples did not meet the Yi of QC at each level must be within 75% - 125% criteria
for the method. All liver QC samples (3) spiked at 10 ppb were >125% recovery. All other liver QC samples (6) were within criteria, therefore the second QC criteria was met in that 2/3 of all QC
were within 75% - 125%.
STATEMENT OF CONCLUSION
Sera results from the male control group portion of this study showed no detectable levels of c8Fl7Soi in 19 of 19 quail (c400 ng/mL). The sera results from the female control group portion of this study showed no detectable levels of C8F17soi in 16 of 16 birds (c400 ng/mL) (Table 15). Analytical results for twenty sera samples from the lOppm dosed male group showed an average
of 141000 ng/mL C8Fl7S0i (range 94400 - 226000 ng/mL, Table 14). Analytical results for
seventeen sera samples from the lOppm dosed female group showed an average of 8670 ng/mL
c8F17SO(irange 4710 - 14700 ng/mL, Table 15).
Sera results from the male offspring control group showed no detectable levels of C ~ F I ~ SinO6~
of 6 birds (c400 ng/mL). The sera results from the female offspring control group portion of this study showed no detectable levels of c8F17soi in 4 of 4 birds (c400 ng/mL, Table 14). Analytical
results for five sera samples from the 10ppm dosed male offspring group showed an average of
12600 ng/mL (range 8220 - 19200 ng/mL, Table 14). Analytical results for five sera samples from the 10ppm dosed female offspring group showed an average of 12400 ng/mL (range 7640 -
18500 ng/mL, Table 14).
Liver results from the male control group showed no detectable levels of C8Fl7S0; in 19 of 19 birds ( 4 0 . 2 ng/g, Table 15) and quantifiable concentrations of C8Fl7S0i in 1 of 20 (209 ng/g, Table 14). The liver results from the female control group showed no detectable levels of C8F17S03i-n 20 of 20 birds (c50.2 ng/g, Table 14). Analytical results for twenty liver samples
from the 10ppm dosed male group showed an average of 88500 ng/g C8Fl7S09 (range 50100 -
147000 ng/g, Table 14). Analytical results for twenty liver samples from the lOppm dosed female
group showed an average of 4900 ng/g c8Fl7So3(-range 3290 - 7550 ng/g, Table 14).
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PFOS: A Reproduction Study with the Northern Bobwhite
Liver results from the male offspring control group portion of this study showed no detectable levels of C8Fl7S0i in 6 of 6 birds (-50.2 ng/g, Table 14). The liver results from the female
offspring control group portion of this study showed no detectable levels of CSFl7SOiin 4 of 4 birds (c20.0ng/g, Table 14). Analytical results for four liver samples from the 1Oppm dosed male
offspring group showed an average of 5760 ng/g (range 4940 - 6520 ng/g, Table 15). Analytical
results for four liver samples from the lOppm dosed female offspring group showed an average of
5490 ng/g (range 4590 - 7030 ng/g, Table 15).
Table 14. Summary Table, CsF17SOB Concentration in Sera and Liver
I I 1 1 I 1 1 F e m ~ ~ ? ~ 1t7r o l
NA
<400 ng/mL (16 of 17) 20 <50.2ng/g* <50.2 ng/g (20 of 20)' 2110 ng/mL (1 of 17)
I 1 I 1 Male10ppm 20
141000ng/mL 94400-226000ng/mL
88500 ng/g*
50100 - 147000ns/g*
I I Group
2o
1 I 1 ! I I FemaGlerloopuppm
18
9990ng/mL
4710 - 31900 ng/mL
4900 ng/g*
3290 - 7550 ns/g*
2o
1 1 1 Maleoffspring 1 I I ControlGroup
NA
<400 ng/mL (6 of 6)
6
<20.0ng/g'
<20.0 ng/g (6 of 6)'
Female
<400 n@mL(4 of 4)
<20.0 ng/g (4 of 4)'
Control Group
1 1 1 1 1 1 M1OapplemmGsropupring 5
Female
1 I 1 1 Offspring10ppm
5
12600ng/mL
8220 - 19200 ng/mL
5
7350ng/g'
12400 ng/mL
7640 - 18500 ng/mL ~
5 ~ 7180ng/g'
4940 - 13700 ns/g* 4590 - 13900 ng/g*
Group
For individual sample values see Tables 10 to 13 and Attachment B.
Accuracy: Sample results are accurate to 100% +/- 30%. Sera QC samples met the acceptance criteria for the method.
Liver QC samples did not meet the Yz' of QC at each level must be within 75% - 125%criteria for the method. All liver
QC samples (3) spiked at 10 ppb were >125% recovery. All other liver QC samples (6) were within criteria, therefore the
second QC criteria was met in that 2/3 of all QC were within 75% - 125%.
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Table 15. Summary Table, C ~ F I ~ SCOon~centration in Sera and Liver with Outliers Removed
I I I I MaleControlGroup I I I I 19'
I I 1 I I I FemaleControl
16
I Group
19 *
<400ng/mL <400ng/mL(16of 16)
20*
<50.2 ndg" <50.2 ng/g (19 of 1 9 r
Male 1Oppm Group
I I I I I I I 1 20*
20*
Female 1Oppm
I I I I I I I Group
17
8700ng/mL
4710-14700ng/mL
20'
Male Offspring
I I . I 1OppmGroup
Female Offspring
I I I I 1OppmGroup
5*
1 I I I 4
5760ng/g"
4940-6520ng/g*'
I I I I 4
5490ng/g**
4590-7030ng/g**
* No outliers from this data set. Refer to Table 1 for results. For individual sample values see Tables 10 to 13 and
Attachment B.
Accuracy: Sample results are accurate to 100% +/- 30%. Sera QC samples met the acceptance criteria for the method.
** Liver QC samples did not meet the !h of QC at each level must be within 75% - 125% criteria for the method. All liver
QC samples (3) spiked at 10 ppb were 2125% recovery. All other liver QC samples (6) were within criteria, therefore the second QC criteria was met in that 2/3 of all QC were within 75% - 125%.
STATISTICAMLETHODS
Statistical methods were limited to calculating means, standard deviations, % coefficient of variation and the Dixons Q-Test. The Dixons Q-Test, used for the rejection of outliers, has values ordered from lowest to highest. A Q-value is determined from the difference of a result and the next closest result which is divided by the difference of the highest and lowest value in the group of values. A critical Q-value is determined based on the number of samples in the group and the desired confidence interval. If the Q-value is greater than the critical Q-value then the value will be rejected.
STATEMENT OF DATAQUALITY
The measurement of accuracy available at this time is the quality control and matrix spike results. For sera data, the accuracy (the observed amount in the QC and MS samples, divided by the amount spiked, expressed as a percent) was found to range from 74.1% to 126%; while
precision, expressed as the standard deviation of the recoveries, was found to range from 2.14%
to 9.56%. For liver data, the accuracy was found to range from 72.6% to 141%; while precision
was found to range from 2.1 1Yoto 5.51Yo.
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The protocol and method state that 213 of all QC and a minimum of YZ of QC at each level must
be within 75% - 125% criteria. All three of the liver "QC-1Oppb" spikes exceeded the stated
criteria, therefore the liver data reported in the low range of the curve (Day 0 samples) may be biased high. Since all study samples that were not "Day 0" show analyte levels significantly above the low range of the curve, the overall impact (or bias) on data is minimal or none at all.
REFERENCES
1. Wildlife International, Ltd. Protocol No. 454-108 "PFOS: A ReproductionStudy with the Northern Bobwhite".
2. Wildlife International, Ltd. Protocol No. 454/120700/QR/SUB454 (3M Environmental Laboratory Project Number U2723) "PFOS: A Reproduction Study with the Northern Bobwhite".
3. Centre Analytical Laboratories, Inc. Study 023-044, `Validation of Analytical Methods "Extraction of Potassium Perfluorooctanesulfonate or Other FluorochemicalCompounds From Serum for Analysis Using HPLC Electrospray/Mass Spectrometry" and "Extraction of Potassium Perfluorooctanesulfonate or Other FluorochemicalCompounds From Liver for Analysis Using HPLC Electrospray/Mass Spectrometry in Quail Serum and Liver."
4. 3M EnvironmentalLaboratory Standard Operating Procedure ETS-8-231.1, "Solid Phase Extractionand Analysis of FluorochemicalCompounds form Biological Matrices".
LISTOF A~ACHMENTS
0 Attachment A: Extraction and Analytical Method Attachment B: Data Summary Tables
0 Attachment C: Sample Chromatograms, Calibration Information, and Instrument Parameters 0 Attachment D: Sample PreparationSheets 0 Attachment E: Study Protocol, Protocol Amendments, and Deviations
Attachment F: Example Calculations
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SIGNATURPEAGE
We certify that this report is a true and complete representation of the data for this study:
Lisa A. Stevenson Principal Analytical Investigator
Date
William K. Reagen Laboratory Management
Date
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ATTACHMENTA: EXTRACTIOANND ANALYTICAML ETHOD,ETS-8-231. I ,
"SOLID PHASE EXTRACTIOANND ANALYSISOF FLUOROCHEMICAL COMPOUNDS FROM BIOLOGICAMLATRICES"
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Method Solid Phase Extraction and Analysis of Fluorochemical
Compounds from Biological Matrices Method Number: ETS-8-23f.f Adoption Date: / / / / 3 / $ 1 Revision Date: ~ / L ? / O L EffectiveDate: 3/18/62
Approved By:
Laboratory Manager
ETS-8-231.1
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1 ScoDe and Atmlication
This method describes the extraction of target malytes from fish. rat liver, rat sera. mouse liver, and mouse sera using solid phase extraction (SPE). This method may also be extended to other biological matrices provided that the data quality objectives are met.
2 Method Summary
An amount of biological miterial. detemunedby the analyst. is prepared (fluidsdiluted and tissues lioinogenized)at a lih dilution, or other dilution as determined by the analyst using reagent grade water. An aliquot of the dilutioili'homogenate is spiked with the appropriate surrogate or analyte mixture. Acetonitrile (ACN) is added 3s an extraction solvent and also serves to precipitate the proteins. The saniple is capped. mixcd. and put on the centrihge to clarif?rthe supernatant, The supematant is transferred to a clean hibe. diluted with water, and passed through a pre-
conditioned CIKSPE cartridge. Finally, the analytesof interest are eluted from the SPE cartridge and analyzed by high
performance liquid chromatographyelectrospraytandem mass spectrometry(HPLC-ES/MSiMS).
3 Definitions
3.1 Dilution
A dilution expressed as 1.5 or 16! is deffiiedas: 1 niL of sample + 5 m L s of diluent for a total o f 6 n L s combined, unless otherwise noted.
3.2 SPE cartridge
A colunin containing an open solvent reservoir at one end and packed with bonded silica sorbents at the other end. It is designed to retain the compounds of interest under wnie solvent conditions and elute them wider others. A separation is thus achieved; compounds C N ~be removed from difitcult biological matrices and introduced into appropriate solvents for analysis.
3.3 Reagent grade water
Water with no detectable concentratiods) of the target analyte(s).
3.4 Quality control sample
Sample used to monitor the exhxtion efficiency (as a nutrix spike)and to veri@ the continued accuracy of the initial calibration cwve (as a continuing calibration verification).
4 Warnings and Cautions
4.1 Health and Safety Warnings
Always wear appropriate gloves, eyewear, and clothing when working with solvents, samples andior equipment. Use caution with die voltage cables for the probe. When engaged, the probe employs a voltage of approximately 5000 volts.
4.2 Cautions
Take care not to allow the SPE column to run to dryness afler the methanol and water washes. Afler washing is complete. add sample then allowall ofthe liquid to pass through the SPE column to dryness.
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UO not operate solvent pumps above capacity of400 bar (5x00 psi) back pressure. If the back pressure exceeds 400 bar, the HPLC will initiate automatic shutdown. Jh not mn solvent punips to dryness.
5 Interferences
To niininiize interferences,Teflon should not be used for snmple storage or any part of instrunentationthat comes in contact with the sanipleor extiact.
6 Instrumentation, Supplies, and Materials
The following instrunlentation, supplies. and materials are used while performing this method. Equivalent instmrnentiltioii. supplies. and nuterials niay be used in place ofthose listed.
6.1 Instrumentation
Vortex mixer, VWR, Vortex Genie 3 Ultia-Turrax T25 tissue homogenizer \iacuun Pump SPE Extraction Manifold Cenhihge. Mistral 1000or IEC Shaker, Eberbach or VWR Balance (+!- 0.1000 g) Micromass. QuattroI1 or Ultima h<pk quadnipoleMass Spectrometerequipped with an electrospmy ionizihon source HPl 100or Agilent low pulse solvent pumping system. solvent degisser. column compartment.and autosampler
6.2 Supplies and Materials
Eppendorf or disposable pipettes. plastic or glass Dissecting scalpels
Polypropylene bottles, capable ofholding 50 mL to I L (Nalgene)
Volumetric flasks, glass. type A
40 i d glass vials (ICHEM)
Plastic sampule vials, Wheaton, 6 i d (or other appropriate size) Centrifuge tubes, polypropylene. 15 mL and 50 mL Lnbels (kaduated pipettes; glass Syinges. capable of measuring 5 pL to 1000 pL Bottle-Top Dispenser (capable of dispensing 51nL of solvent) SPEextraction cartridge, 1 g, Sep-Pak 6 cc tri-fiuictional Clx(Waten) 75 mL samplereservoir (or otherappropriate size) C h i p cap glass autovials and caps
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Crimpers HPLC analytical column, specifics to be determined by the analyst and documented in the raw data.
7 Reagents and Standards
Reagent grade water. Milli-QT",Nanopwe 11. or equivalent Acetonitrile. HPLC grade or equivalent Methanol, HPIX _-de or equivalent Ammonium acetate, reagent gmde or equivalent Biological fluids or tissues. frozen from supplier
7.1 Reagents preparation
2.0 n M annionium acetate solution: Weigh approximately 0,300 g ammonium acetate. Pour into a 2000 inL volumetric container containing reagent grade water. mix until all solids are dissolved, bring to volume wing reagent grade water. Store at room temperature. Note: When preparing different volurnes than those listed in reagents preparation. target analyte standard preparation, and surrogate stanhrd piqmation, adjmt accordingly.
7.2 Target analyte standard preparation
Prepare target analyte standard(s) for the standard curve. Multicomponent analyte standards are acceptable. The following is an example only and nmy or may not be appmpriate for all standard preparations. Weigh approximately 100 mg of target analyte into a 100 niL voluinetric flask and record the acturtl weight in the standard logbook or other appropriate location
Bringto volume with methanol for a stockstandard ofapproximately 1000ppm (pghiiL). Dilute the stock solution with methanol for a working standard I solution of approxinlately 50 ppm. Example calculation: 1000 pg'mLx 5 nlLil00 i d = 50 p&nL. Dilute working standard 1 with methanol to produce a working standard 2 solution of approx 5.0 ppm. Example wlculation: 50 pg/mL x IO mL!lOOniL = 5.0 pg`mL. Dilute working ,standard 1 with methanol to produce a working standard 3 solution of approx. 0.50 ppm. Example calculation: 50 p g h L x 1.O niLil00 mnL =0.5 pginiL.
7.3 Surrogate standard preparation
Prepare surrogate standard(s). The follo\ving is an example only and nlay or may not be appropriate for all surrogate standard preparations. Weigh approximately 90-I I O ing of surrozate standard into a lM)-mL volumetric flask arid record the actual weixht. Bringto volume with niethanol for a surrogate standard stock ofapproxirnately900 - 1100ppm. Prepare a surrogate standard working standard. Transfer approximately I mL of surrogate standard stock to a IO-nL volumetric flask and bring to volunie with methanol for a cvorking standard of 90-110ppni. Record the actual volume transferred and standard concentrations in the standards logbook or other appropriate location.
7.4 Internal standard preparation
Prepare internal standard(s). The following is an example only and may or [nay not be appropriate for all internal standard prepantions. Weigh approximately 90-1I O mg of internal standard into a 100-mL volumetric flask and record the actual weight.
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Bringto volume with methanol for an internal standard stock of approxinutely 900 - I 100ppm.
Prepare ui internal standard working standard. Transfer approxinlately 1 n L of internal standard stock to a 10-1nL volumetric flask and bring to volunie with methanol for a working standard of90-1 IOppm. Record the actual volume tnnsfmed and standard concentrations in the standards logbook or other appropriatelocation.
8 Sample Handling
All saniples are received kozen and must be kept frozen until the extraction is performed. Allow samples to thaw to rooni temperature prior to extraction Typically fresh matrix staiulards are prepared )pith each analysis. Extracted stai~hrdsand samples are stored in capped autovials until miilysis. If arlalysis will be delayed, extracted standardsand sanlples nmy be refiigerated at approximately4C indefinitely or may be stored at rooin temperature until analysis can be perfonned.
9 Qualitv Control
9.1 Blanks
9.1.1 Solvent Blank
An aliquot ofniethanol is used as a solvent blank. Solvent blanks are not extracted.
9.1.2
Method Blank
An aliquot of I .0 mL of mter. or other appropriateamount. is used as a method blank. Four niethod blanks are extracted and analyzed with each set following this procedure (two are spiked with surrogate and hvo are not spiked).
9.1.3 Matrix Blank
An aliquot of 1.0inL or 1.0g ofinatrix (diluted or homogenized)is used as a nlatrixblank. Other amountsn t ~ bye used. as appropriate. Matrix blanks are prepared from one of three sources: I ) a study control nmtiix from a study control aniinal received with a sample set; 21 a conunercially obtained simple of the same species as the study aniinals; or 3) a sunogate matrix, also obtained commercially, but o f a different species than the study animal. (eg. if rat is used to generate standard curves and C'CVs for a mouse study). The nlatrix to use is dependent on the nlatrix used for the curve.
9.1.3.1 Study control matrix curve - ifthe study control matrix is used for the curve. prepare four (4) nmtrix blanks
using the study control matrix (two spiked with surrogate a i d two not spiked).
9.1.3.2 Coinnierciallyobtained (samespecies) nlatrix cuive - if the commercially obtained nutrix is used for the
curve. prepare four (4)matrix blanks using the same coniinercially available matrix (t\vo spiked with surrogateand two not spiked).
9.13.3 Surrogate nmtrix curve- ifa surrogateimtrix is used for the curve. prepare four (4) matrix blanks wing the
same cotnmetdly availablematrix and prepare four (4) matrix blanks using a conunerciallyavailablematrix of the Same species as the study animals (twospiked with surrogate and two not spiked).
9.13 . 4 If limited matrix is available.the number ofmethod and matrix blanks m y be adjuyted and will be noted in
the study protocol or in the raw data.
9.2 Sample Replicate
Samplesreplicatesare prepared accordingto each study protocol or pro.iect outline
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9.3 Surrogate standard
If suiTogate standard is a component of the study, all samples arc spiked with surrogate standard prior to extraction to obtain a concentration in the mid-range of the calibration cuwe. with the exception of blank sample above.
Typically surrogate standard is spiked into the 1.0 niL dilutedhomogenizedsample removed for extraction. However, surrogate may be spiked directly into the matrix prior to diluting with water. into the dilutedhomogenized saniple prior to removing the 1.01 n L sample, or into the 1.0n L dilutect'homogeaizedlsample removed for extraction.
9.4 Internal standard
If intermil s%indardis a component of the shidy, dl samplesare spiked with internal standard after extraction to obtain a concentration in the mid-range of the calibration curve.
Typically internal standard is spiked into the 2.0 mL of extract in the 15 mL centrifuge tube, before transfemng to the autovial.
9.5 Lab Control Sample
L,ah control samples are not a coinpoilent ofthis method.
9.6 Quality Control (QC) Sample
Prepare quality control (QC) saniples to monitor extrnction eficiency and to veri@ the continued accuracy of the initial calibration curve. Typically 1.0 mL. or other appropriate amount, of the same matrix used to prepare the initial calibration curve is used for each QC sample.
Twelve (12) quality control samples (QC) bill be prepared for each matrix during the course of a study. A niuiinium of 3 QC samples must be prepared (one at each level) on each day of sample extraction. (e.g. If the study is such that samples will be extracted on three direrent days then four QC samplesmust be prepared on each day of extraction for a total oftwelve.)
QC samples will consist of four samples at each of three levels of analyte. The levels listed below may he used and may represent sample concentrations diluted into the range of the calibration curve:
Low level: 3X to SX the LLOQ,
Mid-level: equivalent to a point near the middle of the calibration curve.
High level: 8G"hof the LXOQ
Two QC sample levels are anal)zed after eveT tenth sample injection starting after the last calibration standard injection, with a minimum of three QC: per analysis. Solvent blatks are not considered samples but may be included as such for determining when QC samples will be analyzed.
QC saniples extracted with a particular sample set must be analyzed in the same analytical run. Any QC samples extracted diuing the course ofthe study may be included in subsequentanalyses.
If sarnples fiorn rnultiple extraction dates are analyzed in one analytical run. then QC: samples from the same saniple eutr'action dates niust be included in h t analysis.
Each is expected to show an accumcy of 75-125Yiofexpected. A minimum of 213 of all QC:samples must meet this criteria, and a minimum of 1 2 of the QC samples at each level must meet this criteria. If not, the set must either be re-analyzed or re-extncted.
9.7 Sample Dilution
Any sample with an area greater than that ofthe highest acceptable standard wIll need to be diluted into the range of the calibration curve. If srtniplesare diluted into the range of the curve during analyses and enough sample remains, a post-run dilution validation will be performed to veri@ saniple values.
To peilbnn the dilution validation one sample will be separated into two representative samples (Le. two I .O inL aliquots for fluid sctniples or two 1.0 &ramamounts for tissue samples. or other amount x determined by the analyst
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and documented in a note to tile) then diluted using two procedurcs. The first procedure comists of diluting the sarnple with additional matrix prior to extraction (fluid adding fluid). while the second procedure consists of diluting the extract with solvent postcxtraction (methanol extract adding additional methanol solvent.)
If the relative peicent direrence is not within 15% for these two samples: additional testing will he required to deteimine which value is a cortect representation of the sample concentration.
10 Calibration and Standardization
10.1 Instrument Calibration
One calibtation cuve mi11 be prepared from extracted matrix standards. in the sane matrix asthe samples, per study. It will consist of a ininununi of nine (9) levels. Additional calibration curves may he extracted on separate sample extraction dates, as determined by the analystand documented in a note to file.
Transfer 1.0 nL. or other appropriate mount. of diluted control fluid or homogenized control tissve to a 15 mL centrifuge hibe using a disposable plastic pipette. This will he repeated while preparing aliquots for the standard curve. Be suc to nliv or shake the control matrix container between aliquots to ensure a homogenous sample is
removed.
Record each standard volume on the weight/volumes sheet or extraction worksheet as appropriate,
Four I .O ILaliquots,or other appropriateamount, of control nlatrixserve as imtrix blanks.
The standard concentrations and spiking amounts listed in Table 1 nlay be used, hhen appropriate, to spike one standard cin-ve. A total o f 9 standards, four matrix blanks. nnd four nietliod blaiks are prepared in addition to the QC sanples and test samples. The nuniber of staticlards and blanks nlay be adjusted as determined by the analyst and documented in a note to file.
Use Attachment C. or other appropriate fonn. as ai aid in calculating the concentrationsof the working standards. Refer to section 12 to calculatethe actual concentration of analyte in each calibration standard and QC; sample.
Typically the target amlyte standard is spiked into the 1.0 mL dilute&holnogcnized sample removed for extraction. Homcver, it may be spiked directly into the matrix prior to diluting With water. into the diluted/homogenizedsample piior to removing the 1.0 mL sample,or into the 1.0 mL diluted!homogeni7rd sampleremoved for extraction.
Analyze the extracted matrix standard curie prior to each set of extracts. The curve equation will be deterniined by regression analysis using the peak areas ofthe target analyte(s)using MassLynx or other suitablesoftware.
Any level outside 75% - 125%of nominal must he deactivated,and regressionrecalculated. except the LLOQ which must be within 30% ofnominal. All levels mitit show a response @eaterthan twice that ofthe blank. A maximum of three (3)levels may be deactivatedin any one set, or the set \ d l be re-analyzed.
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Working standard (approximlte concentration)
0.500 ugimL 0.500 ug/mL 0.500 ug/mL 0.500 u g h L 0.500 u&iL
Approxinute final
Approximate final
ILL
concentration ofanalyte concentration ofanalyte
in Matrix diluted 1:s in Final 2.0 mL volume
Blnnk
Blank
1.5
5.00 n g g or ng/niL
0.375 ngimL
3.0
10.0 ngig or ngniL
0.750 ngimL
I 8.0
25.0 npig or n,@niL
16 I 50.0ng/g or n @ n L I
32
I 00 ng/g or ng/mL
2.00 nginiL 4.00 ng'mL 8.00 &mL
I I I 50.0 uginiL
1750ngig or ngirnL I
Surrogate Std 100 uginiL
10
6500 ngig or ngimL
11 Procedures
150 ng'niL 500 n@mL
11.I Tissue Sample Preparation
Obtain fiozen tissue samples
Cut approximately 1.COO0 g of tissue (+i-0.1ooO g), or other appropriate amount. using a dissecting scalpel. This part ofthe procedure is best performed quickly,not allowing the tissue to thaw.
Weigh the tissue directly into a tared plastic sunpule vial.
Record the weight on the weight~\duinesheet. cxtraction worksheet. or other appropriate location.
Return unused tissue to the freezer after extraction amounts have been renioved.
Add 2.5 n L of reagent water to sampule vial. or other volume as detennined by the analyst and documented in a note to tile.
Homogenize the sample. hit the Ultia-Tunax grinder probe in the sample and grind for approximately2 minutes, or until the sample is homogeneous. Rinse the probe intothe tube containingthe smiple with 2.5 nlL ofreagent grade water. or other volume as determined by the analyst and documented in a note tu file. using a pipette.
Take the grinder apart and clean it with methanol after each snmple. Refer to ETS-9-52 for more infommtion.
If an amount other tltm 1.0ooO g (not within +i-0.1000 g) is removed for an initial weight. adjust the water volume accordingly to maintain a li6 dilution. (e.g. if 0.5 g is removed for extraction.add a totd of2.5 mL of water.). or other ixtio as determined by the analyst and documented in a note to file.
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11.2 Fluid Sample Preparation
Obtain frozen fluid sample and allow it to thaw at room tenipeiatureor in lukewaiin watcr.
Label a IS niL polypropylene centrifuge tube with the study number, saniple ID, extraction date and analyst initials. See attached worksheet (AttachmentA or similar worksheet) for documenting the remaining steps.
Vortex mix the fluid sample for approxinutely 15 seconds. then transfer 1.0 mL of fluid, or other appropriateamount to a plastic snnipule vial, or other appropriatecontainer.
Retuni unused samplesto freezer after exhaaction miounts have been removed.
Add 5.0 niL of reagent water to the 1.0 mL of fluid for a I,% dilution, or other dilution as deterniined by the analyst and documentedin a note to file.
Ifa volume other tlian 1.0 n L is removed for ai initial volume. adjust the mater volume accordinglyto nuintain the sanie dilution as above.
11.3 Tissue and Fluid Sample Extraction
After tissue or fluid sampleshave been prepared accordingto sections 11.1 and 11.2,vortex mix or shake by hand the dilutedhoniogenized sample for approximately 15 seconds then transfer 1.0 mL, o r other appropriate volume. to ;i clean 15 mL polypropylene centrihge tube.
Retuin unused dilutedi'hoinogenizedportionsto the fieezzr after extraction amountshave been removed.
Record the volume removed on the extractionworksheet, (Attachment A or similar worksheet).
Spikeblanks. samples,and standards. ready for extraction with surogate standard as described in this method
Spike each calibration standard nutrix with the appropriate amount of standard as described in this method for thc calibrationcurve standards and each QC sample.
Vortex mix the stindad curve samples and QC samples for approximately 5 seconds.
To each sample aid standard. add 5.0 i d of acetonitrile. cap. and vortex mix or shake by hand approximately 15 seconds.
Place all samples on the shaker at an appropriate speed for 20 minutes to adequately mix (a setting ofapproxinxitely 300 rpm on the n i d e l s listed in section 6. I ).
Remove from the shaker and centrihge at an appropriatespeed for 10 minutes to adequately pellet the precipitate (a setting of approximately2000 rpni on the models listed in section6 .I ).
Add 40.0 i d , of reagent gnde water to a clean SO id centrifuge tube. Remove samples fiom the centrifuge and decant the supernatant into the water in the SO mL tube, taking care not to introduce any of the matrix solids into the solution. Cap and mix by inverting several times. In this step the order of addition may he changed (i.e. the s`mple nxiy he put into the centrihge tube and then the water added). Attach the reservoir to the SPE cartridge and attach this reservoirkartridgeunit to a ~acuummanifold.
NOTE: When runningthe vacuum. set the vacuum chamber at approxinuitely 15kPA - t o give an approxinute elution flow of 5-7 mLimin. Flows may vary through cartridges and the kPA may be raised fix slow tubes and drying after most have been drawn doun.
Prepare the SPE cartridge by washing twice with approximately 5.0 niL of methanol, followed by approxinutely two 5.0 niL aliquotsof wter. taking care not to allow the columnto run to dryness after each wash.
After washing is complete, pour the sample into the resewoiricartridge unit and allow all of the liquid to pass through the column to dryness.
Run the vacuum on hi& for approximately 5 minutes to adequately dr);each SPE cartridge.
Place a collection 15mL polypropylene centrihge tube under each cartridge and elute with 2.0 mL ofnietlanol.
Spike extracted blanks, samples,and standruds l i t h internal standard as described in this method.
ETS-8-23 I. 1 Solid Phase Extraction and Analysis of Fluorochemical
Compounds from Biological Matrices
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Label each glass autovial. as appropriate. with the study number, vial file archive number. aninml iiumberlgenderitirnepoint or LIMS number. matrix, final solvent, analyte components (if needed). extraction type. extraction date. and analyst(s) performing the extraction.
Transfereach eluant to a glassautovial and cap.
11.4 Extract Analysis
1I.4.1 Software set-up
On the MassLqnx main page. set up a saniple list name. Save the list as instruinent designator letter, last 2 digits of
test year-month-day.and a letter that will increasethrough the alphabet with each additional list for that day.
Example Sample List: IWMMDDa or A0202Ma
1 =Initial ofthe instmnient nanie (A = "Amelia")
YY = Test year (02)
MM = Test month (02)
DD = Test day (04)
a = First sample list (run) ofthe day (the next saniple list will end with 'V.the next IC',
and so on.)
Assign a filenanie using the instrument designator letter, the last 2 digits of the test sequential file nuniher that starts with 1and increasesby one for each filename.
-month-day. and a 3-digit
Example filename: IYYMMDDi#Mlor A0202W001
I =initial of instrumentname
YY = Test yea1
MM = Test month
DD = Test day
##i: = 3digit sequential file number starting with 1 through 999 (001)
Also. as part ofthe saniplelist, assign a method (MS) for acquiring. an inlet file. a bottle number, an injection volume, and sample descriptions.
To create a method. click on Method Editor button in the MS Status Pane and select SIR (Single Ion Recording)or
MRM [Multiple Reaction Monitoring). Set Ionization Mode as appropriate and imss to 4'99 or other appropriate mass(es). Also set the acquisition start and stop times. Swe acquisition method. If MSiMS instruments are employed. additional product ion fragmentationinformation may be collected. See Micronlass MassLynx "Guideto Data Acquisition" for additional infornution on MRM.
Typically the analytical batch nin sequence begins mith system suitability. solvent blanks, and a set of extncted nmtrix stiindards.
Sample extracts are analyzed with two QC samples injected after every tenth saniple injection. Solvent blanks should he analyzed periodically to monitor possible analyte carryover and are not considered sample extracts but may be included as suck
ETS-R-73I. 1
Solid Phase Extraction and Analysis of Fluorochemical Compounds from Biological Matrices
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11.4.2 HPLC set-up
Set up sample tmy accordingto the sample list prepared above. Set up the HPLC to the following conditions or at conditions the analyst consideis appropriate for optimal response. Record actual conditions in the instrumentlogbook, or other appropriate location: Sample size = 10pL injection 1n.ject'saniple= 1 Cycle time = 10.0minutes Flow rate = 300 @min Mobile phase: Solvent A = 2 niM Animonium Acet1te. Solvent B = Methanol Solvent Fadient program:
I .oo
10%
I
I
I
11.' 3 Instrumen set-up
Refer to ETS-9-24, "Operation and Maintenance of the Micromass Quattro I1 Triple Quadrupole Mass Spectrometer Fitted with an Atmospheric Pressure Ionkition Source." for details. Check tlie solvent level in HPLC reservoirs 'and refill if necessluy. Check the stainless steel capillaiy at the end ofthe probe. Use an eyepieceto check the tip. The tip should be flat with nojagzed edges. Ifthe tip is found to be unsatisfactoiy, disassembletlie probe and replace the stainless steel capillaiy.
T u n on the nitrogen. Open the tune page. Click on operate to initiate sowce block and desolvation henters. Open the Inlet Editor. Download the HPLC method and initiate solvent flow to begin system equilibrium.
Set the flow to 1C-SOOuLhnin or as appropiiate
Set HPLC pump to "On" Observe droplets or inist corning out ofthe tip ofthe probe. A fine mist should be
expelled with no nitrogen leaking around the tip of the probe. Readjust the tip ofthe probe if no mist is observed Allow to equilibrate for approximately IO minutes lypical instrument parametersinclude: Drying gas 250-100 litersihour ES nebulizing gas IC15 literdhour
ETS-8-23I. 1 Solid Phase Extraction and Analysis of Fluorochemical
Compounds from Biological Matrices
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HPLC constant flow mode. flow rate 10-500 pLimin Pressure 400bar (this paranieter is not set. it is a guide to ensurethe
HPLC is operating correctly.) Source block temperature approximately 150C Desolvationtemperature approximately250C These settings inay change in order to optimize the response Print the tune page. sample list, and acquisition method from MassLynx and store it in the study binder with a copy taped into the inaumcnt log. Click on start button in the Acquisition Control Panel (the location of the start button may vary aniong MassL~mx versions, refer to appropriate MassLynx User's Guide).
12 Data Analvsis and Calculations
12.1 Calculations
If other calculations are used than those listed. they will be docuinented in the raw dah.
Calculate the matrix amount contained in the initial dilution using the following equation: IW (g) (or 1V (niL))
Matrix Amount (gimLor mLimL) = (IW(g) (or IV(mL))+ DV (mL)
Calculate actual concentrations ofanalyte in calibration standardsusing the followingequation:
Concentration (ngig or ng/mL) = Spike Concentration (ug/mL) x Spiked Amount (mL) X- 1000ng
SV (mL)xMatnx Amount (gimLor mLimL)
1 ug
IW = Initial wei@t (where 1.Og = 1.0 mnL ) IV = Initial volume DV = Diluent volume (reagentgade water)
SV = Sample voiuine removed for extraction (typically i.0 mL) AR = Analyticalresult from MassLyx summary DF =Dilution tictor
FV = Final volume
MA =Matrix amount
3 curve = MA oftissueiflnidstandard curve. assiimed to be I g or 1 m i 5 mL water 3 sample = MA oftissue/fluidsample L g or mL of samplei5 mL water)
Calculate spike percent recoveries using the following equation: % Recovery = Observed Result - Matrix Blank Result x 100
Spiking Level
ETS-8-23 1.1 Solid Phase Extraction and Analysis of Fluorochemical
Compounds from Biological Matrices
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Calculate relative standard deviation using the following eqilation:
Standard Deviation
Relative Standard Deviation =
x I00
Mean
Calculate percent deviation using the following cquation:
Expected Conc. -Calculated Conc.
%, Deviation =
x 100
Expected Conc.
Calculate actual concentration of analyte in fluid @g/mL):
AR (ngiid) x DF x d curve (&nL) x FV (mL)in Curve x
sample(mL/mL) FV (inL) in Matrix 1000ng
= (pg'g)
Calculate actual concentration ofanalyte in tissue (ldg): AR (ng'g) x DF x (3 curve IdmL) X FV hnL) in Curve X
r) sample (g/nL) FV (nL) in Matnx
].ou9 1000 ng
= (pgg)
13 Method Performance
13.1 System Suitability
System suitability will be determined prior to the start and at the completion of each walytical run. Prior to the wlibrdtion curve and after the last sainple of the run t h e e (3) mid-level unextracted culibmtion standards will be analyzed. As applicable, the peak area precision. retention time precision, resolution, and peak asymmetry will be monitored at the beginning and the end ofthe nm separately. The peak area precision must be equal to or less than 5,0% RSD. the precision of the retention time inust be equal to or less than 2.5% RSD. the resolution must be >: 2.0, and the peak asynnxhy (fionting or tailing) mwt be 0.5<AF<2.0.ubere AF is the asynunetry factor.
If any item of the system suitability fjils, system miiintenance must he completed prior to running a second set of system suitability samples and the system suitabilitymust pass before starting the calibntion. If system suitability fails at the completion ofa nm. the saniple set niust be reanalyzed.
13.2 Quantitation
The coeffcient of detemination value for the calibration curve, plotted by regression using the peak areas of the mlyte(s). must be 0.990 or better.
All active calihration curve points must be within 25% of the theoretical value with the exception of the LOO point, which may deviate up to 30%.
Calibration standards with peak areas less than two times the curve matrix blank will be deactivated to disqualify a data range that may be affectedby background levels ofthe analyte.
A valid calibration curve must contain at least 6 active points above and including the LOQ.
Ifthe curve cannot meet these criteria, the sanipleset must be reanalyzed or reextracted.
13.3 Accuracy
Two thirds of all qilality control samples and 1/2 of each quality control sample at each level are expected to show an accuracy of 75- 125"/0.
ETS-8-23 1.1 Solid Phase Extraction and Analysis of Fluorochemical
Compounds from Biological Matrices
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Surrogates and internal standards must have a percent deviation < 50%. Deviations outside this range will be re'malyzed to confirm. If the second analysis confirms the original, the deviation wll be documented in the raw data. Ifthe second analysis is within 50%. then the second value will replace the original value.
14 Pollution Prevention and Waste Management
Sample waste is disposed of in noninfectiousbiohazard waste containers.
Flammable solvent waste is disposed of in high BTU containers.
Glass pipette waste is disposed of in broken glass containers located in the laboratory
15 Records
Complete the extraction worksheet attached to this method. or other applicable worksheet,and store with the studyraw data. Each page generated for a study must contain the following infomation (if applicable): studyiproject or instrument number, acquisition method, integration method. sample name, extraction date. dilution factor (if applicable). and analyst. Other information nlay be added ifapplicable to the study. Print the tune page. sample list, and acquisition method from MassLynx to include with the study raw data. Copy these pages and tape into the instrumentnmlog. Plot the calibration curve by the appropriate regression. Print these graphs and store with the study raw data. Print data integration summary, integration method, and chrom1toganxs from MassLynx and store with the study raw data. Sumnnl;trize data using suitable s o h e (Excel7.0 or LIMS) and store in the study folder. Back up electronic data to appropriate medium. Record in sTudy notebook the file m n e and location of haclcup electronic data.
16 Attachments
Attachment A Extraction Worksheet Attachment B: Sample WeighUVolune Worksheet Attachment C, Calibration Standard Concentration Worksheet Attachment D, Dilutions Sunlnlary Worksheet
17 References
ETS-9-24, "Optxition and Maintenance of the Micromass Quattrn I1 Triple Quadrupole Mass Spectrometer Fitted with an Atmospheric Pressure Ionization Source" ETS-Y-52, "Operation and Maintenance ofa Tissue Grinder"
18 Affected Documents
None
ETS-8-23 1.1 Solid Phase Extraction and Analysis of Fluorochemical
Compounds from Biological Matrices
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19 Revisions
Revision Number
1
Revision Descrintion Minor formatting changes. Added detailed iuforniation to all sections concerning the extraction procedure, analytical procedure. and calculations. Added c~tttachmentsand references.
Revision
Uatt: 0211 Ki02
ETS-8-231.1 Solid Phase Extraction and Analysis of Fluorochemical
Compounds from Biological Matrices
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Study Number: Prep Date: Analysts initials: Box#:
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A ReproductionStudy with the Northern Bobwhite
Attachment A - Extraction Worksheet
Method Revision:ETS-8-231.1 Matrix:
Sample Timepoint:
Blank matrix
TN-A-
: Amount weighed/aliquoted:
g/mL
1. Homogenize sample
2. Aliquot 1 mL of diluted matrix into 15 mL polypropylene tube
3. Spike samples accordingly
4. Add __ mL of ACN (TN-A--
) to each diluted sample and shake or vortex mix
5. Shake sample for 20 min Q
rpm (Shaker
)
6. Centrifuge sample for 10 min @I
rpm (Centrifuge
)
7. Add 40 mL of
water to 50 mL polypropdene centrifuge tube.
8. Decant extract Into centrifuge tubes with water 9. Shake sample slightly lo ensure proper mixing
10. Attach 6 mL C18 SPE cartridges and 75 mL reservoirs to vacuum manifold
11. Condition wlumn with two washes of -5 mL MeOH (TN-A-______-___-) do not allow column to go to dryness
12. Wash column with two washes of -5 mL
water - do not allow column to go to dryness
13. Filter sample through conditioned column, discarding filtrate
14. Allow column to go to dryness. Afler dripping stops, draw a high vacuum through column for at least 5 minutes.
15. Elute column with solvent (
TN-A-
) into appropriate 15 mL centrifuge tube
16. Spike samples with
uL of internal standard t#
, conc.
17. Transfer sample into appropriately labeled autovlal and cap
Note: In vacuum steps above set the vacuum chamber at approximately 15 kPA - this should give approximately 5-7 mLlmin elution flow Flows may vary through cartridges - kPA may be raised for slow tubes and drying after most have been drawn down and shut off.
ETS-8-23 1.1 Solid Phase Estraction and Analysis ofFluorochemica1
Compounds from Biolopical Matrices
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Prep Date(s): AWdlySt(S): Sample Matrix: MethodlRevision:
Sample ID
"......"
Attachment B - Sample WeightiVoluine Worksheet
Study Number: Equipment Number: Final Solvent & TN Number:
Initial
wt.nroi. g/mL/L
Water Volume added (mL)
Volume Removed
(mI,)
................
"
".... .".... .............
Comments
" ...........
" "......"_ ...... lil "."l_lll"." ...."
..............................................................
"......"..... ............ "._ ..........................................................................
.- ...................
~
............"..................."
.................
.......""...................................
... ......."....... ...."
" .- .....................
."........."
................................................................................................................................................................................................................................................................0
........................
..."".......
.................................. " "... ^" ""... ........... "..........
................................................................................................................................................................................................................................................................
..... "..............
"" "-".-.........".......I "
I
...
lllll.ll...."
"........." -
........................... " .......................................... "
1 -
............ "
"
~ ...............
" ...................
..
" ...................................................................
........... "..."".l. ........ "............ ._...........
..........."... "...............................................................................................
Fonn Coiiipietion Verified By:
ETS-8-23 1.1 Solid Phase Extraction and Analysis of Fluoroclmnical
Coinpounds from Biological Matrices
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PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A ReproductionStudy with the Northern Bobwhite
Prep date(s): Analyte(s): Sample matrix: MetLod/revision:
Attachment C: Calibration Standard Concentration Worksheet
Standard number: Equipment number: Final solvent and TN: Blank Tissue or Fluidhdentifier:
Analyte Std conc u@mL
All Ani't spiked
mL
All Final Volume: mL
All Initial Fluid Dilution
All Initial Tissue Deiisi ty g'mL
(1.1600
0.1600
0.1600 0.1600 0.1600 0. 1600 0.1600 0. I600 0.1000 0.1600 0 .I600 0.l600 0.1600
Calculated concentrationsofstruidxds in relation to the final 2.0 mL solvent and initial inatrix
2.0 mL Final Volume
Fluid Matrix
Tissue Matrix
Analyte Final
Surrogate Std conc
Analyte Final
Surrogate Std conc
Analyte Final
Surrogate Std conc
125
1500
1500
150
1750
I750
Solid Phase Extraction and Analysis of Fluorochemical Compounds from Biological Matrices
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PFOS: A Reproduction Study with the Nothern Bobwhite
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Study: Dilution I)ate/Analyst: Box Number:
Sample Number I
Attachment D: Dilutions Sunlmary Worksheet
Solvent/TN Number: Extraction DatelAnalyst: Matrifliniepoint:
Dilutions
Notes: 1/10 dilution =
of sample +
of solvent
Form Completion Verified By:
ETS-8-23 I . 1 Solid Phase Extraction and Analysis of Fluorochemical
Compounds from Biological Matrices
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ATTACHMENBT: DATASUMMARTYABLES
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Study number E01-1245 - QUAIL SERA DATA SUMMARY, BLANKS AND SPIKES
PFOS: A Reproduction Study with the Nothern Bobwhite
E01-1245-35766 E01-1245-35825 E01-1245-35825
1/31/2002 2/1/2002 2/1/2002
E01-1245-35767 E01-1245-35826 E01-1245.35826
1/31/2002 2/1/2002 2/1/2002
Water blank-day 1 Blank H2O-day2 Blank H20-day 2
quail sera blank-day 1 Blank quail sera-day 2 Blank quail sera-day 2
d020207031
0.05
40
1
10.0
400
400
d0202030 19
0.05
40
1
10.0
400
400
d020207035
0.05
40
1
10.0
400
400
d020207032
0.05
40
1
10.0
400
400
d020203020
0.05
40
1
10.0
400
400
d020207036
0.05
40
1
10.0
400
400
E01-1245-35768 E01-1245-35827
E01-1245-35827
1/31/2002 2/1/2002
2/1/2002
E01-1245-35769 E01-1245-35828
E01-1245-35828
1/31/2002 2/1/2002
2/1/2002
quail Sera MS-day 1 quail Sera MS-day 2 quail Sera MS-day 2
quail Sera MSD-Day1 quail Sera MSD-Day2 quail Sera MSD-Day2
d020207033
0.05
d020203021
0.05
d020207037
0.05
d020207034
0.05
d020203022
0.05
d020207038
0.05
Conc of PFOS in Sample (ng/ml) = (Inst conc(ng/ml)) x (additional dilution) x (dilution(di1utedsera))
dilution(di1utedsera) =final volume(mL)/amount of sera in diluted sample(mL) = 2.0 mU0.05 mL= 40 amount of sera in diluted samule = amount of sera used.
40
1
225.29
400
40
1
254.33
400
40
1
227.43
400
9012 10173
9097
40
1
217.03
400
40
1
254.55
400
40
1
219.54
400
8681 10182 8782
for both ms and msd
I 3 avg % rec 92.84 std dev of % rec 6.980
avg conc. 9321 std dev of conc. 680.2
89.76 101.3 90.61
86.47 101.4 87.47
true value 10040 avg %rec 93.9 avg cone 9427
sld dev of cone 647.4
true value 10040 avg %rec 91.8 avg cone 9215 std dev of cone 839.0
3M EnEvxicrelo20n00mental Laboratory
Blanks QCs and MSs quail sera samples summary 030418.xls
printed: 4/18/2003, 8% AMPage 49
Report E01-1245
Study number E01-1245 - QUAIL SERA
Absolute Recoveries
PFOS: A Reproduction Study with the Nothern Bobwhite
E0l-1245-35780 01/31/2002 qc-25ppb-2.01-31-02 (1004 n&L diluted seraj d0202131M
0.05
40
EOl-1245-35781 01/31/2002 qc-25ppb-3,01-31-02 (1004 ng/mL diluted sera) d020213103
0.05
40
E0l-1245-36155 02/13/2002 ms-5ppb-l,02-13-02 (201 ng/mL diluted sera)
d020213104
0.05
40
E01-1245-36156 02/13/2002 ms-5ppb-2,02-13-02 (201 ngmL diluted sera)
d020213105
0.05
40
E01-1245-36157 02/13/2002 ms-5ppb-3, 02-13-02 (201 ng/mL diluted sera)
d020213106
0.05
40
E01-1245-36158 02/13/2002 ms-200ppb-1.02-13-02 (8032 ng/mL diluted sera) d020213107
0.05
40
E01-1245-36159 02/13/2002 ms-200ppb-2,02-13-02 (8032 ng/mL diluted sera) d020213108
0.05
40
E01-1245-36160 02/13/2002 ms-200ppb-3,02-13-02(8032 ng/mL diluted sera) dO20213109
0.05
40
Study number E01-1245 - QUAIL SERA
versus unextracted curve
E01-1245-35779 01/31/2002 qc-25ppb-1, 01-31-02 (1004 ng/mL diluted sera) d020405082
0.05
40
E01-1245-35780 01/31/2002 qc-25ppb-2, 01-31-02 (1004 ng/mL diluted sera) d020405083
0.05
40
E01-1245.35781 01/31/2002 qc-25ppb-3, 01-31-02 (1004 ng/mL diluted sera) d020405084
0.05
40
E01-1245-36155 02/13/2002 ms-5ppb-I, 02-13-02 (201 ng/mL diluted sera)
d020405085
0.05
40
E01-1245-36156 02/13/2002 ms-5ppb-2.02-13-02 (201 ngmL diluted sera)
d020405086
0.05
40
E01-1245-36157 02/13/2002 ms-5ppb-3,02-13-02 (201 ng/mL diluted sera)
d020405087
0.05
40
E01-1245-36158 02/13/2002 ms-200ppb-1,02-13-02 (8032 ng/mL diluted sera) d020405088
0.05
40
E01-1245-36159 02/13/2002 ms-200ppb-2,02-13-02 (8032 ng/mL diluted sera) do20405089
0.05
40
E01-1245-36160 02/13/2002 ms-200ppb-3,02-13-02 (8032 ng/mL diluted sera) d020405090
0.05
40
A = Not within +/-25% criteria
Conc of PFOS in Sample (ng/ml) = (Ins1conc(ng/rnl)) x (additional diluiion) x (dilution(di1utedsera))
dilution(di1utedsera) =final volume(mL)/amount of sera in diluted sample(mL) = 2.0mU0.05mL= 40 amount of sera in diluted sample =amount of sera used.
1
39.12
201
1
45.18
201
1
5.54
201
1
5.51
201
1
5 23
201
1
248.13
201
1
254.19
201
I
253.36
201
1
36.06
201
1
41.69
201
1
44.96
201
1
6.17
201
1
5.88
201
1
6.17
201
1
248.12
201
1
260.27
201
1
254.58
201
.=I"i" ,.,.c 1 1
1565
A
155.9
std dev 14.46
1807
A
180.0
%RSD 8.853
222
110.2
avg 108.0
220
109.7
std dev 3.403
209
104.1
%RSD 3.151
9925
10168
A
10134
A
123.6 126.6 126.2
avg 125.4 Std dev 1.636 %RSD 1.304
1442
A
143.7
avg 163.0
1668
A
166.1
std dev 17.97
1799
A
179.2
%RSD 11.03
247
122.8
avg 120.9
235
117.0
std dev 3.332
247
122.8
%RSD 2.757
9925
10411
A
10183
A
123.6 129.6 126.8
avg 126.7 std dev 3.027 %RSD 2.390
3M EnEvxicrelo20n0m0 ental Laboratory
Blanks QCs and MSs quail sera samples summary 030418.xls
printed: 4/18/2003, 8:53 AMPage 50
Report E01-1245
Study number E01-1245 - QUAIL SERA
versus extracted curve
QC Sample Recoveries
oriainal of all and rerun of 8ODDm
t0l-1245-35785 01/31/2002 qc-80ppm-1.01-31-02 (3227040 ng/mL diluted sera) d020201035
0.05
40
E01-1245-35786 01/31/2002 qc-80ppm-2, 01-31-02 (3227040 ng/mL diluted sera) dO20201036
0.05
40
E01-1245-35787 01/31/2002 qc-80ppm-2.01-31-02 (3227040 ng/mL diluted sera) d020201037
0.05
40
E01-1245-35779 01/31/2002 qc-25ppb-1, 01-31-02 (1004 ng/mL diluted sera) d020207044
0.05
40
E01-1245-35780 01/31/2002 qc-25ppb-2,01-31-02 (1004 ng/mL diluted sera) d020207045
0.05
40
E01-1245-35781 01/31/2002 qc-25ppb-2, 01-31-02 (1004 ng/mL diluted sera) d020207046
0.05
40
E01-1245-35782 01/31/2002 qc-40ppm-1, 01-31-02 (1613520 ng/mL diluted sera) d020207047
0.05
40
E01-1245.35783 01/31/2002 qc-40ppm-2, 01-31-02 (1613520 ng/mL diluted sera) d020207048
0.05
40
E01-1245-35784 01/31/2002 qc-40ppm-2. 01-31-02 (1613520 ng/mL diluted sera) do20207049
0.05
40
E0l-1245-35785 01/31/2002 qc-80ppm-I. 01-31-02 (3227040 ng/mL diluted sera) d020207050
0.05
40
E01-1245-35786 01/31/2002 qc-80ppm-2.01-31-02 (3227040 ng/mL diluted sera) d020207051
0.05
40
E01-1245.35787 01/31/2002 qc-80ppm-2,01-31-02 (3227040 ng/mL diluted sera) d020207052
0.05
40
Study number E01-1245 - QUAIL SERA
versus extracted curve
rF)n,n
E01-1245-35780 01/31/2002 qc-25ppb-2.01-31-02 (1004 ng/mL diluted sera) d020405083
0.05
40
E0l-1245-35781 01/31/2002 qc-25ppb-3. 01-31-02 (1004 ng/mL diluted sera) d020405084
0.05
40
E01-1245-36155 02/13/2002 ms-5ppb-1,02-13-02 (201 ng/mL diluted sera)
d020405085
0.05
40
E01-124536156 02/13/2002 ms-5ppb-2,02-13-02 (201 ng/mL diluted sera)
d020405086
0.05
40
EOl-1245-36157 02/13/2002 ms-5ppb-3, 02-13-02 (201 ng/mL diluted sera)
d020405087
0.05
40
E0l-124536158 02/13/2002 ms-200ppb-1,02-13-02 (8032 ng/mL diluted sera) d020405088
0.05
40
E01-1245.36159 02/13/2002 ms-200ppb-2,02-13-02 (8032 ng/mL diluted sera) d020405089
0.05
40
Eol-1245-36160 02/13/2002 ms-200ppb-3,02-13-02 (8032 ng/mL diluted sera) d020405090
0.05
40
E01-1245-36155 02/13/2002 ms-5ppb-I. 02-13-02 (201 ng/mL diluted sera)
d020410019
0.05
40
E01-1245-36156 02/13/2002 ms-5ppb-2.02-13-02 (201 ng/mL diluted sera)
d020410020
0.05
40
E0l-1245-36157 02/13/2002 ms-5ppb-3, 02-13-02 (201 ng/mL diluted sera)
d020410021
0.05
40
A = Not within +/-25% criteria
Cone of PFOS in Sample (ng/ml) = (Ins1conc(ng/ml)) x (additional dilution) x (dilution(di1utedsera))
dilution(dilutedsera) =final volume(mL)/amountof sera in diluted sarnple(mL) = 2.0 mU0.05 mL= 40 amount of sera in diluted sample = amount of sera used.
PFOS: A Reproduction Study with the Nothern Bobwhite
1MX)
95.65
400
1000
93.45
400
1000
85.75
400
1
26.99
400
1
27.89
400
1
31.52
400
100
299.0
400
100
316.2
400
100
306.4
400
1000
88.66
400
1000
85.99
400
1000
79.33
400
3826000 3738000
3430000
1080
1116
1261
A
1196120
A
1264880
1225440
3546400
3439600 31 73200
for all in original analysis (recovery avg%rec 101.5
I Std dev 19.89 I
118.6 115.8 106.3 107.5 111.1 125.6 74.13 78.39 75.95 109.9
106.6 98.33
avg 113.6 std dev 6.444 %RSD 5.674
avg 114.7 std dev 9.555 %RSD 8.327
avg 76.16 std dev 2.138
%RSD 2.808 avg 104.9
std dev 5.956
XRSD 5.676
1
28.49
201
1
30.78
201
1
3.85
201
1
3.65
201
1
3.84
201
1
177.0
201
1
186.2
201
1
181.9
201
1
5.19
100
1
4.64
100
1
4.62
100
1140 1231 154 146 154
7080 7447
7275 208
186 185
113.5 122.6
avg 111.3 std dev 12.51 %RSD 112 4
76.62
avg 75.22
A
72.64
std dev 2.243
76.42
%RSD 2.981
88.15 92.72
avg 90.48 std dev 2.285
90.58 103.3
%RSD 2.525 avg 95.85
92.34
std dev 6.437
91.94
%RSD 6.716
3M EnEvxicreol 2n00m0 ental Laboratory
Blanks QCs and MSs quail sera samples summary 030418.xls
printed: 4/18/2003. 8:53 AMPage 51
Report E01-1245
Study number E01-1245 - QUAIL SERA
PFOS: A Reproduction Study with the Nothern Bobwhite
t E0l-1245.28444
* E01-1245-28446 * E01-1245 28449
06/15/2001 06/15/2001 06/15/2001
t E01-1245.28451
06/15/2001
E0l-1245-28453
06/15/2001
t E01 1245-28456 06/15/2001
E01-1245-28458
06/15/2001
* E01-1245-28460 06/15/2001
t E01-1245-28462 06/15/2001
* E01-1245-28464 * E01-1245-28466
06/15/2001 06/15/2001
* E01-1245-28468 06/15/2001
* E01-1245-28470 06/15/2001
* E01-1245-28472 06/15/2001
* E01-1245-28474
06/15/2001
* E01-1245-28477 06/15/2001
* E01-1245-28479 06/15/2001
+Concentration <LOO
d020131055
04
40
1
454-108-330.Oppm female, adult, 01-31-02 -~ d020207059
40
1
d020131057
0 05
40
1
454-108-332, Oppm female, adult 01-31-02
d020207061
o5
40
1
d020131060
03
40
1
454-108-336, Oppm female, adult, 01-31-02
d020207064
40
1
-__________
d020131062
03
40
1
454-108-338,Oppm female, adult, 01 31-02
do20207066
,3
40
1
-__________
do201 31 069
0 2
40
1
454-108-340,Oppm female, adult, 01-31 02
d020207073
-~ ~ _ _ _ _ _ _ _ _ _
40
1
do201 31 072
0 2
40
1
454 108-344,Oppm female, adult, 01-31 02
-
~o~0207076
40
1
d020201043
0 1
40
1
454-108-346 Oppm female, adult, 02-01-02
d020207087
40
1
~
d020201045
0 3
40
1
454-108-348 Oppm female, adult, 02-01-02
d020207089
0 3
40
1
454 108.350, Oppm female, adult, 02-01 02 454-108-352, Oppm female. adult, 02-01-02
d020201047
0 4
40
1
~ ~ d020207091
~0 4
:
~4 4 4
0
0 0
:
~
:1
1 1
454-108 354, Oppm female, adult, 02-01-02 454-108-356. Oppm female, adult, 02-01-02 454-108-358. Oppm female, adult, 02-01-02 454-108-360.Oppm female, adult, 02-01-02 454-108-362,Oppm female, adult, 02-01-02 454-108-366, Oppm female, adult, 02-01-02 454-108-368. Oppm female, adult, 02-01-02
40
1
dd002200220071009540
0 3
40
1
d020201052
40
1
d020207096
0 3
40
1
~ : ~ ~ : d020201059
40
1
d020207103
0 3
40
1
0.3
40
1
o,3 40 1
40
1
d020201063
O2
d020207107
0.2
40
1
40
1
dd002200220071101606
O2 0.2
40
1
40
1
d020201073
0.3
d020207117
0.3
40
1
10 0
- 10 0 100
-roo100 10 0 10 0
10 0 10 0
100 10 0
10 0 10 0
100 10 0
10 0
10 0
~
~10 0
10 0 10 0
10 0
10 0
10 0
10 0
10 0
~1 0 51.27 54.43 ~~~~~~~
10.0
10.0 10.0 10.0 10.0 10.0
~0
400
400 400
400 400
400
400
400
400
400
400
400
400
400
-~
400
400 - 400 400
400 400
400
400
400
400
400
~ 400
400 400
.
~~
400
400 ~~
~~~
~~
~~
400
400
~~
~
400
400
400
400--400
400 400 400 400 400 400 400 400 400 400
400 400
400 400 400
400 400
400 400 400 400 400
~400
2051 2177 400
400 400 400 400 400
+
400
+
+ 400
-+_+
+
+
400
+
+
400 -
+
+
400
+
+
400
+
+
400
+ ~~
400
__
+
+
400
+
400
+
--
400
+
~~
+
400
+
. ?.
+
400
. __ -~~
rejected rejected
400
+
400
+
+
+
400
There are two results reported for these samples. Both values are included in the average Conc of PFOS in Sample (ng/ml) = (Inst conc(ng/ml)) x (additional dilution) x (dilution(di1uted sera))
dilution(di1utedsera) =final volume(mL)/amount of sera in diluted sample(mL) = 2.0 mU0.05 mL = 40
amount of sera in diluted sample = amount of sera used/total amount of sera + water. For all samples >0.05 mL this value is 0.05 mL. For samples 4 0 5 mL this value is = t o the amount of sera used
For example, sample E01-1245.28519- dilution(di1uted sera)= 2.0 mL final volumel0.02 mL amount of sera used = 100
With outliers avg 500.8
std dev 409.7 %RSD 81.80
Without outliers avg 400
- std dev 0
%RSD
3M EnEvxicrelo20n0m0 ental Laboratory
summary by sex quail sera samples summaly 030418.xls
printed: 4/18/2003, 853 AMPage 52
Report E01-1245
Study number E01-1245 - QUAIL SERA
PFOS: A Reproduction Study with the Nothern Bobwhite
E01-1245-28485
28487 28489
28491 E0l-1245-28493
E01-1245-28496 E01-1245-28498 E01-1245-28500 E01-1245-28502 E01-1245-28504 EO1-1245-28506 E01-1245-28508 E01-1245-28511 E01-1245-28513 E01-1245-28515 E01-1245-28517
* E01-1245-28518
06/J5/2001
06/15/2001 06/15/2001
06/15/2001 06/15/2001
0611 512001 0611 5/2001 0611 5/2001 06/15/2001 06/15/2001 06/15/2001 06/15/2001 06/15/2001 06115/2001 06115/2001 06/15/2001
07/23/2001
* E01-1245-28521 * E01-1245-28524
07/23/2001 07/23/2001
* E01-1245-28525 07/23/2001
* E01-1245-28528 07/23/2001
* E01-1245-28530 07/23/2001
* E01-124528532
07/23/2001
* E01-1245-28535
07/23/2001
~~
~
E01-1245.28536
07/232001
+ Concentration <LOQ
454-108-374, 10ppm female.adult 02-01-02 454 108-376 lOppm female, adult 02-01-02 454 108-378. lOppm female adult, 02 01 02 454-108 380 lOppm female, adult, 02 01 02 454-1013 382. IOppm female, adult 02-01-02
454-108-386. IOppm female, ad@, 02-01-02 454-108-388. IOppm female, adult, 02-01-02 454-108 390, IOppm female, adult. 02-01-02 454-108-392. IOppm female, adult, 02-01-02 454-108-394. IOppm female, adult, 02-01-02 454-108-396,lOppm female, adult, 02-01-02 454-108-398, lOppm female, adult, 02-01-02 454-108-402,loppm female, adult, 02-01-02 454-108-404,lOppm female, adult, 02-01-02 454-108-406,lOppm female, adult, 02-01-02 454 108-408, lOppm female, adult, 02 01 02
454-108-246 Oppm female, offspring, 02 01 02
4020203028 -d020%3029
d020203030
d020203031 dgO416019 d020?F3033 d020203CJM d020203038 d020203039 d0202030$0 d020203041 d020203042 d020203043 d020203044 d020203045 d020203046
dd002200220071115332
454-108 259, Oppm female offspring. 02 01 02 454-108-273 Oppm female, offspring, 02 01 02 454-108-277, Oppm female, offspring, 02-01-02 454-108-517, lOppm female, offspring, 02-01-02 454-108-525, loppm female. offspring, 02-01-02 454-108-538,lOppm female, offspring, 02-01-02 454-108-557, loppm female. offspring, 02-01-02 454-108-561, lOppm female, offspring,02-01-02
~~~~~~~~~
dd002200220017115398 dd002200220071116309 dd002200220071116487 dd0022002200711147'0 dd002200220071172 d020201154 do20207175 dd002200220017117565
0 2
03
0 1
OL-_
0 3 04 03
p
02 03 03 0 09 01 04 01 02 0 2
0 1
0 08
O2 0.2
00.'0022
00..0033
00.'0088
00..006E
00.'0055
40
I
210 00
40
1
231 92
40
1
124 46
4E ~
1
144 86
40 -
10
7981 ~
40
1
367 26
400
-~ 8400~
400
~- 9277__
400
-~ 4978
- -
400
5794
201
31 924
400
14690
__ ___ __ - _ _ _ rejected
40 _ - - 1
289 04
-
-
~
400
11562
~ 40
1
157 64
400
6306
With outliers
40
1 ---
235 08
400
'Lo
1
284 92
400
9403 11397
--
avg 9990
std dev 6010
40-_ -
-1 -- 11784
400
4714
~
%RSD 60.2
40
-
1
261 76
400
10470
. .
40
-
1
167 91
400
6716
-
Without outliers
40 ~~1 226 40
4 0-
1
224 49
40
1
196 03
40
1
10 0
40
1
10 0
40
1
10 0
40
1
100
40
1
10 0
40
1
10 0
40
1
10.0
40
1
10.0
400
9056 ~~ ~~
400
_ - 8980
400
7841
400
400
+
400
400
+
400
400
400
+
400
400
400 + ~-_____
400
400
+
400
400 -+
400 --
400
400
+
400
400
400
+
avg 8699 std dev 2557 %RSD 29.4
avg 400 std dev 0
%RSD -
100
1
185.25
400
100-~~ - -~ 1
166.M
400
18525 16606
17566
66.67 66.67
1
192.74
400
12849
12452
1
180.81
400
1?054 ~ ~
~~
~~~~~p
40 0 4
- - 1 - 330645..8434- - 440000 L - 1124169138- ~1- 3405 - . ~
---
40
1
208.24
400
40
.
186.59
400
8330
7897
7464 ~ - ~ ~ - ~~- - ~ ~ _ _ _ _ _ _ _ _ _ _
avg of dups 12423
40
1
287.26
400
40
1
252.41
400
11490 10096
10793
Std dev 3457 %RSD 27.8
* There are two results reported for these samples. Both values are included in the average
Conc of PFOS in Sample (ng/ml) = (Inst conc(ng/ml)) x (additional dilution) x (dilution(di1utedsera))
dilution(di1utedsera) =final volume(mL)/amount of sera in diluted sample(mL) = 2.0 mU0.05 mL = 40 amount of sera in diluted sample = amount of sera used/total amount of sera +water. For all samples >0.05 mL this value is 0.05 mL. For samples <0.05 mL this value is = to the amount of sera used. For example, sample E01-1245-28519- dilution(di1utedsera)= 2.0 mL final volume/0.02 m L amount of sera used = 100
3M EnEvxcierlo20n00mental Laboratory
summary by sex quail sera samples summary 030418.~1s
printed. 4/18/2003. 8:53 AMPage 53
Report E01-1245
Study number E01-1245 - QUAIL SERA
PFOS: A Reproduction Study with the Nothern Bobwhite
* E01-1245-28443
-
* E01-1245-28445
* E01-1245-28447
0611 5/2001 06/15/2001 0611 5/2001
E01-1245-28448 0611WOO1
* 01-1245-28450 * E01-1245-28452 * E01-1245-28454 * E01-1245-28455 * E01-1245.28457 * E01-1245-28459
0611 5/2001 06/1 5/2001 06/15/2001 06/15/2001 06/1 5/2001 06/15/2001
* E01-1245-28461 * E01-1245.28465 * E01-1245-28467 * E01-1245-28469
06/15/2001 0611 5/2001 06/15/2001 06/1 5/2001
E01-1245-28471 06/15/2001
* E01-1245-28473 06/15/2001
* 01-1245-28475
- p
* E0l-1245.28476
-~
* E01-1245-28478
06/15/2001 06/15/2001 06/15/2001
+Concentration <LOCI
454-108-329.Oppm male, adult. 01-31-02
p
- ~
~-
454-108-331, Oppm male, adult, 01-31-02
-
454-108-333.Oppm male, adult, 01-31-02
_______~
454-108-335.Oppm male, adult, 01-31-02
454-108-337, Oppm male, adult. 01-31-02
454-108-339. Oppm male, adult, 01-31-02
454-108-341. Oppm male, adult, 01-31-02
~p
454-108-343,Oppm male, adult, 01-31-02
454-108-345,Oppm male, adult, 01-31-02
454-108-347, Oppm male, adult, 02-01-02
454-108-349. Oppm male, adult. 02-01-02
454-108-353.Oppm male, adult. 02-01-02
454-108-355,Oppm male, adult, 02-01-02
454-108-357,Oppm male, adult, 02-01-02
454-108-359,Oppm male, adult, 02-01-02
454-108-361, Oppm male, adult, 02-01-02
454-108-363, Oppm male, adult, 02-01-02
454-108-365,Oppm male, adult. 02-01-02
454-108-367,Oppm male, adult. 02-01-02
d020131054 d020207058-
-
do20131056 d020207060 do20131 058 d020207062 do20131 059 d020207063 do20131061 d020207065 do20131063 d020207067 do20131070 d020207074 d020131071 d020207075 do20131073 d020207077 d020201044 d020207088 d020201046 d020207090 d020201049 d020207093 d020201051 d020207095 d020201058 d020207102 d020201060 d020207104 d020201062 d020207106 d020201064 d020207108 d020201006 d020207109 d020201067 d020207111
02 0.2 ~~ 0.4 0.4 0.4
0.4-0.2 0.2 0.1
0.1-
0.2 0.2 0.2 0.2 0.1 0.1 0.2 0.2 0.2 0.2 0.02 0.02 0.3 0.3 0.2 0.2 0.07 0.07 0.2 0.2 0.2 0.2 0.1 0.1 0.4 0.4 0.1 01
40
1
40
1
40
1
- 40 ~
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
100
1
100
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
40
1
10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 100
loopp
10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0 10 0
400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 ~ 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400
~~~
p
~
~
400
400 400 400 4M) 400
- ~
400 400
~
400 400 400 400 400 400 400
p~~~ ~
400 400
50%
400
400
~
400
400 400
400
--400
~An-n 400
400 400
400 400
p-pp
400 400
400 400
~~ 400 400
400
+ 400
++ 400 +~~
+ 400
+ . - - ~
-
~
p
+ 400
+ - - ~
-
p
p
+ 400 + p~
+ 400 + p -
+ 400
_ _ -- - +
~p
+ 400
+ p~
+
400
+ + p +p + + + +
+
400
_
- p
_
400
p
~
400
400
+ 400
-Lp ~
+
+
400
+ 400
*++ -- --
+
+
+ +
400
400
_.. ^-^4uu
-
~
-
avg 400
std dev 0
%RSD -
There are two results reported for these samples. Both values are included in the average Conc of PFOS in Sample (nglml) = (Inst conc(ng/ml)) x (additional dilution) x (dilution(di1uted sera))
dilution(di1utedsera) =final volume(mL)/amount of sera in diluted sample(mL) = 2.0 mU0.05 mL = 40 amount o i sera in diluted sample =amount of sera useUtotal amount of sera +water. For all samples ~ 0 . 0 5mL this value is 0.05 mL. For samples 4 0 5 mL this value is = t o the amount of sera used. For example, sample E01-1245.28519- dilution(diluted sera)= 2.0mL final volume/0.02 rnL amount of sera used = 100
3M Environmental Laboratory Excel 2000
summary by sex quail sera samples summary 030418.xls
printed: 4/18/2003, 853 APM age 54
Report E01-1245
Study number E01-1245- QUAIL SERA
PFOS: A Reproduction Study with the Nothern Bobwhite
or t E01-1245-28480 06/15/2001 454-108-369. 10ppm male, adult, d100.02-01-02 do20201074
0.2
-________~ ~
d020g07118
40
100
26.73
400
40
100
~29-20
400
* E0l-1245-28482 * E01-1245.28484
0611 5/2OOl 06/15/2001
454-108-371, lOppm male, adult, d100.02-01-02 - ~-
454-108-373, lOppm male, adult, d100.02-01-02
d020201076 d020ZOzg do20201 078 d020207m
02 0~ 2 01
OL
40
100
45 31
400
40-
100
445
400
40
100
35 90
400
40-
- - 100 ~ 3913-
400
t E0l-1245-28486
06/132001 454-108-375. 1Oppm male, adult. d100,02-01-02 d020201080
03
d020207121
03
40
100
34 52
400
40 ~- -
100
~
34%
400
* E01-1245-28488
06/15/2001
454-108-377. lOppm male, adult, d100,02-01-02
-~
do20201082 d0202071Z
0 07 0 07
40
100
23 60
400
40
1 00
~~ 24 03
400
* E01-1245-28490 06/15/2001 454-108-379. lOppm male, adult, d100,02-01-02 d020201089
01
40
100
37 59
400
d020207128
01
40
10%
~ 41 62
400
d020201091
01
E01-1245-28492 06/15/2001 454-108-381, lOppm male, adult, d100.02-01-02 do20207129
01
40
100
35 26
400
40
100
37 13
400
-- ~~~
~
* E01-1245-28494 06/15/2001 454-108-383, lOppm male, adult, d100,02-01-02 d020201093
03
d020207130
03
40
100
36 65
400
40
1?!-
39 06
400
* E01-1245-28495 06/15/2001 454-108-385, lOppm male, adult, d100,02-01-02 d020201094
01
do20207131
01
40
100
29 64
400
40
1 0
0 30 68
400
* E01-1245-28497 06/15/2001 454-108-387, lOppm male, adult, d100,02-01-02 d0202O1096
03
d020207132
03
40
100
43 62
400
40 -
100
49 02-
400
* E01-1245-28499 06/15/2001 454-108-389. 10ppm male, adult, d100,02-01-02 do20201 103
01
40
100
32 26
400
do20207133
01
40 ~- 100
-3~3 91
400
E01-1245-28501 06/15/2001 454-108-391. lOppm male, adult, dl00,02-01-02 do20201 105
0 06
40
100
35 28
400
do20207134 0 06 40 ~ 100 36 72 400
E01-1245-28503 06/15/2001 454-108-393. 1Oppm male. adult, d100,02-01-02 do20201 107
02
dg20207135
02
40
100
40 06
400
40
100
41 16
400
* E01-1245-28505 06/15/2001 454-108-395, lOppm male, adult, d100,02-01-02 d020201109
02
do20207136
02
* E01-1245-28507 06/15/2001 454-108-397. 1Oppm male. adult. d100,02-01-02 dO20201111
03
d020207137
03
40
100
31 80
400
40 _100 _ ~~ ~33 93 400
40
1 00
24 90
400
40
1 0 0 - -__2_6__63__
400
E01-1245.28509 06/15/2001 454-108-399. lOppm male, adult. d100,02-01-02 do20201118 0 1
do20207143
01
40
100
34 45
400
40
100
-39 62-
400
t E01-1245-28510
06/15/2001 454-108-401, 1Oppm male, adult, d100,02-01-02 do20201 119
01
do20207144
01
40
100
50 85
400
40 ~
1%
56 60
400
I E01-1245-28512
06/15/2001 454-108-403, lOppm male, adult, d100,02-01-02 do20201 121
02
do20207145
02
* E01-124528514
06/15/2001 454-108-405. lOppm male, adult, d100,02-01-02 d020201123
01
do20207146
01
E01-1245-28516 06/15/2001 454-108-407. lOppm male, adult. d100.02-01-02 do20201125
01
do20207147
0.1
40
100
31 64
400
40 100 ~34 39 400
40
100
26 94
400
40
- - 100
29 23
400
40
100
24 79
400
40
100
27.90
400
106920 1 16800
~~~---
lllUbU
181240 179440
180340
~~
143600 156520 -
150060
138080
137920 94400 96120
138000
~-
-
95260
150360 166480
158420
141040
148520 146600 156240 118560 122720
-
~
144780
151420
~___
120640
174480 196080
185280
129040 135640 141120 146880
132340 ~-
144000
160240 164640 127200 135720
-
_ 162440
-
_
-
131460
99600 106520
~-
103060
-~
137800 158600
148200
203400 226400
214900
126560 137560 107760 116920
132060 ~--
1 12340 -
99160 111600
4nllon 4 "_).J)o"
There are two results reportedfor these samples. Both values are included in the average
Conc of PFOS in Sample (nglml) = (Inst conc(ng/ml)) x (additional dilution) x (dilution(di1utedsera))
dilution(di1utedsera) =final volume(mL)/amount of sera in diluted sample(mL) = 2.0 mU0.05 mL = 40
amount of sera in diluted sample = amount of sera used/total amount of sera + Water. For all samples ~0.05mL this value is 0.05 mL. For samples <0.05 mL this value is = to the amount of sera used.
For example, sample 01-1245-28519. dilution(di1utedsera)= 2.0 mL final volume/0.02 rnL amount of sera used = 100
avg of dups 141112 std dev 30225 %RSD 21.4
3M EnEvxcierlo20n00mental Laboratory
summary by sex quail sera samples summary 030418.xls
printed: 4/18/2003, 8.53 AM Page 55
Report E01-1245
Study number E01-1245 - QUAIL SERA
PFOS: A Reproduction Study with the Nothern Bobwhite
* E01-1245-28519 * E01-1245-28520 * EOl-1245-28522 * E01-1245-28523
07/23/2001 07/23/2001 07/23/2001 07/23/2001
E01-1245-28526
* E01-1245-28527
E01-1245-28529
* E01-1245-28531
07/23/2001
07/23/2001 07/23/2001 07/23/2001
E0l-1245-28533
07/23/2001
* E0l-1245-28534
07/23/2001
t E01-1245-28537 07/23/2001
+ Concentration <LOQ
d020201133
0.02
100
454-108-253, Oppm ma.le_ , offspring, 02-01-02~~ _ _ do20207154 _-o.02pppp_p1100
d020201134
0.02
454-108-256.Oppm male, offspring, 02-01-02
do20207155
0.02
~
p
~
~
~
_
_
_
_
_
~
_
454-108-266,Oppm male, offspring, 02-01-02
d020201136 d020207157
0.07 o,07 ~ _
100 100 40 ~40
~ ~
454-108-270.Oppm male, offspring, 02-01-02
-
454-108-283, Oppm male, offspring, 02-01-02
454-108-291, Oppm male, offspring, 02-01-02
d020201137 d020207158
d020201140 ~~ d020207161
d020201141 d020207162
0.2 0.2 0.02 0.02 0.05 0.05
40 40 100
loo_--
40 40
454-108-522. 10ppm male, offspring, 02-01-02
d020405091
0.07 ~
40
454-108-533, IOppm male, offspring, 02-01-02
_~ ~~
~~~
~~
454-108-545, IOppm male, offspring, 02-01-02
~~
d020201150
0.07
d020207_171- ~ -0,07_ ~
d020201152
0.04
do202071E ~~_ ~0-.04~_~
40 40 50
50
~~
d020201153
0.07
40
454-108-552, IOppm male, offspring, 02-01-02
d020207174
0.07
40
~_ ~ ~ ~ ~ ~ _ _ _ _ _ _ _ _
40
454-108-568, loppm male. offspring, 02-01-02
dd0022002200711157'7
0.1
40
1
10.0
400
10.0~~~~
400
o e 1
10.0
400
1
1
400
1
10.0
400
1 10.0 ~p~~~
~
400
1
10.0
400
10.0
400
1
10.0
400
1 ~
~ _ _1_0_.0_ _ _ _ _ _ -
400
1
10.0
400
1
10.0
400
10
48.13
201
1
232.67
400
1
205.40
400
1
309.79
400
1
~
272.51
400
~
1
339.60
400
1 ~~~
286.47 _
400
1
301 .89
400
1
260.08
400
400
~ 400 400
400
400
-~
400
400
.. .. 400 400
~~ .. 400 400
400
_____ 19252 9307
.
8216
15490
~
13626
_
13584
11459
12076
10403
+ 400
++ _____________
+
400
+ 400
+ +
--..5 .
+
+...
+ +
~p_______
__
400
~~~p~~
400
~..... ~
-
~
p
400
avg 400
std dev 0
%RSD -
~~ ~_ 19252
8761
.~~
~-~ ~ _ _ _ _ _ _ _ _ _
14558
~
p
~
12521 11239
avg 12601 std dev 3374 %RSD 26.8
There are two results reported for these samples. Both values are included in the average Conc of PFOS in Sample (ng/ml) = (Inst conc(ng/ml)) x (additional dilution) x (dilution(dilu1ed sera))
+ dilution(dilu1edsera) =final volume(mL)/amount of sera in diluted sample(mL) = 2.0 mU0.05 mL = 40
amount of sera in diluted sample = amount of sera usedtotal amount of sera water. For all samples >0.05 mL this value is 0.05 mL. For samples 4 0 5 mL this value is = to the amount of sera used For example, sample E01-1245-28519-dilution(dilu1edsera)= 2.0 mL final volurne/0.02 m L amount of sera used = 100
3M Environmental Laboratory Excel 2000
summary by sex quail sera samples summary 030418.xIs
printed 4/18/2003, 8:53 AMPage 56
Report E01-1245
Study number E01-1245- QUAIL LIVER DATA SUMMARY, BLANKS AND SPIKES
PFOS: A Reproduction Study with the Nothern Bobwhite
01-1342-36000 02/1W O O 2 Blank HPO-day 1
d020211037
1.oooo
9.00
E01-1342-36026 02/12/2002 Blank HPO-day 2
d020212025
1.oooo
9.00
E01-1342-36031 02/13/2002 Blank HPO-day 3
d020301024
1.oooo
9.00
E01-1342-36036 02/15/2002 Blank HPO-day 4
d020218025
1.oooo
9.00
E01-1342-36001 02/11/2002 Blank female liver-day 1 d020211038
5.0353
45.0
E01-1342-36027 02/12/2002 Blank female liver-day 2 d020212026
5.0353
45.0
E01-1342-36032 02/13/2002 Blank female liver-day 3 d020301025
5.0353
45.0
E01-1342-36037 02/15/2002 Blank female liver-day 4 d020218026
5.0353
45.0
E01-1342-36002 02/11/2002 Blank male liver-day 1
d020211039
1.0015
9.00
E01-1342-36028 02/12/2002 Blank male liver-day 2
4020212027
1.0015
9.00
E01-1342-36033 02/13/2002 Blank male liver-day 3
4020301026
1.0015
9.00
E01-1342-36038 02/15/2002 Blank male liver-day 4
d020218027
1.0015
9.00
2.00
0.100000
1
2.51
50.2
50.2
2.00
0.100000
1
2.51
50.2
50.2
2.00
0.100000
1
0.502
10.0
10.0
2.00
0.100000
1
1.oo
20.0
20.0
2.00
0.100635
1
2.51
50.2
50.2
2.00
0.100635
1
2.51
50.2
50.2
2.00
0.100635
1
0.502
10.0
10.0
2.00
0.1 00635
1
1 .oo
20.0
20.0
2.00
0.100135
1
2.51
50.2
50.2
2.00
0.100135
1
2.51
50.2
50.2
2.00
0.100135
1
0 502
10.0
10.0
2.00
0.1001 35
1
1.oo
20.0
20.0
EOl-1342-36029 02/12/2002 Female liver MS-day 2
d020212028
5.0353
45.0
2.00
E01-1342-36034 02/13/2002 Female liver MS-day 3
d020301027
5.0353
45.0
2 00
E01-1342.36039
02/15/2002 Female liver MS-day 4
d020218028
5.0353
45.0
2.00
E01-1342-36004 02/11/2002 Female liver MSD-day 1 d020211041
5.0353
45.0
2.00
E01-1342.36030
02/12/2002 Female liver MSD-day2 d020212029
5.0353
45.0
2.00
E01-1342-36035 02/13/2002 Female liver MSD-day 3 d020301028
5.0353
45.0
2.00
EOI-1342.36040 02/15/2002 Female liver MSD-day 4 d020218029
5.0353
45.0
2.00
* Concentration cLOQ
Cone of PFOS in Sample (ng/g) = (Inst conc(ng/mL))x (additionaldilution) x (final volume (mL))/ amount of liver in diluted sample (g)
amount of liver in diluted sample (9) = amount of liver weighed (g)/ (water added for homogenizing (rnL=g)) + amount of liver weighed(g))
0.100635 0.100635 0.1 00635
0.100635 0.100635 O.lOE35 0.100635
1
28.77
50.2
1
26.03
10.0
1
26.33
20.0
1
29.78
50.2
1
28.53
50.2
1
26.99
10.0
1
27.02
20.0
for both ms and msd
std dev of % rec 5.514 avg conc. 552.6
true Val. 499
572
114.6
avg %rec 109.7
517
103.7
avg conc 547.2
523
104.9
std dev of conc 31.25
592
118.6
true Val. 499
567
113.6
avg%rec I1I.8
536
107.5
avg conc 558.1
537
107.6
Stddev Of conc 26.67
3M Environmental Laboratory Excel 2WO
Blanks QCs a n d MSs quail liver samples summary 030418 XIS
printed 4/18/2003. 8 52 AMPage 57
Report E01-1245
Study number E01-1245 - QUAIL LIVER
versus unertracted curve
nrininil
E01-1342-36017
qc-10ppb-1 (200ngJg) do20211047
5.0353
45.0
E01-1342-36018
qc-IOppb-2 (POOng/g) d020211048
5.0353
45.0
E01-1342-36019
qc-l0ppb-3 (2OOnglg) d020211049
5.0353
45.0
EO1-1342-36020
qc-75ppb-1 (1496 ngg) d020211050
5.0353
45.0
E01-1342-36021
qc-75ppb-2 (1496 ng/g) d020211051
5.0353
45.0
E0l-1342-36022
qc-75ppb-3 (1496 ng/g) d020211052
5.0353
45.0
EOI-1342.36023
qc-150ppb-l (2993 ng/g) d020211053
5.0353
45.0
E01-1342.36024
qc-150ppb-2(2993 ng/g) do20211054
5.0353
45.0
E01-1342-36025
qc-150ppb-3(2993 nq'g) do20211055
5.0353
45.0
Study number E01-1245 - QUAIL LIVER
PFOS: A Reproduction Study with the Nothern Bobwhite
Absolute Recoveries
2.00
0.100635
1
13.59
50.2
270
A
135.0
avg 131.2
2.00
0.100635
1
12.74
50.2
253
A
126.6
std dev 4.274
2.00
0.100635
1
13.28
50.2
264
A
132.0
%RSD 3.258
2.00
0.100635
1
95.65
50.2
1905
A
127.3
avg 123.4
2.00
0.100635
1
90.27
50.2
1794
119.9
std dev 3.725
2.00
0.100635
1
92.58
50.2
1840
123.0
%RSD 3.018
2.00
0.100635
1
169.63
50.2
3371
112.6
avg 113.1
2.00
0.100635
1
167.02
50.2
3319
110.9
std dev 2.395
2.00
0.100635
1
174.15
50.2
3461
115.6
%RSD 2.119
lor all QC in original analysis (absolute recovely)
E01-1342-36017
qc-l0ppb-1 (200ngJg) do20405136
5 0353
45 0
200
E01 1342 36018
qc-loppb-2 (2OOn.gl~ g) do20405137
5 0353
45 0
2 00
E01-1342-36019
qc-1Oppb-3 (2OOnglg) d020405138
5.0353
45.0
2.00
E01-1342-36020
qc-75ppb-l (1496 ng/g) do20405139
5.0353
45.0
2.00
E01-1342-36021
qc-75ppb-2(1496 n. g/. g) d020405140
5.0353
45.0
2.00
E01-1342-36022
qc-75ppb-3 (1496 ng/g) d020405141
5.0353
45.0
2.00
E01-1342-36023
qc-l5Oppb-1 (2993 ndg) d020405142
5.0353
45.0
2.00
E01-1342-36024
qc-150ppb-2(2993 ng/g) d020405143
5.0353
45.0
2.00
E01-1342-36025
qc-150ppb-3(2993 ng/g) do20405144
5.0353
45.0
2.00
A = Not within +/-25% criteria.
Conc of PFOS in Sample (ng/g) = (Inst conc(ng/mL)) x (additionaldilution) x (linal volume (mL))/amount of liver in diluted sample (9)
amount 01 liver in diluted sample (9) = amount 01 liver weighed (g)/ (water added lor homogenizing(mL=g)) + amount 01 liver weighed(g))
0 100635 0 100635 0.100635 0.100635 0.100635 0.100635 0 100635 0.100635 0.100635
1
14 86
100
1
14 24
100
1
14.77
100
1
100.51
100
1
94.89
100
1
101.10
100
1
187.94
100
1
172.20
100
1
180.27
100
295
A
283
A
294
A
1998
A
1886
A
2009
A
3735
3422
3583
lor all QC in rerun analysis (absolute recovery)
147 7 141 5 146.8 133.5 126.1 134.3 124.8 114.3 119.7
avg 145 3 Std dev 3 329 %RSD 2.291
avg 131.3 std dev 4.554 %RSD 3.468
avg 119.6 std dev 5.226 %ASD 4.369
3M Environmental Laboratory Excei 2WO
Blanks QCs and MSs quail liver samples summary 030418.~1s
Page 58 printed: 4/18/2003. 8:52 AM
Report E01-1245
Study number E01-1245 - QUAIL LIVER
versus extracted curve
onainal
PFOS: A Reproduction Study with the Nothern Bobwhite
QC Sample Recoveries
E01-1342-36018
qc-l0ppb-2 (200ng/g) d020211048
5.0353
45.0
E01-1342-36019
qc-l0ppb-3 (ZOOnq'g) d020211049
5.0353
45.0
E01-1342-36020
qc-75ppb-1 (1496 ng/g) d020211050
5.0353
45.0
E01-1342-36021
qc-75ppb-2 (1496 nq'g) d020211051
5.0353
45.0
E01-1342-36022
qc-75ppb-3 (1496 ng/g) d020211052
5.0353
45.0
E01-1342-36023
qc-150ppb-1 (2993 nq'g) d020211053
5.0353
45.0
EOI-1342.36024
qc-150ppb-2 (2993 nq'g) d020211054
5.0353
45.0
E01-1342-36025
qc-150ppb-3 (2993 nq'g) d020211055
5.0353
45.0
Study number E01-1245 - QUAIL LIVER
versus extracted curve
rerun
2.00
0.100635
1
13.41
50.2
267
A
133.3
Std dev 3.971
2.00
0.100635
1
13.91
50.2
276
A
138.2
%RSD 2.887
2.00
0,100635
1
89.60
50.2
1781
119.0
avg 115.5
2.00
0.100635
1
84.54
50.2
1680
112.3
std dev 3.378
2.00
0.100635
1
86.63
50.2
1722
2.00
0.100635
1
155.46
50.2
3090
115.1 103.2
%RSD 2.925 avg 103.6
2.00
0.100635
1
153.16
50.2
3044
2.00
0.100635
1
159.43
50.2
3168
101.7 105.9
std dev 2.106 %RSD 2.033
for all QC in original analysis (recovery)
01-1342-36017
qc-lOppb-1 (POOng/g) do20405136
5.0353
45.0
2.00
E01-1342-36018
qc-IOppb-2 (PWng/g) d020405137
5.0353
45.0
2.00
E01-1342-36019
qc-IOppb-3 (200ng/g) d020405138
5.0353
45.0
2.00
E01-1342-36020
qc-75ppb-I (1496 ng/g) do20405139
5.0353
45.0
2.00
EOl-1342-36021
qc-75ppb-2 (1496 nq'g) do20405140
5.0353
45.0
2.00
E01-1342-36022
qc-75ppb-3 (1496 ng/g) d020405141
5.0353
45.0
2.00
E01-1342.36023
qc-150ppb-1 (2993 ng/g) d020405142
5.0353
45.0
2.00
E01-1342-36024
qc-150ppb-2 (2993 ngg) d020405143
5.0353
45.0
2.00
E01-1342-36025
qc-l50ppb-3 (2993 nq'g) d020405144
5.0353
45.0
2.00
A = Not within +/-25% critena.
Conc of PFOS in Sample (ng/g) = (Inst conc(ng/mL))x (additionaldilution) x (final volume (mL))/ amount of liver in diluted sample (g)
amount of liver in diluted sample (9) = amount of liver weighed (g)/ (water added lor homogenizing (mL=g))+ amount of liver weighed(g))
0.100635
0.100635 0.100635 0.100635 0.100635 0,100635 0.100635 0.100635 0.100635
1
13.43
100
1
12.91
100
1
13.35
100
1
84.61
100
1
79.97
100
1
85.09
100
1
155.84
100
1
143.14
100
1
149.66
100
267
A
257
A
265
A
1682
1589
1691
3097
2845
2974
for all QC in rerun analysis (recovery)
133.5
128.3 132.7 112.4 106.2 113.0 103.5 95.05 99.38
avg 131.5 std dev 2.782 %RSD 2.1 16
avg 110.6 sld dev 3.756 %RSD 3.398
avg 99.30 std dev 4.217 %RSD 4.247
3M EnEvxicrelo20n00mental Laboratory
Blanks QCs a n d MSs quail liver samples summary 030418 . ~ 1 ~
printed: 4/18/2003. 8-52AMPage 59
Report E01-1245
Study number E01-1245 - QUAIL LIVER DATA SUMMARY
PFOS: A Reproduction Study with the Nothern Bobwhite
E01-1342-30339 E01-1342-30357
06/19/2001 0 ppm a.i. 332 F Liver 04/30/2001 0 ppm a.i. 334 F Liver
d020211064 d020211066
E01-1342-30375 06/19/2001 0 ppm a.i. 336 F Liver
d020211068
E01-1342-30393 06/19/2001 0 ppm a i 338 F Liver
d020211070
E01-1342-30411 E01-1342-30429
06/19/2001 0 ppm a.i. 340 F Liver 05/31/2001 0 ppm a.i. 342 F Liver
d020212034 d020212036
E01-1342-30447 06/19/2001 0 ppm a.i. 344 F Liver
d020212038
E01-1342-30465 06/19/2001 0 ppm a.i. 346 F Liver
d020212040
E01-1342-30483 06/19/2001 0 ppm a.i. 348 F Liver
d020212042
E01-1342-30501 06/19/2001 0 ppm a.i. 350 F Liver
d020212047
E01-1342-30519 06/19/2001 0 ppm a.i. 352 F Liver
d020212049
E01-1342-30537 06/19/2001 0 ppm a.i. 354 F Liver
d020212051
E01-1342-30555 06/19/2001 0 ppm a.i. 356 F Liver
d020212053
E01-1342-30573 06/19/2001 0 ppm a.i. 358 F Liver
d020212055
E01-1342-30591 06/19/2001 0 ppm a.i. 360 F Liver
d020212059
EO1-1342-30609 06/19/2001 0 pprn a.i. 362 F Liver
dO20212061
EO1-1342-30627 06/19/2001 0 ppm a.i. 364 F Liver
d020212063
E01-1342-30645 06/19/2001 0 ppm a.i. 366 F Liver
d020212065
E0l-1342-30663 06/19/2001 0 ppm a.i. 368 F Liver
d020212067
E01-1342-30681 06/20/2001 10 ppm a.i. 370 F Liver
d020301032
E01-1342-30699 06/20/2001 10 ppm a.i. 372 F Liver
d020301033
E01-1342-30717 06/20/2001 10 ppm a.i. 374 F Liver
d020301034
E01-1342.30735 06/20/2001 10 ppm a.i. 376 F Liver
d020301035
E01-1342.30753 06/20/2001 10 ppm a.i. 378 F Liver
d020301036
E01-1342-30771 06/20/2001 10 ppm a.i. 380 F Liver
d020301037
E01-1342-30789 06/20/2001 10 ppm a.i. 382 F Liver
d020301038
E01-1342-30820 04/11/2001 10 ppm a.i. 384 F Liver
d020301039
E01-1342-30838 06/20/2001 10 ppm a.i. 386 F Liver
d020301040
E01-1342-30856 06/20/2001 10 ppm a.i. 388 F Liver
d020301041
E01-1342-30874 06/20/2001 10 ppm ai. 390 F Liver
d020301045
EO1-1342-30892 06/20/2001 10 ppm a.i. 392 F Liver
d020301046
E01-1342-30910 06/20/2001 10 ppm a.i. 394 F Liver
d020301047
E01-1342-30928 06/20/2001 10 ppm a.i. 396 F Liver
d020301048
E01-1342-30946 06/20/2001 10 ppm a.i. 398 F Liver
d020301049
E01-1342.30964 06/20/2001 10 ppm a.i. 400 F Liver
d020218033
E01-1342-30982 06/20/2001 10 ppm a.i. 402 F Liver
d020218034
E01-1342-31000 06/20/2001 10 ppm a.i. 404 F Liver
d020218035
EO1-1342-31018 06/20/2001 10 ppm a.i. 406 F Liver
d020218036
E01-1342-31036 06/20/2001 10 ppm a.i.408 F Liver
d020218037
E01-1365-31184 07/23/2001 0 ppm a.i. 246 F Liver, Offspring d020218038
E01-1365-31204 07/23/2001 0 ppm a.i. 259 F Liver, Offspring d020218041
E01-1365-31219 07/23/2001 0 ppm a.i. 273 F Liver, Offspring d020218047
E01-1365-31224 07/23/2001 0 ppm a.i. 277 F Liver, Offspring do20218048
E01-1365-31240 07/23/2001 10 ppm a.i. 517 F Liver, Offspring d020218051
E01-1365-31250 07/23/2001 10 ppm a.i. 525 F Liver, Offspring do20218053
E01-1365-31260 E01-1365-31275
07/23/2001 10 ppm a.i. 538 F Liver, Offspring do20405158 07/23/2001 10 ppm a.i. 557 F Liver, offspring d020218061
E01-1365-31280 07/23/2001 10 ppm ad. 561 F Liver, Offspring d020218062
* Concentration <LOO
1.0469 1.0232 1.01 88 1.0543 1.0182 1.0904 1.0087 1.0998 1.1036 1.0237 1.1509 1.0578 1.0312 1.1031 1.0586 1.0424 1.0364 1.0577 1,0920 1.0868 1.0748 1.0790 1.1036 1.0021 1.0825 1.0122 0.6864 1.1215 1.0878 1.0078 1.0060 1.0238 1.0370 1.0240 1.0181 1 .OB76 1.0173 1.0047 1.0044 0.7302 0.4434 0.5004 0.4326 0.6570 0.5720 0.5211 0.4654 0.9417
9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 6.30 9.00 9 00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 6.30 3.60 4.50 3.60 5.40 5.40 4.50 4.50 8.10
2.00
0.104201
1
2.51
50.2
2.00
0.102083
1
2.51
50.2
2.00
0.1 01 689
1
2.51
50.2
2.00
0.1 04861
1
2.51
50.2
2.M)
0.1 01 635
1
2.51
50.2
2.00
0.108063
1
2.51
50.2
2.00
0.100782
1
2.51
50.2
2.00
0.108893
1
2.51
50.2
2.00
0.1 09228
1
2.51
50.2
2.00
0.102128
1
2.51
50.2
2.00
0.113379
1
2.51
50.2
2.00
0.1 051 72
1
2.51
50.2
2.00
0.102799
1
2.51
50.2
2.00
0.109184
1
2.51
50.2
2.00
0.1 05243
1
2.51
50.2
2.00
0.1 03800
1
2.51
50.2
2.00
0.1 03264
1
2.51
50.2
2.00
0.1 051 63
1
2.51
50.2
2.00
0.108205
1
2.51
50.2
2.00
0,107745
1
319.18
10.0
2.00
0.106682
1
236.52
10.0
2.00
0.1 07054
1
290.48
10.0
2.00
0.109226
1
217.55
10.0
2.00
0.100189
1
187.79
10.0
2.00
0,107364
1
214.22
10.0
2.00
0.1 01 097
1
166.41
10.0
2.00
0.0982460
1
206.04
10.0
2.00
0.110804
1
418.20
10.0
2.00
0.1 07833
1
187.91
10.0
2.00
0.1 00701
1
245.00
10.0
2.00
0.100540
1
298.53
10.0
2.00
0.102137
1
256.81
10.0
2.00
0.103318
1
253.83
10.0
2.00
0.102155
1
224.76
10.0
2.00
0.101626
1
255.94
20.0
2.00
0.1 07816
1
318.13
20.0
2.00
0.101554
1
275.17
20.0
2.00
0.100423
1
294.79
20.0
2.00
0.1 00396
2.00
0.103866
2.00
0.109660
2.00
0.100072
2.00
0.1 07276
1
228.77
20.0
1
1 .oo
20.0
1
1.oo
20.0
1
1.oo
20.0
1
1 .oo
20.0
2.00
0.108470
1
308.44
20.0
2.00
0.0957803
1
336.48
20.0
2.00
0.103782
10
72.30
100
2.00
0.0937286
1
219.12
20.0
2.00
0.1 04151
1
238.83
20.0
Conc of PFOS in Sample (ngig) = (Inst conc(ng/mL))x (additional dilution) x (final volume (mL))/ amount of liver in diluted sample (9)
amount of liver in diluted sample (9) =amount of liver weighed (g)/ (water added for homogenizing(mL=g))+ amount of liver weighed(g))
50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 5925 4434 5427 3983 3749 3991 3292 4194 7548 3485 4866 5939 5029 4914 4400 5037 5901 5419 5871 4557 20.0
20.0 20.0 20.0 5687 7026 13933 4676 4586
*
*
*
*
*
*
*
*
*
*
*
*
*
* ' '
*
avg 50.2
*
std dev 0
+
%RSD -
*
' * *
rejected
avg 4898 std dev 1035 %RSD 21.1
avg 20.0
std dev 0
%RSD -
Without outliers avg 5494
std dev 1137 %RSD 20.7
With outliers avg 7182
std dev 3900 %RSD 54.3
3M Environmental Laboratory Excel 2000
samples by sex quail liver samples summary 030418 . ~ 1 ~
Page 60 printed.4/18/2003. 8:52 AM
- Report E01-1245 Studv number E01-1245 QUAIL LIVER DATA SUMMARY
PFOS: A Reproduction Study with the Nothern Bobwhite
EOl-l%2-30312 E01-1342-30330 E01-1342.30348 E01-1342-30366 E01-1342-30384 E01-1342-30402 E01-1342-30420 E01-1342-30438 E01-1342-30456 EOl-1342.30474 E01-1342-30492
06/19/2001 0 ppm a.i. 329 M Liver 06/19/2001 0 ppm a.i. 331 M Liver 06/19/2001 0 ppm a.i. 333 M Liver 06/19/2001 0 ppm a.i. 335 M Liver 06/19/2001 0 ppm a.i. 337 M Liver 06/19/2001 0 ppm a.i. 339 M Liver 06/19/2001 0 ppm a.i. 341 M Liver 06/19/2001 0 ppm a.i. 343 M Liver 06/19/2001 0 ppm a.i. 345 M Liver
06/19/2001 0 ppm a.i. 347 M Liver 06/19/2001 0 ppm a.i. 349 M Liver
do20211061 d020211063 d020211065 d020211067 do2021 1069 d020212033 d020212035 d020212037 d020212039 d020212041 d020212046
E01-1342-30510 EOl-1342.30528 E01-1342.30546 EO1-1342-30564 E01-1342-30582 E01-1342-30600 E01-1342-30618 E01-1342-30636
06/19/2001 0 ppm a.i. 351 M Liver 06/19/2001 0 ppm a.i. 353 M Liver 06/19/2001 0 ppm a.i. 355 M Liver 06/19/2001 0 ppm a.i. 357 M Liver
06/19/2001 0 ppm a.i. 359 M Liver
06/19/2001 0 ppm a.i. 361 M Liver 06/19/2001 0 ppm a.i. 363 M Liver 06/19/2001 0 ppm a.i. 365 M Liver
d020212048 d020212050 d020212052 d020212054 d020212058 d020212060 d020212062 d020212064
E01-1342-30654 06/1912001 0 ppm a.i. 367 M Liver
d020212066
E01-1342-30672 EO1-1342-30690 E01-1342-30708 E01-1342.30726 E01-1342-30744 E01-1342-30762 E01-1342-30780 E01-1342-30798 E01-1342-30829 E01-1342-30847 E01-1342-30865 E01-1342-30883 E01-1342-30901 EOl-1342-30919 E01-1342.30937 EO1-1342-30955 E01-1342-30973 E01-1342-30991 E01-1342-31009
06/20/2001 10 DDm a.i.369 M Lwer 06/20/2001 10 ppm a.i. 371 M Liver 06/20/2001 10 ppm a.i. 373 M Liver 06/20/2001 10 ppm a.i. 375 M Liver 06/20/2001 10 ppm a.i. 377 M Liver 06/20/2001 10 ppm ad. 379 M Liver 06/20/2001 10 ppm a.i. 381 M Liver 06/20/2001 10 ppm a.i. 383 M Liver 06/20/2001 10 ppm a.i. 385 M Liver 06/20/2001 10 ppm a.i. 387 M Liver 06/20/2001 10 ppm a.i. 389 M Liver 06/20/2001 10 ppm a.i. 391 M Liver 06/20/2001 10 ppm a.i. 393 M Liver 06/20/2001 10 ppm a.i. 395 M Liver 06/20/2001 10 ppm a.i. 397 M Liver 06/20/2001 10 ppm a.i. 399 M Liver 06/20/2001 10 ppm a.i. 401 M Liver 06/20/2001 10 ppm a.i. 403 M Liver 06/20/2001 10 DDm a.i. 405 M Liver
d020301050 do20405148 do20405149 d020301053 d020301054 d020405150 do20405151 d020301060 d020405152 d020301062 d020301063 do20301 064 do20405153 d020301066 do20301 067 d020218064 d020405159 d020405160 d020405161
E01 1342-31027 E0l-1365.31194 E01-1365-31199
06/20/2001 10 ppm a I 407 M Liver
do20405162
07/23/2001 0 ppm a I 253 M Liver. Offspring do20218039
07/23/2001 0 ppm a.i. 256 M Liver, Offspring d020218040
E01-1365.31209 E0l-1365-31214
07/23/2001 0 ppm a.i. 266 M Liver, Offspring d020218042 07/23/2001 0 ppm a.i. 270 M Liver, Offspring d020218046
E01-1365-31229 07/23/2001 0 ppm a.i. 283 M Liver, Offspring d020218049
E0l-1365-31234 07/23/2001 0 ppm a.i. 291 M Liver, Offspring d020218050
E0l-1365-31245 E01-1365-31255 E01-1365.31265
07/23/2001 10 ppm a.i. 522 M Liver, Offspring do20405157 07/23/2001 10 ppm a.i. 533 M Liver, Offspring do20218054 07/23/2001 10 ppm a.i. 545 M Liver, Offspring d020218059
E01-1365-31270 E01-1365-31285
07/23/2001 10 ppm a.i. 552 M Liver, Offspring d020218060 07/23/2001 10 ppm a.i. 568 M Liver, Offspring d020218063
* Concentration <LOCI
1.0050 1.0530 1.0338 1.0062 1.0269 1.0886 1.0235 1.0090 1.1046 1.0586 1.0358 1.0583 1.0183 1.0899 1.0382 1.0941 1.0084 1.0818 1.0916 1.0327 1.0010 1.0856 1.0276 1.1008 1.0236 1.0312 1.0501 1.0110 1.0678 1.0315 1.0310 1.0947 1.0834 1.0489 1.0309 1.0276 1.0361 1.0019 1.0336
10956 0 3806 0.5947 0.2673 0.5900 0.6666 0.6072 0.7325 0.6903 0.4624
0.5353 0.7581
9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9-00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00 9.00
9 00 3 60 5.40 2.70 5.40 6.30 5.40 6.30 6.30 4.50
4.50 7.20
2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2 00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00
2 00 2 00 2.00 2.00 2.00 2.00 2.00 2.00 2.00 2.00
2.00 2.00
0.100450
1
0,104745
1
0.103032
1
0.100558
1
0.1 02415
1
0,107904
1
0.102110
1
0.100809
1
0.109317
1
0.105243
1
0.10321 1
1
0.105217
1
0.1 01644
1
0.10801 9
1
0.103425
1
0.1 08390
1
0.100755
1
0.1 07302
1
0.108169
1
2.51 2.51 10.76 2.51 2.51 2.51 2.51 2.51 2.51 2.51 2.51 2.51 2.51 2.51 2.51 2.51 2.51 2.51 2.51
0.102933
1
2.51
0.100090
10
393.21
0.107639
10
422.59
0.102477
10
441.96
0.108981
10
381.61
0.102119
10
409.88
0,102799
10
466.19
0,104487
10
417.98
0.100989
10
371.06
0.1 06061
10
442.30
0.102826
10
407.70
0.102781
10
361.37
0,108443
10
381.87
0.1 07444
10
466.09
0.1 04380
10
339.50
0.1 02772
10
257.69
0.1 02477
10
322.88
0.1 03237
100
76.08
0.100171
100
72.89
0.103014
100
712 4
0 108523
100
0 0956137
1
0.0992043
I
0.0900819
1
0.0984975
1
0.0956851
1
0.101079
1
71 64
1 00
1.oo
1 .lo
1 .oo 1 .oo 1.oo
0.104159
10
71.33
0.098751 1
1
244.12
0.0931807
1
259.80
0.106309
1
318.62
0.0952614
1
310.49
Conc of PFOS in Sample (ngig) = (Inst conc(ng/mL)) x (additional dilution) x (final volume (mL))/ amount of liver in diluted sample (9)
amount of liver in diluted sample (9) = amount of liver weighed (g)/ (water added for homogenizing (mL=g))+ amount of liver weighed(g))
50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2
10.0 100 100 10.0 10.0 100 100 10.0 100 10.0 10.0 10.0 100 10.0 10.0 20.0 100 100 100
100 20 0 20.0 20.0
20.0 20.0 20.0 100 20.0 20.0
20.0 20.0
50.2 50.2 209 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 50.2 78571 78520 86255 70032 80275 90699 80006 73485 83405 79299 70318 70428 86760 65051 50148 63015 147389 145531 138311
132028 200 20.0 20.0
20.0 20.0 20.0 13696 4944 5576
5994 6519
* *
rejected
*
' * * *
* * * * '
* *
'
*
With outliers avg 58.1
std dev 35.5 %RSD 61.0
Without outliers avg 50.2
Std dev 0
%RSD -
* * * * *
rejected
avg 88416 Std dev 28517 %RSD 32.2
avg 20.0
std dev 0
%RSD -
Without outliers avg 5758
std dev 666 %RSD 11.6
With outliers avg 7346
std dev 3591 %RSD 49.0
3M Environmental Laboratory Excel 2CQO
samples by sex quailliver samples summary 03041&xis
Page 61 printed: 4/18/2003. 8 52 AM
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A ReproductionStudy with the Northern Bobwhite
A~ACHMENCT: SAMPLECHROMATOGRACMASL,IBRATIOINNFORMATION,
AND INSTRUMENT INFORMATION
3M Environmental Laboratory
3M Environmental Laboratory
Page 62 of 226 Page 62
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Report E01-1245
Methanol Solvent Blanks
nethanol blank IM Environmental Lab j020212032 Srn (Mn, 1x2) 100
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northern Bobwhite
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3M Environmental Laboratory
3M Environmental Laboratory
Page 63 of 226 Page 63
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Report EO1-1245
JeOH blank iM EnvironmentalLab
1020201057Sm (Mn, 1x2) 100
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A ReproductionStudy with the NorthernBobwhite
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3M Environmental Laboratory
Page 64 of 226
Page 64
Report E01-1245
Report E01-1245
100-
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A ReproductionStudy with the Northern Bobwhite
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3M Environmental Laboratory
Page 65 of 226 Page 65
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Report E01-1245
Water Blank Samples
01-1342-36026, Blank H2O-day 2 M Environmental Lab 020212025 Sm (Mn, 1x2)
100
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A ReproductionStudy with the Northern Bobwhite
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3M Environmental Laboratory
3M Environmental Laboratory
Page 66 of 226
Page 66
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Report E01-1245
Blank H2O-day 4 IM EnvironmentalLab
1020228107Sm IMn. 1x21
100
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A ReproductionStudy with the Northern Bobwhite
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3M Environmental Laboratory
Page 67 of 226 Page 67
Report E01-1245
Report E01-1245
E01-1342-36036,Blank HZO-day 4 IM EnvironmentalLab
1020218025 Sm (Mn, 1x2) 100
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northem Bobwhite
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3M Environmental Laboratory
Page 68 of 226
Page 68
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Report E01-1245
Sera Blank Samples
pe, sera blank-1, day 2, 02-01-02 M EnvironmentalLab
020201032 Sm /Mn. 1x2) 100
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northern Bobwhite
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Page 69 of 226
Page 69
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Report E01-1245
ipe, sera blank-I, day 2, 02-01-02 IM EnvironmentalLab 1020201032Sm I.Mn.. 1x2,)
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PFOS: A Reproduction Study with the Nothern Bobwhite
uction Study with the Northern Bobwhite
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3M Environmental Laboratory
Page 70 of 226 Page 70
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Report E01-1245
;pe, sera blank-1, day 2,02-01-02 IM EnvironmentalLab 1020207036Sm (Mn,1x2)
100
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS A ReproductionStudy with the Northem Bobwhite
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3M Environmental Laboratory
Page 71 of 226 Page 71
Report E01-1245
Report E01-1245
Female Liver Blank Samples
01-1342-36001 Blank female liver-day 1 M Environmental Lab 320211038 Sm (Mn, 1x2)
PFOS: A Reproduction Study with the Nothern Bobwhite
PFQS: A ReproductionStudy with the NorthernBobwhite
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Page 7 2 of 226
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FO1-1342-36032, Blank female liver-day 3 IM Environmental Lab 1020213026 Sm (Mn, 1x2) 100
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reprqduction,$tudywittl the Northern Bobwhite
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PFOS: A ReproductionStudy with the Northern Bobwhite
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Male Liver Blank Samples
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PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduation qtydy Jth the Northern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite 4ththe Northern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A ReprcduFtionStudy with the Northem Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northem Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
PWS A Reproduction Stucly with the Northern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
Study with the Northern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A ReproductionStudy with the Northem Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS:A Reprodqqn Study With ths Northern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
A Seprod@on Study with the Northern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
4 qeprqduction Study with the Northern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A iReproduCbion Qtudy with the Northern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Refpbction Study with the NorthernBobwhite ~ /I
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PFOS: A Reproduction Study with the Nothern Bobwhite
tudy with the Northern Bobwhite j
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3M Environmental Laboratory
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PFOS: A Reproduction Study with the Nothern Bobwhite
with the Northem Bobwhite
Dosed Group Male Offspring Sera Samples
154-108-522, 10ppm male, offspring, 02-01-02 IM Environmental Lab
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PFOS: A Reproduction Study with the Nothern Bobwhite
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3M Environmental Laboratory
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PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reprwction Study with the Northem Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
dy with the Northern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite y yith the Northern Bobwhite '~
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PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
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IM Environmental Lab
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PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northem Bobwhite
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3M Environmental Laboratory
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PFOS: A Reproduction Study with the Nothern Bobwhite
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PFOS: A Reproduction Study with the Nothern Bobwhite
RTm,qli PFoS:A
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Dosed Group Male Liver Samples
101-1342-30762,lO ppm a.i. 379 M Liver,dlO 1M Environmental Lab
1020301058 Sm (Mn. 1x2) 100
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PFOS: A Reproduction Study with the Nothern Bobwhite
ction Study with the Northern Bobwhite I
t01-1342-30883,lO ppm a.i. 391 M Liver,dlO IM EnvironmentalLab
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3M Environmental Laboratory
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Report E01-1245
' i~~~
201-1342-30829,lO ppm a.l.385 M Liver,dlO
IM EnvironmentalLab
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PFOS: A Reproduction Study with the Nothern Bobwhite
Report E01-1245
' y PIiiF~O'S:
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3M Environmental Laboratory
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PFOS: A Reproduction Study with the Nothern Bobwhite
with the Northern Bobwhite
i01-1342-30847, 10 ppm a.i. 387 M Liver,dlO IM Environmental Lab
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3M Environmental Laboratory
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PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northern Bobwhite
:Ol-1342-30798, 10 ppm a.i. 383 M Liver,dlO IM Environmental Lab
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3M Environmental Laboratory
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PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northern Bobwhite
iO1-1342-30780,lOmrn a.i. 381 M Liver.dl0
M Environmental Lab
020301059 Sm (Mn, 1x2)
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3M Environmental Laboratory
3M Environmental Laboratory
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PFOS: A Reproduction Study with the Nothern Bobwhite
201-1342-30937,lO ppm a.i. 397 M Liver,dlO IM EnvironmentalLab 1020301067Sm (Mn, 1x2)
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TIC 3.35ef
Arez
1.00 2.00 3.00 4.00 5.00 6.00
3M Environmental Laboratory
3M Environmental Laboratory
Page 116 of 226 Page 116
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Report E01-1245
'~
t01-1342-30919, 10 ppm a.i. 395 M Liver,dlO IM EnvironmentalLab
1020301066 Srn (Mn, 1x2) 100
6.74 388593
V@I the Northern Bobwhite
davey 0707% 02-Mar-2002,03:01:5:
I : MRM of 1 Channel ESTIC
3.98et
Are;
%
0
3M EnvironmentalLaboratory
3M Environmental Laboratory
Page 117 of 226 Page 117
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A ReproductionStudy with the Northem Bobwhite
Dosed Group Female Liver Samples
f01-1342-30771,lO ppm a.i. 380 F Liver
IM Environmental Lab
i020301037 Sm (Mn. 1x2)
I
.
I
1oa
6.73 271982
davey O?O% OI-Mar-2002,21:39:2(
I:MRM of 1Channel ES-
TIC 3.13ef
Arei
%
0
' 1.00 ' 2.00 ' 3.00
4.00 ' 5.00
3M Environmental Laboratory
3M Environmental Laboratory
Page I1a of 226 Page 118
Report E01-1245
Report EO1-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS A ReproductionStudy with the Northern Bobwhite
f01-1342-30838, 10 ppm a.i. 386 F Liver IM EnvironmentalLab j020301040 Sm (Mn, 1x2)
100
6.73 446002
davey 07079! 01-Mar-2002,22:12:4! 1: MRM of 1 Channel ES-
TIC 4.76ef
Are:
%
Time 1.00 2.00 3.00 4.00 5.00 6.00 7.00 8.00 9.00 10.00
3M Environmental Laboratory
3M Environmental Laboratory
Page 119 of 226 Page 119
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A ReproductionStudy wlth the Northem Bobwhite
iO1-1342-308561,0 ppm a.i. 388 F Liver IM Environmental Lab
1020301041 Sm (Mn, 1x2)
100
6.72 243562
davey 07079! Ol-Mar-2002,22:23:5: 1: MRM of 1 Channel ES-
TIC 2.84et
Are:
%
0 IIIII,III,,,,I,,,,I,,,,(,,,,I,,,,I,,,,I,,,,I,,,,I,,I,I,,I(I,,,,I 1.00 2.00 3.00 4.00 5.00 6.00
3M Environmental Laboratory
3M Environmental Laboratory
Page 120 of 226 Page 120
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northern Bobwhite
E01-1342.30820, 10 ppm a.i. 384 F Liver, d10 IM Environmental Lab 1020301039 Sm (Mn, 1x2)
100
6.74 263292
davey 07079! Ol-Mar-2002,22:01:4: 1: MRM of 1 Channel ES-
TIC 2.83et
Are;
%
0
3M Environmental Laboratory
3M Environmental Laboratory
Page 121 of 226 Page 121
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
I
y with the Northern Bobwhite
!01-1342-30735, 10 ppm a.i. 376 F Liver IM EnvironmentalLab 1020301035 Sm (Mn, 1x2)
100
6.73 275483
davey 07079! OI-Mar-2002,21:I7:14 1: MRM of I Channel ES-
TIC 3.19et
Are;
%
0
3M Environmental Laboratory
3M Environmental Laboratory
Page 122 of 226 Page 122
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northern Bobwhite
f01-1342-30717, 10 ppm a.i. 374 F Liver IM Environmental Lab
!020301034 Sm (Mn, 1x2)
ioa
6.74 346653
davey 07079! Ol-Mar-2002,21:06:0! 1: MRM of 1 Channel ES-
TIC 3.78et
Are:
%
a
3M Environmental Laboratory
3M Environmental Laboratory
Page 123 of 226 Page 123
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite udy Nththe NorthernBobwhite
f01-1342-30789,lO ppm a.i.382 F Liver IM EnvironmentalLab
1020301038 Sm (Mn, 1x2)
100
6.72 219312
davey 07079! Ol-Mar-2002,21:50:3; 1: MRM of 1 Channel ES-
TIC 2.60ef
Are:
%
0
1.00 2.00 3.00 4.00 5.00 6.00 7.00 8.00 9.00 10.00 1
3M Environmental Laboratory
3M Environmental Laboratory
Page 124 of 226 Page 124
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFQS:A ReproolwctidnStudy with the Northern Bobwhite
E01-1342-30681,lOppm a.i. 370 F Liver IM EnvironmentalLab
1020301032 Sm (Mn, 1x2)
100
6.74 371782
davey 07079! Ol-Mar-2002,20:43:5;
1: MRM of 1 Channel ESTIC
4.09et Are:
%
1 0
t
I I I Time
' 1.00 ' 2.00 ' 3.00 ' 4.00 ' 5.00 ' 6.00 ' 7.b0 I 8.bO
9.00 I lO!OO
3M Environmental Laboratory
3M Environmental Laboratory
Page 125 of 226 Page 125
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Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A ReproductionStudy with the Northern Bobwhite
EOI-1342-30699,lOppm a.i. 372 F Liver
IM Environmental Lab
1020301033 Sm (Mn, 1x2)
100
6.72 295007
davey 07079! Ol-Mar-2002,20:55:0! 1: MRM of 1 Channel ES-
TIC 3.36ef
Arec
%
0
' 1.00 ' 2.00 ' 3.00 ' 4.00 ' 5.00 ' 6.00 '
3M Environmental Laboratory
3M Environmental Laboratory
Page 126 of 226 Page 126
~~
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Study with the Northern Bobwhite
E01-1342-30753, 10 ppm a.1. 378 F Liver
IM EnvironmentalLab
!020301036 Sm (Mn, 1x2)
100
6.73 243424
davey 0707% Ol-Mar-2002,21:28:2(
1: MRM of IChannel ESTIC
2.86ef Are;
%
a , , , , , , , , , , , 1 1 1 1 1 1 , 1 1 I , , , , , , , Time
1.00
2.00
3.00
4.00
5.00
6.00
7.00
8.00
9.00 10.00
3M Environmental Laboratory
3M Environmental Laboratory
Page 127 of 226 Page 127
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Report E01-1245
'I
Dosed Group Male Offspring Liver QahpJlbs
IO1-1365-31245,lO ppm a.i. 522 M Liver, offspring IM Environmental Lab
j020218052 Sm (.Mn..1x2) I
100
6.72 426343
with the Northern Bobwhite
1
I
davey070799 18-Feb-2002, 16:59:46 1: MRM of 1Channel ES-
TIC 4.43et
Are;
%
0
' 1.00 ' 2.00 ' 3.00 ' 4.00 ' 5.00 ' 6.00 '
3M EnvironmentalLaboratory
3M Environmental Laboratory
Page 128 of 226 Page 128
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PpPS A ReproductionStudy with the Northem Bobwhite
01-1365-31270,lO ppm a.i. 552 M Liver, offspring M Environmental Lab
020218060 Sm (Mn, 1x2)
IO0
6.70 302473
davey 07079! 18-Feb-2002, -18:28:3r 1: MRM of 1 Channel ES-
TIC 3.23ef
Are:
%
a
"""~l'.OO""'2.b"b"""'4.OO''"'5.bb:'''''6.OO"'
7.00 ' 8.00 ' 9.00 ' l0:OO - !
3M Environmental Laboratoty
3M Environmental Laboratory
Page 129 of 226 Page 129
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Report E01-1245
udy With the Northern Bobwhite
~
t01-1365-31285,lO ppm a.i. 568 M Liver, offspring IM Environmental Lab
1020218063 Sm (.Mn, -1x2),
100
6.72 296813
davey 07079! 18-Feb-2002, -19:01:51 1: MRM of 1 Channel ES-
TIC 3.19d
Are:
%
0
3M Environmental Laboratory
3M Environmental Laboratory
L^
I ,7iTime
.OO 8.00 9.00 10.00
Page 130 of 226 Page 130
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A ReproductionStudy with the Northern Bobwhite
E01-1342-30955, 10 ppm a.i. 399 M Liver, d10 IM Environmental Lab j020218064 Sm (Mn, 1x2)
100
6.73 305393
davey 0707M 18-Feb-2002,19:1 2 5 6 1: MRM of 1 Channel ES-
TIC 3.11e6
Area
%
I
0 ' 1.00 ' 2.00 ' 3.00 ' 4.00 ' 5.00 ' 6.00 ' 7.00 ' 8.00 ' 9.00 ' 1O:OO'"- 1
3M Environmental Laboratory
3M Environmental Laboratory
Page 131 of 226 Page 131
Report E01-1245
Report EO1-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
y with the Northern Bobwhite
:01-1365-31255,lO ppm a.i. 533 M Liver, offspring IM Environmental Lab
j020218054 Sm (Mn, 1x2)
100
6.72 246631
davey 0707% 18-Feb-2002,i7:21:5;
1: MRM of 1 Channel ESTIC
2.74et Are:
%
0
3M Environmental Laboratory
3M Environmental Laboratory
- I
.OO
8.00
9.00
Time 10.00
Page 132 of 226 Page 132
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A ReproductionStudywith the Northern Bobwhite
t01-1365-31265,lO ppm a.i. 545 M Liver, offspring IM Environmental Lab
1020218059 Sm (Mn, 1x2)
100
6.73 2591 29
daveyO7079d 18-Feb-2002, -l8:17:2 1: MRM of IChannel ES-
2.83TeI{6
Area
%
a
3M Environmental Laboratory
3M Environmental Laboratory
Page 133 of 226 Page 133
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northern Bobwhite
Dosed Group Female Offspring Liver Samples
,01-1365-31260,lOppm ami5.38 F Liver, offspring M Environmental Lab
020218055 Sm (Mn, 1x2)
100
6 73446716
davey 07079! l&Feb-2002, 17:33:0!
I: MRM of 1 Channel ESTIC
4.59ef Arez
%
a
3M Environmental Laboratory
3M Environmental Laboratory
Page 134of 226 Page 134
Report E01-1245
Report EOl-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFO$: A R e m q d i p n Study with the Northern Bobwhite
E01-1365-31250,10 ppm a.i. 525 F Liver, offspring
)M EnvironmentalLab
io20218053 Sm (Mn, 1x2)
ioa
6.73 314521
davey 070799 18-Feb-2002, 17:10:50 1: MRM of 1 Channel ES-
TIC 3.38e6
Area
!
%
0
3M Environmental Laboratory
3M Environmental Laboratory
Page 135 of 226 Page 135
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A PeproCludonStudy with the Northem Bobwhite
r01-1365-31275, I O ppm a.i. 557 F Liver, offspring LM Environmental Lab 1020218061 Srn (Mn, 1x2)
100
6.71 22587i
davey 07079: 18-Feb-2002, 18:39:3! 1: MRM of 1Channel ES-
TIC 2.28e
Are:
%
n 1.00 2.00 3.00 4.00
5.00 6.00
.OO 8.00 9.00
Time 10.00
3M Environmental Laboratory
3M Environmental Laboratory
Page 136 of 226 Page 136
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A ReproductionStudy with the NorthernBobwhite
iO1-1365-31280, I O ppm a.i. 561 F Liver, offspring M Environmental Lab 020218062 Srn (Mn, 1x2)
1 oa
6.72 242318
davey 07079t 18-Feb-2002, 18:50:41
1: MRM of 1 Channel ESTIC
2.73e6 Area
%
3M Environmental Laboratory
3M Environmental Laboratory
Page 137 of 226 Page 137
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite tudy yith the Northern Bobwhite
iO1-1365-31240,lO ppm a.i. 517 F Liver, offspring
M EnvironmentalLab
020218051 Sm (Mn, 1x2)
100
6.73
davey07079 18-Feb-2002, 16:48:4 1: MRM of 1Channel ES-
TIC 3.21e6
Area
%
' ' ' C
b,,88
88n8rTime
' 1.00 ' 2.00 ' 3.00 ' 4.00 ' 5.00 ' 6.00 ' 7.00
8.b0
9.00 10.00
~
3M Environmental Laboratory
3M Environmental Laboratory
Page 138 of 226 Page 138
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northern Bobwhite
Control Group Male Sera Sample
54-108-357, Oppm male, adult, 02-01-02 M Environmental Lab 020201058 Sm (.Mn.. 1x2,) IO0
davey 07079!
02-Feb-2002,03:59:2!
1: MRM of 1 Channel ES-
6.77
TIC
1695
2.12tM
Are:
%
3M Environmental Laboratory
3M Environmental Laboratory
Page 139 of 226 Page 139
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
:A
udy with the Northern Bobwhite
Control Group Female Sera Sample
54-108-366.- O.p.pm female, adult, 02-01-02
M EnvironmentalLab
320201066 Sm (Mn. 1x2)
oa
davey 070799
02-Feb-2002,05:28: 12
1: MRM of 1 Channel ES-
6.76-
590
TIC 7.4383
Area
%
I , ,0 , I I , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , I I I I I I I I I I I I I I I I 8 I I
I I I I t I I q I I I I I I I I I I I I I I I I I I Time
1.00 2.b0 I 3.00 I 4.00 5.00 6.00 7.00 8.00 9.00 10.00
3M Environmental Laboratory
3M Environmental Laboratory
Page 140 of 226 Page 140
Report E01-1245
Repott E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Control Group Male Offspring Sera Sample
54-108-253, Oppm male, offspring, 02-01-02
M Environmental Lab
10.0 % IO0 67.1784.
davey 07079!
OS-Feb-2002,1354:l! 1: MRM of 1Channel ES-
TIC 8.47eI
Are;
%
3M Environmental Laboratory
3M Environmental Laboratory
J
Page 141 of 226 Page 141
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
y ylth the Northern Bobwhite
I
Control Group Female Offspring Sera Sample
54-108-259, Oppm female, offspring, 02-01-02 M Environmental Lab 020207156 Sm (Mn, 1x2)
100 65.1793'
davey 07079! 08-Feb-2002,13:56:3'
1: MRM of 1 Channel ES-
TIC 6.10e:
Are;
0/1
1
3M Environmental Laboratory
3M Environmental Laboratory
t
Page 142 of 226 Page 142
Report E01-1245
Report E01-1245
Control Group Male Liver Sample
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A RepWJ1IF.blonStudy with the Northern Bobwhite
j020212058 Sm (Mn, 1x2)
1: MRM of 1 Channel ES
6.74
TI(
2246
2.55e
Are
3M EnvironmentalLaboratory
3M Environmental Laboratory
Page 143 of 226 Page 143
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northem Bobwhite
Control Group Female Liver Sample
1-1342-30627,O ppm a.i. 364 F Liver Environmental Lab !0212063 Sm (Mn,1x2)
0
davey 07079! 13-Feb-2002,01:58:0:
1: MRM of 1 Channel ESTIC
8.13e: Are:
c
3M Environmental Laboratory
3M Environmental Laboratory
Page 144 of 226 Page 144
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS A Reproduotian study with the Northern Bobwhite
Control Group Male Offspring Liver Sample
01-1365-311940,ppm a.i. 253 M Liver, offspring M Environmental Lab
020215039 Sm (Mn, 1x2) IO0 69.1765
davey 07079!
15Feb-2002,21:12:3;
1: MRM of 1 Channel ES-
TIC
9.66eI Are:
%
3M Environmental Laboratory
3M Environmental Laboratory
Page 145 of 226 Page 145
~
~~
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
8 orthem Bobwhite
PI
Control Group Female Offspring Liver Sample
E01-1365-31184, 0 ppm a.i. 246 F Liver, offspring 1M Environmental Lab 1020215038 Sm (Mn, 1x2)
I 0 0 610.7341.
davey 07079! 15-Feb-2002,21:01:2;
1: MRM of 1 Channel ESTIC
1.06s Arez
%
3M Environmental Laboratory
3M Environmental Laboratory
Page 146 of 226 Page 146
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
th the Northern Bobwhite
I
Extracted Sera Calibration Curve Point
bpb extracted curve point, sera 01-31-02 I Environmental Lab 20201020 Sm (Mn, 1x2)
6.76 13162
davey 07079!
OI-Feb-2002,20:57:21 1: MRM of 1 Channel ES-
TIC 1.Met
Are;
c
3M Environmental Laboratory
3M Environmental Laboratory
f"."----"------""--^, Time
00 8.00 9.00 10.00
Page 147 of 226 Page 147
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Report EO1-1245
111 j 1
I
rudy withthe NorthernBobwhite
Extracted Liver Calibration Curve Point
:01-1342-36007 Curve point-1 ppb in liver extract
IM EnvironmentalLab
. . 1020211022 Sm IMn. 1x2,)
100
6.72 1969
davey07079d ll-Feb-2002,20:16:33 1: MRM of 1 Channel ES-
TIC 2.53e4
Area
%
0
3M Environmental Laboratory
3M Environmental Laboratory
Page 148 of 226 Page 148
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
tpdy with the Northern Bobwhite
Unextracted Calibration Curve Point
12003-15-1 2.61 ppb unext IM EnvironmentalLab
1020201008 Sm (Mn. 1x2)
100
6.74 4858'
%
0
3M Environmental Laboratory
3M Environmental Laboratory
-I
1 Time I
.OO 8.00 9.00 10.00 ~
Page 149 of 226 Page 149
Report E01-1245
Report 01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
P-6: A Reprodudon Study wlth the Northern Bobwhite
Extracted Sera Calibration Curve
Dmpound 1 name: pfos (499>99) func 1 Method File: d020201a oefficient of Determination: 0.988137 alibration curve: -0.862805 * XY+ 1603.72 * x + 8692.86
esponse type: External Std, Area urvetype: 2nd Order, Origin: Exclude,Weighting: l/x, Axis trans: None
8.01e5
X
Sesponse
3M Environmental Laboratory
3M Environmental Laboratory
Page 150 of 226 Page 150
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
with the Northem Bobwhite
Extracted Liver Calibration Curve
Impound1name: pfos (499~99f)unc 1 MethodFile: d020215a lefficient of Determination: 0.988785 [librationcurve: -0.689309 * xA2 + 1283.97 * x + 845.279
sponse type: External Std, Area iwetype: 2nd Order, Origin: Exclude,Weighting: Ilx, Axis trans: None
6.43eE
X
Lesponsc
3M Environmental Laboratory
3M Environmental Laboratory
Page 151 of 226 Page 151
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A ReproductionStudy with the Northern Bobwhite
Mass Spectrometer Tune Settings
Tuning Method Report
Method :
C:\M?SSLYNX\DAVEY070799.PRO\ACQUDB\CENTREl
Printed:
Tue Mar 19 10:22:06 2002
Page 1
MS
SOURCE ( ESP- 1
Capillary Cone Hexapole 1 Aperture 1 Hexapole 2 Source Block Desolvation
Temp. Temp.
Set Rdbk
2.56 20 0.5 0.2 0.8 150 250
-2.48 -20
148 24 9
Pressures
Analyser Vacuum Gas Cell
Rdbk
3.8e-5 2.9e-3
Analyser
LM Res 1 HM Res 1 IEnergy 1 Entrance Collision Exit LM Res 2 HM Res 2 IEnergy 2 Multiplier
Gas Flows
Cone Gas Desolvation
Set Rdbk
13.0 13.0 0.7 2 11 1 11.0 11.0
1.0 650
1 11 0
-646
Rdbk
150.5 701.5
3M Environmental Laboratory
3M Environmental Laboratory
Page 152 of 226 Page 152
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS:A ReproductionStudy with the Northern Bobwhite
HPLC Settings
Method Report Method File: Last Modified: Printed:
Page 1
C:\MASSLYNX\DAVEY070799.PRO\A( Monday, March 11,2002 08:Ol:Ol
Tuesday, March 19, 2002 08:37:50
HPllOO LC Pump Initial Conditions
Solvents
A%
90.0
B %
10.0
C%
0.0
D%
0.0
Valve A set to channel
Valve B set to channel
Flow (mllrnin) Stop Time (mins) Min Pressure (bar) Max Pressure (bar) Oven Temperature Left("C) Oven Temperature Right("C)
0.300 10.0 0 400 40.0 40.0
HPllOO LC Pump Gradient Timetable
The gradient Timetable contains 5 entries which are :
Time
A%
B%
C%
D%
Flow
0.00
90.0
10.0
0.0
0.0
0.300
1.00
90.0
10.0
0.0
0.0
0.300
5.50
5.0
95.0
0.0
0.0
0.300
7.50
5.0
95.0
0.0
0.0
0.300
8.00
90.0
10 0
0.0
0.0
0 300
t - l P L~C~Pu~mpEmtlrfEvent Timetsbae
The Timetable contains 3 entries which are :
Time
Initial 0.00 0 10
Cctlunn Switch
OR
Off
OR
On
Ofl
Off
Contact1
CHI On
off
Contact2
OR OR Qfl
Gantac 6ff
On
off
HPIl o a Arahammplerlnixjd CcwlclEtions
Draw S p e d Eject S p e d (vlhin) Draw Position [mm)
S h p Time (rnins) Injection Volurne(pI] Vial Number Thema&& On
Thermostat Twnpenture(nC)
2m.o 2or3
0.00 1B.00 10.0 94
20.0
3M Environmental Laboratory
3M Environmental Laboratory
Page 153 of 226 Page 153
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A ReproductionStudy with the Northern Bobwhite
Mass Spectrometer Scanning Parameters
Scanning Method Report
Method:
C:\~SSLYNX\DAVEYO7O799.PRO\ACQUDB\1OMIN-PFOS-PFDA
Last Modified: Mon Jan 28 15:20:24 2002
Printed :
Tue Mar 19 08:38:22 2002
Solvent Delay ( mins ) :
0.00
Function : 1
MRM of 1 Mass Pair ( ESP- )
Inter Channel Delay ( Span ( Daltons ) : Start Time ( Mins ) :
End Time ( Mins ) : Repeats :
Channel Parent
Secs ) : Daughter
0.03
0.00 0.00
10.00 1 Dwell
(Secs) Coll
Energy
(eV)
Cone ( V )
1
499.00 99.00
0.30
43
60
Function : 2
MRM of 1 Mass Pair ( ESP- )
Inter Channel Delay ( Span ( Daltons 1 : Start Time ( Mins ) : End Time ( Mins ) : Repeats :
Channel Parent
Secs ) : Daughter
0.03 0.00 0.00 10.00 1
Dwell
(Secs) Coll
Energy
(eV)
Cone ( V )
1
513.00 2 1 9 . 0 0
0.30
20
20
3M Environmental Laboratory
3M Environmental Laboratory
Page 154 of 226 Page 154
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A ReproductionStudy with the Northern Bobwhite
ATTACHMENTD: SAMPLEPREPARATIOSNHEETS
3M Environmental Laboratory
3M Environmental Laboratory
Page 155 of 226 Page 155
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite SPE Columns Extraction Worksheet
Prep Date: Analysts initials:
I I Lims Assgned sample number
E01-1245-35773 E01-1245-35774
1/31/2002
\
1
3-i-.03caz
Method Revision: ETS-8-231 .O Study Number: EO1-135d@*j
(.j./ 02
Matrix: Sera
I I
Sample Number or description
Volume of sample filtered
(mi)
Type of column used and lot
Amount and spike Elution solv
mix used
and volurr
40+6
Waters, l g , 6ml, lot129082
2ml of MeOH
NA
TN-A-5457
40+6
Waters, l g , 6ml, lot 129082
NA
2ml of MeOH TN-A-5457
40+6 40+6
Waters, Ig, 6ml, lot 129082
Waters, I g , 6ml, lot 129082
1' Oul of 02001-53
.J
1OUl Of 02001-53
2ml of MeOH TN-A-5457
2ml of MeOH MA5457
I
40+6 40+6
Waters, l g , 6ml, lot I29082
Waters, l g , 6ml, lot 129082
,//2ul of 02001-52 4ul Of 02001-52
2ml of MeOH TN-A-5457
2ml of MeOH TN-A-5457
40+6
Waters, l g , 6ml,
2ml of MeOH
lot 129082
1' Oul of 02001-52 TN-A-5457
150 ppb sera curve I 100 ppb sera curve
40+6 40+6
Waters, l g , 6ml. lot 129082
!Waters, I g , 6ml, llot 129082
I ,/ 20ul of 02001-52
I./
I 4ul of 02001-53
2ml of MeOH 1TN-A-5457 12ml of MeOH ITN-A-5457
E01-1245-35775
250 oob sera curve
E01-1245-35776
500 ppb sera curve
E01-1245-35777
750 ppb sera curve
E01-1245-35778
1000 ppb sera curve
E01-1245-35779
QC-25 ppb-1
E01-1245-35780
QC-25 ppb-2
E01-1245-35781
QC-25 ppb-3
E01-1245-35782
QC-40 ppm-1
E01-1245-35783
QC-40 oom-2
E01-1245-35784
QC-40 ppm-3
E01-1245-35785
QC-80 ppm-1
E01-1245-35786
QC-80 ppm-2
E01-1245-35787
QC-80 ppm-3
n.~ l
:@lank Sera TN-A- 597 z ; Amount of sera aliquated:
Dilute Sera with Kandiyohiwater; Amount of water added
40+6
40+6 40+6 40+6 40+6
~~
40+6 40+6 40+6 40+6
2 ? fi
Waters, I g , 6ml, lot 129082 Waters, l g , 6ml,
Waters, l g , 6ml,
Waters, l g , 6ml, lot I29082 Waters, l g , 6ml, lot I29082 Waters, I g , 6ml, lot 129082 Waters, l g , 6ml, lot 129082
.Waters, lg, 6ml,
lot129082 Waters, l g , 6m!, lot I29082
Waters, l g , 6ml,
lot I29082 Waters, l g . 6ml, lot 129082 waiers,79. bmi, lot 129082
ml ml
J
20ul of 02001-53
,r
" 30ul of 02001-53
40Ul of 02001-53
1OUI Of 02001-52
.-1Oul of 02001-52
/l Oul of 02001-52 J
361.11of 02001-15
36ul Of 02001-15 J
361.11of 02001-15
/
7 2 ~o1f 02001-15
/
72ul of 02001-15
72ul of 02001-1 5
2ml of MeOH TN-A-5457
2ml of MeOH TN-A-5457
2ml of MeOH TN-A-5457 2ml of MeOH TN-A-5457 2ml of MeOH TN-A-5457
2ml of MeOH TN-A-5457 2ml of MeOH TN-A-5457
2ml of MeOH TN-A-5457
2ml of MeOH TN-A-5457 2ml of MeOH TN-A-5457 2ml of MeOH TN-A-5457 2ml of MeOH
TN-A-5457
Add 5ml of ACN (TN-A-
) to aliquat d Sam le0
sample for 20 min a300 rpm (Shaker&'z-c&?TqL )y"/ogg94-
Centrifugesample forOI min Q 2000 rpm (Centrifug&JWc I 3 )
Wash Column with KandiyohiWater
conditioned column, discarding filtrate
Allow column to go completelly dry
Elute column with indicatedamount of solvent ( HA3H TN-A- 5?5+
standard PFDA standard number &" I - 6 5
OJCa
b , 7 a 7 1 c 4 , &J / . / f . d~
ifi+wJ ~ ~ c . . D # ~ Gzf- 6AEx ~ ~ ~
) into appropriate 15 ml centrifugetube
, conc. 100.3 W
s@ otU2802-
3M Environmental Laboratory
Page 156
Report E01-1245
Prep Date: Analysts initials:
1/31/2002 WMOJ
~
~~
PFOS: A Reproduction Study with the Nothern Bobwhite
SPE Columns ExtractionWorksheet @ QW;~
&Sw1aijV2
%P
Method Revision: ETS-8-231 .O
Study Number: E01-126' r/..J (.J6 4
Matrix: Sera
@
Lims Assgned sample number
E01-1245-28443
EO 1-1245-28444
,vAAZ
454-108-329,OPPM, Male, Adult
454-108-330,0 PPM, Female, Adult
454-108-331,OPPM, Male,
sample
filtered
I
Type of column used and lot
Waters, l g , 6ml,
40+6
lot 129082
Waters, l g , 6ml,
40+6
lot 129082
Waters, Ig. 6m1,
E01-1245-28446 E01-1245-28447 E01-1245-28448 E01-1245-28449 E0l-1245-28450
L-lLYJ-L64J 1
E01L - I L 4 J -n L 6n4' r>-L E0l-1245-28453 E01-1245-28454
Eo1-l,A2~,vA~c
454-108-332,OPPM, Female,
.Adult
454-108-333,OPPM, Male,
Adult
454-108-335,OPPM, Male,
Adult
454-108-336,OPPM, Female,
Adult
454-108-337,OPPM, Male,
. .A_rli-il-t .-
...".. . 1454-108-338.0PPM, Female,[
I
AAiilt
I
I
I 454-108-339.0PPM. Male.' I
I I Adult
454-108-340,OPPM, Female,
Adult
454-108-341,OPPM, Male,
Adult
454-108-343,OPPM, Male,
40+6 40+6 40+6 4.0- +-6
d.n- +-6
40+6
40+6
Waters, l g , 6ml, lot 129082 Waters, I g , 6ml, lot 129082 Waters, lg. 6ml. lot 129082
iWaters. lg. 6ml,
lot 129082
I
[Waters, l g , 6ml, 129082
Waters, I g , 6ml, lot129082
Waters, lg. 6ml, lot 129082 Waters. I g , 6ml,
EO 1 - 1245-28456
l,Aq ,vAq7
-IATJ-LO-t,,
454-108-344,OPPM, Female,
A.d_ ul.t
I I 454-108-345,OPPM, Male, I Adult
I
I
40+6
IWaters, I g , 6ml, llot129082
I
Amount and spike Elution solvent
mix used
and volume
Comments
2ml of MeOH
NA
TN-A-5457
*13okAr
NA
2ml of MeOH TN-A-5457
4&@4~[
NA
2ml of MeOH TN-A-5457
4d6L
2ml of MeOH
-0
I 9 E d NA
TN-A-5457
12mlofMeOH 1 1
&a,+-.& NA
TN-A-5457
2ml of MeOH
NA
TN-A-5457
%owi
2ml of MeOH
NA
TN-A-5457
..
2ml of MeOH
NA
TN-A-5457
TN-A-5457
2ml of MeOH TN-A-5457
2ml of MeOH TN-A-5457
Q
lank Sera TN-A- 3994 ; Amount of sera aliquated:
ml
1ilute Sera with Kandiyohiwater; Amount of water
0 Aliquot 1ml of sera into 15 ml polypropelenetube
Spike samples accordingly
added
3 8 ml
3 . 3 t(0' +e&p'8E;oZ
Add 5ml of ACN (TN-A-4145 )to aliquated sample-
iShake sample for 20 min e300rpm (Shakervlr3c! ORa( FL/4'&N/G9$ Centrifugesample for 10 min 2000 rpm (Centrifuge.NftW613 Add 40 ml of Kandiyohiwater to 50 ml polypropelenecentrifugetube. Decantextract into centrifugetubes with water shake sample slightly to ensure proper mixing
Condition columnwith MeOH (TN-A- 754 )
Wash Column with KandiyohiWater
Filtersample through conditionedcolumn, discarding filtrate
/%)u Allow column to go completelly dry
Elute column with indicatedamount of solvent (
Spike samples with internalstandard PFDA standard number c
-T3raMnsfeEr nsavmirploeninmtoeanpptraiplriaLteallbyomraarkteodrayutovial
r p z e oWz&2
I
Page 157
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Study: E01-1245 Dilution DateIAnalyst: Box Number: /+t-=+W@L4s'
I
Attachment D: Dilutions Summary Worksheet
ii/.ZL/oz
Solvent/TN Number: Meow5457 w/ IS PFDA Extraction Date/Analyst: 1/31/02
Matrixmimepoint: &c;, I S Q ~ @LIS 1 1 / 2 L / ~ 2
I
Notes:
-
.-.
3M Environmental Laboratory
Page 158
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
SPE Standard CuNes--Fhids
Prep Dale(s): Analyst@): Sample Matrix: MethidlRevision: Target Analylets):
PFOS Sld: 5.02 ppm: PFOS Sld: 50.2ppm: PFOS S t d 2241 ppm: Surr.Sld Appnir. 100.7 ppm:
oiniio2. ozioiio2, oz113ioz OWHOl Quail Sera ETS-8-231. I PFOS
02001-52 02001-53 02001-15 02001-45
PFDA
-tual Concentrdtians of Standards in PFOS
Std Conc. ug/mL 5.02 5.02
5 .M
5.02 50.2 50.2 50.2 50.2 50.2 5.02 2241
5 FC Mix
Am't Spiked
0.0020
n.wo
n.nio0 n.0200 0.0040 0.0100 0.0200 0.0300 0.0400 0.0100 0.0360 0.0720 0.0100
Std Conc. u mL
100.7 100.7 100.7 100.7 100.7 100.7 100.7 100.7 100.7 100.7 100.7 100.7
0.0800 I 100.7
0.002 0.002
0.002
0.002 0,002
Standard Number
EOI-1245-35770.5.0 pph EOl-1245-35771, IO pph EOI-1245-35772.25 pph EOI-1245.35773.50 pph EOI-1245-35774, 1 0 0 pph EOI-1245-35775,250 pph EOI-1245.35776.500 pph EOI-1245.35777.750 m h
QC-25 pph pCC-40 ppm
Quail Sera MSIMSD-Day 1 Quail Sera MSMSD-Day 2 Quail Sera MS-5 pph IQuail Sera MS-200 pph
PFOS Std Conc.
nUmL 201 402 1004 2008 4016 10040 20080 30120
40160
PFDA Std Conc.
ng/mL 4028 4028 4028 4028 4028 4028 4028 4028
I 613520
3227040
loo40
I II 10040
4028
I 201
4028
I I R032
4028
Standard Number
EOl-1245-35770,5.0 pph EOl-1245-35771,10 pph EOl-1245-35772,25 pph EOl-1245-35773,50 pph EOl-1245-35774, 100 pph EOl-I245-35775,250 pph EOI-1245-35776,5Wpph EOl-1245-35777,750 pph EOI-1245-3577R, loo0 pph W-25 pph
O.C-40w..m
pC-SO ppm Quail Sera MSIMSD-Day I
Quail Sera MS-5 pph Quail Sera MS-200 pph
PFOS Std Conc.
ng/mL 5.02
10.0 25.1
50.2 100 25 I 502 753 1004 25.1
I 40338 RM76
I 251
PFDA Std Conc.
nUmL 101
101 101
in1 101 101 in1 101 in1 101
I in1 101
I 101
5.02
101
201
101
Study Number: E01-1245 Equipment Number: NA Find Siilvrnt & TN Number: MeOHfIT-A-05457 Blank Tissneildentifier: Quail Sera-TN-A-5992
All
mumL 0.0500 0.0500 0.0500 0.0500 0.0500 0.0500 0.0500 0.0500 0.0500 0.05~ 0.0500 0.0500 0.0500 0.0500 0.0500 0.0500
All Final Vol.
mL 2.OOO 2.W 2.W 2.000 2.ooO 2.000 2.ooO 2.ooO 2.W 2.W 2.W 2.W 2.ooO 2.ooO 2.W 2.W
Blank sera initial dilution (mWmL) for curves: Final siilvent viilume (mL) for C U N ~ S :
0.0500 2 W
Verified hy: , / ! . -
7/uL
3M Environmental Laboratory
SPE-013 102-QUA1LSERA-02001-52(PFOS).xls
Page 159
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Prep Date: Analysts initials:
I
Lims Assgned sample number
E01-1245-35825
E01-1245-35826
E01-1245-35827
E01-1245-35828
E01-1 245-28458
EO1- 1245-28459
E01-1245-28460
E01-1245-28461
E01 -1245-28462
E01-1245-28464
E01-I 245-28465
E01-1 245-2846
E01-1 245-28467
E01 -124528468
E01 -1245-28469
E01-1 245-28470 E01 - 1245-28471
I E01-1245-28472
E01-1245-28473 E01-1 245-28474
I E01-1245-28475
&& 211J2002
OWHOJ
ac
fi , c -"7_
I
Sample Number or description
(
t
y
' Blank H2O-day 2 eIJp1c.ow 3i*
'
L
Bwlanhk-lsLerae-da0,y6
2
I,~I+LYL
AAaHarrl Sera M5-day 2
I
W A I L OK l 3 / * Sera MSD-Day2
1454-108-346,O PPM. Female,
Adult
454-108-347,O PPM. Male, Adult
454-108-348,O PPM, Female, Adult
454-108-349, 0 PPM, Male,
.Adult
454-108-350,O PPM. Female,
Adult
454-108-351,O PPM, Male,
Adult
454-108-352,O PPM, Female,
Adult
454-108-353,O PPM, Male,
Adult
454-108-354,O PPM. Female, Adult
454-108-355,O PPM, Male, Adult
454-108-356,O PPM, Female, Adult
,454-108-357,O PPM, Male,
Adult
454-108-358,O PPM, Female,
Adult
454-108-359,O PPM, Male,
Adult
454-108-360,O PPM, Female,
Adult
I VUlUlIlt! VI
sample filtered Type of column
(.ml.)
used and lot
Waters, lg, 6ml,
40+6 lot 129082
Waters, lg, 6ml,
40+6 lot 129082
40+6
Waters, lg, 6ml, lot I29082
40+6
Waters, lg, 6ml, lot 129082
Waters, lg. 6ml,
40+6
Waters, Ig, 6ml, lot 129082 Waters, lg, 6ml,
Waters, Ig, 6ml,
. Adult - - u m,Male, Adult
M+6
Waters, l g , 6ml,
a ers, g, m I lot 129082
I Amount and spike mix used NA NA 1OUl Of 02001-53 1OUI Of 02001-53
Method Revision: ETS-8-231.O Study Number: E01-1245 Matrix: Sera
and volume
2ml of MeOH TN-A-5457
2ml of MeOH TN-A-5457
2ml of MeOH TN-A-5457
I
ux3-I+)*a
\%L p D 'hLAr
t
'
4
,
\
u.\
.s-iPc&.oPx*
e
d
2ml of MeOH TN-A-5457
2ml of MeOH
2ml of MeOH TN-A-5457
20ba
I 1 2ml of MeOH 1TN-A-5457
.c)
5RYd
2ml of MeOH TN-A-5457
2ml of MeOH TN-A-5457
2ml of MeOH TN-A-5457
5 1"' '4""r
r45y shake sample slightlyto ensure proper mixi
Condition column with MeOH (TN-A-
)
Wash Column with KandiyohiWater
Filter sample through conditioned column, discarding filtrate
Allow column to go completelly dry
Elute columnwith indicatedamount of solvent
Spike sampleswith internalstandard PFDA standard number h
Transfer sample into appripriatelly marked autovial
qj2e ~es.ad&
3M Environmental Laboratory
P h - 4 L&ll
h%-/ut-A i:, ck@5@*
Y@#7 -%w6 444
JX;rz;NJ
/ A L 66,'- Z/.z&L
- 3.8,
~ U W L i. / / G <
"- / d $ - V L
Page 160
Report E01-1245
Prep Date:
Analysts initials:
2/1/2002
PFOS: A Reproduction Study with the Nothern Bobwhite SPE Columns Extraction Worksheet
2.I.02
Method Revision: ETS-8-231 .O
lank Sera TN-A
liquot 1ml of sera into 15 ml polypropelenetube
pike samples accordingly
ql4c dd 5ml of ACN (TN-A-
) to aliquated sample
&?,w hake sample for 20 min @300 rpm (Shaker&$
6 9 Centrifugesample for 10 min @ 2000 rpm (CentrifugAg 7
y/N0'&6f4
6~
dd 40 ml of Kandiyohiwater to 50 ml polypropelenecentrifugetube.
Condition column with MeOH (TN-A-
Wash Column with Kandiyohi Water
Filter sample through conditioned column, discarding filtrate
Allow column to go completelly dry
Elute column with indicatedamount of solvent & m k TN-A-f?fd
) into appropriate 15 ml centrifugetube
Spike samples with internalstandard PFDA standard number 0 7 3 ~ 7-/&
, conc./&. h!!4 , amount added L L
T3rMansEfernsvaimrpolenimntoeanptparliprLiaatebllyomraartkoerdyautovial
&%
~
Page 161
Report E01-1245
Prep Date: Analysts initials:
211 12002 OW,!OJ
SPE
Columns
PFOS: Extraction
e $;$: A Reproduction Study with
Worksheet
q j the Nothern Bobwhite LRS 08/2110s
42 .*a OIL
Method Revision: ETS-8-231 .O Study Number: E01-1245
Lims Assgned sample number
E01-1245-28498 E01 -1245-28499 E01-1 245-28500 EOl-1245-28501
E01-1245-28502 E01-1245-28503
E01-1245-28504 E01-1245-28505 E01-1245-28506 E01-1245-28507
Unl-1 IA<-?P<nP
Y"L-.I7_I-I"_I"Y
E01-1245-28509 E01-1245-285IO
E01-1245-28511 E01-1245-28512
Sample Number or description
Volume of sample filtered
(mu
Type of column used and lot
Amount and spike Elution solvent
mix used
and volume
Comments
454-108-388, 10 PPM, Female, Adult
40+6
Waters, Ig, 6mI. lot129082
2ml of MeOH
NA
TN-A-5457
454-108-389, IO PPM, Male, Adult
.--. 454-108-390, 10PPM, Female,
Arliilt
I
I
I
I
I
454-108-391, IO"r"'riw iIv`li'ie, 1 H*U'UI`J
''II 454-108-392, 10PPM, Female,
I
Adult
454-108-393. IO"r""rw M'a'e, xa'u
I 454-108-394, IOPPM,Female,
I
Adult
I
d 1454-108-395. 10 PPM, Male, Adul 454-108-396, lOPPM, Female,
Adult
40+6
M.-+6
40+6 40+6
40+6 40+6 40+6
Waters, I g , 6ml, lot 129082
I Waters, I g , 6ml,
llot 129082 Waters, I g , 6ml. lot129082 Waters, I g , 6ml, lot 129082
Waters, I g , 6ml. lot129082 Waters, l g , 6ml. lot 129082 Waters, I g , 6ml. lot 129082
NA
2ml of MeOH TN-A-5457
p oc
2ml of MeOH
9
NA
ITN-A-5457
1 LC%k?&
. Gf - 2ml of MeOH
NA
TN-A-5457
&a .-c/
2ml of MeOH
NA TN-A-5457 I " I/
2ml of MeOH
NA
TN-A-5457
NA
2ml of MeOH TN-A-5457
3~ a y c ,
NA
2nd of MeOH TN-A-5457
z----c.
2ml of MeOH
0
NA
TN-A-5457
70kL
454-108-397, lOPPM,Male, Add
454-108-398, IO PPM, Female, Adult
40+6 40+6
Waters, Ig. 6ml,
lot Waters, I g , 6ml, lot 129082
NA
2ml of MeOH TN-A-5457
7-
2ml of MeOH
NA
TN-A-5457
.--" I Waters, Ig, 6ml,
454-108-399, IO PPM, Male, Adult
40+6
lot 129082
NA
454108401, IOPPM,Male, t"
IWaters, l g , 6ml,
40+6 /lot129082
NA
454.108402, IO PPM, Female,
Adult
NA
2ml of MeOH TN-A-5457
2ml of MeOH -A3457
2ml of MeOH TN-A-5457
/OV..L
I
454-108403, IO PPM, Male, Add
40+6
IWaters. l g , 6ml, lot 129082
I
NA
2ml of MeOH ITN-A-5457
I @w[-
454-108-404,lO PPM,
lank Sera TN-A- j / s 4 2 ; Amount of sera aliquated: &/A- ml
ilute Sera with Kandiyohiwater; Amount of water added A&- ml
Aliquot 1ml of sera into 15 ml polypropelenetube
Spike samples according1
Add 5ml of ACN (TN-A- ?45 ) to
Shake sample for 20 min @300 rpm Centrifugesample forOI min 2000 rpm (centrifuge2
3~y~t~
40 ml of Kandiyohiwater to 50 ml polypropelenecentrifugetube.
Decantextract into centrifugetubes with water
TTff shake sample slightlyto ensure proper mixing
Condition column with MeOH (TN-A-
)
Wash Column with KandiyohiWater
Filter sample through conditioned column, discarding filtrate
Allow column to go completelly dry
f [a, ?A/ Elute column with indicatedamount of solvent
T N - A - 5 7 1 4 into appropriate 15 ml centrifugetube
Spike samples with internalstandard PFDA standard number %?W !-
, conc.
?&4, amount added
-/-0
Tr3aMnsfeEr snavmiprloeninmtoeapnptraiplriaLteallby omraarkteodrayutovial
Page 162
Report E01-1245
Analysts initials:
3 SPE
Columns
ExtraPcFtiOoSn:WAoRrekpsrhoeduecttion@StudQyucw*;lith
the
Nothern Bobwhite US ~8jail~2
PG@ Y o f Y
Method Revision: ETS-8-231.O
Add 40 ml of Kandiyohiwater to 50 ml polypropelenecentrifugetube.
D', ecant
extract into centrifugetubes with water
s& shake sample slightlyto ensure proper mixing
Condition column with MeOH (TN-A-
)
Wash Column with KandiyohiWater
Filter sample through conditioned column, discarding filtrate
fqr' Allow columnto go completelly dry
Elute column with indicatedamount of solvent ( &a# TN-A-
.Spike samples with internalstandard PFDA standard number 02-1
T3raMnsfEernsavmirpoleninmtoeanptpariplrLiataelblyomraartkoedrayutovial
-41 J ) into appropriate 1 ml qentrifugetube , conc. d o $// amount added
ZwL
Zvd7/*
Page 163
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
BOTTLE-TODPISPENSEDRAILYCALIBRATION CHECK
Manufacturer andModel:
5d
Date: 2 I ' 0 2
Initials: 0 p(l
Dispenser ID: 07 9 9
BalanceID: q C u
Volume: 5nhE-Q
Solvent: A C d
m#:W-A- 4I4<
I Mass of solvent (g) I
Density'
I Volume of Solvent I
Std. Dev.: ?A0C.V. :
Passmail:
Volume,
I
Accuracy,
(d) 1 to 10
(%I
98.0 - 102 %
00.3%
C.V., f 1.0 %
1Density values taken from the Merck Index, 12'h Edition, Copyright 1996 dy, =specific gravity at ydegreesreferred to water at xdegrees n-Hexane dZo4=0.660 Acetone d2504 . 7 8 8 Methanol d254=0.7866 Methylene Chloride dZo4=1.3255
3M Environmental Laboratory
Page 164
Report E01-1245
SPE Columns ExtracPtiFoOn WS:oArkRsheeperot duction Study with the Nothern Bobwhite
I
Lims Assigned sample number
1E01-1342-30312
1E01-1342-30323
lE0l-1342-30330
~_____
EOl-1342-30339
E01-1342-30348
E01-1342-30357
EO 1- 1342-30366
E01-1342-30375
E01-1342-30384
EO 1 - 1342-30393 IEO1 - 1342-30402
IEO1-1342-30411
~~~~
EO 1-1342-30420
EO 1-1342-30429
EO 1-1342-30438
EO 1-1342-30447
E0l-1342-30456
EO 1-1342-30465
lE0l-1342-30474
1801-1342-30501
Sample Number or description
0 ppm a.i. 329 M Liver
0 ppm a.i. 330 F
Liver 0 ppm a.i. 331 M
Liver 0 ppm a.i. 332 F
Liver
0 ppm a.i. 333 M
Liver 0 ppm a i . 334 F
Liver 0 ppm a.i. 335 M
Liver 0 ppm a.i. 336 F
Liver
0 ppm a.i. 337 M
Liver 0 pprn a.i. 338 F
Liver 0 ppm a.i. 339 M
Liver
0 ppm a.i. 340 F
Liver
0 ppm a.i. 341 M
Liver
0 ppm a.i. 342 F Liver
0 ppm a.i. 343 M
Liver 0 p. .pm a.i. 344 F
Liver 0 ppm a.i. 345 M
Liver 0 ppm a.i. 346 F
Liver 0 ppm a.i. 347 M
Liver
0 ppm a.i. 348 F
Liver 0 ppm ai. 349 M
Liver
0 ppm a.i. 350 F Liver
Blank Liver TN-A-
; Amount of liver:
g
Homogenizeliver with Kandiyohiwater; Amount of water added
ml
Aliquot 1ml of liver into 15 rnl polypropelenetube
Spike samples accordingly
Add 5ml of ACN (TN-A-
) to aliquated sample
Shake sample for 20 min a300 rpm (Shaker
)
Centrifuge sample for 10 min Q 2000 rpm (Centrifuge
)
Add 40 ml of Kandiyohiwater to 50 ml polypropelenecentrifugetube.
Decant extract into centrifugetubes with water
shake sample slightly to ensure proper mixing
Condition column with MeOH (TN-A-
Amount of liver
* I<OJ E;-
3M Environmental Laboratory
Page 165
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
SPE Columns Extraction Worksheet
Blank Liver TN-A-
; Amount of liver:
g
Homogenizeliver with Kandiyohiwater; Amount of water added
ml
Aliquot 1ml of liver into 15 ml polypropelenetube
Spike samples accordingly
Add 5ml of ACN (TN-A-
) to aliquated sample
Shake sample for 20 min Q300 rpm (Shaker
)
Centrifuge sample for 10 min Q 2000 rpm (Centrifuge
)
Add 40 ml of Kandiyohiwater to 50 ml polypropelenecentrifugetube.
Decant extract into centrifugetubes with water
shake sample slightly to ensure proper mixing
Condition column with MeOH (TN-A-
3M Environmental Laboratory
Page 166
Report E01-1245
SPE Columns ExtracPtiFoOnSW:oArkRsheeperot duction Study with the Nothern Bobwhite
Prep Date: Analysts initials:
C:+L I
~CJIJ
Method Revision: C31- 8 . 23t. / Study Number: e-&/-/F?r
Matrix: L-1
number E01-1342-30708 E01-1342-30717
or description
Volume of sample Type of column used Amount and Elutionsolvent Amount of liver
filtered (ml)
and lot
spike mix used and volume
I
Liver
10 ppm a.i. 374 F
I ;\mr
EO 1-1342-30865
Liver
Liver
EO 1- 1342-30892
I Liver 10 ppm a.i.392 b
Liver
EO 1-1342-30901
Liver
EO 1-1 342-30910
-.
Blank Liver TN-A- 514 3 ;Amount oh&:
Homogenize liver with Kandiyohiwater; Amount of water addegd
Aliquot 1ml of liver into 15 ml polypropelenetube
Spike samples accordingly
Add 5ml of ACN (TN-A-
) to aliquated sample
Shake sample for 20 min e300 rpm (Shaker
)
Centrifuge sample for 10 min Q 2000 rpm (Centrifuge
)
Add 40 ml of Kandiyohiwater to 50 ml polypropelenecentrifugetube.
Decantextract into centrifugetubes with water
shake sample slightly to ensure proper mixing
Condition column with MeOH (TN-A-
)
Wash Column with KandiyohiWater
Filter sample through conditioned column, discarding filtrate
Allow column to go completelly dry
Elutecolumnwith indicatedamount of solvent (
TN-A-
Spike samples with internalstandard PFDA standard number
Transfer sample into appripriatelly marked autovial
) into appropriate 15 ml centrifugetube
, conc.
, amount added
I
3M Environmental Laboratory
Page 167
Report E01-1245
Lims Assigned sample number
EO 1-1342-30919
Sample Number
I or descriDtion
I
10 ppm. .a.i. 395 M
E01-1342-30928
EO1-1342-30937 -
E01-1342-309476E%~
2
E01-1342-30955
EO 1-1342-30964
E01-1342-30973
E0l-1342-30982
EO 1-1342-30991
I
Liver
It 12%10 ppmk an.iL. 3,98wF~
10 ppm a i . 399 M Liver
10 ppm a.i. 400 F Liver
10 ppm a.i. 401 M Liver
10 ppm a.i. 402 F Liver
10 ppm. .a.i. 403 M
10 ppm a.i. 404 F
10 ppm a.i. 405 M
EO 1-1342-31018
10 ppm a.i. 406 F
EO 1-1342-31 0 2 7 EO 1-1342-31036
Liver 10 ppm a.i. 408 F
Liver
PFOS: A Reproduction Study with the Nothern Bobwhite
SPE Columns ExtractionWorksheet
Matrix: C / r
Amount of live weighed (9)
Comments
Blank Liver TN-A-
; Amount of liver:
g
Homogenizeliver with Kandiyohiwater; Amount of water added
ml
Aliquot 1rnl of liver into 15 ml polypropelenetube
Spike samples accordingly
Add 5ml of ACN (TN-A-
) to aliquated sample
\
V
7
3M Environmental Laboratory
riate 15 ml centrifugetube
, conc.
, amount added
Page 168
Report E01-1245
Prep Date:
I
Lims Assigned Sample number
I
Sample Number or description
E01-1365-31199
EO1-1365-3 1214
I
0 ppm a.i. 256 M
Liver F
M
8".
0 ppm a.i. 270 M
' -
Liver %.i2. 73 F
I
Liver
PFOS: A Reproduction Study with the Nothern Bobwhite
SPE Columns ExtractionWorksheet
E01-1365-31270 EO1-1365-3 1275 E01-1365-31280 E01-1365-31285
10 ppm a.i.9ZlW Liver
10 ppm a.i. bbl F
Liver 10 ppm a.i.561 I-
Liver
10ppm 8.1.568 IT
Liver
Blank Liver TN-A-
; Amount of liver:
g
Homogenize liver with Kandiyohi water; Amount of water added
Aliquot 1ml of liver into 15 ml polypropelenetube
Spike samples accordingly
/
Shake sample for 20 min e300 rpm (Shaker
Condition column with Wash Column with Kandiyhi Water
/vM.&e-y 0./1 4d.J M b F 4 h Y m f Lurt*ry
A 4 c - d A%- a k l k A e / a
0 < 3 3 --z-$-P&
- G -49 - 0 J-9
C"b3
3 - k AL
4.5hL
-5.44
6.3-j -k*J*,L
6 .87 -3-2-sL
&2&*
2-8 q+-
@ Tf(i5 j5 7-eut.
m;C3 wv f=& ALC
L , bfeqc3 we f q H e 3
id
C>waY.
3M Environmental Laboratory
Page 169
Report E01-1245
SPE Columns ExtractPioFnOWSo: rAksRheepertoduction Study with the Nothern Bobwhite
Prep Date:
211 112002
Analysts initials: 0K.HOJ
$./pa
OK - I
Lims Assigned sample number
Sample Number or description
1
Volume of sample
filtered (ml)
40+6
+ I E01-1342-36003
E01-1342-36004
Female liver MSday 1 Female liver MSDday 1
40+6
40+6
40+6
I
40+6
E01-1342-36005
Curve point-0.2 ppb in liver extract
40+6
E01-1342-36006
Curve point-OS ppb in liver extract
40+6
E0 1- 1342-36007
Curve point-I ppb in liver extract
40+6
E01-1342-36008
Curve point-2.5 ppb in liver extract
40+6
E0 1-1342-36009
Curve point-5 ppb in liver extract
40+6
E01-1342-36010
Curve point-IO ppb in liver extract
40+6
E01-1342-36011
Curve point-25 ppb in liver extract
40+6
E01-1342-36012
Curve point50 ppb in liver extract
40+6
E01-1342-36013
Curve point-75 ppb in liver extract
40+6
E01-1342-36014
Curve point-I00 ppb in liver extract
Curve point-I00 ppb-2 in
extract
40+6
I I I 40+6
40+6 I
@AL@
"
Method Revision: ETS-8-231.o
Study Number:E01-+34W36S , y B r @&d
?e/f.dz
I
Type of column Amount and spike
used and lot
mix used
Matrix:
Elution solver and volume
Liver
Comments
C18, l g , 6cc, lot
W202581
NA
2ml MeOH TNA-5754
C18, l g , 6cc. lot W202581
C18, lg, 6cc, lot W202581
C18, l g , 6cc. lot
W202581 C18. Ig.6cc. lot
W2025B1 C18, l g , 6cc, lot
W2025B1
NA
NA
I I 50ul of 02001-66
I
I
I
2rnl MeOH TN-A-5754 2ml MeOH TNA-5754 2ml MeOH TN-A-5754 2mlMeOH
2mlMeOH
C18, lg. 6cc, lot
W202581
C18, l g , 6cc, lot
W202581
C18, lg. 6cc, lot W202581
5Ul Of 02001-66
TNA-5754
C18, l g , 6cc, lot W2025B1
1OUl of 02001-66
2ml MeOH TNA-5754
CIS, lg, 6cc, lot W202581
20Ul Of 02001-66
2rnl MeOH TN-A-5754
C18, l g , 6cc. lot W202581
5 0 ~o1f 02001-66
2ml MeOH TN-A-5754
C18, l a . 6cc. lot
W2025B1
1OOUI Of 02001-66
2rnl MeOH TN-A5754
C18, lg, 6cc, lot W202581
C18. l g , 6cc, lot W202581
150~O1f 02001-66 200~1Of 02001-66
2ml MeOH TN-A-5754 2ml MeOH TN-A-5754
W202581
41.11Of 02001-53
2ml MeOH TN-A-5754
W202581
1 0 ~O1f 02001-53
2ml MeOH TNA5754
W202581
C18, I g , 6cc, lot W2025B1
ti1LI. l a . occ, IO1 W2025B1
I I 20ul of 02001-53
I
1
I I 30ul of 02001-53
I
I
I I 40ul of 02001-53
2ml MeOH
TN-A-5754
2mlMeOH TN-A-5754
L LrniMevn
HALewfgI3 @ TN-A-5754
OA q . 4 e 2
Blank Liver T N - A - 5 1 4 3 ; Amount o
d C)35'3g
Blank Liver T N - A - S / 4 & ; Amount ofk&- 1
Homogenize liver with Kandiyohi water; Amount of water added qg ml
Amount of water added 7
Aliquot 1ml of liver into 15 ml polypropelene tube
1 4 5 Spike samples accordingly
Add 5ml of ACN (TN-A- '!
) to aliquated sample
Shake sample for 20 min @300 rpm (Shaker deb 3d/q+eL
Centrifuge sample forOI min @ 2000 rpm (Centrifuge ~ - 7 9d6 9 g j 3
' B4'6'9G
Add 40 ml of Kandiyohi water to 50 ml polypropelene centrifuge tube.
Decant extract into centrifuge tubes with water
shake sample slightly to ensure proper mixing
Condition column with MeOH (TN-A- 57 54 )
Wash Column with Kandiyohi Water
Filter sample through conditioned column, discarding filtrate
g ml
Allow column to go completelly dry
4 Elute column with indicated amount of solvent (
TN-A- 5? 5
2 , d Spike samples with internal standard PFDA standard number oac-at-
Transfer sample into appripriatelly marked autovial
) in& appropriate 15 ml centrifuge tube
4 5
7 , conc. (00-pTM, amount added I\
c & $ ~ p O x h Q p A k W @ ' ! $7 6'** fa?-o2op(
d.
U
3M Environmental Laboratory
Page 170
Report E01-1245
a - l r ' PrepDate:
OR
Analysts initials: 06
0 1-1342-360 18
PFOS: A Reproduction Study with the Nothern Bobwhite
SPE Columns Extraction Worksheet
Method Revision: t7 5-P-231-
Blank Liver TN-A- 2 14% ; Amount of liver: 9.0353g
Homogenize liver with Kandiyohi water; Amount of water added
Blank Liver TN-A- 5 I42J ; Amount of liver: /,O&sg
4 5 ml
Amount of water added 9 ml
Aliquot 1ml of liver into 15 ml polypropelene tube
Spike samples accordingly
4/45 Add 5rnl of ACN (TN-A-
) to aliquated sample
duoe ' Shake sample for 20 rnin Q300 rpm (Shaker
s&04'
M Centrifuge sample for IO min Q 2000 rpm (Centrifuge W t C 9
Add 40 ml of Kandiyohi water to 50 ml polypropelene centrifuge tube.
Decant extract into centrifuge tubes with water
shake sample slightly to ensure proper mixing
Condition column with MeOH (TN-A- 5j44 )
Wash Column with Kandiyohi Water
Filter sample through conditioned column, discarding filtrate
Allow column to go completelly dry
%Ov w3q Elute column with indicated amount of solvent (
TN-A-
) into appropriate 15 ml centrifuge tube
o ? @ /4 5 Spike samples with internal standard PFDA standard number
-
Transfer sample into appripriatelly marked autovial
3M Environmental Laboratory
Page 171
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
SPE Standard Curver--Sohds
Prep Date($: Analysl(s): Sample Matrix: MethodlRevision: Target Analyte(s):
FC Mix Std Apprar. I 00 ppm: FC Mix Sld Approx. 5 02 ppm FC Mix Std Approx. 50 2 ppm: Surr. Std Approx. 100 7 ppm:
0211 1/02. 02/12/02, 02/13/02, 02/15/02 OWHOJ Qual Liver ETS-8-231 1 PFOS
02001-66 02001-52 02001-53 02001-45
PFDA
Actual Concentrationsof Standards Standard Number
E01 -1342-36005 E0l-1342-36006 EO I - 1342-36007 E01-1342-36008 E01-1342-36009 E01-1342-36010 E01-1342-36011 E01-1342-36012 EOI-I 342-36013 E0l-1342-36014 EO1-1 342-36062 E01-1 342-36015 E0l-1342-36016 EO 1-1342-36060 E01-1342-36061 QC-IOppb QC-75 ppb QC-I50 ppb Qual Liver-MSMSD-Day 1 Qual Liver-MSNSD-Day 2 Qual Liver-MSMSD-Day 3 Qual Liver-MSMSD-Day 4
le FC Mix PFOS
Std Conc UdmL 1004 I 004 I 004 I 004 1004 1004 I 004 I004 1 004 1 004 50 20 50 20 50 20 50 20 50 20 5 020 5 020 5 020 1 004 1 004 1004 I004
PFOS Am't Spiked
mL 0 0004 0 0010 0 0020 0 0050 00100 0 0200 0 0500 0 1000 0 IS00 0 2000 0 0040 00100 0 0200 0 0300 0 0400 0 0040 0 0300 0 0600 0 OS00 0 0500 0 0500 0 0500
Calculated Concentrationsof Standa Standard Number
E01-1342-36005 E01-1342-36006 01-1342-36007 EOI-1342-36008 E0l-1342-36009 EOI-1342-36010 EOI-1342-3601 I E01-1342-36012 E01-1342-36013 E01-1342-36014 EO1- 1342.36062 E0l-1342-36015 E0l-1342-36016 01-1342-36060 E01- 1342.36061 QC-IO ppb QC-75 ppb QC-150 ppb Qual Liver-MSMSD-Day I Qual Liver-MSMSD-Day 2 Qual Liver-MSMSD-Day 3 Quail Liver-MSNSD-Day 4
in the sample I PFOS
Std Conc nglg 3 99 9 98 20 0 49 9 99 8 200 499 998 I496 1995 1995 4988 9977 14965
I9953
zoo
1496 2993 499 499 499 499
IIX
PFDA Std Conc
ndr: 2001 2001 2001 2001 2001 2001 2001 2001 2001 2001 200 I 2001 2001 2001 2001 2001 2001 2001 2001 2001 2001 2001
PFDA Std Conc
"g/mL 100 7 100 7 100 7 100 7 100 7 100 7 100 7 1007 100 7 100 7 100 7 100 7 100 7 100 7 100 7 100 7 100 7 100 7 100 7 100 7 100 7 100 7
Study Number: 01-I245 Equipment Number: NA Final Solvent & TN Number: M e o w - A - 5 7 5 4 Blank Tissuelldentifier: Qual Liver(female)KN-A-5 I43
Qual Liver(male)m-A-5 I42
h t i a l female homogenate = 5 0353d50 0353g+mL = 0 1006 g/mL hiha1 male homogenate = I 0015glIO 0015g+mL = 0 1001glmL
Blank liver initial homogenate (g/mL) for curies. MS, QC: Final solvent volume (mL) for cwves, MS, QC:
3Initial L:ogenate
mL
g/mL
0002
'
0 1006
0 002
0 1006
0 002
0 1006
0 002
0 1006
0 002
0 IO06
0 002
0 1006
0 002
0 1006
0 002
0 1006
0 002
0 1006
0 002
0 1006
0 002
0 1006
0 002
0 1006
0 002
0 IO06
0 002
0 I006
0 002
0 1006
0 002
0 1006
0 002
0 1006
0 002
0 1006
0 002
0 1006
0 002
0 1006
0 002
0 1006
0 002
0 1006
All Final Vol
mL 2 000 2 000 2 000 2 000 2 000 2 000 2 000 2 000 2 000 2 000 2 000 2 000 2 000 2 000 2 000 2 000 2 000 2 000 2 000 2 000 2 000 2 000
0 1006 2 000
Calculated Concentrationsof Standa Standard Number
EO 1-1 342-36005 EO 1-1 342-36006 01-1342-36007 E01-1342-36008 E01-1342-36009 E01-1342-36010 EOl-1342-3601 I EOI-1342.360 I2 01- I 342-360I 3 EOI-1342-36014 E01-I 342-36062 EOI-1342-36015 EO1 -1342-3601 6 EO I - 1342-36060 EOl-1342-36061 QC-l0ppb QC-75 ppb
Qual Liver-MSMSD-Day I Oual Liver-MSMSD-Dav 2 Qual Liver-MSiMSD-Day 3 Qual Liver-MSMSD-Day 4
m the final sol PFOS
Std Conc og/mL 0 201 0 502 100 2 51 5 02 IO0 25 I 50 2 75 3 100 IO0 25 I 502 753 1004 10 0 75 3 151 25 I 25 I 25 1 25 1
PFDA Std Conc
nglmL 101 101 101 101 101 101 101 101 101 101 101 101 101 101 101 101 101 101 101 101 101 101
3M Environmental Laboratory
SPE-021102-QUAILLIVER-02001-66(PFOXSI)S
0 1006 0 1001
Page 172
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
BOTTLE-TOPDISPENSERDAILYCALIBRATION CHECK
Manufacturer VCUL
and Model:
Date: 67-(/.a2
Initials:& Dispenser ID: c-`35
6~ Balance ID: 900 Volume: Solvent: /dLy In #: ,T A. Q / 4 f
Mass of solvent (g)
Density'
I Volume of Solvent I
I Averagevolume: I
1 %Accuracy: Std. Dev.:
f`- 0333/aa. '30 ,6 b 3987-
Volume,
(d) 1 to 10
Accuracy,
(%>
98.0 - 102 %
Ma&
b44
Corrective Actions:
&J 2 -C t - T L
C.V.,
("A) k 1.0%
`Density values taken from the Merck Index, 12thEdition, Copyright 1996 dY,=specific gravity at ydegreesreferred to water at xdegrees n-Hexane dzo4=0.660 Acetone dzs0=0.788 Methanol d254=0.7866 Methylene Chloride dZo4=1.3255
3M Environmental Laboratory
Page 173
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Prep Date: Analysts initials:
Lims Assigned sample number
E01-1342-36026 EO 1- 1342-36027 EO 1-1342-36028 EO 1-1342-36029 EO 1- 1342-36030
2/12/2002 Qt( OWHOJ 2.12.02
Sample Number or description
Blank HZO-day 2 Blank female liver-day 2 Blank male liver-day 2 Female liver MSday 2 Female liver MSDday 2
Volume of sample filtered (ml)
40t6 40+6 40+6 40t6 40t6
Method Revision: ETS-8-231. Study Number: E01-
O
r
-~ *
-
A??
Matrix: Liver
Type of column Amount and
used and lot spike mix used
Cnmrnnntc
C18, l g , 6cc, lot W2025B1
CIS, l g , 6cc. lot W2025B1
C18, l g , ~ C C l,ot
W2025B1
C18, l g , ~ C C l,ot
CISW, 2l g0.265cBc1, lot I'
NA NA NA
NA
I NA
I NA
NA NA
2ml MeOH TN-A5754 2ml MeOH TN-A-5754 2ml MeOH
TN-A-5754 2ml MeOH
'"LA5754
I - . ,2ml MA.e?OH-,.-.
I
mi M e v n
-.,*r-,r,
I
I
zmi M e w TNA-5754 2ml MeOH
bf T-N-.A.-.57-5.4.
Blank Liver TN-A- 6 / 4 3 ; Amount of liver: 3 0 3 s 3 g
Homogenize liver with Kandiyohi water; Amount of water added Aliquot 1rnl of liver into 15 ml polypropelene tube
'a Blank Liver TN-A-
; Amount of liver: I . G O I 5- 9
45 ml
Amount of water added 9
ml
Spike samples accordingly
414 Add 5ml of ACN (TN-A-
) to aliquated sample
Shake sample for 20 min Q300 rpm (Shaker V W f L 5@
041694
Centrifuge sample for IO min Q 2000 rpm (Centrifugew@ 3 6w13
Add 40 ml of Kandiyohi water to 50 ml polypropelene centrifuge tube.
Decant extract into centrifuge tubes with water
shake sample slightly to ensure proper mixin
Condition column with MeOH (TN-A- 575-4 )
Wash Column with Kandiyohi Water
Filter sample through conditioned column, discarding filtrate
Allow column to go completelly dry
r 7 5 q Elute column with indicated amount of solvent ( HeoH TN-A-
oaoo - m, Spike samples with internal standard PFDA standard number
) into appropriate 15 ml centrifuge tube
4%
, conc. [*' =f. amount added
Transfer sample into appripriatelly marked autovial
3M Environmental Laboratory
Page 174
Report E01-1245
Prep Date: Analysts initials:
2/12/2002 OWHOJ
3 us SPE Columns ExtractioPnFWOoSr:kAshReeetproduction Study with the Noot~he/rn~Boabwl h~ite~
.a 2.Q.&
Method Revision: ETS-8-231
Study Number: EOl-t5Mft365 f 9 r &
Matrix: Liver
Lims Assigned sample number
E01-1342-30537
EO 1- 1342-30546
Sample Number or description
0 ppm a.i. 354 F Liver
0 ppm a i . 355 M Liver
Volume of sample filtered (ml)
40+6
40t6
Type of column used and lot
C18, l g , 6cc, lot W202581
C18, lg, 6cc, lot
Amount and
. spike mix used
I
Elutionsolvent and volume
E01-1342-30555 E01-1342-30564 E01-1342-30573
EO 1-1342-30582 1E01-1342-30591
1E01-1342-30600 lE01-1342-30609
0 ppm a.i. 356 F Liver
0 ppm a.i. 357 M Liver
0 ppm a.i. 358 F Liver
0 ppm a.i. 359 M Liver
I 0 ppm a.i. 360 F Liver I I 0 ppm a.i. 361 M Liver I
I 0 ppm a.i. 362 F Liver I
40t6 40+6 40t6 40+6 40t6 40+6 40+6
C18, l g , 6cc, lot
v-----.
C18, l g , 6cc, lot W202581
C18. l g , 6cc, lot
C18W, 2l g02, 65c8c1, lot I'
I c1!8n'nlng ?c69 .cac+' lot
I c1!8nsnl gn'?6ccnciDlot
I innlng 'l6c'cnci ' lot
Comments
Blank Liver TN-A- 5 'h3 ; Amount of liver: ,0353 g
Homogenize liver with Kandiyohi water; Amount of water added Aliquot 1ml of liver into 15 ml polypropelene tube
Blank Liver TN-A-4 '42 ; Amount of liver: ).-)<
45 ml
Amount of water added 9
g ml
Spike samples accordingly
5 Add 5ml of ACN (TN-A- 1114 ) to aliquated sample
' Shake sample for 20 min @300 rpm (Shaker VU-)@ " y d "
67 6 Centrifuge sample for 1o min Q 2000 rpm (Centrifuge N/+3
5/M 04 I 69$ I 3
Add 40 ml of Kandiyohi water to 50 ml polypropelene centrifuge tube.
Decant extract into centrifuge tubes with water
shake sample slightly to ensure proper mixing
Condition column with MeOH (TN-A- s7s 7 )
Wash Column with Kandiyohi Water
Filter sample through conditioned column, discarding filtrate
Allow column to go completelly dry
Elute column with indicated amount of solvent (
TN-A-ST5
Spike samples with internal standard PFDA standard number
4 ) into appropriate 15 ml centrifuge tube
~ 4-5 , conc.
%w%amount added
Transfer sample into appripriatelly marked autovial
n
3M Environmental Laboratory
Page 175
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
BOTTLE-TOPDISPENSEDRAILYCALIBRATIOCNHECK
Manufacturer y,Q e,5&
a and Model:
Date: 3 .I
L' 2.
Initials: WC Dispenser ID: 07 94
Balance ID: ?cL>
Volume: 5 CJ-
Solvent: A C h j
-
ID#: W - A 4/45
p,<,me +*
I
I Mass of solvent (g) I
Density'
I Volume of S o l v p t I
I Average Volume:
%Accuracv: I
I Std. Dev.:
Y0C.V.: I
5.03-
100. F
0.o a g 3
Performance SDecifications
I
Volume,
I
Accuracy,
I
C.V.,
I
Corrective Actions:
5 'Density values taken from the Merck Index, 12'hEdition, Copyri h t 1996 dY,=specific gravity a t ydegreesreferred to water a t xdegrees n-Hexane dZo4=0.660 Acetone d250=0.788 Methanol d254=0.7866 Methylene Chloride dZo4=1.3255
3M Environmental Laboratory
Page 176
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite SPE Columns Extraction Worksheet
Prep Date:
2113/2002
Analysts initials: OWHOJ
I
Lims Assgned sample number
E01-1245-36153
I
Sample Number or description
Blank-H20
E01-1245-36154 Blank sera
E01-1245-36155 Sera MSdppb in sera extract-1
E01-1245-36156 Sera MSBppb in sera extract-2
E01-1245-36157 Sera MS-5ppb in sera extract-3
E01-1245-36158 Sera MS-200ppb in sera extract-I
E01-1245-36159 Sera MS-200ppb in sera extract-2
E01-1245-36160 Sera MS-200ppb in sera extract-3
Volume of ;ample filterec
(mu
40+6
40+6 40+6
40+6
~~
40+6
40+6
40+6 40+6
Type of column used and lot
C18, l g , 6cc, lot W202581
C18, l g , 6cc. lot W202581
C18, lg. 6cc, lot
W202581
C18, l g , 6cc, lot W202581
C18, l g , 6cc, lot W202581
C18. l g , 6cc, lot W202581
C18, l g , 6cc. lot W202581
C18, l g , 6cc, lot W202581
Amount and spike mix used
Method Revision: ETS-8-231.O
Study Number: E01-1245
Matrix: Sera
Elution
solvent and
volume
Comments
NA
NA
2UI Of 02001-52 2UI Of 02001-52 2UI Of 02001-52 8 0 ~O1f 02001-52 80ul Of 02001-52 8 0 ~O1f 02001-52
2ml of MeOH TN-A-5457
2ml of MeOH TN-A-5457
2ml of MeOH TN-A-5457 2ml of MeOH TN-A-5457 2ml of MeOH TN-A-5457 2ml of MeOH TN-A-5457 2ml of MeOH TN-A-5457 2ml of MeOH TN-A-5457
I
U
Blank Sera TN-A- 577 2 ; Amount of sera aliquated: 2
ml
Dilute Sera with Kandiyohi water; Amount of water added r m I
Aliquot 1ml of sera into 15 ml polypropelene tube
Spike samples accordingly
Add 5ml of ACN (TN-A- 45) to aliquated sample
Shake sample for 20 min @300 rpm (Shaker VW@ $d @41$94
Centrifuge sample forOI min 2000 rpm (Centrifuge 3~wY76q613
Add 40 ml of Kandiyohi water to 50 ml polypropelene centrifuge tube.
Decant extract into centrifuge tubes with water
shake sample slightly to ensure proper mixing
Condition column with MeOH (TN-A- ps7i34 )
Wash Column with Kandiyohi Water
Filter sample through conditioned column, discarding filtrate
Allow column to go completelly dry
Elute column with indicated amount of solvent ( tw'p TN-A- sT5G
Spike samples with internal standard PFDA standard number C@*l.-
)
5
into
appropriate 15
,cone. m
ml centrifuge
,7p< .
~tube
&
~
J
J
A
Transfer
sample
into
appripriatelly marked autovial
pxhc)csi.o&A
dow
bs Qoc.
3M Environmental Laboratory
Page 177
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Bottle-Top Dispenser Daily Calibration Check ~ ~ - ~r ~ ~ p y
I Manufacturer and Model: Date: Initials: Dispenser ID: Balance ID: Volume (mL): Solvent: ID #:
VWR 5ml dispenser
q-fe o K G i h j f K
- 3 $.OR8
211 312002
OK 0799 900
5 ACN TN-A-4145
f'f6
Q.1"
aw
Mass of solvent (9)
Density'
Volume of
(gW
Solvent
1
3.965
0.7857
5.046
2
3.9715
0.7857
5.055
I
3
I
3.9818
I 0.7857 I 5.068 I
4
3.9484
0.7857
5.025
5
3.9788
0.7857
5.064
Averagevolume:
5.052
I
Std. Dev.:! 0.0169
I
I
I
%C.V.:
0.33
PASS
PassIFail: PASS
Volume,
W)
1 to 10
-
Accuracy,
("A>
98.0 - 102 0'9
Corrective Actions:
C.V.,
("h)
Zk 1.0%
1Density values taken from the Merck Index, 12`hEdition, Copyright 1996 dY,=specific gravity a t ydegrees C referred to water a t xdegrees n-Hexane dZo,=0.660 Acetone dZsO=0.788 Methanol dZs4=0.7866 Methylene Chloride dZ", =1.3255
3M Environmental Laboratory
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Report E01-1245
Prep Date: Analysts initials:
2/13/2002 OWHOJ
SPE Columns ExtractioPnFWOoSr:kAshReeetproduction Study with the Nothern Bobwhite
Study Number: E01-
Matrix:
Liver
50ul of 02001-66
2ml MeOH
TN-A-5754
2ml MeOH
TN-A-5754
2ml MeOH
TNA-5754
~~~~~~
Blank Liver TN-A- 5143 ; Amount of liver: 5.03539
Blank Liver TN-A- 5142 ; Amount of liver: 1.0015q
Homogenize liver with Kandiyohi water; Amount of water added-&I-% Aliquot 1ml of liver into 15 rnl polypropelene tube
4 4 PA&
0
&.,3.&"2
Amount of water added s m l
Spike samples accordingly
Add 5ml of ACN (TN-A- 4145 ) to aliquated sample Shake sample for 20 min @300 rpm (Shaker
C'%LLqq
Centrifuge sample for I O min Q 2000 rpm (Centrifuge j# 764613)
Add 40 ml of Kandiyohi water to 50 ml polypropelene centrifuge tube.
Decant extract into centrifuge tubes with water
shake sample slightly to ensure proper mixing
Condition column with MeOH (TN-A- 5 3
Wash Column with Kandiyohi Water
ct )
Filter sample through conditioned column, discarding filtrate
Allow column to go completelly dry
kkc s75q Elute column with indicated amount of solvent (
kl TN-A-
c2Gc Spike samples with internal standard PFDA standard number
Transfer sample into appripriatelly marked autovial
-4<) into appropriate 15 ml centrifuge tube , conc. 10" q.pf.%L, , amount added
'Ld
e q p A epod 3 t W C
3M Environmental Laboratory
Page 179
Report E01-1245
SPE Columns ExtractioPnFWOoSr:kAshReeetproduction Study with the Nothern Bobwhite
Prep Date: Analysts initials:
211 312002 OWHOJ
Method Revision: ETS-8-231.O
Study Number: E01-1342/1365
Matrix: Liver
Lims Assigned sample
I I I I I I I I number
I I I IEO1- 1342-30820
..-----. Nh EO 1- 1342-30829
EO 1-1342-30838 EO 1-1342-30847
EO 1- 1342-30856
I EO1- 1342-30865
Sample Number or description
10 ppm a.i. 384 F Liver 10 ppm a.i. 385 M Liver 10 ppm a.i. 386 F Liver 10 ppm a.i. 387 M Liver
1 0 ppm a.i. 388 F Liver
1 0 ppm a.i. 389 M Liver
Volume of sample filtered (ml)
40+6 40+6 40+6 40+6 40+6 40+6
Type of column used and lot
C18, l g , 6cc. lot
W~T~RI
C18, l g , 6cc, lot
W202581
C18, l g , 6cc, lot
W202581
C18, l g . 6cc, lot
- W 2 0 2U = Y = 4I
C I.A_,I. nJ , 6cc, lot
W202581
C18, l g , 6cc, lot
W202581
Amount and Elution solvent and
spike mix used
volume
NA
2ml MeOH
TN-A5754
NA
2ml MeOH
TN-A-5754
,Ik l n
Wl
2ml MeOH
TN-A5754
NA 2ml MeOH TN-A5754
NA
2ml MeOH
TN-A-5754
NA
2ml MeOH
TN-A5754
Comments
\
\
1 NA 2ml MeOH TN-A-5754 2mlMeOH
Blank Liver TN-A- 5143 ; Amount of liver: 5.03539
Blank Liver TN-A- 5142 ; Amount of liver: 1.0015q
Homogenize liver with Kandiyohi water; Amount of water added>'c:,y
Amount of water added A m 1
Aliquot I m l of liver into 15 ml polypropelene tube
97\3
Spike samples accordingly
Add 5ml of ACN (TN-A- 4145 ) to aliquated sample
wk Shake sample for 20 min @300 rpm (Shaker
5 [ d)04\ bq4
a Centrifuge sample for I O min 2000 rpm (Centrifuges'JP?bcjQiP
Add 40 ml of Kandiyohi water to 50 ml polypropelene centrifuge tube.
Decant extract into centrifuge tubes with water
shake sample slightly to ensure proper mixing
Condition column with MeOH (TN-A- 6 7 G? )
Wash Column with Kandiyohi Water
Filter sample through conditioned column, discarding filtrate
Allow column to go completelly dry
5?&9 Elute column with indicated amount of solvent ( He L'H TN-A02-1' Spike samples with internal standard PFDA standard number
/)
4 5
Transfer sample into appripriatelly marked autovial
EYbefiOL
c4c3-v.Q 08
into appropriate 15 ml centrifuge tube
, conc. / O i . . 7 P , amount added
1'
ow.& op
3M Environmental Laboratory
Page 180
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Bottle-Top Dispenser Daily Calibration Check
' Manufacturer and Model:
Date:
Initials: Dispenser ID:
Balance ID: Volume (mL):
Solvent: ID #:
VWR 5ml dispenser
211 312002
OK
0799 900 5
am et6
Q.13
ACN
TN-A-4145
Mass of solvent (8)
Density'
Volume of
(dml)
Solvent
1
3.965
0.7857
5.046
2
3.9715
0.7857
5.055
I 3 I 3.9818 0.7857 5.068
4
I 3.9484 I 0.7857 I 5.025
I
5
I
3.9788
I 0.7857 I 5.064 I
5.052
PASS
Volume,
(mLI 1 to 10
Pass/Fail:l PASS
I I Performance Specifications
Accuracy,
(%I
I
98.0 - 102%
C.V.,
*
(%I
1.0%
PASS
1Density values taken from the Merck Index, 12'hEdition, Copyright 1996 dY,=specific gravity a t ydegreesC referred to water a t xdegreesC n-Hexane dZn,=0.660 Acetone dz50=0.788 Methanol d25,=0.7866 Methylene Chloride dzn4=1.3255
3M Environmental Laboratory
Page 181
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Attachment D:
Study: E01-1245 Dilution Date/Analyst:
6)
Box Number: E01-1245
- Dilutions SummaryWorksheet Solvent/TN Number: MeOW5457 W/IS PFDA Extraction Date/Analyst: 27"#&qgvc. r d?.*
Matriflimepoint: Quail sera
Notes: 1/100 dilution= lOul of sample +990ul of solvent D A l l dilutionswere made on day of extractionor the day after analysis.
Form Completion Verified By: & 9'k07
3M Environmental Laboratory
Page 182
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
3 Study: E01-1342
Dilution Date/Analyst: Box Number: E01-1342
Attachment D: Dilutions Summary Worksheet
-
i
2
6'OQ?J k
'*" g&ent/TN
Number: MeOH/5457 W/IS PFDA
Extraction Date/Analyst: 2/13/02
Matrixflimepoint: Quail liver
E01-1342-30991 x
E01-1342-31009 x I
E01-1342-31027 x
Notes:
1/10 dilution = lOOul of sample + 900ul of solvent
1/100dilution= 1Oul of sample +990ul of solvent
0All dilutions were made on day of extraction or the day after analysis.
Form Completion Verified By:
- c \
-o@iP9
-
3M Environmental Laboratory
Page 183
Report E01-1245
Prep Date: Analysts initials:
211 512002 OWHOJ
SPE Columns ExtractioPnFWOoSr:kAshReeetproduction Study with1t4h5eoNsloztzh]eornr Bobwhite
Method Revision: ETS-8-231.O
Study Number: E 0 1 - #& m/ z 4 r
Matrix: Liver
Blank Liver TN-A- 5143 ; Amount of liver: 5.03539
Blank Liver TN-A- 5142 ; Amount of liver: 1.0015q
Homogenize liver with Kandiyohi water; Amount of water a d d e d A m l -
Amount of water added 3rd
Aliquot lrnl of liver into 15 ml polypropelene tube
9f q5 Spike samples accordingly
Add 5ml of ACN (TN-A-
) to aliquated sample
Shake sample for 20 min a 3 0 0 rpm (Shaker WVR S/N 041694)
Centrifuge sample for 10 min 2000 rpm (Centrifuge 3M# 769613)
Add 40 ml of Kandiyohi water to 50 ml polypropelene centrifuge tube.
Decant extract into centrifuge tubes with water
shake sample slightly to ensure proper mixing
Condition column with MeOH (TN-A- 575 4 )
Wash Column with Kandiyohi Water
Filter sample through conditioned column, discarding filtrate
Allow column to go completelly dry Elute column with indicated amount of solvent (
TN-A- 5 7%
Spike samples with internal standard PFDA standard number
1-
)
4
into 7
appropriate , conc.
15
w , ml centrifuge tube amount added
%$
Transfer sample into appripriatelly marked autovial
opow 03
3M Environmental Laboratory
Page 184
Report E01-1245
SPE Columns ExtractioPnFWOoSr:kAshReeetproduction Study with the Nothern Bobwhite
Prep Date: Analysts initials:
I
Lims Assigned sample number
E01-1365-31214
E01-1365-31219
E01-1365-3 1224
E01-1365-3 1229
E01-1365-31234
1E01-1365-31240
E01-1365-3 1245
E01-1365-31250
E01-1365-31255
E01-1365-31260
E01-1365-31265 E01-1365-31270
IE01- 1365-31275
~~~
E01-1365-31280
E01-1365-31285
211 512002 OWHOJ
I
Sample Number or description
0 p p m a.i. 270 M Liver
0 p p m a.i. 273 F Liver
0 p p m a.i. 277 F Liver
0 p p m a.i. 283 M Liver
0 p p m a.i. 291 M Liver
I 10 p p m a.i. 517 F Liver
10 p p m a.i. 522 M Liver
10 p p m a.i. 525 F Liver
10 p p m a i . 533 M Liver
10 p p m a.i. 538 F Liver
10 p p m a.i. 545 M Liver 10 p p m a.i. 552 M Liver
I 10 ppm a.i. 557 F Liver
10 p p m a.i. 561 F Liver 10 p p m a.i. 568 M Liver
QK VO~UmeOf Sample
I I filtered (ml)
40+6
40+6
40+6
40+6
40+6
I
40+6
I
40+6
40+6
40+6
40+6
40+6
I I 40+6 40+6 40+6
40+6
Type of column used and lot
C18, l g , 6cc, lot W202581
C18. l g , 6cc, lo1 W202581
C18. l g , 6cc. lot W202581
C18, l g , 6cc. lot W202581
C18, l g , 6cc. lot
\N?n?L;R1
l A Dlng 76KcR'cI ' lot
C18, lg. 6cc, lot W202581
C18, 1g,6cc, lot W202581
C18, l g , 6cc, lot W202581
C18, l g , 6cc, lot W202581
C18, 19, 6cc, lot W202581
C18. l g , 6cc, lot
W~?SRI
C18. lg, ~ C Clot, \nnn?s~i
C18, l g , 6cc, lot W202581
C18, l g , 6cc, lot W202581
Method Revision:
Study Number: E01-
Matrix:
I I I
I
Amount and Elution solvent and
spike mix used
volume
NA
2ml MeOH
TN-A-5754
NA
2mlMeOH
1
TN-A-5754
NA
2ml M e O H
TN-A-5754
NA
2ml M e O H
TN-A5754
NA
2ml M e O H
TN-A-5754
NA
2ml MeOH
TNA-5754
NA
2ml MeOH
TN-A-5754
NA
2ml M e O H
TN-A-5754
NA
2ml M e O H
TN-A-5754
NA
2ml MeOH
TN-A-5754
NA
2ml M e O H
TN-A-5754
NA 2ml M e O H TNA-5754
NA
2ml MeOH
TN-A-5754
NA
2ml M e O H
TNA-5754
NA
2ml M e O H
Thl A C 7 C A
Comments
AJA
I
c- I
Blank Liver TN-A- 5143 ; Amount of liver: 5.03539
Blank Liver TN-A- 5142 ; Amount of liver: 1.0015q
Homogenize liver with Kandiyohi water; Amount of water a d d e d A m l -
Amount of water added s m l
Aliquot I m l of liver into 15 ml polypropelene tube
Spike samples accordingly
Add 5ml of ACN (TN-A- 4 / 4 5
) to aliquated sample
Shake sample for 20 min a 3 0 0 rpm (Shaker WVR SIN 041694)
Centrifuge sample for 10 min @ 2000 rpm (Centrifuge 3M# 769613)
Add 40 ml of Kandiyohi water to 50 ml polypropelene centrifuge tube.
Decant extract into centrifuge tubes with water
shake sample slightly to ensure proper mixing
Condition column with MeOH (TN-A- 575 4 )
Wash Column with Kandiyohi Water
Filter sample through conditioned column, discarding filtrate
bfpaw 4 Allow column to go completelly dry
Elute column with indicated amount of solvent (
TN-A- ' ' f 5
Spike samples with internal standard PFDA standard number
) into appropriate 15 ml centrifuge tube
4s- , conc. 100,-
, amount added
1'
Transfer sample into appripriatelly marked autovial
gsoz
3M Environmental Laboratory
Page 185
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
BottleTop Dispenser Daily Calibration Check
Manufacturer and Model:
Date: Initials: Dispenser ID: Balance ID: Volume (mL): Solvent:
I D #:
VWR 5ml
211 512002 OK 0799 900 5 ACN
TN-Ad 145
1
1
2
3
4
5
I Mass of solvent (g) I
3.8904
I I 3.9526 3.9724
Density'
(gW 0.7857 0.7857 0.7857
I Volumeof
Solvent
4.9515
I I 5.0307 5.0559
3.961
0.7857
5.0414
3.964
0.7857
5.0452
AverageVolume:
I %Accuracy:l
5.0249 100.50
I PASS
PASS
Volume,
(mLI
1 to 10
I I Performance Specifications Accuracy, ("/.I 98.0 - 102 % I
Corrective Actions:
C.V.,
("/.I
f 1.0%
1Density values taken from the Merck Index, 12'hEdition, Copyright 1996 dY,=specific gravity a t ydegreesreferred to water a t xdegrees n-Hexane d204=0.660 Acetone dZ5,=0.788 Methanol d254=0.7866
3M Environmental Laboratory
Page 186
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northern Bobwhite
ATTACHMENTE: STUDY PROTOCOL, PROTOCOL AMENDMENTSA,ND
DEVIATI oNS
3M Environmental Laboratory
3M Environmental Laboratory
Page 187 of 226 Page 187
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
WILDLIFE INTERNATIONAL. LTD
PROJECTNO.: 454-108,
EO1-1245
AMENDMENT TO STUDY PROTOCOL STUDY TITLE: PFOS: A REPRODUCTION STUDY WITH THE NORTHERN BOBWHITE
PROTOCOL NO.: 454/120700/QR/SUB454
AMENDMENTNO.: 9
SPONSOR 3M Corporation
PROJECTNO.: 454-108, E01-1245
EFFECTNE DATE: January 24,2002
AMENDMENT:
This amendment includes an attachment (Attachment A) which provides the information necessary to complete the analflcal phase of this study.
REASON:
The protocol did not include information for completing the analyses required by the sponsor.
AMENDMENT:
Harold Johnson is the Principal Analflcal Investigator
REASON:
The sponsor requested that a principal analytical investigatorbe added to the protocol. AMENDMENT:
The 3M Environmental Laboratory Project IdentificationNumber to be included with the study is E01-1245.
REASON:
The sponsor requested that the 3M Project IdentificationNumber be included in the protocol.
3M Environmental Laboratory
Page 1 of 2 Page 188
- . _Re0p1o/r2t9E/0012-1214.65:25 FAX 410 a22 0632
JAN. 29. 2002 1 1 : 34AM ENVIEONh!ENTAL
WILDLIFEPFIONTSE:RANARTeIpOrNoAdLuction Study with the Nothern Bobwhite
LAB 2 3E 09
w UUL
110,6313 P. 3
WILDLIFE INTERNATIONAL, LTD
PROJECTNO.; 454-108, EOl-1245
3M Environmental Laboratory
Page 189
Report E01-1245 WILDLIFE INTERNATIONAL, LTD
PFOS: A Reproduction Study with the Nothern Bobwhite
PROJECTNO.: 454-108,
EO 1- 1245
Sean P. Gallagher, Study Director
Date
Joann B. Beavers, Wildlife International, LTD
Date
Laboratory Management
Harold 0.Johnson, Principal Analytical Investigator
Date
William K. Reagen, 3M EnvironmentalLaboratory,
Date
Laboratory Management
Rochelle R. Robideau, Sponsor's Representative
Date
3M Environmental Laboratory
Page 2 of 2
Page 190
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Protocol Amendment # 9 = Attachment A
Wildlife International Ltd. ## 454-108
STUDY TITLE PFOS: A Reproduction Study with the Northern Bobwhite
SPONSOR 3M Environmental Laboratory
Building 2-3E-09 PO Box 3333 1 St. Paul, MN 55133-3331
PERFORMING ANALYTICAL LABORATORY 3M EnvironmentalLaboratory Building 2-3E-09 PO Box 33331 St. Paul, MN 55133-3331
LABORATORY PROJECT IDENTIFICATION
3M Environmental Laboratory: E01-1245
Wildlife International Ltd. : 454- 108
3M Environmental Laboratory
Page 191
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Sponsor
Study Identification
PFOS: A Reproduction Study with the Northern Bobwhite
3M Environmental Laboratory Building 2-3E-09 PO Box 33331 St. Paul, MN 55133-3331
Principal Analytical Investigator
Study Locations
ANALYTICAL TESTING LABORATORY
ANALmCAL TESTINGLABORATORY
Harold Johnson 3M Environmental Laboratory Building 2-3E-09 PO Box 33331 St. Paul, MN 55133-3331 651-770-6479
3M Environmental Laboratory Building 2-3E-09 935 Bush Ave. PO Box 33331 St. Paul, MN 55133-3331
PACE Tier 2 1700 Elm Street, Suite 200 Minneapolis, MN 55414
Proposed Study Timetable
ANALYTICAL mPERIMEMAL START DATE
ANALMEAL EXPERIMENTAL TERMINATION DATE
01/24/02 03/24/02
3M Environmental Laboratory
2
3M Environmental Laboratory
Page 192
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
1. PURPOSEIOBJECTIVES In the in-life phase of this study, Northern Bobwhite quail were regularly exposed to nominal doses of perfluorooctanesulfonate, potassium salt (PFOS) in their feed in order to evaluate the effects of dietary exposure upon adults over a five-month period. The purpose of this analytical phase of the study is to quanti@PFOS in the liver and sera of both control and dosed Northern Bobwhite quail. The analytical information may be used to compare with toxicologicalhstopathologicalresults from the in-life portion of this bird study. The in-life portion of the study was completed at Wildlife International, Ltd. in study 454-108.
2. REGULATORCYOMPLMNCE This analytical phase study will be conducted in accordance with the United States Environmental Protection Agency Good Laboratory Practice Standards, 40 CFR 792.
3. QUALITAYSSURANCE The 3M Environmental Laboratory Quality Assurance Unit will audit analytical phase study conduct, data, and the final report to determine compliance with Good Laboratory Practice Standards and with 3M Environmental Laboratory Standard Operating Procedures. The Quality Assurance Unit will report all findings to the Sponsor Representative and the Study Director.
4. REFERENCSEUBSTANCE 4.I Physical Description- Perfluorooctanesulfonate, potassium salt from Lot 217 is a white crystalline material.
4.2 Purity a n d Stabi/*The purity of Lot #217 has been determined to be 86.9%. PFOS has been shown to be stable in methanol solutions for up to 6 months at ambient temperature in the validation report from study PS013, "Method Validation and Instrument Detection Limit Determination for LCMS and GCMS Analysis of FC807 Compounds in Methanol." Refer to the Certificate of Analysis (stored in the Test, Control, and Reference database in the 3M Environmental Laboratory) for further purity and stability information.
4.3 Storage Conditions-The test article may be stored at ambient temperature or lower.
4.4 Reserve Samples--A reserve sample of PFOS from Lot #217 has been frozen at -
20C *5"C or colder and is kept in the 3M Environmental Laboratory.
4.5 CAS Number-The CAS number is: 2795-39-3.
4.6 Mo/ecu/ar Weight-The molecular weight is 538 ( C ~ F I ~ S O ~NKo)t.e: The molecular weight of the anion (PFOS) is 499 ( C ~ F U S O ~ ) .
3M Environmental Laboratory
3
3M Environmental Laboratory
Page 193
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
5. CONTROMLATRICES
Types of control matrices and their source, physical description, storage requirements, and traceability numbers will be recorded in the raw data and included in the final report.
6. TESTSYSTEM
The test system is Northern Bobwhite quail. The test system was dosed (at Wildlife International Ltd. during the in-life phase of this study) with food prepared by mixing PFOS with feed in a large mixer in appropriate portions to achieve the nominal 10 ppm level. A food dose verification validation study was performed by Wildlife International under study number 454C-110 (3M #U2723), "Analytical Method Verification for the Determination of PFOS in Avian Diet." Wildlife International verified the actual dosed food for this study and the results will be contained in the in-lie Wildlife phase report. Northern Bobwhite serum and liver samples were collected by Wildlife International, Ltd. and sent to 3M Environmental Laboratory for analysis.
6.1
Justification of the Selection of the Test System
Northern Bobwhite quail represent wild bird populations and they are an EPA
recommended species because they do well in a laboratory environment. The use
of these matrices for the study is to determine if PFOS was deposited in the liver
and serum of mating adults that were fed PFOS. Furthermore, analysis of these
matrices from hatchlings will determine if PFOS was passed on to mating adults'
offspring.
7. SOURCE OF SUPPLY FOR THE TESTSYSTEM
The birds were obtained by Wildlife International, Ltd. See their protocol (study 454-108) for information about bird origination location.
8. SPECIMEN AND SAMPLE RECEIPATND MAINTENANCE
Sera and liver were collected by Wildlie International, Ltd. and shipped to the 3M Environmental Laboratory for analysis. The 20-week endpoint sera and liver samples received by the 3M Environmental Laboratory were fiom the following birds:
40 control adult birds (20 mating pairs) that ingested food containing 0 ppm PFOS 40 experimental adult birds (20 mating pairs) that ingested food containing 10 pprn PFOS 20 first generation offspring birds that ingested food containing 0 ppm PFOS
Samples will be maintained frozen except when removed for extraction and analysis as described in the method. The samples will be kept isolated from the test substance during storage.
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9. SUB-CONTRACTED ANALYSIS
9.7
All sera and liver extractions as detailed in this protocol amendment will be
performed at Pace Tier 2, 1700 Elm Street, Suite 200, Minneapolis, MN 55414.
9.2
All sera and liver analyses as detailed in this protocol amendment will be performed
at 3M Environmental Laboratory, Building 2-3E-09, 935 Bush Avenue, St. Paul,
MN 55106.
70. EXPERIMENTACLONDUCT
The 21-week endpoint liver and sera samples received (see section 8) will be extracted and analyzed for PFOS quantities using the methods listed below.
70.7
Preparatory Methods
70.7.7 ETS-8-6, Extraction of Fluorochemical Compounds from Liver for Analysis
Using HPLC-ElectrosprayMass Spectrometry
70.7.2 ETS-8-4, Extraction of Fluorochemical Compounds from Serum for Analysis
Using HPLC-Electrosprayhdass Spectrometry
70.2 Analytical Methods 70.2.7 ETS-8-7, Analysis of Fluorochemicalsin Liver Extracts Using HPLCElectrospray / Mass Spectrometry 70.2.2 ETS-8-5, Analysis of Potassium Perfluorooctanesulfonateor Other Fluorochemicalsin Serum Extracts Using HPLC-ElectrosprayMass Spectrometry
77. METHODVAUDA~ON
Method validation for PFOS quantitation in quail sera and liver was performed at Centre Analytical Inc. in study 023-054. The method will be applied to sample analyses without additional validation.
72. DATAQUALITYOBJECTIVESDURING SAMPLEANALYSIS
The following criteria will be met using the validated calibration levels and fortification levels determined in section 11:
72.7 System Suitability System suitability will be determined prior to the start and at the completion of each analytical run. Prior to the calibration curve and after the last sample of the run three (3) mid-level unextracted calibration standards will be analyzed. The peak area precision and retention time precision and peak asymmetry will be monitored at the beginning and the end of the run separately. The peak area precision must be equal to or less than 2.0% RSD, the precision of the retention time must be equal to or less than 2.5% RSD and the peak asymmetry (fronting or tailing) must be 0.5<AF<2.0,where AF is the asymmetry factor. If any item of the
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12.2 12.3
system suitability fails, system maintenance must be completed prior to running a second set of system suitability samples and the system suitability must pass before starting the calibration.
Calibration It will consist of a minimum of nine (9) levels, including a blank with surrogate and a blank without surrogate, the lowest standard will be at approximately 50% of the LLOQ and the highest standard will be approximately 50% higher than the ULOQ.
The standard curve equation will be determined by regression analysis using the peak areas of the analyte. The accuracy of each level will be verified. Any level
outside 80% - 120% accuracy must be deactivated, and regression re-calculated.
The curve must have a correlation of determination (8)greater than or equal to
0.985. All levels must show a response greater than two times that of the blank.
The total number of standards excluded my not exceed 20%. If the preceding criterion are not met, the curve and sample set will be reanalyzed.
Limits of Quantitation (LOQ) The lower limit of quantitation (LLOQ) was determined to be 10 ng/g in liver and 10ng/mL serum during the method validation as described above in section 11. The LLOQ may be determined to be higher than that found in the validation study during a screening to be done for endogenous levels of PFOS in the blank matrices available at 3M Environmental Laboratory. If endogenous levels of PFOS are found to be higher than the LLOQ or if the levels are found to be highly variable, the LLOQ will be adjusted to accommodate this. The screening procedures and LLOQ determinationwill be recorded in a note to file and kept with the raw study data as well as being reported in the final report. Recovery efficiency at the LLOQ will be determined during each run using an extracted quality control sample spiked at the LLOQ level. Ifthe quality control sample at the LLOQ level fails during a run, the LLOQ for that specific run would be considered to be the next lowest passing quality control sample and any samples below the new LLOQ must be reanalyzed.
The upper limit of quantitation (ULOQ) was determined to be 250 ng/g in liver and 250 ng/mL in serum during the method validation as described above in section 11. An extracted quality control sample spiked at the ULOQ will be used to measure recovery efficiency at the ULOQ. If the quality control sample at the ULOQ fails during a run the ULOQ for that specific run would be considered to be the next highest passing quality control sample and any samples above the new ULOQ must be reanalyzed.
Any sample with an area greater than that of the highest acceptable standard will need to be diluted into the range of the calibration curve. If samples are diluted into the range of the curve during analyses and enough sample remains, a post-run dilution validation will be performed to v e m sample values. To perform the
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dilution validation, one sample will be separated into two representative samples (i.e. two 1 mL aliquots for fluid samples or two 1 gram amounts for tissue samples) then diluted using two procedures. The first procedure consists of diluting the sample with additional matrix prior to extraction (sera adding sera), while the second procedure consists of diluting the extract with solvent postextraction (methanol extract adding additional methanol solvent).
If the values are not within 15% of each other additionaltesting will be required to determine which value is a correct representation of the sample concentration.
12.4 Continuing Calibration Verifications An unextracted midlevel standard (continuing calibrationverification - CCV) will be analyzed after every 10 injections (starting after the last injection of the calibration curve). The accuracy of the CCV must be within 20%. Data may only be reported if bracketed by passing CCV's (or a CCV and the same level calibration curve point). Data bracketed by one or more failing CCV's must be reanalyzed.
12.5 Quality Control Samples A minimum of three (3) quality control samples (QC) will be prepared with each set of samples. They will consist of blank matrix spiked with three levels of analyte. The levels are: 0 Low level: at the LLOQ (10 ng/mL in serum and 10 ng/g in liver), Mid-level: 5 times the LLOQ, High level: at the ULOQ (25 times the LLOQ)
12.6 QC Performance Criteria
Each QC is expected to show an accuracy of 80-120%of expected. A minimum
of 2/3 of all QC must meet these criteria. If not, the entire sample set must either be re-analyzed or re-extracted (as decided by the Study Director).
12.7 Use of Confirmatory Methods Confirmatory methods are typically not needed with L C M S M S analysis.
12.8 Demonstration of Specificity PFOS specificitywill be substantiated by chromatographic retention time, by the characteristic primary ion (499), and the characteristic product ion (99) using LCMSMS.
13. SUB-CONTRACTEDANALYSIS
13.1 All fluid and tissue extractions as detailed in this protocol amendment will be
performed at Pace Tier 2, 1700Elm Street, Suite 200, Minneapolis, MN 55414.
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13.2 All fluid and tissue analyses as detailed in this protocol amendment will be performed at 3M Environmental Laboratory, Building 2-3E-09, 935 Bush Avenue, St. Paul, MN 55106.
13.3 Pace Analytical Services, Inc. will follow all applicable 3M Environmental
Laboratory Standard Operating Procedures and the following Pace Analytical Inc.
Standard Operating Procedures.
PSS-Admin-01 Quality System
PSS-Admin-04 Laboratory Facilities
PSS-Admin-06 Training Record Files Maintained by QAU
PSS-ARC-02 Disposition of Archive Materials
PSS-ARC-04 Archiving Data, Specimen and Logbooks
PSS-DC-05 Lab Notebooks, Logbooks, and Phone Logs
PSS-DM-03 StatisticalEvaluation of Data
PSS-OPS-0 1 Use and Maintenance of Ultra-Turrax T25 Homogenizer
PSS-OPS-02 Raw Data
PSS-OPS-03 Hazardous Waste Disposal
PSS-OPS-04 Use and Maintenance of N-Evap Analytical Evaporator
PSs-OPS-05 Use of Compressed Gases in the Laboratory
PSS-OPS-06 Use and Maintenance of NANOpure 11Water Purification System
PSS-OPS-07 Cleaning Non-disposable Volumetric Pipettes
PSS-OPS-08 Laboratory Calculations
PSS-OPS-09
P sS-OPS- 10
Deviations from Established Procedures Analytical Definitions
PSS-OPS-11 Use and Calibration of a Bottle-Top Dispenser
PSS-OPS-13 Use and Maintenance of Lab Refrigerators, Freezers, and Ovens
PSS-OPS-14 Use and Calibration of Syringes with a Hamilton Chaney Adapter
PSS-OPS-15 Glassware Cleaning
PSS-OPS-16 Use and Maintenance of the Fisher Scientific Isotemp Freezer
PSS-OPS-17 Use and Maintenance of Ultrasonic Water Baths (Sonicators)
PSS-OPS-18 Use and Maintenance of Vortex Shakers
PSS-OPS-24 Use and Maintenance of a Desiccator
PSS-OPS-3 1 Use and Maintenance of Shakers
PSS-OPS-32 Operation, Maintenance and Calibration of Laboratory
PSS-OPS-37 Operation, Maintenance, and Calibration of pH Meters and pH
Electrodes
PSS-MC-0 1 Purchasing of Laboratory Supplies
PSS-MC-02 Receipt of Laboratory Supplies
PSS-MTR-01 Calibration of Certified Weight Set
PSS-MTR-02 Calibration of Certified ThermorneterdThermocouples
PSS-MTR-05 Calibration of Eppendorf Pipettes
PSS-MTR-06 Verification of Calibration of the Eppendorf Pipettor
PSS-MTR-07 New Equipment Qualification (IQ, PQ, OQ)
PSS-MTR-08 Verification of Calibration and Use of Analytical Balances
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PSS-MTR-09
PSS-Safety-01 PSS-Safety-02 PS S-Safety-04 PSS-Safety-05 PSS-TS-01
Use and Maintenance of Fisher Scientific Electronic Temperature Monitoring Devices General Laboratory Safety Use and Maintenance of Biological Safety Cabinets Emergency Evacuation Procedures Use and Maintenance of Laboratory Fume Hoods Training Procedures
13.4 An amendment to the protocol will be written if extractions and analyses are performed at laboratories other than the Pace Tier 2 or 3M Environmental Laboratory, respectively.
14. STATlsnCAL ANALYSIS Statistical methods will be limited to the calculation of means and standard deviations. Examples of the calculations used in the analyses will be included in the analytical phase report.
15. REPORT A final report will be prepared by the 3M Environmental Laboratory. The final report will follow all GLP requirements, and will include a description of all materials and methods used, including a narrative discussion with a tabular presentation of all analyses results.
16. LOCAnON OF RAWDATA, RECORDSA,ND FINAL REPORT
When the final report is completed, all original paper data, including protocol, phase
report, study correspondence, sample receipt and tracking, sample preparation, and analytical data, will be retained in the archives of 3M Environmental Laboratory. All corresponding training records, calibration records, instrument maintenance logs, standard operating procedures, equipment procedures, and methods will be retained either at Pace Tier 2 or the 3M EnvironmentalLaboratory, as applicable.
I 7. SPECIMEN RETENllON
Samples of the test substance (any leftover control sera or liver and samples) and the analytical standards will be maintained in the laboratory for a period of time as specified by regulation or as long as the quality of the preparation affords evaluation. However, samples will not be maintained more than 10 years after the effective date of the final test rule (if applicable). 3M Environmental Laboratory Standard Operating Procedures also apply to sample retention times.
18. REFERENCES
18.I
Wildlife International, Ltd. Protocol No. 454-108, "PFOS: A Reproduction Study
with the Northern Bobwhite". 18.2 Centre Analytical Laboratories, Inc. Study 023-054, "Validation of Analytical
Methods "Extraction of Potassium PeffluoroocatanesuKonate or Other
Fluorochemical Compounds From Serum for Analysis Using HPLC ElectrospryhAass Spectrometry" and "Extraction of Potassium
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Pefluorooctanesulfonateor Other Fluorochemical Compounds From Liver for Analysis Using HPLC ElectrosprayMass Spectrometry in Quail Serum and Liver." 18.3 3M Study U2723, Wildlife Study 454C-110, "Analytical Method Verification for the Determination of PFOS in Avian Diet."
19. PROTOCOLAMENDMENTANSD D E W ~ O N S
Planned changes to the protocol will be in the form of written amendments signed by the Study Director and the Sponsor Representative. Amendments will be considered as part
of the protocol and will be attached to the finalprotocol. Any other changes will be in the
form of written deviations, signed by the Study Director and Sponsor Representative and filed with the raw data. All changes to the protocol will be indicated in the final report.
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-. R0e1p/o3r0t/-.E.0021-11284:- 52 8 FAX - 410 8 2 2 0 6 3 2
WILDLIFE PIFNOTESR:NAATRIOeNpAroLduction Study with the Noth@ e0rnI0 3Bobwhite
WILDLIFE INTERNATIONAL, LTD
- PROJECT NO.: 454-108,
EO 1 1245
AMENDMENT TO STUDY PROTOCOL STUDY TITLE: PFOS: A REPRODUCTION STUDY WITH TIE NORTHERN BOBWHITE
PROTOCOL NO.:454/12070O/QUSUB454
SPONSOR: 3M Corporation
AMENDMENT NO.: 10 PROJECT NO,: 454-108,E01-1245
EFFECTIVE DATE: January 30,2002
AMENDMENT:
This amendment includes ai attachmeilt (AttachmentA) which provides updated informationnecessary IO complctc the analytical phase of this study. This attaclment A replaccs the attachment A in amendmmt 9.
REASON:
c
The amendment 9 attachment A was updated to include 3 different extraction and analytical method, to
and to changethe liver and sera cxtraction location.
Sean P. Gdlagher, Study birector
J o 3. ~havers, Wildlife International, LTD, Laboratory Management
c
William K.Reage4 3M Environmental Laboratory,
Date
Date
1 30 O L
1
L
0 1 /3//cQ-
Date
CW!3,/dL
Date
Date
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PFOS: A Reproduction Study with the Nothern Bobwhite
PROJECT NO.: 454-108, E01 -1245
AMENDMENT TO STUDY PROTOCOL STUDY TITLE: PFOS: A REPRODUCTION STUDY WITH THE NORTHERN BOBWHITE
PROTOCOL NO.: 454112070O/QR/SUB454
AMENDMENT NO.: 10
SPONSOR: 3M Corporation
PROJECT NO.: 454-108, E01-1245
EFFECTIVE DATE: January 30,2002
AMENDMENT:
This amendment includes an attachment (Attachment A) which provides updated information necessary to complete the analytical phase of this study. This attachment A replaces the attachment A in amendment 9.
REASON:
The amendment 9 attachment A was updated to include a different extraction and analytical method, to update the data quality objectives, and to change the liver and sera extraction location.
Sean P. Gallagher, Study Director
Date
Joann B. Beavers, Wildlife International, LTD,
Date
Laboratory Management
Harold 0.Johnson, Principal Analytical Investigator
Date
William K. Reagen, 3M EnvironmentalLaboratory,
Date
Laboratory Management
Rochelle R. Robideau, Sponsor's Representative
Date
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Protocol Amendment # I O - Attachment A
Wildlife International Ltd. # 454-108
STUDY TITLE PFOS: A Reproduction Study with the Northern Bobwhite
SPONSOR 3M Environmental Laboratory
Building 2-3E-09 PO Box 33331
St. Paul, MN 55133-3331
PERFORMING ANALYTICAL LABORATORY 3M Environmental Laboratory Building 2-3E-09 PO Box 33331
St. Paul, MN 55133-3331
LABORATORY PROJECT IDENTIFICATION 3M Environmental Laboratory: EO1-1245 Wildlife International Ltd.: 454-108
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Sponsor
Study Identification
PFOS: A Reproduction Study with the Northern Bobwhite
3M Environmental Laboratory Building 2-3E-09 PO Box 33331 St. Paul, MN 55 133-3331
Principal Analytical lnvestigator
Study Locations ANALYTICATLESTINGLABORATORY
Harold Johnson 3M Environmental Laboratory Building 2-3E-09 PO Box 33331 St. Paul, MN 55133-3331 65 1-778-6479
3M Environmental Laboratory Building 2-3E-09 935 Bush Ave. PO Box 33331 St. Paul, MN 55133-3331
Proposed Study Timetable ANALYTICAELXPERIMENTASLTARTDATE ANALYTlCAL EXPERIMENTATLERMINTAION DATE
01/31/02 0313 1/02
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I. PURPOSE~~BJECTIVES In the in-life phase of this study, Northern Bobwhite quail were regularly exposed to nominal doses of perfluorooctanesulfonate, potassium salt (PFOS) in their feed in order to evaluate the effects of dietary exposure upon adults over a five month period. The purpose of this analytical phase of the study is to quantify PFOS in the liver and sera of both control and dosed Northern Bobwhite quail. The analytical information may be used to compare with toxicologicalhistopathological results from the in-life portion of this bird study. The in-life portion of the study was completed at Wildlife International, Ltd. in study 454- 108.
2. REGULATORYCOMPLIANCE This analytical phase study will be conducted in accordance with the United States Environmental Protection Agency Good Laboratory Practice Standards, 40 CFR 792.
3. QUALITAYSSURANCE The 3M Environmental Laboratory Quality Assurance Unit will audit analytical phase study conduct, data, and the final report to determine compliance with Good Laboratory Practice Standards and with 3M Environmental Laboratory Standard Operating Procedures. The Quality Assurance Unit will report all findings to the Sponsor Representative and the Study Director.
4. REFERENCSEUBSTANCE 4.I Physical Description- Perfluorooctanesulfonate, potassium salt from Lot 217 is a white crystalline material.
4.2 Purity a nd Stability-The purity of Lot #217 has been determined to be 86.9%. PFOS has been shown to be stable in methanol solutions for up to 6 months at ambient temperature in the validation report from study PSO13, "Method Validation and Instrument Detection Limit Determination for L C M S and GUMS Analysis of FC807 Compounds in Methanol." Refer to the Certificate of Analysis (stored in the Test, Control, and Reference database in the 3M Environmental Laboratory) for further purity and stability information.
4.3 Storage Conditions-The test article may be stored at ambient temperature or lower.
4.4 Reserve Samples-A reserve sample of PFOS from Lot #217 has been frozen at 20C 4~5Cor colder and is kept in the 3M Environmental Laboratory.
4.5 CAS Number-The CAS number is: 2795-39-3.
4.6 Molecular Weight-The molecular weight is 538 ( C ~ F I ~ S O ~NKo)t.e: The molecular weight of the anion (PFOS) is 499 (C*F,$03-).
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5. CONTROML ATRICES
Types of control matrices and their source, physical description, storage requirements, and traceability numbers will be recorded in the raw data and included in the final report.
6. TESTSYSTEM
The test system is the Northern Bobwhite quail. The test system was dosed (at Wildlife International Ltd. during the in-life phase of this study) with food prepared by mixing PFOS with feed in a large mixer in appropriate portions to achieve the nominal 10 ppm level. A food dose verification validation study was performed by Wildlife International under study number 454C- 110 (3M #U2723), "Analytical Method Verification for the Determination of PFOS in Avian Diet." Wildlife International verified the actual dosed food for this study and the results will be contained in the in-life Wildlife phase report. Northern Bobwhite serum and liver samples were collected by Wildlife International, Ltd. and sent to 3M Environmental Laboratory for analysis.
6.1
Justification of the Selection of the Test System
Northern Bobwhite quail represent wild bird populations and they are an EPA
recommended species because they do well in a laboratory environment. The use
of these matrices for the study is to determine if PFOS was deposited in the liver
and serum of mating adults that were fed PFOS. Furthermore, analysis of these
matrices from hatchlings will determine if PFOS was passed on to mating adults'
offspring.
7.
SOURCE OF SUPPLY FOR THE TESTSYSTEM
The birds were obtained by Wildlife International, Ltd. See their protocol (study 454108) for information about bird origination location.
8. SPECIMEN AND SAMPLE RECEIPTAND MAINTENANCE
Sera and liver were collected by Wildlife International, Ltd. and shipped to the 3M Environmental Laboratory for analysis. The 21-week endpoint sera and liver samples received by the 3M Environmental Laboratory were from the following birds:
0 40 control adult birds (20 mating pairs) that ingested food containing 0 ppm PFOS 40 experimental adult birds (20 mating pairs) that ingested food containing 10 ppm PFOS
0 20 first generation offspring birds that ingested food containing 0 ppm PFOS
Samples will be maintained frozen except when removed for extraction and analysis as described in the method. The samples will be kept isolated from the test substance during storage.
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9. SUB-CONTRACTED ANALYSIS All sera and liver extractions and analyses as detailed in this protocol amendment will be performed at 3M Environmental Laboratory, Building 2-3E-09, 935 Bush Avenue, St. Paul, MN 55106.55414.
10. EXPERIMENTAL CONDUCT The 21-week endpoint liver and sera samples received (see section 8) will be extracted and analyzed for PFOS quantities using the methods listed below.
10.1 Preparatory and Analytical Method I O . I.I ETS-8-231 Solid Phase Extraction and Analysis of Fluorochemical Compounds from Biological Matrices
11. DATAQUALITYOBJECTIVESDURINGSAMPLE ANALYSIS Method validation for PFOS quantitation in rat and mouse sera and liver is in process in the 3M Environmental Laboratory study EO1-1277. Limited Northern Bobwhite control matrix preclude a cross validation, however, the E01-1277 study methods will be applied to sample analyses of Northern Bobwhite sera and liver samples using the following performance based criteria:
11.1 System Suitability System suitability will be determined prior to the start and at the completion of each analytical run. Prior to the calibration curve and after the last sample of the run three (3) mid-level unextracted calibration standards will be analyzed. The peak area precision and retention time precision will be monitored at the beginning and the end of the run separately. The peak area precision must be equal to or less than 2.0% RSD, the precision of the retention time must be equal to or less than 2.5% RSD. If any item of the system suitability fails, system maintenance must be completed prior to running a second set of system suitability samples and the system suitability must pass before starting the calibration.
11.2 Absolute Recovery The absolute recovery of the method will be evaluated one time in both liver and serum. For each matrix a minimum of triplicate samples will be fortified at a minimum of two levels of PFOS that bracket the range of analyte determined for the samples (i.e., at near the highest level determined in samples and at -150% of LOQ for samples). The samples will be extracted through the method, and analyzed by comparison with an external calibration of non-extracted standards. The non-extracted standard calibration curves will be prepared in methanol, and will consist of a minimum of nine (9) levels, including a methanol blank. The best appropriate regression will be used to describe this curve (for best accuracy at all levels of the standards).
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The accuracy (% absolute recovery) and precision (%CV of the recoveries) will be determined at each level using the external calibration curve for quantitation. There is no control limit for accuracy; precision must be better than 20% at each level. Should a level (high or low) not meet this precision, the method will only be considered valid for levels between the two valid levels. Additional testing may be conducted at other levels to extend the acceptable range of the method.
11.3 Calibration A calibration curve should be prepared in each matrix by spiking the matrix with known concentrations of the analyte and surrogate. A calibration curve should consist of at least nine standard curve points covering the expected range, including the LLOQ. The simplest model that adequately describes the concentration-response relationship should be used. The accuracy of each level will be verified. Any level outside 75% - 125% of nominal must be deactivated, and regression re-calculated, except the LLOQ which must be within 30% of nominal. All levels must show a response greater than twice that of the matrix blank. A maximum of four (4) levels may be deactivated in any one set, or the set will be re-analyzed.
11.4 Limits of Quantitation (LOQ) The lower limit of quantitation (LLOQ) will be defined in liver (ng/g) and in serum (ng/mL) as the lowest acceptable extracted calibration curve point that is within the 70% -130% nominal criteria and with an analyte peak area at least 2 times the blank. The LLOQ determination will be recorded in a note to file and kept with the raw study data as well as being reported in the final report.
The upper limit of quantitation (ULOQ) will be defined in liver and in serum as the highest acceptable extracted curve point that is within the 75% - 125% nominal criteria and includes applicable dilution factor corrections.
71.5
Quality Control Samples
A minimum of one set of nine (9) quality control samples (QC) will be prepared
one time in each matrix. They will consist of three levels of analyte, each in
triplicate. The quality control samples should be prepared in each matrix by
spiking the control matrix with known concentrations of the analyte. The levels
bracket the sample concentrations determined in the study:
0 Low level: equivalent to an analyte concentration near or below the lowest level of analyte determined in samples
0 Mid-level: equivalent to an analyte concentration near the middle of the sample range
0 High level: equivalent to an analyte concentration near or above the highest level of analyte determined in samples
11.6
Quality Control Sample Acceptable Recoveries
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Each QC is expected to show an accuracy of 75-125% of expected. A minimum of 2/3 (6 out of 9) of all QC must meet these criteria and a minimum of one half (2 out of 3) of the QC at each level must meet these criteria. If not, the entire sample set must either be re-analyzed or re-extracted (as decided by the Principal Analytical Investigator).
11.7 Matrix Spikes Two matrix spikes will be extracted with each sample preparation. The matrix spikes will consist of one fortification level in the range of the samples, extracted in duplicate. If the matrix spike and/or matrix spike duplicate fall outside of 25% accuracy, the curve, CCV's, matrix spikes and samples will be reanalyzed.
11.8 Blanks One control matrix and one water method blank will be extracted with each sample preparation.
11.9
Continuing Calibration Verification
Two extracted standards (continuing calibration verification - CCV) will be
analyzed after every 10 injections (starting after the last injection of the calibration
curve). The accuracy of the CCV must be within 25%. Data may only be
reported if bracketed by passing CCV's (or a CCV and the same level calibration
curve point). Data bracketed by one or more failing CCV must be reanalyzed.
7 I .I O
Use of Confirmatory Methods Confirmatory methods are typically not needed with LC/MS/MS analysis.
7 1.1I
Demonsfrafion of Specificity PFOS specificity will be substantiated by chromatographic retention time, by the characteristic primary ion (499), and the characteristic product ion (99) using LC/MS/MS.
12. SUB-CONTRACTED ANALYSIS
72-I
All fluid and tissue extractions and analyses as detailed in this protocol
amendment will be performed at the 3M Environmental Laboratory, Building 2-
3E-09,935 Bush Avenue, St. Paul, MN 55106.
12.2 An amendment to the protocol will be written if extractions and analyses are performed at laboratories other than the 3M Environmental Laboratory.
13. STATISTICAALNALYSIS
Statistical methods will be limited to the calculation of means and standard deviations. Examples of the calculations used in the analyses will be included in the analytical phase report.
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14. REPORT
A final report will be prepared by the 3M Environmental Laboratory. The final report will follow all GLP requirements, and will include a description of all materials and methods used, including a narrative discussion with a tabular presentation of all analyses results.
15. LOCATIONOF RAWDATA,RECORDSA,ND FINALREPORT
When the final report is completed, all original paper data, including protocol, phase report, study correspondence, sample receipt and tracking, sample preparation, and analytical data, will be retained in the archives of 3M Environmental Laboratory. All corresponding training records, calibration records, instrument maintenance logs, standard operating procedures, equipment procedures, and methods will be retained at the 3M Environmental Laboratory, as applicable.
16. SPECIMEN RETENTION
Samples of the test substance (any leftover control sera or liver and samples) and the analytical standards will be maintained in the laboratory for a period of time as specified by regulation or as long as the quality of the preparation affords evaluation. However, samples will not be maintained more than 10 years after the effective date of the final test rule (if applicable). 3M Environmental Laboratory Standard Operating Procedures also apply to sample retention times.
17. REFERENCES
18. I
Wildlife International, Ltd. Protocol No. 454-108, "PFOS: A Reproduction Study
with the Northern Bobwhite".
18.2 3M Study U2723, Wildlife Study 454C-110, "Analytical Method Verification for
the Determination of PFOS in Avian Diet."
18. PROTOCOL AMENDMENTASND DEVIATIONS
Planned changes to the protocol will be in the form of written amendments signed by the Study Director and the Sponsor Representative. Amendments will be considered as part of the protocol and will be attached to the final protocol. Any other changes will be in the form of written deviations, signed by the Study Director and Sponsor Representative and filed with the raw data. All changes to the protocol will be indicated in the final report.
3M Environmental Laboratory 3M Environmental Laboratory
9 of 9
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PFOS: A Reproduction Study with the Nothern Bobwhite
WILDLIFE INTERNATIONAL, LTD
PROJECT NO.: 454-108, EO 1-1245
AMENDMENT TO STUDY PROTOCOL STUDY TITLE: PFOS: A REPRODUCTION STUDY WITH THE NORTHERN BOBWHITE
PROTOCOLNO.: 454/120700/QR/SuB454
AMENDMENTNO.: 11
SPONSOR 3M Corporation
PROJECT NO.: 454-108, E01-1245
EFFECTIVE DATE: March 27,2002
AMENDMENT:
Section 11.1, Sentence4
Change: The peak area precision must be equal to or less than 2.0% RSD, the precision of the retention time must be equal to or less than 2.5% RSD.
To: The peak area precision must be equal to or less than 5.0% RSD, the precision of the retentiontime must be equal to or less than2.5% RSD.
REASON: Information received h m our instrument supplierindicates that a 2.0 % RSD for the area count is common to W detector specifications. Mass spectrometers, which we used for this study, are more sensitive, in general and the fiict that analyte ionization can be suppressedby other speciespresent in the sample matrix and mobile phase make area reproducibility more challenging to maintain. Sample and source
cleanliness are the determining factors, but 5 2.0% is still a bit aggressive for mass spec. The applicationchemists at Micromass, the instrument vendor, suggest a value
of 5 5.0%.
AMENDMENT:
Section 11.3, Sentence 5.
Change: Any level outside 75% - 125%of nominal value must be deactivated, and regression
recalculated, except the LLOQ which must be within 30% of nominal.
To: In some cases the lowest curve point, although outsidethe 30%nominal requirement, may be included in the linear range to influence the lower end of the curve. Only one point, the lowest level point, can be left in for this purpose. It will not be used to determine the limit of quantitation. The limit of quantitation will be the next point on the curve meeting the 30% nominal requirement.
REASON: The removal of the lowest calibration curve point in some cases causes the next lowest calibration point to deviate by greater than 30%. Removal of this point in turn causes the next calibrationpoint to deviateby greaterthan 30%. This continued deletionof calibration points in some cases could continue until there are very few points
3M Environmental Laboratory
Page 1 of 3 Page 211
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
remaining in the curve. The inclusion of a curve point with a deviation greater than 30% is used to influence the lower end of the curve and is not used for determination of the LOQ.
AMENDMENT:
Section 11.3, the last sentence.
Change: A maximum of four (4) levels may be deactivated in any one set, or the set will be reanalyzed.
To: The calibration curve will contain a minimum of six (6) calibration curve points.
REASON: In most cases the calibrationcurves contain greater thannine (9) calibration points. The largenumber of points in the curve is used to select a range representativeto the
samples. Limiting the removal of only four (4) points in some cases could cause a calibration range not representative of the samples.
AMENDMENT:
Section 11.3
Add: The coefficient of determination for the calibration curve should be 0.985.
REASON: No coefficient of determination is included in the protocol. It was inadvertently removed prior to printing of the final copy.
3M Environmental Laboratory
Page 2 of 3 Page 212
- Report E01-1245 04/02/02 17:17 FAX 410 822 0632 ..
PFOS: A Reproduction Study with the Nothern Bobwhite WILDLIFE INTERNATIONAL
@lo07
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18:25 RSD INF TECH 2-E-01 + *84188228915
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PRoJEcrNO.: 456108,
.TD
EO1-1245
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3M Environmental Laboratory
i
Page 213
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
WILDLIFE INTERNATIONAL, LTD
PROJECTNO.:454-108, EO 1-1245
Sean P. Gallagher, Study Director
Joann B. Beavers, Wildlife International, LTD
harold 0.Jo-
rincipal Analyt~caIl nvestigator
Date
Date
4-Z-OZ
Date
Laboratoi
3M Environmental Laboratory
Page 3 of3 Page 214
Report E01-1245 WILDLIFE INTERNATIONAL, LTD
PFOS: A Reproduction Study with the Nothern Bobwhite
PROJECT NO.: 454-108, EO 1- 1245
AMENDMENT TO STUDY PROTOCOL STUDY TITLE: PFOS: A REPRODUCTION STUDY WITH THE NORTHERN BOBWHITE
PROTOCOL NO.: 454/120700/QlUSUB454
AMENDMENT NO.: 12
SPONSOR: 3M Corporation
PROJECT NO.: 454-108, E01-1245
EFFECTIVE DATE: August 16,2002
AMENDMENT:
Change: The 3M Environmental Laboratory Project Identification Number (LIMS) to be included with the study is E01-1245.
To: The main 3M Environmental Laboratory Project Identification Number (LIMS) to be included with the study is E01-1245. Additional tracking numbers associated with this study are U2723, E01-1342, and EO 1-1365.
REASON:
Bobwhite samples were received in the 3M Environmental at several time points. Upon arrival, samples were assigned a LIMS tracking number. Not aware of the scope of this or any other particular study pertaining to these samples, they were checked in to different 3M LIMS projects. LIMS project numbers assigned to this study include the following: U2723, E01-1245, E01-1342, and E01-1365. Samples in each of these projects pertaining to this study were analyzed under one main study number E01-1245.
AMENDMENT:
Change: Harold Johnson is the Principal Analytical Investigator.
To: Lisa A. Stevenson is the Principal Analytical Investigator.
REASON:
To change role of the Principal Analytical Investigator.
3M Environmental Laboratory
Page 1 of 2
Page 215
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
WILDLIFE INTERNATIONAL, LTD
- - Sean P. Gallagher,Study director
r
ut-
Joann B. Bea;ers, Wildlife International,LTD,
Laboratory Management
JLJOh
h a A. Stevenson, Principal AnalyticalInvestigator
William K. Reagen, 3M Environmental Laboratory, Laboratory Management
PROJECT NO.: 454-108, E01-1245
9 a5/oa
Date
4 1 4o x
Date
Date
&?/JG/O
J-
Date
3M Environmental Laboratory
Page 2 of 2
Page 216
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
WILDLIFE INTERNATIONAL. LTD
PROJECT NO.: 454-108, E01- 1245
AMENDMENT TO STUDY PROTOCOL STUDY TITLE: PFOS: A REPRODUCTION STUDY WITH THE NORTHERN BOBWHITE
PROTOCOL NO.: 454/120700/QR/SUB454
AMENDMENT NO.: 13
SPONSOR: 3M Corporation
PROJECT NO.: 454-108, E01-1245
EFFECTIVE DATE: September 27,2002
AMENDMENT:
Change: Rochelle R. Robideau is the Sponsor Representative.
To: Susan A. Beach is the Sponsor Representative.
REASON:
To change role of the Sponsor Representative.
L P. W\+ Sean P. Gallagher, Study Directod
- - Joann B. BeaLrs, Wildlife International, LTD,
Laboratory Management
A , d a S h t n s o n
%sa A. Stevenson, Principal Analytical Investigator
Wilxam K. Reagen, 3M EnvironmentalLaboratory,
Date
Labgratory Management
Su&n
G .& A aJL
A. Beach, Sponsor's Representative
Date
3M Environmental Laboratory
Page 1 of 1
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Report E01-1245 3M Confidential
~
~~
PFOS: A Reproduction Study with the Nothern Bobwhite
Record of Deviation
Study I Project No.
EO 1-1245
Deviation type (Check one)
XSOP
0Protocol
Document number ETS-4-4.0
I. Identification
0Method 0 Other:
0Equipment Procedure
Date(s) of occurrence
1131102,211102,2113102,217102,218102,211 1/02,
2112102,2113102,2115/02
/I. Description
Required procedure/process:
ETS-4-4.0 Internal chain of custody The internal chain of custody form to be used to track all movement of samples Within the lab. The form should be filed with study data or other relevant sample documents.
Actual procedure/process:
Internal chains of custodies were not used to track samples and sample extracts. Since receipt samples were Stored in freezer F1. After homogenizing liver and aliquating sera samples were stored in Freezer F8
Until extraction date. Samples remained frozen until extraction.
Deviation to SOP written.
Ill. Actions Taken
(such as amendment issued, SOP revision, efc.)
Recorded by Authorized by
Date
4 ?-wl
Deviation No.
Dat4e. t c . t , 2
I
or Project Lead at the end of study or project)
Attachment A
3M Environmental Laboratory
ETS-4-8.2 Documentation of Deviations
Page 5 of 1
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PFOS: A Reproduction Study with the Nothern Bobwhite
Record of Deviation
1. Identification
Study 1 Project No.EO1-1245
Deviation Type (Check one)
0 SOP dProtocol
0 Method 0 Equipment Procedure 0 Other:
Document Number :Protocol # : 454/12070O/QR/SuB454, amendment #: 10
Date(s) of occurrence: :1131/02, 2/1/02,2/2/02,2/7/02, 2111/02,2/12/02,2/13/02, 2/14/02,2/18/02,4/11/02, 411 6/02 11. Description:
Required Procedure/process: Section 11.1, System Suitability, second sentence says that a mid-level unextracted calibration standard will be analyzed.
Actual Procedure/process: On occasion through the dropping of calibration points, the system suitability samples were on the high end of the curve or outside the working range of the curve. Although these were unextracted curve points their area counts were at the high end of the calibration curve range, they do pass the system suitability criteria and these data packet will be considered acceptable. The data from 2/7/02 was just above the calibration range. These data will also be considered acceptable.
Ill. Actions Taken: (such as amendment issued, SOP revision, etc.) Issuing of this protocol deviation.
3M Environmental Laboratory
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PFOS: A Reproduction Study with the Nothern Bobwhite
Record of Deviation
1. /denfificafion
Study 1 Project No.EO1-1245
Deviation Type (Check one)
.iSOP
0 Protocol
0 Method 0 Equipment Procedure 0 Other:
Document Number:ETS-8-23 1.1
Date(s) of occurrence:1131/02, 2/1/02,2/2/02,2/7/02, 2111/02,2/12/02,2/13/02,2/14/02, 2/18/02,4/11/02, 411 6/02 II. Description:
Required Procedure/process: Section 12.1,Calculations: If other calculations are used than those listed, they will be documented in the raw data.
Actual Procedure/process:
Standard E01-1342-36010, Prep sheet description "Curve Point - IOppb in liver", was prepped by spiking 20uL of 02001-66 (1.OOug/mL) into 1 mL of liver homogenate. This homogenate consists of 5g liver plus 45mL water. Since ImL out of 5 O m L homogenate is used to prep each extracted standard, 1/50 of the 5g (0.Ig) of liver is "spiked". After this homogenate is spiked and prepared using SPE, the final eluate is 2.0mL of MeOH. THEREFORE...
( 2 0 4 (1 .OOugPFOS-/mLMeOH) (1.OmL/lOOOuL) (1OOOngil.Oug) = 20ng PFOS- onto SPE column
20ng PFOS-/ 2.0mL MeOH = 1Ong PFOS/mL MeOH. (Since this standard is recorded as lOppb, the correct units are IOngPFOS-/mLof MeOH.) These are therefore the units being measured and reported on the chromatographic system.
Similarly, the following statement is true.
(20ng PFOS-/ 1. O m L homogenate) (1 .OmL homogenate / 0.1g liver) = 200ng PF0S-l g liver
This relationship shows the factor of 20 used to "correct" the units when calculating the final result in ng/g from the chromatographic result that is in ng/mL.
Samde Calculation: "EO1-1342-30348, Oppm a i . 333 M liver"
Chromatographic result is 10.76 ng/mL; reported value is 208.4 ng/g. Since the 1.0333g initial sample weight of liver is homogenized with 9.0mL water, and ImL (10% oftotal liver weighed, since a liver density of 1.00 is assumed) is used for the entire SPE procedure, the calculation is as follows:
(10.76ng PFOS-/ mL MeOH) (2mL MeOH / 0.1033 g liver) = 208.4 ng PFOS- / g liver
Sample Calculation: Sample "E01-1342-36017, QCo-lOmb-I": This QC sample is prepared by adding 4uL of 02001-53 (5.020ug PFOS-/ mL MeOH) spiked into I m L liver homogenate.
((4ul) (5.020ug/mL) (lmL/1000uL) (1000ng/ug)) / (0.lg liver) = 200.8ng PFOS- / g liver
Using the earlier calculation, the analytical result of 13.59ng/mL calculates to 271.8ng/g liver. Since the spike level is 200.8ng PFOS-/ g liver, the recovery is (271.8/200.8)(100)=135.4%.
3M Environmental Laboratory Form ETS-4-8.0
3M Environmental Laboratory
Deviation No.
3
(assigned by Study Director or Project Lead at the end of study or project)
Page 220
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Record of Deviation
111. Actions Taken: (such as amendment issued, SOP revision, etc.) Issuing of this SOP deviation and a note to file.
Recorded By
&c-Lc
&IV. Impact on Study / Project
There will be no impact on the study as this is for clarification purposes.
Date
4<(ei.oz
Date
4 19.c-2-
/
3M Environmental Laboratory Form ETS-4-8.0
3M Environmental Laboratory
Deviation No.
3
(assigned by Study Director or Project Lead at the end of study or project)
Page 221
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Record of Deviation
II Study / Project No. E01-1245 .-.____ ^~"_"I""""""""""""."""_llll"""llll."""
""""""".""_l^
""""".""^_^^"^.
1. Identification
" ^..^^
....
.. ... .. ... ....
Deviation Type
0 SOP
0 Method 0 Equipment
(Check one)
4Protocol 0 Other:
.........._.."._ "."_ ____ " __ _ "^" ,,,,,
Procedure
Document Number: ETS-8-23 1.1 Date(s) of occurrence: Throughout the study
Required Procedure/process:
Section 11.3, Sentence 5 states: Any level outside 75% - 125% of nominal value must be
deactivated. and rea-ession recalculated.. .
Actu__a__ l Procedure/proce~ ss: -
--
_--. - -
__ -
Many of the high calibration points in this study are kept in the curve despitebeing above the
apex of the curve. When a calibration point lies above the apex, it is considered indeterminant
(flagged with an I) and no concentration is calculated for the standard. If no concentration is
calculated, no percent difference is calculated for evaluating whether or not that standard is
within the stated criteria.
Removal of these points in most cases causes the next calibration point to then be above the
apex of the curve. This continued deletion of points could continue until there are no points
remaining on the curve. Therefore, calibration points above the apex were included in the
range of the curve with no evaluation of percent deviation criteria.
Ill. Actions Taken:
---_- ~
- -(such as amendment_i__ssu_e-d,.LSOP" re___ vision, etc.)
I
~
I
I_
~~~
111--
1 1 1 1 1
I
This deviation was written, a note to file was written, and data points which were above the
next highest calibration point were reanalyzed.
Lisa A. Stevenson
Date
08116/0023 I J L I X L
3M Environmental Laboratory Form ETS-4-8.0
3M Environmental Laboratory
Deviation No.
?
(assigned by Study Director or Project Lead at the end of study or project)
Page 222
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Record of Deviation
I. Identification
1 1 1 1 1 1
I - - - __
-- -
".-.Is"o-p Study / Project No.-EO1-1245
""
" """"" " ". __"_l.""
~.II
_l".""_"."__",."__.I~..-""_l."...""
.. .
Deviation Type
Method 0 Equipment Procedure
(Check one)
0 Protocol 0 Other:
"".. "" """_
Document Number: ETS-8-231.1
Date(s) of occurrence: Entire Study II. Description:
Required Procedure/process:
Section 12.1, Calculations: If other calculations are used than those listed, they will be documented in the raw data.
Actual Procedurdprocess:
Standard EOi---1345-35771,Prep sheet description "10 ppb sera curve point", was prepped by spiking 4uL of 02001-52 -(5.02OuglmL)into 2 mL of pooled sera. This diluted sera consists of 2mL sera plus 38mL water. Since 1mLout of 40mL diluted sera is used to prepare each extracted standard, 1/40 of the 2mL of sera is "spiked". After 1.0 mL of diluted sera is
spiked and prepared using SPE, the final eluate is 2.0mL of MeOH. THEREFORE.. .
(5.02Oug PFOS-/mLMeOH) * (4111) * (1.OmUlOOOuL) * (1000ngll.Oug) = 20ng PFOS- onto SPE column
20ng PFOS / 2.0mL MeOH = long PFOS/mL MeOH. (Since this standard is recorded as IOppb, the correct units are long PFOS-/mL MeOH.) These are therefore the units being measured and reported on the chromatographic system.
Similarly, the following statement is true.
(20ng PFOS / 1. O m L diluted sera) * (40.0mL diluted sera/ 2.0mL initial sera) = 400ng PFOS-/mL Sera
This relationship shows the factor of 40 (or 2.0mL MeOW 0.05mL Sera) used to "correct" the units when calculating the final result in ng PFOS/mL Sera from the chromatographic result that is in ng PFOS/mL MeOH.
Samde Calculation: "E01-1245-28481,454-108-370,10ppm female, adult, 02-01-02 Chromatographic result is 229.2 ng/mL MeOH; reported value is 9170 ng/mL Sera. Since the 1.0 mL initial sample volume of sera is diluted with 38fhnL water, and 1mL is used for the entire SPE procedure, the calculation is as follows:
i"i.0, or o. Vao ciiluhcn @LAX ~ ~ l a o / i u
(229.2ng PFOS-/ 1.0mL MeOH) * (2.0mL MeOH/ 0.05mL Sera) = 9170ng PFOS- / mL Sera
Samule Calculation: Sample "E01-1245-36155, QC@lOOppb-1": This QC sample is prepared by adding 2uL of 02001-52 (5.02ugPF0S-ImL
MeOH) spiked into 1mLdiluted sera-(or 0.05 mL of initiai sera):
((5.02ug/mL) * (2ul) * (lmU1000uL) * (1000nglug)) / (0.05 mL Sera) = 200.8 ng PFOS- I mL Sera
Using the earlier calculation, the analytical result of 6.17 nglmL calculates to 246.8ndmL Sera. Since the spike level is
2.-0.0...8.-%....PF-.OS-../.mL""""S""e" ra9-t.h.e recove.r.y is (246.^8_/.2^_0""0".._8.")"*I(_1_.0..0..).=..1..2.2......9%...1 .. , , "" ," _"
" ^"^^ "",," . ...... ...... .. .
Ill. Actions Taken:
(such as amendment issued, SOP revision, etc.)
T__h__i_s__d-eviation was_written-and a_ n_ o- -te to- file was _w__r_itten.
__ -
-
I
-
I
Recorded By Lisa A. Stevenson
loa, Date
08/16/02 0 $ / 1 ~
Form ETS-4-8.0
3M Environmental Laboratory
(assignedby Study Director or Project Lead at the end of study or project)
Page 223
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Record of Deviation
I
1. Identification
Study / Project No. E01-1245
Deviation Type (Check one)
0 SOP 0 Protocol
4 Method 0 Equipment Procedure
0 Other:
Document Number: ETS-8-231.1 Date(s) of occurrence: Throughout the study
11. Description:
Required Procedure/process: Section 13.3 of the method states: Two thirds of all quality control samples and 1/2 of eac quality control -s_a_m__ple at each level are expected to show a_n_ accuracy of 75-12_5_ %- .
Actual Procedure/process:
A1125 ppb quail liver quality control sam- ple recoveries were >125%.
@as 03111103
cLih2h3
. Ill. Actions Taken: J
,.
(such as amendment issued, SOP revision, etc.)
This deviation was written, liver data reported at the low range of the curve may be biased
and quality control data not _w_ ithin criteria are flagged in the raw data. I
1 Recorded By
h
I fl-fiA Lisa A. Stevenson
JLlllO?
1 Authorized By (Study Director /Project Lead)
Date 08/26/02
fd
Date
3M Environmental Laboratory Form ETS-4-8.0
3M Environmental Laboratory
Deviation No.
%L
(assigned by Study Director or Project Lead at the end of study or project)
Page 224
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
Record of Deviation
1. Identification
Study / Project No.EO1-1245
Deviation Type (Check one)
4 SOP
Protocol
E Method 0 Equipment Procedure [ 1 Other:
Document Number:ETS-8-23 1.1
Date(s) of occurrence: 1131/02, 2/1/02, 2/2/02, 2/7/02, 2111/02, 2/12/02. 2/13/02. 2/14/02. 2/18/02.4/11/02.4/16/02
II. Description:
Required Procedure/process:Section 12.1, Calculations: If other calculations are used than those listed, they
will be documented in the raw data.
Actual Procedurehrocess:
This deviation supersedes deviation #3 explaining the liver calculation:
Standard E01-1342-36010, Prep sheet description "Curve Point - lOppb in liver", was prepped by spiking 20uL of 02001-66 (l.OOug/mL) into 1 mL of liver homogenate. This homogenate consists of 5.03538 liver plus 45.0mL water. Since ImL out of
50.0353mL homogenate is used to prep each extracted standard, 1/50 of the 5.03538 (0.100635g = 5.0353 g/(9.0 of water +
5.0353 g of liver) is "spiked". After this homogenate is spiked and prepared using SPE, the final eluate is 2.0mL of MeOH. THEREFORE.. .
(20 uL) * (1.000ug PFOS-/mLMeOH) * (1.0 mL/lOOO uL) * (1000 ngll.0 ug) = 20.0 ng PFOS-onto SPE column
20.0 ng PFOS- / 2.0 mL MeOH = 10.0 ng PFOS`/mL MeOH. (Since this standard is recorded as IOppb, the correct units are 10.0ng PFOS-/mLof MeOH.) These are the units being measured and reported on the chromatographic system.
Similarly, the following statement is true.
(20.0ng PFOS-/ l.0mL homogenate) * (l.OmL homogenate / 0.100635 g liver) = 199ngPFOS-/ g liver
Samule Calculation: "E01-1342-30348, Oppm a.1. 333 M liver"
Chromatographic result is 10.76 ng/mL; reported value is 209 ng/g. Since the 1.03388 initial sample weight of liver is homogenized with 9.0mL water, and 1.0 mL is used for the entire SPE procedure, the calculation is as follows:
1.0338 g / (9.0 mL water + 1.0338 g liver) = 0.103032 g of liver in 1.0 mL of homogenate removed for extraction.
(10.76 ng PFOS-/ mL MeOH) * (2.0 mL MeOH IO.103032 g liver) = 209 ng PFOS- / g liver
Sample Calculation; Sample "E01-1342-36017, OCQ1ODpb-l": This QC sample IS prepared by adding 4 uL of 02001-52 (5.020ug PFOS- / mL MeOH) spiked into 1mL liver homogenate.
((4ul) * (5.020ug/mL)* (lmL/IOOOuL)* (1000ng/ug)) / (0.1006358 liver) = 200 ng PFOS-/ g liver
Using the earlier calculation, the analytical result of 13.59ng/mLcalculates to 270 ng/g liver. Since the spike level IS 200ng
PFOS-/ g liver, the recovery is (270/200) * (100)=135.0%. Ill. Actions Taken:
(such as amendment issued, SOP revision, etc.)
Issuing of this S O P deviation.
A\ Recorded By
d
Date
Lisa A. Stevenson &.-..h
&A/-f?nI-,, .
Authorized By (Study Director /Project Lead)
Form ETS-4-8.0
3M Environmental Laboratory
(assigned by Study Director or Project Lead at the end of study or project)
Page 225
Report E01-1245
Report E01-1245
PFOS: A Reproduction Study with the Nothern Bobwhite
PFOS: A Reproduction Study with the Northern Bobwhite
ATTACHMENTF: EXAMPLCEALCULATIONS
FORMULA USED FOR SERA ANALYSES IN STUDY E01-1245 AR (ng/mL MeOH) x DF x Dilution(di1utedsera) = ng/mL Sera
Calculation Used for E01-1245-28481,454-108-370,lO ppm Female, adult (initial volume = 0.3 mL) 229.24 ng/mL MeOH x 1 x 40 = 9170 ng/mL Sera
FORMULUASED FOR LIVERANALYSES IN STUDY E01-1245
AR (ng/mL MeOH) x DF x
Final Volume (mL)
= nglg Liver
amount of liver in diluted sample (9)
Calculation Used for E01-1342-30672,lO ppm, a.i. 369 M Liver (initial weight = 1.0010 g)
393.21 ng/mL MeOH x 10 x
2.0 mL MeOH = 78600 ng/g Liver 0.100090 g Liver
AR = Analytical result from MassLynx summary DF = Dilution factor Dilution(di1utedsera) = Final volume(mL)/amount of sera in diluted sample(mL) A m o u n t of sera in diluted sample(mL) = amount of sera used(mL)/total amount of sera + water(mL)
Amount of liver in diluted sample(g) = amount of liver weighed(g)/ amount of liver weighed(g) + water added for
homogenizing(mL=g)
Examples:
Amount of sera in diluted sample(mL) = amount of sera used (0.3 mL)/total amount of sera + water (6 mL) = 0.05 mL
Dilution(di1utedsera)(mL) = final volume (2.0mL)/amount of sera in diluted sample (0.05 mL) = 40
Amount of liver in diluted sample(g) = amount of liver weighed (1.0010 g)/amount of liver weighed (1.0010 g) + water
added for homogenizing (9.00 mL) = 1.0010 g / 10.0010 g = 1.00090 g
Note: For sera samples with less than 0.05 mL sera received, additionalwater was added in order to remove 1.O mL of diluted sera for extraction. For these samples, the dilution(di1uted sera) value was updated to reflect the correct dilution. For example, if a sample was receivedwith 0.02mL sera available, 0.98 mL of water was added. the amount of sera in diluted sample = 0.02mU1 .O mL = 0.02mL.
The dilution(di1utedsera)(mL)= 2.0 mU0.02 mL = 50
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