Document 0gN902N3V4qkkM6X8gZ7XObgd
AR226-2691
13
AR226-2691
DuPont EMSE Report No. 15-03
Study Title
ACCELERATED BlODEGRADATION OF 8-2 TELOMER B ALCOHOL- A
PRELIMINARY SCREENING STUDY
|
Test Guideline
This study uses the concept ofOECD Guideline for Testing of Chemicals; Section 3: Inherent
Biodegradability (1992).
Author Ning Wang, Ph.D.
Study Completion Date 20 March 2003
Test Facilities E.I. du Font de Nemours and Company
Central Research & Development Corporate Center for Engineering Research Environmental and Microbiological Sciences & Engineering Glasgow Building 300, P.O. Box 6101
Newark, DE 19714-6101, USA
and
E.I. du Pont de Nemours and Company Haskell Laboratory for Health and Environmental Sciences Newark, DE 19714, USA
Submitter E.I. du Pont de Nemours and Company DuPont Chemical Solutions Enterprise Wilmington, DE 19898, USA
EMSE Study /Project Number
15-03/4842
Report Number EMSER 15-03
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DuPont EMSE Report No. 15-03 PAGE RESERVED FOR SPECIFIC COUNTRY REQUIREMENTS
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DuPontEMSE Report No. 15-03
CERTIFICATION OF AUTHENTICITY
ACCELERATED BlODEGRADATION OF 8-2 TELOMER B ALCOHOL - A
',<
PRELIMINARY SCREENING STUDY
We, the undersigned, declare that the work described in this report was performed under our
supervision, and that this report provides an accurate record of the procedures and results.
Report by:
^
Ning Wang, Ph.D. Senior Research Biologist
Approved by:
V L ^ ^ JRoTiTn, Gannon, Ph.D.
gxyx/y^rz^^s.^
(Research Manager
63J^Q/^
Date
03/3 0 103
/
Date
Study Initiation Date:
14-July-2002
Date Study Completed: 20-March-2003
Submitter: E.I. du Pont de Nemours and Company DuPont Chemical Solutions Enterprise Wilmington, DE 19898, USA
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DuPont EMSE Report No. 15-03
TABLE OF CONTENTS
Page Reserved for Specific Country Requirements........................................................................^ Certification of Authenticity............................................................................................................3
Table of Contents............................................................................................................................^
1.0 Summary .................................................................................................................................6 2.0 General Study Information......................................................................................................? 3.0 Materials and Methods............................................................................................................8
3.1 TestSystem..........................................................................................................................8 3.2 Test Conduct......................................................................................................................10 3.3 Sample Extraction and Analysis........................................................................................12
3.3.1 Sample Collection and Extraction............................................................................12 3.3.2 Analytical Methods for Test Substance and Products..............................................13
4.0 Results and Discussion..........................................................................................................17
5.0 Conclusions...........................................................................................................................18
6.0 Reference...............................................................................................................................18
Figure 1 8-2 Telomer B Alcohol (8-2 TBA) concentration during the 28-day test*................... 19
Figure 2 Fluoride concentration during the 28-day test*.............................................................20 Table 1: Estimated Concentrationsf offluorinated acid metabolites at day 0 (19-Jul-
2002) and day 28 (16-Aug-2002).........................................................................................21 Table 2: Daily temperature readings in the lab where the test was conducted. The
temperature was recorded by a calibrated Dickson Recorder (Model THDx, serial #
0118247)................................................................................................................................22
Appendix A:...................................................................................................................................23
Table A-l. Analytical results of 8-2 TBA concentration at day 0 (19-Jul-2002), day 14
(2-Aug-2002), and day 28 (16-Aug-2002)............................................................................24
Table A-l (continued)...................................................................................................................^ Table A-l (continued)...................................................................................................................^ Table A-2. Analytical results of Spike recovery of 8-2 TBA from the sample matrix
(Treatment 3, adapted bacterial culture plus growth medium in coated glass serum bottles) at day 0 (19-Jul-2002), day 14 (2-Aug-2002), and day 28 (16-Aug-2002) .............27 Table A-3. Analytical results offluoride concentration at day 0 (19-Jul-2002), day 14 (2Aug-2002), and day 28 (16-Aug-2002).......................................................................,.........28 Table A-3 (continued)...................................................................................................................^ Table A-4. Analytical results offluorinated acid metabolite 2-perfluorooctyl ethanoic acid (2-PFOEA) at day 0 (19-Jul-2002), and day 28 (16-Aug-2002)...................................30 Table A-5. Analytical results offluorinated acid metabolite 2H-hexadecafluoro-2-
decenoic acid ( 2H-HDF-2-DA) at day 0 (19-Jul-2002), and day 28 (16-Aug-2002) .........31 Table A-6. Analytical results offluorinated acid metabolite perfluorooctanoic acid
(PFOA) at day 0 (19-Jul-2002), and day 28 (16-Aug-2002) ................................................32 Table A-7. Analytical results offluorinated acid metabolite perfluorohexanoic acid
(PFHA) at day 0 (19-Jul-2002), and day 28 (16-Aug-2002) ................................................33
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DuPontEMSE Report No. 15-03
Table A-8. Components of bacterial growth medium used for the test........................................34 Figure A-l A fluoride standard calibration curve........................................................................35 Figure A-2 A calibration curve used for 8-2 TBA quantification of samples TA 50-1 to
TA 50-26...............................................................................................................................36 Figure A-3 A chromatograph of sample TA50-3 used for 8-2 TBA analysis .............................37 Figure A-4 A calibration curve used for 8-2 TBA quantification of samples TA 51-1 to
TA51-17 and TA 52-1 to TA52-17.......................................................................................38 Figure A-5 A chromatograph of sample TA 52-3 used for 8-2 TBA analysis ............................39 Figure A-6 Chromatographs of samples TA52-3 and TA52-6, 30 ug L"1 of standard acid
mix made in sample matrix TA50-15, sample matrix TA52-16, and a methanol
solvent blank.........................................................................................................................40
Figure A-6 Chromatographs of samples TA52-3 and TA52-6, 30 ug L'1 of standard acid mix made in sample matrix TA50-15, sample matrix TA52-16, and a methanol
solvent blank - Continued from page 42..............................................................................41
Figure A-7 A GC/MS chromatograph of material characterization of 8-2 TBA test
substance used in this study ..................................................................................................42 Appendix B:...................................................................................................................................43
Table B-l. Analytical results of spike recovery of2-perfluorooctyl ethanoic acid (2PFOEA) at day 0 (17-Sep-2002), and day 2 (19-Sep-2002)................................................. 44
Table B-2. Analytical results of spike recovery of2H-hexadecafluoro-2-decenoic acid< 2H-HDF-2-DA) at day 0 (17-Sep-2002), and day 2 (19-Sep-2002)...................... ?;;............45
Table B-3. Analytical results of spike recovery ofperfluorooctanoic acid (BFOA) at day 0 (17-Sep-2002), and day 2 (19-Sep-2002).......................................sn..^.).........................46
Table B-4. Analytical results of spike recovery ofperfluorohexanoic acid (PFHA) afcday 0 (17-Sep-2002), and day 2 (19-Sep-2002)................................................................w,.......47
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1.0
DuPont EMSE Report No. 15-03
ACCELERATED BlODEGRADATJON OF 8-2 TELOMER B ALCOHOL- A
PRELIMINARY SCREENING STUDY
Author Ning Wang, Ph.D.
SUMMARY
Rationale of the Study
This test generates environmental fate information potentially relevant to the persistence of the test substance. When a chemical enters the environment, biodegradation i& one of the major routes that determines the environmental fate of the chemical. The biodegradation of 8-2 Telomer B Alcohol (8-2 TBA, CAS# 678-39-7) may be slow, because only 2 hydrocarbons of the molecule may be readily accessible for microbial metabolism, the rest of the 8 perfluorinated carbons are expected to be difficult to be metabolized by
microorganisms. Hypothetically, microorganisms that have been pre-exposed to the test chemical may adapt to have a higher metabolic capacity to transform and potentially
defluorinate 8-2 TBA under favorable growth conditions. A test with pre-adapted bacterial
culture under favorable growth conditions may give a clearer indication of the
biotransformation potential for a given test chemical. Such a test may provide optimal
conditions for potential microbial metabolism of 8-2 TBA. For example, if a chemicaliis.not
metabolized undersuch optimized conditions, it is less likely to be metabolized/biodsgraded
in the environmeA^he test system is also useful to rapidly identify potentia.lnrneat.yTh'; biotransformation poducts and this will enable use of authentic standards to facilitafeod identification and quantification of transformation products in the subsequent definitive' .!
biodegradability studies.
Test System:
The primary biotransformation potential of the test substance 8-2 TBA in bacterial growth medium plus bacterial culture that has pre-grown in 50-100 mg/L of 8-2 TBA was
determined. The bacterial culture originated from an industrial waste water treatment facility. The test system consisted of individually crimped test vessels (glass serum bottles). The test
was conducted at room temperature (~24C). The 8-2 TBA stock solution (made in ethanol) was introduced into the bacterial growth medium (Table A-8) with the bacterial inoculum and was kept in closed bottles in the dark at room temperature. Periodically (days 0,14, and 28), sample bottles were sacrificed for extraction and analysis of the test chemical, fluorinated acid metabolites, and fluoride (F~ion).
Findings:
The primary biotransformation of 8-2 TBA was rapid (>70% at day 14 and near 100% at day 28) compared with the abiotic control. Significant defluorination of 8-2 TBA was observed during the test. Four of the potential biotransformation products were monitored for
and were identified through tandem mass spectrometry analysis and comparison with analytical standards: 1) 2-perfluorooctyl ethanoic acid (2-PFOEA, FQ^gCHhCOOH, CAS# 27854-31-5); 2) 2H-hexadecafluoro-2-decenoic acid (2H-HDF-2-DA, F(CF2)7CF=CHCOOH, CAS# 161094-76-4); 3) perfluorooctanoic acid (PFOA,
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2.0
DuPont EMSE Report No. 15-03
F(CF2)7COOH, CAS# 335-67-1); and 4) perfluorohexanoic acid (PFHA, F(CF2)5COOH, CAS# 307-24-4). Other potential transformation products that formed during the test were not determined.
Conclusions:
Under the test conditions, 8-2 TBA is being rapidly transformed to fluorinated acids and other unidentified transformation products. Although PFOA is one of the identified metabolites, it accounted for <2% of mass balance. PFOA apparently may be farther metabolized to form PFHA and may not be an ultimate (stable) metabolite under the test
conditions.
GENERAL STUDY INFORMATION
v w'c-N.rf
Study Objectives
Determine the biotransformation potential of 8-2 TBA by monitoring its concentration changes during a biodegradation test with optimized conditions
Determine the degree of defluorination of 8-2 TBA
Identify potential metabolites such as fluorinated acids during the test
Assess whether perfluorinated acids can be farther metabolized
Determine possible biodegradation pathways of 8-2 TBA
Confirm expectatioi^femt ass balance will be difficult to achieve in cold studies due. i.iS.' :',;
to potential abiotic rIBBval mechanisms - volatility and adsorption.
'
' mov
Test System Justification The test system is modified from OECD 302 guidelines and was requested by the submitter.
Study Personnel
E.I. du Font de Nemours and Company Central Research & Development - Corporate Center for Engineering Research -
Environmental and Microbiological Sciences & Engineering
Haskell Laboratory for Health and Environmental Sciences
: r.ii-
Management:
John T. Gannon, Ph.D. E.I. du Pont de Nemours and Company Central Research and Development Corporate Center for Engineering Research Environmental and Microbiological Sciences & Engineering Glasgow Building 300, P.O. Box 6101 Newark, DE 19714-6101, USA and
S. Mark Kennedy, Ph.D. Haskell Laboratory for Health and Environmental Sciences Newark. DE 19714, USA
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3.0
3.1 3.1.1
DuPont EMSE Report No. 15-03
Study Director: Analytical Chemists: Technical Personnel:
Ning Wang, Ph.D. E.I. du Pont de Nemours and Company Central Research and Development Corporate Center for Engineering Research Environmental and Microbiological Sciences & Glasgow Building 300, P.O. Box 6101 Newark, DE 19714-6101, USA
Engineering
Bogdan Szostek, Ph.D.
E.I. du Pont de Nemours and Company Haskell Laboratory for Health and Environmental Sciences Newark, DE USA 19714, USA
Vladimir Capka, Ph.D.
E.I. du Pont de Nemours and Company Haskell Laboratory for Health and Environmental Sciences Newark, DE USA 19714, USA
Patrick W. Folsom, DuPont Central Research & Development Keith B. Prickett, DuPont Haskell Laboratory Richard F. Rossi, DuPont Haskell Laboratory
Study Execution Dates Experimental Start Date: Experimental Completion Date: Study Completion Date:
19-Jul-2002 19-Sep-2002 20-March-2003
MATERIALS AND METHODS
Test System Test Substance
Name: Synonym: Active substance(s) CAS Name:
Molecular weight CAS Number(s):
8-2 Telomer B Alcohol
(Perfluorooctyl)ethanol, 8-2 TBA 8-2 Telomer B Alcohol, 99%
1-Decanol, 3,3,4,4,5,5,6,6,7,7,8,8,9,9,10,10,10heptadecafluoro464.12gmole'1
678-39-7
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Structure:
DuPont EMSE Report No. 15-03
3.1.2 3.1.3
3.1.4
Lot Number: EMSE Sample Number: Concentration ofa.s., nominal: Concentration ofa.s., analyzed: Major impurity
Certificate of Analysis Date:
Date Received: Solubility at 25C.: Vapor pressure: Stability:
Appearance/Color: Storage Conditions: Safety Precautions:
P.00/001 E93386-80 99%
99.2% 0.8% as C7FisCF=CHCH20H (Figure A-7) 13-Sept-2001
26-Mar-2002 -140 ug L-1 0.023 mm Hg Stable at ambient room temperature White solid Room temperature; keep tightly closed Wear lab coat, protective gloves, and safety glasses
Reference Substance None
Preparation of Bacterial Growth Medium The 20% yeast extract and different mineral stock solutions were prepared and were autoclaved. The bacterial growth medium was prepared by dilution of the different stock solutions (see Table A-8 for details of the medium components). The growth medium was
sterile filtered into Nalgene 1 liter filter units and was stored at room temperature.
Test vessel Coating with 8-2 TEA solution On 15-Jul-2002, Glass serum bottles (120 mL volume) were filled with 100 mL of sterile water and 10 uL of 8-2 TBA stock solution (3 mg/mL in ethanol) was injected into each of the bottles for a final concentration of 300 ug/L. The bottles were sealed and incubated for 3 days at room temperature with about 250 RPM shaking. The bottles were rinsed with sterile deionized water and capped for the test the next day.
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3.1.5
3.1.6 3.7.7 3.2
DuPont EMSE Report No. 15-03
Adapted bacterial culture preparation Approximately 500 mL of industrial waste sludge from an industrial waste water treatment facility was collected from aeriation tanks on 13-June-2002 and were sent to the test lab. Upon arriving at the test lab the same day, the sludge was assigned an ID number E93386-87. The sludge was mixed by briefly shaking the jug to suspend the microorganisms. After settling the sludge for approximately 15 min to remove coarse matters, about 2 mL aliquot of the sludge was transferred to a 250 mL sterile cell culture flask that contained about 50 mg/L of 8-2 TBA in 100 mL bacterial growth medium. The bacterial culture was maintained at room temperature by periodically transferring about 0.5 mL of the culture into another 50 mL polypropylene tube that contained about 5 mL of the bacterial growth medium plus 50-100 mg/L of 8-2 TBA. The culture was mixed by constant shaking at about 210 RPM. The day before the initiation of the test (18-Jul-2002), 0.5 mL of the bacterial culture was transferred into a 250 mL flask that already contained 100 mL of the bacterial growth medium plus 600 ug/L of 8-2 TBA and incubated overnight at room temperature. The cell culture was centrifuged and the pellet was redissolved in the growth medium after discarding the supernatant. This wash step was repeated once. The washed bacterial culture will serve as inoculum for the test. Ten mL of the washed bacterial culture was transferred with a plastic pipette to a 20 mL scintillation vila and was autoclaved. The autoclaved culture was referred to as killed bacterial culture and will be used for abiotic control treatment.
Activated Sludge Collection Approximately 4 liters of activated sludge was collected from the City ofWilmington (DE) Municipal Waste Treatment Facility (POTW) - Aeriation Basin # 2 on 16 September 2002.
Upon arriving at the test lab, the sludge was assigned an ID number E93386-100. The sludge
was mixed by briefly shaking the jug to suspend the microorganisms. After settling the sludge for approximately 15 min to remove coarse matters, the upper aqueous phase of the sludge was filtered through a nylon net with a pore size of 85 um. The filtrate was inoculated into the bacterial growth medium and incubated overnight. This bacterial culture was used as inoculum in a separate experiment to conduct spike recovery of four specific fluorinated acid standards, which were quantified in the study. These spike recoveries are assumed to be also representative of fluorinated acids recovery from the adapted baterial culture.
Test Units
Test vessels were 120 mL borosilicate glass serum bottles with pre-cleaned aluminum-lined crimp caps. The pre-cleaning was done by rinsing the aluminum foil and septa with methanol once and then with sterile deionized water three times.
Test Conduct
Five types of experimental treatments were conducted. The pre-cleaning was done by rinsing the aluminum foil and septa with methanol once and then with sterile deionized water three
times.
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3.2.1 3.2.2 3.2.3
3.2.4 3.2.5 3.2.6
DuPontEMSE Report No. 15-03
Treatment I - 600 /us/L of 8-2 TEA in Bacterial Growth Medium plus the Bacterial
Culture Inoculum in Coated Bottles
For a total of 15 coated glass serum bottles (5 replicates x 3 sampling time points), 29.34 mL of of the growth medium, 0.663 mL of the washed bacterial culture, and 6 uL of 8-2 TBA stock solution (3 mg/mL in ethanol) were added to each of the glass serum bottles. The
bottles were crimped with pre-cleaned aluminum foil and PTFE/silicone septa.
Treatment 2 - 600 us/L of 8-2 TBA in Bacterial Growth Medium plus Killed Bacterial Culture in Coated Bottles For a total of 9 coated glass serum bottles (3 replicates x 3 sampling time points), 29.04 mL of the growth medium, 0.663 mL of the killed bacterial culture, 0.3 mL of 0.2 M NaCN, and 6 uL of 8-2 TBA stock solution (3 mg/mL in ethanol) were added to each of the glass serum
bottles. The bottles were crimped with pre-cleaned aluminum foil and PTFE/silicone septa.
This treatment served as an abiotic control.
Treatment 3 - Growth Medium plus Bacterial Culture Inoculum in Coated Bottles for 8-2 TBA Spike Recovery ^ For a total of 9 coated glass serum bottles (3 replicates x 3 sampling time points), 29.34 mL of the growth medium and 0.663 mL of the washed bacterial culture was added to each of the glass serum bottles. The bottles were crimped with pre-cleaned aluminum foil and PTFE/silicone septa.
At each sampling time points (Day 0, 14, and 28), 3 bottles were spiked (dosed) with 6 uL of 8-2 TBA stock solution (3 mg^mL in ethanol) for a final concentration of 600 ug/L. The ,: :;,. bottles were shaken at 200-301PRPM for approximately 30 min before sample collection aWW'
sample extraction.
Treatment 4 - Growth Medium plus Bacterial Culture Inoculum in Coated Bottles For a total of 9 coated glass serum bottles (3 replicates x 3 sampling time points), 29.34 mL of the growth medium and 0.663 mL of the washed bacterial culture was added to each of the glass serum bottles. The bottles were crimped with pre-cleaned aluminum foil and PTFE/silicone septa. This treatment was used to provide an indication whether 8-2 TBA that has been adsorbed to the glass wall of the test vessels was available for biotransformation.
Treatment 5 - Growth Medium plus Bacterial Culture Inoculum in non-Coated Bottles For a total of 9 non-coated'gBBs serum bottles (3 replicates x 3 sampling time points), 29.34 mL of the growth medium and 0.663 mL of the washed bacterial culture was added to each of the glass serum bottles. The bottles were crimped with pre-cleaned aluminum foil and PTFE/silicone septa. This treatment will serve as sample matrix control for quantification offluorinated acid metabolites by LC/MS/MS.
Spike Recovery of Fluorinated Acids from Sample Matrix On 17 September 2002, a separate experiment was conducted to determine the spike recovery of fluorinated acids from bacterial culture sample matrix. Each of the sample bottles was filled with 30 mL of bacterial growth medium plus the bacterial inoculum that had been
prepared the day before {Section 3.1.6). For day 2 samples, the bottles were crimped with pre-cleaned aluminum foil and PTFE/silicone septa and were kept shaken at
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DuPont EMSE Report No. 15-03
3.2.7 3.2.7.1
3.2.7.2
3.2.7.3 3.3 3.3.1 3.3.1.1
3.3.1.2
-250 RPM at room temperature to allow the bacteria to grow. For day 0 samples, 3 bottles
were spiked with fluorinated acid mix solution (made from individual stock solution in ethanol) to a final concentration of 200 ug/L for each acid. The four acids used are: 1)2perfluorooctyl ethanoic acid (2-PFOEA; CAS# 27854-31-5, DuPont,); 2) 2H-hexadecafluoro2-decenoic acid (2H-HDF-2-DA; CAS# 161094-76-4, DuPont,); 3) perfluorooctanoic acid (PFOA; CAS# 335-67-1,97%, Oakwood Products); and 4) perfluorohexanoic acid (PFHA; CAS # 307-24-4, +98%, TCI America). Another 3 bottles were not spiked to serve as sample matrix control. The bottles were shaken at 200-300 RPM for approximately 30 min before sample collection and sample extraction. At day 2 sampling time point (19 September 2002), 3 crimped bottles were spiked with fluorinated acid mix solution (made from individual stock
solution in ethanol) to a final concentration of 200 ug/L for each acid. Another 3 bottles were not spiked to serve as sample matrix control. The bottles were shaken at 200-300 RPM
for approximately 30 min before sample collection and sample extraction.
Test Conditions and Sampling
Sample Incubation The crimped glass serum bottles were incubated with 200-300 RPM of shaking at room temperature in the dark. The room temperature of the test lab was monitored and recorded throughout the course of the study.
Sampling Interval 5 crimped serum bottles from Treatment 1 and 3 bottles from the rest of treatments were sampled for extraction of 8-2 TBA, fluoride, and fluorinated acids at day 0 (19-Jul-2002), day 14 (2-Aug-2002), and day 28 (16-Aug-2002).
Sample Storage Analytical samples were stored at -10 to -20C.
Sample Extraction and Analysis
Sample Collection and Extraction
Sample Collection At days 0,14, and 28, crimped sample bottles were removed from the shaker and the bottles were turned upside down. A total of 10 mL of the test medium from each of the bottles were withdrawn with a 10-mL polypropylene syringe and was injected into a 15 mL
polypropylene tube that contained 100uLof5N sodium hydroxide for fluoride extraction.
Sample Extraction Fluoride extraction: The 15 mL polypropylene tubes containing the 10 mL test medium plus NaOH were incubated at room temperature for 3 - 4 h with 250 - 300 RPM of shaking. Then
83.3 uL of6N HzS04 was added to each of the tubes to neutralize the test medium. The
sample tubes were stored at approximately -20C for fluoride analysis.
8-2 TEA and fluorinated acid extraction: After withdrawing a 10 mL of test medium for
fluoride analysis, 0.34 mLof6N H2SC>4 and 30 mL of chilled MTBE were injected into the
sample bottles. After MTBE and H2S04 were injected, the sample bottles were shaken (250 - 300 RPM) at room temperature for approximately 2 h. After settling the MTBE phase,
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DuPont EMSE Report No. 15-03
3.3.1.3
the crimped sample bottles were decapped and the MTBE phase from each of the sample bottles was transferred to 50 mL polypropylene centrifuge tubes with a glass transfer pipette. The MTBE phase was centrifuged at approximately 2000 RPM for 10 min. A 20 mL aliquot of the MTBE phase from each of the centrifuge tubes was transferred with a glass pipette to a 20 mL glass scintillation vial with a foil-lined cap and the scintillation vials were stored at -- 20C. From each of the glass scintillation vials, 2 mL aliquot of the MTBE phase was transferred with a glass pipette to a GC vial and was sealed with aluminum-lined crimp cap for GC/MS quantification of 8-2 TBA. From each of the glass scintillation vials, 6 mL aliquot of the MTBE phase was sequentially dried in a GC vial under N2 and was redissolved in 1.5 mL ofmethanol for fluorinated acid analysis.
Temperature Measurements
The temperature of the test system was monitored and recorded throughout the course of the
study.
3.3.2 3.3.2.1
Analytical Methods for Test Substance and Products
Analysis of Test Substance
8-2 TBA Analysis:
Analytical standards:
The 1H,1H, 2H, 2H-perfluorodecan-l-ol (8-2 TBA, CAS# 678-39-7, 97.6%, Oakwood Products, West Columbia, SC) was used as the analytical standard. The 1H, 1H, 2H, 2H-perfluoro-9-methyldecan-l-ol (C-l 1 Iso; CAS# 31200-98-3,98%, Oakwood Products,) was used as an internal standard for day 0 samples and the ID, ID, 2D, 2D, 3-13Cheptadecafluoro decanol (M+5) (D-8-2 TBA, DuPont,) was used as the internal standard for day 14 and day 28 sample analysis. Stock solutions (1000 mg/L) of the analytical standard and the internal standards were prepared in methanol and refrigerated. The calibration standards were freshly prepared for each calibration in MTBE by dilution of the freshly made 50-mg/L stocks in methanol. Typically, the calibration standards were made in the range of 25-1000 ug/L of 8-2 TBA. Constant level of internal standard was used: approximately 300 ug/L of C-l 1 Iso for day 0 samples and D-8-2 TBA for day 14 and day 28 samples. For day 0 samples, the calibration curves were constructed using the ratio of the peak area for ion m/z 95 (8-2 TBA) and peak area for ion m/z 95 (C-l 1 Iso) and the ratio of the concentrations of 8-2 TBA and internal standard. An example of a calibration curve was given in Figure A-2 for quantification of samples TA50-1 to TA 50-26. A chromatograph of sample separation (Sample TA50-3) was given in Fugure A-3. For day 14 and day 28 samples, the calibration curves were constructed using the ratio of the peak area for ion m/z 31 (8-2 TBA) and peak area for ion m/z 33 (D-8-2 TBA) and the ratio of the concentrations of 8-2 TBA and the internal standard. An example of a calibration curve was given in Figure A-4 for quantification of samples TA51 -1 to TA 51 -17 and TA52-1 to TA 52-17. A chromatograph of sample separation (Sample TA52-3) was given in Fugure A-5.
Quantification of 8-2 TBA:
A 0.5 mL aliquot of the MTBE phase from the GC vials (Section 3.3.1.2) was placed in a glass GC vial (1.7 mL volume), 3 - 6 uL of 50 ug/mL of D-8-2 TBA internal standard was added to the vial using a GC syringe, the vial was capped and subjected to analysis. Each sample was analyzed twice by a GC/MS instrument according to the following conditions:
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DuPont EMSE Report No. 15-03
GC7MS system:
HP 6890 Plus GC (Agilent), HP 5973 Mass Selective Detector (Agilent), MPS2-MultiPurposeSampler (Gerstal)
Column: Temp. ramp:
Initial:
DB-5MS, 30 m x 0.25 mm, 1 u,m film (Agilent) 80C for 2 min 200C/mmtol200C 50C/min to 3000C and hold for 3 min
Flow rate: Split:
1.0 mL/min; He; constant flow mode
5:1
Inlet temp.: Injection volume:
MSD transfer line temp.:
lonization:
SIM ions monitored:
250C
2uL
280C
El, 70 eV m/z: 31, 95, 131; dwell time: 50 ms for each ion (day 0 samples)
m/z: 31,33,95,98; dwell time: 25 ms for each ion (days 14 and 28 samples)
Retention time:
8-2 Telomer B Alcohol (C8-2A): Internal standard (D-8-2 TBA): Internal Standard (C-l 1 Iso)
4.97 min 4.93 - 4.95 min 5.42 min
Fluorinated acid Analysis:
Analytical standards:
The perfluorohexanoic acid (PFHA; CAS # 307-24-4, +98%, TCI America), perfluorooctanoic acid (PFOA; CAS# 335-67-1, 97%, Oakwood Products), 2Hhexadecafluoro-2-decenoic acid (2H-HDF-2-DA; CAS# 161094-76-4, DuPont), and 2perfluorooctyl ethanoic acid (2-PFOEA; CAS# 27854-31-5, DuPont) were used as standards for analysis offluorinated acids in test samples. The analytical standard stock solutions for each of the above acids were prepared at approx. 200 u,g/mL concentration by dissolving appropriate amount of the acids in methanol. A single, mixed analytical stock solution at approx. 200 ug/L for each acid was prepared by dilution of each of the above primary stock solutions with methanol in a single volumetric flask. An aliquot of the mixed acid stock solution (~200 u.g/L) and an aliquot of a negative control sample matrix (Treatment 5) were diluted together in a single vial to produce approx. 30 ug/L concentration of each acid in lOx diluted sample matrix in methanol. A separate 30 ug/L solution was prepared with a day 0 negative control (Sample TA 50-15) and a day 28 negative control (Sample TA 52-15). These two solutions were designated as 30 ug/L standards and a pure methanol was designated as a 0 ug/L standard. For fluorinated acid spike recovery experiment (Section 3.2.6), a calibration standard curve was constructed in the range of 10 - 50 u.g/L for quantification of individual fluorinated acid in the acid-spiked samples.
EMSER15-03/4842
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DuPont EMSE Report No. 15-03
Sample Analysis:
Aliquots of all samples were diluted lOx with methanol before the analysis. In addition, aliquots of all samples were transferred to HPLC vials for direct analysis without dilution. All lOx diluted and all undiluted samples were analyzed by liquid chromatography-tandem mass spectrometry (LC/MS/MS). A set of standards (see above) was run at the beginning and at the end of the analysis sequence. Quantitation was done using a single two-point calibration curve for each acid constructed using standards from the beginning and the end of the
analysis sequence. For maximal accuracy of results, the results for undiluted samples for PFHA, PFOA, and 2-PFOEA were considered final. For 2H-HDF-2-DA, the results from lOx diluted samples were considered final. This was done to ensure that the peak area data values ofanalytes in samples were as close as possible to those of 30 ug/L standards. For fluorinated acid spike recovery experiment (Section 3.2.6), a calibration standard curve was constructed in the range of 10 - 50 ug/L for quantification of individual fluorinated acid in the acid-spiked samples. Chromatographs of samples TA52-3 and TA52-6,, 30 ng/L of standard acid mix made in sample matrix TA50-15, sample matrix TA52-16, and a methanol solvent blank were given in Figure A-6. Each sample was analyzed twice according to the
following conditions:
HPLC instrument:
Waters 2795 HPLC
MS instrument: HPLC Column:
Micromass Quattro Micro
Phenomenex Luna C18 (2), 20 mm x 2.0 mm, 3 urn particle size
Mobile Phase: Mobile Phase Gradient:
A: 2 mM ammonium acetate in deionized water (18.2M2cm)
C: methanol
purge solvent: deionized water (18.2 MSl cm)
needle wash solvent: isopropanol
Time (min)
Flow Rate
%A
%C
(mL/min)
0
90
10
0.3
0.5
90
10
0.3
1.5
0
100
0.3
4.5
0
100
0.3
4.6
90
10
0.4
6.5
90
10
0.3
Flow Direction Switching:
0 to 1.0 min - flow to waste
to 4.5 min - flow to MS
Column Temperature:
4.5 to 6.5 min 35C
flow to waste
Injection Volume:
10u,L
lonization mode: Capillary voltage:
electrospray ionization in negative mode
3.50 kV
EMSER15-03/4842
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DuPontEMSE Report No. 15-03
Ion source temperature: Desolvation temperature: Desolvation Gas Flow: Cone Gas Flow: Quadrupole Resolution:
Collision Gas, Pressure: Data acquisition mode:
PFHA PFOA 2H-HDF-2-DA 2-PFOEA
140C
350C
N2,500 War
N2, 100 1/hr
Ql - low and high mass resolution 10
Q2 - low and high mass resolution 15 argon, 3.5 x 10'3 mbar
multiple reaction monitoring (0-4.5 min), inter-channel delay 0.05 sec
Reaction
Dwell Time (sec)
Cone Voltage (V)
Collision
Energy (eV)
313 > 269
0.1
15
15
413 > 369
0.1
15
15
457 > 393
0.1
15
15
477 > 393
0.1
20
20
Fluoride Analysis:
Analytical standard:
Certified standard of 100 mg/L offluoride in water (Thermo Orion ) was used for standard calibration. The calibration standards normally were made in the range of 5 - 100 ug/L by dilution of the 100 mg/L offluoride standard with TISABII (total ionic strength adjustment buffer II; Thermo Orion) and deionized water from Bamstead E-Pure system (Megohm-cm = 16 - 18). Half strength TISABII (one part of TISABII plus one part of deionized water) was used for the dilution. A 10 mL aliquot of each of the standard solution was used for fluoride analysis to construct a standard curve for quantification offluoride in samples.
Quantification of Fluoride:
The 10 mL test medium that was treated with NaOH and HzS04 (Section 3.3.1.2) from each of the 15 mL polypropylene tubes was thawed at room temperature and was centrifiiged. Five milliliter from each of the tubes was transferred to a 50 mL polypropylene tube that contained 5 mL of TISABII solution. After mixing, the medium was analyzed for fluoride using a 710 A Plus pH/ISE meter (Thermo Orion, serial # 066814) and a lonplus fluoride selective electrode (Thermo Orion, model 96-09, lot # GX1). After filling the reference chamber with reference electrode filling solution (Thermo Orion), the electrode was inserted into each of the sample medium and fluoride standard solution and the conductivity in millivolts was recorded after 5 min of incubation. Each sample was measured 1 - 2 times. A standard curve was generated by plotting'the standard fluoride concentration in LOG scale versus millivolts (Figure A-l) for quantification offluoride.
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4.0
DuPont EMSE Report No. 15-03
RESULTS AND DISCUSSION
4.1 Under the test conditions, 8-2 TBA was rapidly transformed (Figure 1 and Table A-l).
Spike recovery of 8-2 TBA from the test medium averaged 123 8 % at day 0,120 6.0% at day 14, and 144 2% at day 28 (Table A-2), indicating that MTBE extraction method obtained a good recovery of 8-2 TBA from the test medium.
Spike recovery of fluorinated acids for day 0 samples was moderate, ranged 62-76% (Table B-l, B-2, B-3, and B-4). Spike recovery of2-PFOEA and 2H-HDF-2-DA
was poor for day 2 samples (Section 3.2.6, full-grown bacterial culture), averaged about 36% and 34%, respectively; spike recovery ofPFOA and PFHA was moderate,
averaged about 81% and 66%, respectively (Table B-l, B-2, B-3, and B-4). This
indicated that full grown bacterial culture matrix may cause significant underestimation of2-PFOEA and 2H-HDF-2-DA in day 14 and day 28 samples as well.
At day 14, >70% of 8-2 TBA has been biotransformed in test vessels ( Treatment 1) compared with abiotic control vessels (Treatment 2).
At day 28, no 8-2 TBA was detected in test vessels. The loss of parent chemical was
due to a combination ofbiotransformation and abiotic removal.
In the abiotic controls, the concentration of 8-2 TBA decreased continuously. The loss is possibly caused by volatilization during the incubation or by incomplete extraction due to adsorption to the glass walls of the test vessels and/or the sludge
inoculum.
The 8-2 TBA that adsorbed to the walls of the test vessels during the coating was fully accessible for metabolism, with more than 90% ofbiotransformation at day 14 and 99% at day 28 (Table A-l).
4.2 Under the test conditions, significant defluorination occurred during the test, suggesting
that the adapted microorganisms were able to metabolize 8-2 TBA to fluorinated acids
and other metabolites.
The fluoride concentration in test vessels increased from ~10 ug/L at day 0 to 64 ng/L at day 14, and 70 ug/L at day 28, while there was no increase for the abiotic controls (Table A-3).
4.3 Four fluorinated acid metabolites (biotransformation products) have been identified from the test system and their mass balance contributions at day 28 are roughly estimated
based in Table 1 and Table A-l:
The F(CF2)?CF=CHCOOH (2H-HDF-2-DA) is the most abundant metabolite and accounted for at least 10% of total mass present.
F(CF2)gCH2COOH (2-PFOEA) is the second abundant metabolite, accounted for ~2% of total mass present.
F(CF2)7COOH (PFOA) accounted for <2% of total mass present.
F(CF2)5COOH (PFHA) accounted for -0.4% of total mass present.
The formation of PFHA is not due to impurity of the test chemical, since 6-2 Telomer B Alcohol [F(CF2)6CH2CH20H, CAS# 647-42-7], which could lead to PFHA formation, was not detected in the test chemical (Figure A-7). The concentration of
EMSER15-03/4842
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5.0 6.0
DuPontEMSE Report No. 15-03
PFHA increased significantly from day 0 to day 28 in test vessels, while only background level of PFHA was present in the abiotic controls during the test. Defluorination ofPFOA may lead to the formation of PFHA during the test. 4.4 Based on the metabolites identified, the following is a potential pathway for 8-2 TBA biotransformation (a simplified pathway which does not include all potential
biotransfonnation products): F(CF2)8CH2CH20H
F(CF2)8CHzCOOH
F(CFz)7CF=CHCOOH + F-
F(CFz)7COOH +F-
F(CF2)5COOH + 4 F-
A notable feature of this pathway is that PFOA may be defluorinated (metabolized) to form PFHA.
CONCLUSIONS
-WC. -jStON?
Under the test conditions, 8-2 TBA is being rapidly transformed to fluorinated acids and other unidentified transformation products. Although PFOA is one of the identified metabolites, it accounted for <2% of mass balance. PFOA apparently mayAe farther metabolized to form PFHA and may not be an ultimate (stable) metabolite under the test
conditions.
REFERENCE
6.1 OECD Guideline for Testing of Chemicals, 302B: Zahn-Wellens/EMPA Test (1992); 302C: Inherent Biodegradability: Modified MITI Test (II) (1981).
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DuPont EMSE Report No. 15-03
FIGURE 1
8-2 TELOMER B ALCOHOL (8-2 TBA) CONCENTRATION DURING THE 28-DAY
TEST*
5
10
15
20
Days after the initiation
* The test was initiated on 19 July 2002 and finished on 16 August 2002. The graph is
derived from the original data of Table A-l.
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DuPont EMSE Report No. 15-03
FIGURE 2 FLUORIDE CONCENTRATION DURING THE 28-DAY TEST*
Adapted bacterial culture + 8-2 TBA Killed bacterial culture + 2 mM NaCN + 8-2 TBA
80
U)
^
fl) 40
a
*zz
0
J3
U-
20
5
10
15
20
25
30
Days after the initiation
* The test was initiated on 19 July 2002 and finished on 16 August 2002. The graph is derived from the original data of Table A-3.
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DuPontEMSE Report No. 15-03
TABLE 1: ESTIMATED CONCENTRATIONS! OF FLUORINATED ACID METABOLITES AT DAY 0
(19-JUL-2002) AND DAY 28 (16-AUG-2002).
Type of Treatments
Treatment 1 - Adapted bacterial culture in growth medium plus 600 ug/L of 8-2 TBA in coated serum bottle
Treatment 2 - Killed bacterial culture in growth medium plus 2mM KCN and 600 tig/l ot 8-2 TBA in coated serum
bottle
Day 0 Dw!2Q Day 0
Day 28
2-PFOEA ND^I 20 ND
ND
2H-HDF-2-DA pgL
ND
PFOA ND
147
12
ND
ND
ND
ND
PFHA 0.2 4.2 0.05
0.08
* This table is derived from the original data of Table A-4, A-5, A-6, A-7, B-l, B-2, B-3, and B-4.
f Estimated concentration, Ce = Cf/Sr where: Cf= final concentration of individual fluorinated acid metabolites at day 0 or 28 Sr = % Spike recovery of the individual fluorinated acids.
Due to the low spike recovery of 2-PFOEA and 2H-HDF-2-DA and moderate spike recovery of PFOA and PFHA, the % spike recovery value was used for correcting possible underestimation of fluorinated acids in test samples.
^ ND: Not detected above sample matrix background level
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DuPont EMSE Report No. 15-03
TABLE 2: DAILY TEMPERATURE READINGS IN FHE LAB WH!ERE THE TEST WAS CONDUCTED. THE TEMPERATURE WAS RECORDED> BY A CALIB RATED DIQKS0N RECORDER
(MODEL THDx, SERIAL # 0118247 )
Time Day
0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19
20
21 22 23
24 25 26 27 28 Average, n = 20 Standard Deviation
Date
19-Jul-2002 20-Jul-2002 21-Jul-2002 22-Jul-2002 23-Jul-2002 24-Jul-2002 25-Jul-2002 26-Jul-2002 27-Jul-2002 28-Jul-2002 29-Jul-2002 30-Jul-2002 31-Jul-2002 1-Aug-2002 2-Aug-2002 3-Aug-2002 4-Aug-2002 5-Aug-2002 6-Aug-2002 7-Aug-2002 8-Aug-2002 9-Aug-2002 IO-Aug-2002 11-Aug-2002 12-Aug-2002 13-Aug-2002 14-Aug-2002 15-Aug-2002 16-Aug-2002
Temperature C 24.0 23.5 23.5
23.75 24.0 23.75 25.50 23.75 23.5 24.0 24.50 24.0 24.5 24.5 24.0 24.0 23.75 24.25 24.0 23.75 24.0 24.0 23.5 23.75 24.2S 24.2S 24.25 24.5 25.0 24.1 0.5
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____ ________DuPontEMSE Report No. 15-03
APPENDIX A:
EMSER15-03/4842
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DuPont EMSE Report No. 15-03
TABLE A-1. ANALYTICAL RESULTS OF 8-2 TBA C()NCESNTRATION fIT DAY 0 (19-JUL-2002),
DAY 14 (2-AUG-2002), AND DAY 28 ( 16-/kUG-2002)
Type of
Rep
8-2 TBA
8-2TBA
8-2 TBA final
Treatment
Analytical
Analytical
concsntrationt
No
Time
concentration
Average
TA50-1 TA50-2
day
Treatment 1 - Adapted
0
1
bacterial culture in growth
1
medium plus 600 ug/L of 8-
2 TBA in coated serum
o
2
bottle 2
ML-'
637 652 694 693
WL-'
645
694
pgL-' 968
1041
TA50-3
0
3
699
690
1035
3
681
TA50-4
0
4
769
781
1172
4
792
TA50-5
0
5
710
Average Standard Deviation f (n =5)
5
724
TA50-6
Treatment 2-Killed
0
1
757
bacterial culture in growth
1
740
medium plus 2mM KCN and
TA 50-7 600 ug/L of 8-2 TBA in
0
2
801
coated serum bottle
2
793
717
1076
1058 . 75
749 797
1124 1196
;; OWit;
<CN an:
' .-'
TA50-8
0
3
592
599
899
3
606
Average Standard Deviation (n =3)
1073 155
TA50-12 Treatment 4-Adapted
0
1
139
147
221
bacterial culture in Growth medium in coated serum
1
154
TA50-13 bottle
o
2
194
189
284
2
184
TA50-14
0
3
125
124
186
Average Standard Deviation (n = 3)
TA51-1 TA51 -2
Treatments-Adapted bacterial culture in growth
medium plus 600 ug/L of 8-2 TBA in coated serum
bottle
TA51-3
3
14
1
1
14 2
2
14 3
3 ,
123
13.0 14.6 12.6 13.3 83.2 79.4
13.8 13.0 81.3
23050
20.7
19.5
122
TA51-4
14 4
3.65
3.37
5.1
TA51-5
4
3.08
14
5
79.5
75.9
114
5
72.3
Average Standard Deviation (n = 5)
56.3 57.8
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DuPont EMSE Report No. 15-03
TABLE A-1 (CONTINUED)
No TA51 -6 TA51-7 TA51-8
Type of Treatment
Rep Time
day
Treatment 2 - Killed
14 1
bacterial culture in growth
1
medium plus 2mM KCN and 14 2
600 tig/I-of 8-2 TBA in coated serum bottle
2
14
3
3
Average Standard Deviation (n = 3)
8-2 TBA Analytical CIancentratlon
pgL-' 499 502 607 615 521
531
TA51-12 Treatment 4 -Adapted
14 1
bacterial culture in Growth 1 medium in coated serum
TA51-13 bottle
14 2
2
TA51-14
14 3 3
Average Standard Deviation (n = 3)
8.14 4.53 12.5 9.92 7.05 9.03
TA52-1
Treatment 1 - Adapted
28
1
0
bacterial culture in growth medium plus 600 ug/L of
1
0
TA52-2
8-2 TEA in coated serum
28 2
0
bottle
2
0
TA52-3
28 3
0
3
0
TA52-4
28 4
0
4
0
TA52-5
28 5
0
5
0
Average Standard Deviation (n =5)
TA52-6
Treatment 2 - Kilted
28 1
388
bacterial culture in growth
1
388
TA52-7
medium plus 2mM KCN and 28 2
321
600 ug/L of 8-2 TBA in
2
322
TA52-8
coated serum bottle
28 3
500
3
523
Average Standard Deviation (n =5)
S-2 TBA Analytical Average
ML-'
501
8-2 TBA final concentrationf
WL-'
752
611
917
526
789
81987
6.34 11.2
9.51 16.8
8.04
0
12.1
12.8 3.7
0
0
0
0
0
0
0
0
0
0
388
582
322
483
512
768
611 145
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DuPont EMSE Report No. 15-03
TABLE A-1 (CONTINUED)
Type of Treatment No
TA52-12 TA52-13 TA52-14
Treatment 4 - Adapted bacterial culture in Growth medium in coated serum bottle
Average Standard Deviation
Rep
Time day 28 1
1 28 2
2 28 3
3
8-2 TBA Analytical concentration
ML-'
0
0
6.36 3.96 0.65 1.37
8-2 TBA Analytical Average
WL-'
6.34
8-2 TBA final concentration}:
WL''
0
5.16
7.7
1.01
1.5
3.1 4.1
t Standard Deviation was calculated using the Final concentration of 8-2 TBA. f Final concentration of 8-2 TBA, Cf = Ca x (Vi^iBE/Vt,) where:
Ca= 8-2 TBA analytical average value, VMTBE = 30 tnL (MTBE used to extract the test medium), V( = 20 mL (Test medium used fro extraction).
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DuPont EMSE Report No. 15-03
TABLE A-2. ANALYTICAL RESULTS OF SPIKE RECOVERY OF 8-2 TBA FROM THE SAMPLE
MATRIX (TREATMENT 3, ADAPTED BACTERIAL CULTURE PLUS GROWTH MEDIUM IN
COATED GLASS SERUM BOTTLES) AT DAY 0 (19-JUL-2002), DAY 14
(2-AUG-2002), AND DAY 28 (16-AUG-2002)
Time Rep
8-2 TBA
8-2 TBA
Final 8-2 TBA
% of Spike
Analytical
Analytical Concentration-1
Recovery^
No
Ciancentration Average
day
WL-'
WL-'
WL-'
TA50-9
0
1
638
628
942
119
1
617
TA50-10
0
2
624
626
939
118
2
627
TA50-11
0
3
678
683
1025
133
3
688
Average Standard Deviation
123 8
TA51-9
14
1
459
460
1
461
TA51-10
14
2
502
506
2
509
TA51-11
14
3
502
496
3
489
Average Standard Deviation
690
113
759
124
744
122
120 6
"
TA52-9
28
1
586
568
852
1
549
TA52-10
28
2
572
580
870
2
588
TA52-11
28
3
594
578
867
145 144.0
3
562
Average Standard Deviation
1442
f Final 8-2 TBA concentration, Cf = Ca (VMroE/Vt,) where: Ca = 8-2 TBA analytical average VMTBE = 30 mL (MTBE used to extract the test medium) V( = 20 mL (Test medium used fro extraction)
% % of spike recovery, R = [(Cf-Cc)/Cy x 100, where: Cf = Final 8-2 TBA concentration in the spiked bottles Cc = Final 8-2 TBA concentration in the coated bottles without adding or spiking with 8-2 TBA stock solution (Treatment 4) Cs = Concentration of 8-2 TBA spiked into the sample bottles (600 ug/L; Treatment 3)
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DuPont EMSE Report No. 15-03
TABLE A-3. ANALYTICAL RESULTS OF FLUORIt)EC ONCENITRATION.^T DAY O (19-JUL-2002),
DAY 14 (2-AUG-2002), AND DAY;28 (16-AuG-2002)
Type of
Rep
Fluoride
Fluoride
Final Fluoride
Treatment
Analytical
Analytical
concentration}
No
Time
C<incentration
Average
day
WL-'
ML-'
WL''
TA50-1
Treatment 1 - Adapted
0
1
5.3
bacterial culture in growth medium plus 600 ug/L of 8-
1
5.4
TA50-2 2 TBA in coated serum
0
2
4.5
bottle
2
4.8
TA50-3
0
3
4.4
3
4.2
TA50-4
0
4
4.4
4
4.1
TA50-5
0
5
4.1
Average Standard Deviation (n = 5)f
5
5.9
5.4
10.8
4.7
9.4
4.3
8.6
4.3
8.6
5.0
10.0
9.5 0.9
TA50-6 Treatment 2 - Killed
0
1
bacterial culture in growth 1 medium plus 2mM KCN and
TA 50-7 600 ug/L of 8-2 TBA in
0
2
coated serum bottle 2
TA50-8 Average Standard Deviation (n = 3)
0
3
3
TA51 -1
Treatment 1 - Adapted
14
1
bacterial culture in growth 1 medium plus 600 ug/L of 8-
TA51-2 2 TBA in coated serum
14
2
bottle 2
TA51-3
14
3
3
TA51-4
14
4
4
TA51-5 Average Standard Deviation (n = 5)
14
5
5
TA51 -6 Treatment 2 - Killed
14
1
bacterial culture in growth
1
medium plus 2mM KCN and
TA 51 -7 600 ug/L of 8-2 TBA in
14
2
coated serum bottle 2
TA51-8 Average Standard Deviation (n = 3)
14
3
7.3 7.8 7.6
34.4 33.5 31.6 26.8 32.8
6.4 6.3 6.9
7.3 7.8 7.6
34.4 33.5 31.6 26.8 32.8
6.4 6.3 6.9
fMi& /
tW! W:'!-!- r
:
i-i:r5.: 8-& ^b-
?-" ^r-i^ ^nMSt
15.2
15.1 0.5
68.8
67.0
63.2
53.6
65.6
63.6 6.0
12.8
12.6
13.8
13.1 0.6
EMSER15-03/4842
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DuPont EMSE Report No. 15-03
TABLE A-3 (c;ONTINUED)
Type of Treatment No
TA52-1 TA52-2 TA52-3
Treatment 1 - Adapted bacterial culture in growth medium plus 600 ug/L of 82 TBA in coated serum bottle
TA52-4
TA52-5
Average Standard Deviation (n = 5)
Rep
Time day
28
1
1
28
2
2
28
3
3
28
4
4
28
5
5
Fluoride Analytical 1Concentration
WL-'
36.0 37.6 34.3 34.3 34.3 34.0 36.1 37.4 33.5 34.0
TA52-6 Treatment 2-Killed
28
1
6.5
bacterial culture in growth
1
medium plus 2mM KCN and
TA 52-7 600 ug/L of 8-2 TBA in
28
2
5.4
coated serum bottle 2
TA52-8
28
3
5.0
3
Average Standard Deviation (n = 3)
Fluoride Analytical Average
WL-'
36.8 34.3 34.2 36.8 33.7
6.5 5.4 5.0
Final Fluoride concentration:):
WL-1 73.6
68.6
68.4
73.6
67.4 70.3 3.0
13.0 10.8
.tAtf. ,CN an:!
'
10.0
11.3 1.6
t Standard Deviation was calculated using the final fluoride concentration. % Final fluoride concentration, Cf = Cax [(Vi+Vt,)/Vt] where:
Ca^ Fluoride analytical average value, V; = 5 mL (TISABII buffer added to the test medium for fluoride measurement), Vt = 5 mL (Test medium used for fluoride measurement).
EMSER15-03/4842
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DuPont EMSE Report No. 15-03
TABLE A-4.
ANALYTICAL RESULTS OF FLUORINATED ACID METABOLITE 2-PERFLUOROOCTYL
ETHANOIC ACID (2-PFOEA) AT DAY 0 (19-JUL-2002), AND DAY 28 (16-AUG-2002)
Type of
Rep
2-PFOEA
2-PFOEA Final 2-PFOEA
Treatment
Analytical
Analytical concentration!:
No
Time
concentration Average
day
TA50-2 Treatment 1 - Adapted bacterial 0
1
culture in growth medium plus 1 600 (Jg/L of 8-2 TBA in coated
TA50-3 serum bottle
0
2
ML-'
ND ND ND
ML-'
ND
ND
WL-' NDf
ND
2
ND
Average (n =2)
ND
TA50-6 Treatment 2 - Killed bacterial
0
1
ND
culture in growth medium plus 2mM KCN and 600 ug/L of 8-2
1
ND
TA 50-7 TBA in coated serum bottle
0
2
ND
0
2
ND
Average (n=2)
ND
ND
ND
ND
ND
TA52-2 Treatment 1 - Adapted bacterial 28
1
culture in growth medium plus
1
600 pg/L of 8-2 TBA in coated
TA52-3 serum bottle
28
2
2
Average {n =2)
15.4 15.3 22.1 22.6
15.4 22.4
5.8 8.4 7.1
TA52-6 Treatment 2 - Killed bacterial
28
1
ND
culture in growth medium plus 2mM KCN and 600 ug/L of 8-2
1
ND
TA 52-7 TBA in coated serum bottle
28
2
ND
2
ND
Average (n = 2)
ND
ND
ND
ND
ND
f ND: Not detected above sample matrix background level. $ Final 2-PFOEA concentration, Cf = Ca x [CvNrrBE/Vt,)/(Vs/Vni)] where:
Ca= 2-PFOEA analytical average value, VMTBE = 30 mL (MTBE used to extract the test medium), Vt = 20 mL (Test medium used for extraction), Vs = 6 mL (MTBE phase dried for metabolite analysis), Vm = 1.5 mL (Methanol used to redissolve the dried MTBE phase for metabolite analysis).
EMSER15-03/4842
Page 30 of 47
DuPont EMSE Report No. 15-03
TABLE A-5. ANALYTICAL RESULTS OF FLUORINATED ACID METABOLITE 2HHEXADECAFLUORO-2-DECENOIC ACID ( 2H-HDF-2-DA) AT DAY 0 2002), AND DAY 28 (16-AUG-2002)
(19-JUL-
Type of Treatment No
TA50-2 TA50-3
Treatment 1 - Adapted bacterial culture in growth medium plus 600
ug/L of 8-2 TBA in coated serum
bottle
Average (n=2)
Time
Rep
2H-HDF-2-DA Analytical
1soncentration
2H-HDF-2-IDA Analyticsil Average
Final 2H-HDF-2-DA ( ;oncentrationt
day
0
1
1
WL-' ND ND
WL-' ND
ML-' NDf
0
2
ND
ND
ND
2
ND
ND
TA50-6 Treatment 2- Killed bacterial
0
1
ND
culture in growth medium plus 2mM
KCN and 600 ug/L of 8-2 TBA in
1
ND
TA 50-7 coated serum bottle
0
2
ND
0
2
ND
Average (n=2)
ND
ND
ND
ND
ND
TA52-2 Treatment 1 - Adapted bacterial
28
1
117
culture in growth medium plus 600 ug/L of 8-2 TBA in coated serum
1
111
TA52-3 bottle
28
2
156
2
147
Average (n =2)
114
sti; ."<: 42.8
152
57.0
50
TA52-6 Treatment 2 - Killed bacterial
28
1
ND
culture in growth medium plus 2mM KCN and 600 ug/L of 8-2 TBA in
1
ND
TA 52-7 coated serum bottle
28
2
ND
2
ND
Average (n = 2)
ND
ND
ND
ND
ND
ND: Not detected above sample matrix background level Final 2H-HDF-2-DA concentration, Cf = Ca x [(VMTBE/Vt,)/(Vs/Vn)] where:
Ca= 2H-HDF-2-DA analytical average value, VMTBE = 30 mL (MTBE used to extract the test medium), V( = 20 mL (Test medium used for extraction), Vs = 6 mL (MTBE phase dried for the metabolite analysis), Vm = 1.5 mL (Methanol used to redissolve the dried MTBE phase for metabolite analysis).
EMSER15-03/4842
Page 31 of 47
DuPont EMSE Report No. 15-03
TABLE A-6.
ANALYTICAL RESULTS OF FLUORINATED ACID METABOLITE PERFLUOROOCTANOIC
ACID (PFOA) AT DAY 0 (19-JUL-2002), AND DAY 28 (16-AUG-2002)
Type of Treatment No
TA50-2 TA50-3
Treatment 1 - Adapted bacterial culture in growth medium plus 600 ug/L of 8-2 TBA in coated serum bottle
Time day
0
0
Rep
1 1 2 2
PFOA Analytical concentration
WL-' ND
ND
ND
ND
PFOA Analytical Average
ML-'
ND
Final PFOA concentration!:
Wi-' NDf
ND
ND
Average (n=2)
ND
TA50-6 Treatment 2 -Killed bacterial
0
culture in growth medium plus 2mM
KCN and 600 pg/L of 8-2 TBA in
TA 50-7 coated serum bottle
0
Average (n=2)
ND
ND
ND
ND
ND
ND
ND
ND
ND
TA52-2 Treatment 1 - Adapted bacterial
28
culture in growth medium plus 600
ug/L of 8-2 TBA in coated serum
TA52-3 bottle
28
Average (n =2)
27,5 27.5 25.1 25.8
27.5
10.3 wwo-
25.5
9.6
10.0
TA52-6 Treatment 2-Killed bacterial
28
culture in growth medium plus 2mM
KCN and 600 pg/L of 8-2 TBA In
TA52-7 coated serum bottle
28
Average (n = 2)
ND
ND
ND
ND
ND
ND
ND
ND
ND
f ND: Not detected above sample matrix background level. t Final PFOA concentration, Cf = Ca x [(VMTBE/Vt,)/(V/Vni)] where:
Ca^ PFOA analytical average value, VMTBB = 30 mL (MTBE used to extract the test medium), Vt = 20 mL (Test medium used for extraction), Vs = 6 mL (MTBE phase dried for metabolite analysis), Vm = 1.5 mL (Methanol used to redissolve the dried MTBE phase for metabolite analysis).
EMSER15-03/4842
Page 32 of 47
DuPont EMSE Report No. 15-03
TABLE A-7.
ANALYTICAL RESULTS OF FLUORINATED ACID METABOLITE PERFLUOROHEXANOIC
ACID (PFHA) AT DAY 0 (19-JUL-2002), AND DAY 28 (16-AUG-2002)
Type of Treatment No
TA50-2 TA50-3
Treatment 1 - Adapted bacterial culture in growth medium plus 600 ug/L of 8-2 TBA in coated serum
bottle
Time day
0
0
Rep
1 1 2 2
PFHA Analytical concentration
mL-'
0.6
0.4 ND
ND
PFHA Analytical Average
WL-1
0.5
Final PFHA concentration:):
WL-' 0.2f
NO
ND
Average (n=2)
0.1
TA50-6 Treatment 2 -Killed bacterial
0
culture in growth medium plus 2mM
KCN and 600 ug/L of 8-2 TBA in
TA 50-7 coated serum bottle
o
Average (n=2)
0.2 ND 0.09 0.03
0.1 0.06
0.04 0.02 0.03
TA52-2 Treatment 1 - Adapted bacterial
28
1
culture in growth medium plus 600 -
ug/L of 8-2 TBA in coated serum
TA52-3 bottle
28
2
Average (n =2)
4.6 5.0 9.4 10.8
4.8 10.1
1.8 UW w-ic.w.r":w. p;>A <;'
3.8
2.8
TA52-6 Treatment 2 -Killed bacterial
28
culture in growth medium plus 2mM
KCN and 600 ug/L of 8-2 TBA in
TA 52-7 coated serum bottle
28
Average (n = 2)
ND
0.2
0.08
0.4
0.1
0.05
0.02
ND
0.05
f ND: Not detected above sample matrix background level.
$ Final PFHA concentration, Cf = Ca x [(VMTBE/Vt,)/(V./V,n)] where:
Ca = PFHA analytical average value
VMTBE = 30 mL (MTBE used to extract the test medium)
t
V( = 20 mL (Test medium used for extraction)
Vs = 6 mL (MTBE phase dried for metabolite analysis)
Vm = 1.5 mL (Methanol used to redissolve the dried MTBE phase for metabolite analysis).
EMSER15-03/4842
Page 33 of 47
DuPont EMSE Report No. 15-03
TABLE A-8.
COMPONENTS OF BACTERIAL GROWTH MEDIUM USED FOR THE TEST.
KH2P04 NaH2P04*H20
KC1
MgS04*7H20 CaCL2*2H20 NaCI FeS04*7H20 CuS04*5H20 CoCl2*6H20 MnCl2*4H20 Na2Mo02*2H20 CfiH5Na307*2H20
(Sodium citrate dihydrate tribasic)
NiCl2*6H20
ZnCl2 Yeast Extract
Final Concentration 0.70 g/1 0.395g/l 0.5 g/1 0.5 g/1 0.025 g/1 1.0 g/1
0.5mg/L 0.05 mg/L 0.1 mg/L 0.01 mg/L 0.025 mg/L 1 mg/L
0.1 mg/L 0.005 mg/L 2g/L
PH = 7.2
EMSER15-03/4842
Page 34 of 47
DuPontEMSE Report No. 15-03
FIGURE A-1
A FLUORIDE STANDARD CALIBRATION CURVE
F~ Standard Curve (for TA51, 8/2/02)
180
200
Millivolts
EMSER15-03/4842
Page 35 of 47
DuPont EMSE Report No. 15-03
FIGURE A-2 A CALIBRATION CURVE USED FOR 8-2 TBA QUANTIFICATION OF SAMPLES TA 50-1 TO TA 50-26
Response Ratio
C8-Z&
fit; afctp Ktlteio 1.04~c000 Ant - .<7e-00i
Cool! at Wt (r*a} 0.99S> Curve
wird/a?
Calibration curve used for samples TA 50 - 1:26. The concentration of the internal standard: 300 pg/L ofCl 1-iso; the range of concentrations of 8-2 TBA: 25.1- 4020 ug/L.
EMSER15-03/4842
Page 36 of 47
DuPont EMSE Report No. 15-03
FIGURE A-3 A CHROMATOGRAPH OF SAMPLE TA50-3 USED FOR 8-2 TBA ANALYSIS
Abundance
2800 2600 2400 2200 2000 1800 1600 1400 1200 1000
800 600 400 200
Tlme->
4.97
Ion 95.00 (94.70 to 95.70): 08140227.D
5.42
^ ^
j
wf \^f\^-^/
Ak Wj^^'^ JM^^
4.00 4.50 5.00 5.50 6.00 6.50 7.00 7.50 8.00 8.50 9.00 9.50 10.00
Sample TA50-3. Quantification was done using peak area of ion m/z 95; retention time 4.97 min = 8-2 TBA; retention time 5.42 min = Cl 1-iso.
EMSER15-03/4842
Page 37 of 47
DuPont EMSE Report No. 15-03
FIGURE A-4 A CALIBRATION CURVE USED FOR 8-2 TBA QUANTIFICATION OF SAMPLES TA 51-1 TO TA51-17 AND TA 52-1 TO TA52-17
Response .Ratio
CB-2&
lasawt Batio
Heap Ratio S.BSe-OOl * tab * l.SSe-OOS Coet of Bt tK'^!t) 9.999 CtH-w Pits wl(l/a)
Calibration curve used for samples TA 51-1:17 and TA 52-1:17. The concentration of the internal standard: 514 ug/L ofD-8-2 TBA; the range of concentrations of 8-2 TBA: 25.1 -1005 ug/L.
EMSER15-03/4842
Page 38 of 47
DuPont EMSE Report No. 15-03
FIGURE A-5 A CHROMATOGRAPH OF SAMPLE TA 52-3 USED FOR 8-2 TEA ANALYSIS
Abundance
Ion 31.00 (30.70 to 31.70): 09160259.D
12000 10000
8000 6000 4000 2000
0
|Time->
4.0 4.5 5.0 5.5 6.0 6.5 7.0 7.5 8.0 8.5 9.0 9.5 10.0
Abundance
4.93
Ion 33.00 (32.70 to 33.70): 09160259.D
12000 10000
8000 6000 4000 2000
0
n"ime~>
4.0 4.5 5.0 5.5 6.0 6.5 7.0 7.5 8.0 8.5 9.0 9.5 10.0
Sample TA52-3; Ion 31, retention time 4.95 min = 8-2 TBA; Ion 33, RT 4.93 min = D-8-2 TBA (internal standard).
EMSER15-03/4842
Page 3 9 of 47
DuPont EMSE Report No. 15-03
FIGURE A-6 CHROMATOGRAPHS OF SAMPLES TA52-3 AND TA52-6, 30 |JG L'1 OF STANDARD ACID MIX MADE IN SAMPLE MATRIX TA50-15, SAMPLE MATRIX TA52-16, AND A METHANOL SOLVENT BLANK.
TA 52-6 (Abiotic control, Treatment 2)
TA 52-3 (Test sample, Treatment 1)
1D1502VC61 Smoolh(Mn.2}<2) 100-,
I PFHA
3.26 1
35.10
MRMof4channBls,ES313>269
s.9718+002
101502cS8 SmoDthfMn^ia)
^r-l
1
PFHA_
3.25 167.45
1
|
MRMof4 channels .ES313 > 268
2.338e+003
101502W61 Smoolh(Mn,22) 100-1
. nin
MRMtH4channels.ES-
PFOA "]
3.43
144.06 f
413>369 2.023e+003
0-t; . 101502\ic58
^''-j
Smi)Olh(Mn,2ia)
~rf min
MRMof4 channels ,ES-
PFOA "j
3.43 828.02
|
413 > 369 1.110B+004
101502W6I Srnoolh(Mn,2>a)
MRMof4channels.ES- l01502ic58 Snioolh(Mn,22)
3.52
457 > 393
1.07le*oo2 '""'I
MRMof4channels,ES-
2H-HDF-2-DA
1 3.53 | 6121.70
457 > 393 7.970e*004
(''-'(' MRMof4channels,ES-
3.96 477 > 383 1.193E+002
101502wSS Smoolh(Mn^i<2)
^^
."rl'nTOi'i'r'i4fHw|-m^ min
MRMof4 channels,ES-
| 2-PFOEA_ 3.52 1 63.79
477 > 393 8.900e*002
min 0-t l.^ili.lili.lpi i >^l.'^pnll^lr.l.^.u.^u.ll^lJl^l.T^'j'^l<.lii^l.AI^-'AP"P"^l"^"i min
0.50 1.00 1.50 2.00 2.50 3.00 3.50 4.00 4.50
0.50 1.00 1.50 2.00 2.50 3.00 3.50 4.00 4.50
Standard: TA50-15 (Sample matrix. Treatment 5) + 30 ng L'1 acids
PFHA_ 3.24 | 485.33
TA 52-16 (Sample matrix, Treatment-5)
t00i y.-|
PFOA'_]
3.41 996.53
2H-HDF-2-DA_ 3.51
1519.72
100-|
y.
1.13
1.63
100,0.05 "" 1-06
PFOA_ 3.43 |
142.99 j
100-|
%
2-PFOEA_
'
3.51
96.56
'
'
0.50 1.00 1.50 2.00 2.50 3.00 3.50 4.00 4.50
EMSER15-03/4842
0.50 1.00 1.50 2.00 2.50 3.00 3.50 4.00 4.50
Page 40 of 47
DuPont EMSE Report No. 15-03
FIGURE A-6 CHROMATOGRAPHS OF SAMPLES TA52-3 AND TA52-6, 30 |JG L'1 OF STANDARD ACID MIX MADE IN SAMPLE MATRIX TA50-15, SAMPLE MATRIX TA52-16. AND A METHANOL SOLVENT BLANK - CONTINUED FROM PAGE 42.
Methanol solvent blank
1B15B2iieB8 Smoolh(Mn,2Q) tSO-i
PFHA_
| 3.25
23.58
MRMof4channels,ES313>269
3.52SfH102
101502vc68 Smaoth(Mn,2i2) iW-1
1015Q2vc6a Smootl(l>*l^x2) 1A1
MRMl)f4chBliels,ES-
PFOA
413 > 369
S 3 43 I
125.73
1.731e+003
3.05 MRMof4cliannels^S-
EMSER15-03/4842
Page 41 of 47
DuPont EMSE Report No. 15-03
FIGURE A-7 A GC/MS CHROMATOGRAPH OF MATERIAL CHARACTERIZATION OF 8-2 TBA TEST SUBSTANCE USED IN THIS STUDY
'1 9wstats
?SOOS90
361166011
^
asoao
StWW
"
WWW
itBOian
iaeoe
t.'3 & -t-
Mf-
,'<Mi'
1
'*& ?i4it.to
,
""" " "N"1-"--
' i
.
,,
,.--.
^
t
-1
;
;
*
^^ u "
^- 8-2 TBA (99.2%) '
Z;B
l ^ C7FisCF=CHCH20H ( 0.8%)
: t*:(a
, at:fla , . ..'.....aii^
BC'IH. ,,,,
4.^
EMSER15-03/4842
Page 42 of 47
APPENDIX B:
DuPont EMSE Report No. 15-03
EMSER15-03/4842
Page 43 of 47
DuPont EMSE Report No. 15-03
TABLE B-1.
ANALYTICAL RESULTS OF SPIKE RECOVERY OF 2-PERFLUOROOCTYL ETHANOIC
ACID (2-PFOEA) AT DAY 0 (17-SEP-2002), AND DAY 2 (19-SSP-t002).
No TA86-4 TA86-5 TA86-6
Tinm day
0
0
0
Rep
1 1 2 2 3 3
2i-PFOEA A inalytlcal coricentration
ML-'
113
95.7 99.0
98.7 94.7 108
2-PFOEA Analytical Average
ML-'
104
98.9
101
Final 2-PFC>EA
concentrati "*
ML-'
156
148
152
% of Spike Recovery
78 74 76
Average Standard Deviation"^ (n = 3)
.. 76 2
TA87-4
2
1
1
TA87-5
2
2
2
TA87-6
2
3
3
Average Standard Deviation (n = 3)
45.0 43.5 44.8 44.0 54.6 57.6
44.3 44.4 56.1
66.5
33
66.6
33
84.2
42
<-.-. i awa.'36 i 5
f Standard Deviation was calculated using the final 2-PFOEA concentration. % Final 2-PFOEA concentration, Cf = Ca x CvMi-BE/Vt,) where:
Ca= 2-PFOEA analytical average value, VMTBE = 30 mL (MTBE used to extract the test medium), Vt = 20 mL (Test medium used for extraction). % of spike recovery, R = (Cf/Cs) x 100, where: Cf = Final 2-PFOEA concentration in the spiked bottles, Cs = Concentration of 2-PFOEA spiked into the sample bottles (200 u.g/L).
EMSER15-03/4842
Page 44 of 47
DuPont EMSE Report No. 15-03
TABLE B-2.
ANALYTICAL RESULTS OF SPIKE RECOVERY OF 2H-HEXADECAFLUORO-2-
DECENOIC ACID ( 2H-HDF-2-DA) AT DAY 0 (17-SEP-2002), AND DAY 2 (19-SEP-2002)
2H-HDF-DA
2H-HDF-DA Final 2H-HDF-DA % of Spike
Analytical
Analytical
concentrationt
Recovery
No
Time
Rep
concentration
Average
day
WL-'
P9L-'
ML-'
TA86-4
0
1
91.2
90.4
136
68
1
89.5
TA86-5
0
2
88.0
88.1
132
66
2
88.1
TA86-6
0
3
93.5
94.3
141
71
3
95.0
Average Standard Deviation'}' (n = 3)
'aBii'ttteSBsSMattOR'i
TA87-4 TA87-5 TA 87-6 Average Standard Deviation (n = 3)
38.1 41.1 41.3 40.6 54.6 55.5
39.6 41.0 55.1
59.4 61.5 82.7
30
31 41 w;tSMf.fc6t""n
f Standard Deviation was calculated using the final 2H-HDF-2-DA concentration. % Final 2H-HDF-2-DA concentration, Cf = Ca x (VMTBE/VI,) where:
Ca= 2H-HDF-2-DA analytical average value, VMTBE = 30 mL (MTBE used to extract the test medium), V( = 20 mL (Test medium used for extraction). % of spike recovery, R = (Cf/Cs) x 100, where: Cf= Final 2H-HDF-2-DA concentration in the spiked bottles, Cs = Concentration of 2H-HDF-2-DA spiked into the sample bottles (200 ug/L).
EMSER15-03/4842
Page 45 of 47
DuPont EMSE Report No. 15-03
TABLE B-3.
ANALYTICAL RESULTS OF SPIKE RECOVERY OF PERFLUOROOCTAN01C ACID
(PFOA) AT DAY 0 (17-SEP-2002), AND DAY 2 (19-SEP-2002)
No TA86-4 TA86-5
Timia day
0
0
PFOA
PFOA
Final PFOA
% of Spike
Ainalytical
Analytical
concentration:]'
Recovery
Rep
coricentration
Average
ML-'
ML-'
pgL-'
1
88.2
88.5
133
67
1
88.7
2
89.4
90
135
68
2
90.6
TA86-6
0
3
94.3
94.8
142
71
3
95.3
Average Standard Deviation'1' (n = 3)
692
TA87-4
2
1
1
TA87-5
2
2
2
TA 87-6
2
3
3
Average Standard Deviation (n =3)
98.0 102 95.9 103 122 124
100 99.5 123
150
75
149
75
185
93
81 10 "oi ',
f Standard Deviation was calculated using the final 2-PFOA concentration. 3: Final PFOA concentration, Cf = Ca x (VM-TBE/VI,) where:
Ca= PFOA analytical average value, VMTBE = 30 mL (MTBE used to extract the test medium), V( = 20 mL (Test medium used for extraction). % of spike recovery, R = (Cf/Cs) x 100, where: Cf= Final PFOA concentration in the spiked bottles, Cs = Concentration of PFOA spiked into the sample bottles (200 u.g/L).
EMSER15-03/4842
Page 46 of 47
DuPont EMSE Report No. 15-03
TABLE B-4.
ANALYTICAL RESULTS OF SPIKE RECOVERY OF PERFLUOROHEXAN01C ACID
(PFHA) AT DAY 0 (17-SEP-2002), AND DAY 2 (19-SEP-2002)
No TA86-4 TA86-5 TA86-6
Timie day
0
0
0
Rep
1 1 2 2 3 3
PFHA A.nalyticai coricentration
ML-'
78.8 79.5 82.1
80.7 82.7 89.7
PFHA Analytical Average
WL-' 79.2
81.4
86.2
Final PFHA concentrationt
WL-'
119
% of Spike Recovery
60
122
61
129
65
Average Standard Deviation'!" (n = 3)
623
TA87-4
2
1
1
TA87-5
2
2
2
TA 87-6
2
3
3
Average Standard Deviation (n = 3)
80.4 79.3 84.8 84.7 100 97.4
79.9 84.8 98.7
120
60
127
64
148
74
66 7
t Standard Deviation was calculated using the final 2-PFHA concentration. f Final PFHA concentration, Cf = Ca x (VMTBE/V(,) where:
Ca= PFHA analytical average value, VMTBE = 30 mL (MTBE used to extract the test medium), V( = 20 mL (Test medium used for extraction). % of spike recovery, R = (Cf/Cs) x 100, where: Cf= Final PFHA concentration in the spiked bottles, Cs = Concentration of PFHA spiked into the sample bottles (200 |ig/L).
EMSER15-03/4842
Page 47 of 47