Document aBbX8Z33Zk3OyvnMDYx7rYNvb
/WU06-OS33
BIODEGRADATION
TEST SUBSTANCE
Identity: Perfluorooctylsulfonate, didecyldimethylammonium salt; may also be referred to as Fluoroalkyl ammonium derivative. [1Decaminium, N-decyl-N,N-dimethyl-, salt with 1,1,2,2,3,3,4,4,5,5,6,6,7,7,8,8,8-heptadecafluoro-loctanesulfonic acid (1:1), CAS # 251099-16-8]
Remarks: The 3M production lot number was Lot 1. The test sample is L-14394 referred to by the test laboratory as P3025. The sample was labeled F-11615, Lot 1. The test sample is a mixture of the test substance in water (approximately 30-40% test substance, 60-70% water, and 0-5% of residual perfluorochemicals). All values reported relate to this mixture. The test sample appears to be a 2-phase dispersion (clear liquid with opaque solid) which rapidly separates after agitation. No calculations were made to adjust for the actual concentration of the test substance in
the test sample.
METHOD:
Method: OECD Method 301D Type: Aerobic GLP: No Year completed: 1997 Contact time: 28 days Inoculum: Polyseed- NX (with nitrification inhibitor), lot A306, Polybac Corp, Bethlehem, PA
RESULTS
COD: 125,000 mg O2 / kg chemical
CBOD
Exposure period, Day
5 10 20 28
First Replicate CBOD
Mean Value (mg/kg) <40,000 <40,000 <40,000 55,039
Second Replicate CBOD
Mean Value (mg/kg) <40,000 <40,000 <40,000 <40,000
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Remarks: Values reported are for the test sample. No calculations were made to adjust for the concentration of the test substance in the test sample. CONCLUSIONS This testing indicated that some portion of the test sample biodegraded in aerobic environments capable of supporting biodegradation. This study cannot rule out the possibility that conditions could be found that would allow for biodegradation of the fluorochemical component, nor could it exclude the possibility that a microorganism could eventually be enriched that could metabolically alter this chemical.
Submitter: 3M Company, Environmental Laboratory, P.O. Box 33331, St. Paul, Minnesota, 55133 DATA QUALITY Reliability: Klimisch ranking 2. This study lacks sufficient characterization of the test substance purity and analytical measurement of test concentrations. Because a mixture was tested, the testing cannot conclude what portions of the test sample were responsible for the apparent biodegradation values. REFERENCES This study was conducted by the 3M Company, Environmental Laboratory, St Paul, MN, Lab Request number P3025. OTHER Last changed: 5/24/00
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3M ENVIRONMENTAL LABORATORY
DETERMINATION OF THE 28-DAY CARBONACEOUS BIOCHEMCIAL OXYGEN DEMAND (CBOD) FOR P3025
OECD Closed Bottle Test, #301D (Modified)
STUDY COMPLETED: March 28, 1997 FINAL REPORT COMPLETED: May 20,1997
Env. Lab Request Number P3025
Prepared by: Name: Title:
Laboratory:
Address:
Susan A. Beach Advanced Environmental Biologist 3M Environmental Laboratory Building 2-3E-09 935 Bush Avenue St Paul, MN 55144
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28-Day CBOD Page 1
May 20, 1997
SUMMABY
In this study the aerobic, aquatic ready biodegradability of P3025 in general accordance with the "Closed Bottle Test", OECD Method No. 301 D was determined. The test substance was found to be not readily biodegradable
with removal values of <32% and 44% (duplicate) obtained after 28 days.
OBJECTIVE
The purpose of this study was to evaluate the ready biodegradability of P3025 after 5,10, 20, and 28 days of exposure using a modified form of OECD Method 301 D.
MATERIALS AND METHODS
Test Substance:
P3025, date 10/7/96, Lot 1
Appearance Aqueous Solubility
Two-phase dispersion (clear liquid with opaque solid) Apparently not completely soluble in water at tested concentrations.
Available Physicochemical Properties
Boiling Point: Vapor Pressure: Vapor Density: Evaporation Rate: Solubility in water: Specific Gravity: Percent Volatile: pH:
100C ca. 18 mm Hg @ 20C <1 <1 Insoluble ca. 1.2 60 - 70% 6-8
Date Received
10/16/96
Storage
In the dark at ambient room temperature (22 2C)
Test Solutions
Test solutions were prepared as Water-Accommodated Fractions (WAFs). Four stock solutions, each in duplicate, of approximately 6, 12, 25, and 50 mg/L were prepared in aerated mineral nutrient media. Each was capped and allowed to mix overnight, in the dark, at ambient room temperature. Test substance was apparently not completely miscible with water. A few white particulates were observed in each stock solution after mixing. The clear liquid portion was withdrawn for biodegradation testing.
Reported values
The reported values were based on nominal concentrations in the test media at the beginning of the toxicity test.
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Test Organisms: Type Source Lot number Preparation
Polyseed-NX (with nitrification inhibitor)
Polybac Corp., Bethlehem, PA
A306
Contents of one Polyseed-NX capsule placed into 500 mL aerated mineral media. Solution stirred for sixty minutes on magnetic mixer. Solution kept stirring while aliquots withdrawn to inoculate test bottles.
Test Conditions: Photoperiod Test Vessels
Test Volume Loading
No. Replicates
Mineral Medium
24-hours dark
300 mL clear glass Wheaton BOD bottles with ground glass stoppers sealed with a water seal and capped.
300 mL
5 mL reconstituted inoculum added to each bottle except for media blanks which received none
2 each for medium blank, seeded blank, reference standard and each test concentration. Only one replicate for toxicity check.
Prepared with Hach BOD Nutrient Buffer Pillows (catalogue # 14863-98) each dissolved in 19 liters Millipore Milli-Q water. Glass carboys aerated with laboratory air filtered through a 0.2 pm filter for approximately 2hours. Carboy openings covered with new foam plugs and allowed to stand overnight in the dark at ambient room temperature.
Initial Stock Solution Loadings nominal
First Replicate 6.7 mg/L 12.3 mg/L 26.9 mg/L 51.6 mg/L
Duplicate 5.6 mg/L 10.9 mg/L 24.3 mg/L 54.2 mg/L
Test Bottles
Each test BOD bottle was seeded and filled completely full with solution from the appropriate water-accommodated fraction.
Reference Standard Toxicity Check
Glucose/glutamic acid mixture. Hach BOD standard solution ampules, cat. # 14865-10. Added 1.5 mL of solution to each reference standard BOD bottle.
Added 1.5 mL of Hach glucose/glutamic acid mixture to a seeded BOD bottle containing the test substance P3025 at the highest loading.
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Test Temp., C Stock Solutions pH Exposure Period Measurements
Date Test Initiated Date Test Terminated Procedure
21 - 22C, continuously recorded.
Initial pH values ranged from 6.5 to 6.7.
28-days
Dissolved oxygen at 0, 5,10, 20, and 28 days. Dissolved oxygen meter calibrated by means of Winkler titration of aerated Milli-Q water each day.
2/28/97 3/28/97
The test generally followed the recommendations of the OECD Guidelines for Testing of Chemicals
CALCULATIONS
The reported values are based on nominal stock solution loadings at the beginning of the study. The concentrations tested and the corresponding response data derived from the duplicated test are used to calculate, if possible the mg of carbonaceous biochemical oxygen demand per kg of test substance (BOD). The percent biodegradability is then determined by dividing the CBOD by the Chemical Oxygen Demand (COD) and multiplying by one hundred.
RESULTS
Percent biodegradability values obtained after 5, 10, 20, and 28 days of exposure to P3025 are summarized in Table 1. In duplicated measurements, the percent biodegradability of P3025 was reported as <32% and 44% of chemical oxygen demand.
ACCEPTABILITY CRITERIA
This biodegradation test meets quality criteria provided in test guidelines:
1) The glucose-glutamic acid reference standard 5-day C-BOD results were within the range normally seen in this laboratory. See Figure 1.
2) The oxygen depletion of the medium blanks was < 0.5 mg/L after 5-days.
3) The oxygen depletion of the medium blanks was < 1.5 after 28-days.
4) The C-BOD result for the toxicity check (highest tested concentration plus glucose-glutamic acid) was greater than the value found for glucose-glutamic acid alone. This indicated the test substance did not inhibit the microorganisms.
5) Only those data points where the corrected dissolved oxygen drop was > 2.0 mg/L and the final dissolved oxygen concentration in the bottle was > 0.5 mg/L were used to calculate C-BOD.
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28-Day CBOD Page 4 May 20, 1997 This test was conducted by Trudy K. Stiefenhoefer as requested by Pam Wolf of 3M Specialty Chemicals Division.
REFERENCES APHA, AWWA, WEF. 1995. Standard Methods for the Examination of Water and Wastewater. Method 5210 B, 5-Day BOD Test. APHA, AWWA, WEF. 1995. Standard Methods for the Examination of Water and Wastewater. Method 4500-0 C. Oxygen (Dissolved), Azide Modification. OECD. 1993. 301 D Closed Bottle Test. Guidelines for Testing of Chemicals. Organisation for Economic Co operation and Development, Paris, France. OECD. 1981. Principles of Good Laboratory Practice, Annex 2, C(81) 30 (Final): 7-28. OECD Guidelines for Testing of Chemicals. Organisation for Economic Cooperation and Development, Paris, France. Polybac. 1997. Polyseed-NX, "The Original" CBOD Seed Inoculum. Polybac Corporation, Bethlehem, PA.
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28-Day CBOD Page 5 May 20, 1997
TABLE 1
SUMMARY OF READY BIODEGRADABILITY OF P3025
ExDosure Period
5-Days Duplicate 10-Days Duplicate
20-Days Duplicate 28-Days Duplicate____________
CBOD, ma/Ka
<40,000 <40,000
<40,000 <40,000
<40,000 <40,000
55,039 <40.000
*COD reported as 125,000 mg/kg
Percent of COD*
<32 <32 <32 <32
<32 <32 44 <32
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mg/kg
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FIGURE 1
CBOD GGA 5-day Reference Standard
Date
PFOS didecyldimethylammonium salt
Synonyms: P3025, L-14394
Physical/Chemlcal Properties Title
None
Laboratory or
Date
Author
Completed
Type
Environmental Fata and Transport
Title
Determination of the 28-day Carbonaceous Biochemical Oxygen Demand (CBOD) for P3025
Laboratory or Author
3M Env. Lab
Completion Date
Type
Robust summary,
5/20/97 final report
Ecotoxlcity Elements
Title
Acute Toxicity of P3025 Developmental Material to Fathead Minnow (Pimphates prom elas) Acute Toxicity of P3025 Developmental Material to Daphnia magna
Growth Inhibition of P3025 Green Alga (Selenastrum capricom utum )
Growth Inhibition of P3025 to Green Alga (Selenastrum cap rico m u tu m )
Inhibitory Effects of P3025 on Microtox Inhibitory Effects of P3025 on Activated Sludge Respiration
Laboratory or Completion
Author
Date
Type
AScI Corporation,
Robust summary,
Duluth, MN
1/2/97 final report
AScI Corporation,
Robust summary,
Duluth, MN
1/10/97 final report
AScI Corporation,
Robust summary,
Duluth, MN
1/29/97 final report
AScI Corporation, Duluth, MN
3M Env. Lab
3M Env. Lab
2/21/97 5/12/97 5/12/97
Robust summary, final report Robust summary, final report Robust summary, final report
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