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EC number: 206-616-8 | CAS number: 358-23-6
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From 05 June 2012 to 22 nov 2012
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-E (Determination of the "Ready" Biodegradability - Closed Bottle Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- 11 april 2011
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- sewage, industrial, adapted
- Details on inoculum:
- - Specification: Effluent from a biologic sewage treatment plant was used. The chosen plant is treating mostly household sewage.
- Source: The effluent was taken from the effluent channel of the sewage treatment plant, Edenkoben.
Date of collection: 19. Jun. 2012, batch no: 20120619.
- Pre-Treatment: The effluent was kept aerobic during transport and storage. Before usage, the effluent was left to settle for one hour. The effluent was aerated for five days at room temperature in order to lower the oxygen consumption of the blanks. 0.5 mL/L test medium were used. - Duration of test (contact time):
- 28 d
- Initial conc.:
- 21.97 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium:
Stock solutions:
Solution A:
Potassium dihydrogenephosphate (KH2PO4): 8.5 g
Di-potassium hydrogenephosphate (K2HPO4): 21.75 g
Sodium di-hydrogenephosphate hydrate (NaH2PO4*H2O): 33.4 g
Ammonia chloride (NH4Cl): 0.5 g
H2O demin. ad: 1000 mL
The pH was adjusted to 7,4 +/- 0.1
Solution B:
Calcium chloride dihydrate (CaCl2*2H2O): 36.4 g
H2O demin. ad: 1000 mL
Solution C
Magnesium sulfate heptahydrate (MgSO4*7H2O): 22.5 g
H2O demin. ad: 1000 mL
Solution D
Iron(III) chloride hexahydrate (FeCl3*6H2O): 0.25 g
Di-sodium-ethylendiamintetraacetate dihydrate (Na2EDTA*2H2O): 0.4 g
H2O demin. ad : 1000 mL
The medium was freshly prepared.
Composition:
Solution A 1 mL
Solution B 1 mL
Solution C 1 mL
Solution D 1 mL
H2O demin. ad: 1000 mL
- Test temperature: 19.8 – 21.5°C
- Suspended solids concentration: 0.5 mL/L
- Continuous darkness: yes
- Other: After preparation, the medium was aerated for 50 hours. Then the medium was stored at room temperature for 20 hours without aeration. The O2-concentration was then determined with 8.63 mg/L at 21°C.
TEST SYSTEM
- Culturing apparatus: 250 mL narrow neck bottles with glass stoppers.
- Number of culture flasks/concentration: 2
- Method used to create aerobic conditions: The effluent was taken from the sewage treatment plant and was aerated for five days in order to lower the oxygen demand of the effluent.
- Measuring equipment: Oximeter 538 wtw (for oxygen)
SAMPLING
- Sampling frequency: For each test series, seven samplings were made (on days 0, 3, 7, 11, 18, 23 and 28). For each sampling, the oxygen content of two vessels of each test series was measured (one vessel on day 0).
CONTROL AND BLANK SYSTEM
- Inoculum blank: 2
- Positive control: 2
- Toxicity control: 2 - Reference substance:
- benzoic acid, sodium salt
- Remarks:
- 3.61 mg/L
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 0
- Sampling time:
- 28 d
- Details on results:
- For the determination of the biological results, the data were evaluated without consideration of nitrification. Because neither test item nor positive control contains nitrogen, the O2-uptake caused by nitrification was not considered for the determination of the degradation.
• The test item Trifluoromethanesulfonic acid must be considered as “not readily biodegradable“.
• The degree of biodegradation was 0 % after 28 days
• A 10-day-window could not be detected. - Results with reference substance:
- The positive control reached the pass level already on day 3.
- Validity criteria fulfilled:
- yes
- Remarks:
- O2-consumption in the controls: =< 1.5 mg/L Lowest measured O2-concentration in the test vessels: >= 0.5 mg/L Difference within replicates: =< 20% Degradation of positive control > 60%: =< 14 days Degradation in the toxicity control on day 14: >= 25%
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- Trifluoromethanesulfonic acid is not readily biodegradable in the closed bottle test.
- Executive summary:
The study was performed in order to evaluate the aerobic ultimate biodegradation potential of Trifluoromethanesulfonic acid in a test for ready biodegradability, according to the OECD 301D guideline and under GLP conditions.
This study used a test item concentration of 21.97 mg/L (corresponding to a theoretical oxygen consumption of 5.86 mg/L).
The solution of the test item in mineral medium was inoculated with a relatively small number of micro-organisms from a mixed population and kept in completely full, closed bottles in the dark at constant temperature.
Degradation was followed by analysis of dissolved oxygen over a 28-day period. The amount of oxygen taken up by the microbial population during biodegradation of the test item, corrected for uptake by the blank inoculum run in parallel, is expressed as a percentage of COD.
There was 0% of degradation of test item after 28 days. The positive control reached the pass level already on day 3.As degradation in the toxicity flask was more than 25 % at the end of the test, the test item can be stated as not toxic towards the inoculum in a concentration of 11.72 mg/L
In these test conditions, Trifluoromethanesulfonic acid was not readily biodegradable.
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- The read-across justification is provided in the attached document
- Reason / purpose for cross-reference:
- read-across source
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 0
- Sampling time:
- 28 d
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- By analogy with its hydrolysis product, trifluoromethanesulfonic anhydride is considered to be not readily biodegradable.
Referenceopen allclose all
Degradation without Consideration of Nitrification in %:
Day |
Positive Control |
Test Item |
Toxicity Control |
||||||
|
1 |
2 |
Mean |
1 |
2 |
Mean |
1 |
2 |
Mean |
3 |
68.5 |
67.5 |
68.0 |
-6.7 |
-6.6 |
-6.6 |
-7.3 |
-7.0 |
-7.2 |
7 |
78.4 |
80.6 |
79.5 |
-1.4 |
-1.0 |
-1.2 |
38.0 |
37.7 |
37.9 |
11 |
82.4 |
82.2 |
82.3 |
-1.1 |
-2.0 |
-1.6 |
36.5 |
36.2 |
36.3 |
18 |
77.7 |
80.7 |
79.2 |
-1.5 |
-2.0 |
-1.7 |
38.8 |
37.0 |
37.9 |
23 |
79.4 |
74.1 |
76.8 |
-7.2 |
-7.3 |
-7.2 |
29.7 |
31.0 |
30.4 |
28 |
83.3 |
81.3 |
82.3 |
-1.7 |
-0.9 |
-1.3 |
35.8 |
36.4 |
36.1 |
Negative degradation values are caused by measurement uncertainties resp. small differences between oxygen decrease in the controls and in the test flasks.
Description of key information
Trifluoromethanesulfonic anhydride is rapidly hydrolysed in water, therefore the conclusion as not readily biodegradable of its degradation product, i.e. trifluoromethanesulfonic acid, is considered as relevant for the assessment of trifluoromethanesulfonic anhydride.
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
- Type of water:
- freshwater
Additional information
The read-across justification with trifluoromethanesulfonic acid is provided in the attached document in the endpoint study record.
The aerobic ultimate biodegradation potential of Trifluoromethanesulfonic acid was determined in a test for ready biodegradability, according to the OECD 301D guideline and under GLP conditions.
Degradation was followed by analysis of dissolved oxygen over a 28-day period. The amount of oxygen taken up by the microbial population during biodegradation of the test item, corrected for uptake by the blank inoculum run in parallel, is expressed as a percentage of COD.
There was 0% of degradation of test item after 28 days. The positive control reached the pass level already on day 3. As degradation in the toxicity flask was more than 25 % at the end of the test, the test item can be stated as not toxic towards the inoculum in a concentration of 11.72 mg/L.
In these test conditions, Trifluoromethanesulfonic acid was not readily biodegradable.
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