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EC number: 617-298-9 | CAS number: 82097-50-5
- 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:
- 23 May 1989 to 20 Jun 1989
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 E (Ready biodegradability: Modified OECD Screening Test)
- Version / remarks:
- May 1981
- Deviations:
- yes
- Remarks:
- Filter: 0.45 µm instead of a 0.2 µm for DOC-analysis.
- GLP compliance:
- yes (incl. QA statement)
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- other: secondary effluent from a treatment plant
- Details on inoculum:
- - Source of inoculum/activated sludge: Secondary effluent from the sewage treatment plant of CH-4106 Therwil (mixture of polyvalent bacteria)
- Duration of test (contact time):
- 28 d
- Initial conc.:
- >= 17 - <= 23 mg/L
- Based on:
- DOC
- Parameter followed for biodegradation estimation:
- DOC removal
- Details on study design:
- TEST CONDITIONS
- Composition of medium: Mineral medium prepared according to the method described in the guideline.
- Test temperature: 23 ± 2 ˚C
- Lighting: Indirect daylight, dark brown glass bottles
- Continuous darkness: Yes
TEST SYSTEM
- Culturing apparatus: 2000 mL Erlenmeyer flasks
- Number of culture flasks/concentration: 2
- Sampling frequency: DOC on the days 0, 7, 14, 21, 27, 28
CONTROL AND BLANK SYSTEM
- Mineral nutrient solution without test material but with inoculum (2 replicates)
- Mineral nutrient solution with test material and with inoculum (20 mg DOC/L the test substance, 2 replicates)
- Mineral nutrient solution with reference substance and with inoculum (20 mg DOC/L reference substance aniline; 2 replicates) - Reference substance:
- aniline
- Remarks:
- 20 ± 2 mg DOC/L
- Key result
- Parameter:
- % degradation (DOC removal)
- Value:
- 12
- Sampling time:
- 28 d
- Details on results:
- An overview of the results is provided in Table 1 in 'Any other information on results incl. tables'.
Test substance: Biodegradation measured as mg DOC/L and corrected by the blank control was calculated as 12 % (DOC/DOC) in 28 days. - Results with reference substance:
- Measurements of DOC-values of biodegradation results are shown in Table 1 in 'Any other information on results incl. tables'. Biodegradation measured as mg DOC/L and corrected by the blank control was calculated as 96 % (DOC/DOC) in 28 days.
- Validity criteria fulfilled:
- not specified
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- In a 28-day ready biodegradability study in accordance with OECD TG 301 E, the biodegradation of the test substance was calculated as 12% (DOC/DOC). Thus, it is concluded that the test substance is not biodegradable under the test conditions.
- Executive summary:
The ready biodegradability of the test item was investigated in a modified OECD screening test in accordance with OECD TG 301 E and in compliance with GLP criteria. The ready biodegradability of the test item was investigated using secondary effluent of a sewage treatment plant. The inoculum was incubated with 20 ± 3 mg DOC/L of the test substance (2 replicates) dissolved in the mineral medium at 23 ± 2 °C in the indirect daylight in dark brown glass bottles for 28 days. Mineral nutrient solution without test material but with inoculum (2 replicates), and mineral nutrient solution with reference substance and with inoculum (20 mg DOC/L reference substance aniline; 2 replicates), were incubated under the same conditions. Dissolved organic carbon (DOC) was measured at day 0, 7, 14, 21, 27 and 28. The biodegradation was calculated on the basis of the initial carbon content of the test substance and the carbon content determined on the days of measurements. Biodegradation of the test substance and reference substance measured as mg DOC/L and corrected by the blank control was calculated as 12 and 96 % (DOC/DOC) respectively in 28 days. It is concluded that the test substance is not biodegradable under the test conditions.
Reference
Table 1 Measurements of DOC-values of biodegradation results.
Culture medium | Flask No. | DOC concentrations after x days (mg/L) | |||||
0 | 7 | 14 | 21 | 27 | 28 | ||
Mineral nutrient solution without test material but with inoculum | 1 2 mean | 0,81 0,81 0.81 | 1.71 1.30 1.51 | 0.50 -0.23 0,14 | -0.07 0.20 0.07 | 0.04 0.87 0.46 | 0,01 0.22 0,12 |
Mineral nutrient solution with test material and with inoculum | 1 2 | 17.95 17,95 | 16.71 16,68 | 15.93 15.85 | 14.87 15.09 | 15.34 15.09 | 15.05 15.44 |
Mineral nutrient solution with Reference substance and with inoculum | 1 2 | 19.59 19.59 | 0.77 18,08 | 0 .41 0.80 | 0,90 0.13 | 0.88 1.01 | 0.82 0.82 |
| Flask No, | % DOC removal after x days | |||||||
0 | 7 | 14 | 21 | 27 | 28 |
|
| ||
Test substance | Test 1 Test 2 Test f | 0 0 0 | 11 11 11 | 8 8 8 | 14 12 13 | 13 15 14 | 13 11 12 |
|
|
Reference substance | Ref. 1 Ref. 2 Ref. f | 0 0 0 | 104 12 58 | 99 96 98 | 96 100 98 | 98 97 98 | 96 96 96 |
|
|
Negative degradation values are within the variation of the method.
Description of key information
The test substance is concluded to be "not readily biodegradable" under the test conditions, using secondary effluent from a sewage treatment plant, OECD TG 301 E, Bader 1989
Key value for chemical safety assessment
- Biodegradation in water:
- not biodegradable
- Type of water:
- freshwater
Additional information
There is one ready biodegradability study available, which followed OECD TG 301 E and was performed in compliance with GLP criteria. The ready biodegradability of the test item was investigated using aerobic activated sludge with a mixture of polyvalent bacteria and a secondary effluent of a sewage treatment plant of CH-4106 Therwil. The test sludge was incubated with 20 ± 3 mg DOC/L of the test substance (2 replicates) dissolved in the mineral medium at 23 ± 2 °C in the indirect daylight in dark brown glass bottles for 28 days. Mineral nutrient solution without test material but with inoculum (2 replicates), mineral nutrient solution with test material and with inoculum (20 mg DOC/L the test substance, 2 replicates) and mineral nutrient solution with reference substance and with inoculum (20 mg DOC/L reference substance aniline; 2 replicates), were incubated under the same conditions. Dissolved organic carbon (DOC) was measured on day 0, 7, 14, 21, 27 and 28. The biodegradation was calculated on the basis of the initial carbon content of the test substance and the carbon content determined on the days of measurements. For the calculation, the formula given in the guideline was used. Biodegradation of the test substance and reference substance measured as mg DOC/L and corrected by the blank control was calculated as 12 and 96% (DOC/DOC) respectively in 28 days. It is concluded that the test substance is not biodegradable under the test conditions.
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