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EC number: 470-180-7 | CAS number: 61196-40-5
- 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:
- 2004-12-20 to 2005-01-25
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- Version / remarks:
- 1992
- Deviations:
- no
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- EU Method C.4-D (Determination of the "Ready" Biodegradability - Manometric Respirometry Test)
- Version / remarks:
- Commission Directive 92/69/EEC, Method C.4-D of July 31, 1992: Manometric Respirometry Test (EEC Publication No. L 383 A, December 1992)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge: sewage plant Groß-Zimmern, Germany
- Preparation of inoculum for exposure: 2 x washing with tap water by centrifugation and decantation of the supernatant liquid
- Concentration of sludge: 1.5 g dry material
- Water filtered: no - Duration of test (contact time):
- 28 d
- Initial conc.:
- ca. 100 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- Preparation of Test Flasks:
The amounts of test item and reference item were directly weighed into the test flasks. No emulsifiers or solvents were used, but the solutions were dispersed by stirring to achieve a homogeneous solution of the test item.
Incubation:
The closed test flasks were incubated in a climatic chamber under continuous stirring. The consumption of oxygen was determined by measuring the change of pressure in the flasks. Evolved carbon dioxide was absorbed in an aqueous solution (45 %) of potassium hydroxide. - Reference substance:
- aniline
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 4
- Sampling time:
- 28 d
- Details on results:
- Points of degradation plot (test substance): 0 % degradation after 7 d 1 % degradation after 14 d 2 % degradation after 21 d 4 % degradation after 28 d
- Results with reference substance:
- Points of degradation plot (reference substance):
75 % degradation after 7 d
90 % degradation after 14 d
97 % degradation after 21 d
100 % degradation after 28 d - Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- The degradation rate of the test item did not reach 60 % within the 10-day window and after 28 days of incubation. Therefore, the test item is considered not to be readily biodegradable.
- Executive summary:
The purpose of this assay was to provide information on the biodegradability of the test item in aqueous environment according to OECD TG 301 F and thus serve as a rational basis for risk assessment for environmental fate in aqueous compartments. The test item was exposed to activated sludge from the aeration tank of a domestic waste water treatment plant for 28 days. The biodegradation was followed by the oxygen uptake of the microorganismsduring exposure. As a reference item aniline was tested simultaneously under the same conditions as the test item, and functioned as a procedure control. This study is recognized by the international test guidelines and should provide a rational basis to assess the ready biodegradation properties of the test item when incubated with activated sludge. The test item did not reach 60 % within the 10-day window and after 28 days of incubation. After 28 days a degradation of 4 % was observed. The reference item aniline was sufficiently degraded to 90 % after 14 days, and to 112 % after 28 days of incubation. In the toxicity control containing both, the test item and the reference item, 51 % biodegradation was noted within 14 days and 55 % biodegradation was determined after 28 days of incubation. Thus the test item can be assumed to be not inhibitory on the activated sludge microorganisms.The oxygen demand in the abiotic control was 0 mg/L. The degradation rate of the test item did not reach 60 % within the 10-day window and after 28 days of incubation. Therefore, the test item is considered not to be readily biodegradable.
Reference
Description of key information
According to an OECD TG 301 F compliant study, the test item is not readily biodegradable (reference 5.2.1-1).
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
- Type of water:
- freshwater
Additional information
Ready biodegradation
The purpose of this assay was to provide information on the biodegradability of the test item in aqueous environment according to OECD TG 301 F and thus serve as a rational basis for risk assessment for environmental fate in aqueous compartments. The test item was exposed to activated sludge from the aeration tank of a domestic waste water treatment plant for 28 days. The biodegradation was followed by the oxygen uptake of the microorganisms during exposure. As a reference item aniline was tested simultaneously under the same conditions as the test item, and functioned as a procedure control. This study is recognized by the international test guidelines and should provide a rational basis to assess the ready biodegradation properties of the test item when incubated with activated sludge. The test item did not reach 60 % within the 10-day window and after 28 days of incubation. After 28 days a degradation of 4 % was observed. The reference item aniline was sufficiently degraded to 90 % after 14 days, and to 112 % after 28 days of incubation. In the toxicity control containing both, the test item and the reference item, 51 % biodegradation was noted within 14 days and 55 % biodegradation was determined after 28 days of incubation. Thus the test item can be assumed to be not inhibitory on the activated sludge microorganisms.The oxygen demand in the abiotic control was 0 mg/L. The degradation rate of the test item did not reach 60 % within the 10-day window and after 28 days of incubation. Therefore, the test item is considered not to be readily biodegradable.
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