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EC number: 219-371-7 | CAS number: 2425-79-8
- 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)
Description of key information
The substance is not readily biodegradable, but appears to show evidence of slow aerobic degradation that did not plateau before the end of a 28-day study. An extended Modified OECD Screening test (OECD 301 F, EC C.4-D) demonstrated 98% degradation after 60 days, indicating a potential for complete mineralisation in the environment. Thus, the substance undergoes complete mineralisation in the environment and is considered inherently biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- inherently biodegradable, not fulfilling specific criteria
- Type of water:
- freshwater
Additional information
Ready biodegradability was tested according to the Modified OECD Screening test (OECD 301 F, EC C.4-D) in 2010 by Harlan Laboratories Ltd. (Clarke N). The initial test substance concentration was 20 mg/L. The test was performed with predominantly domestic activated sewage sludge collected from the final effluent stage of the Severn Trent Water Plc sewage treatment plant at Loughborough, Leicestershire, UK, and the oxygen consumption was monitored over a time period of 60 days. The test substance exhibited a slow but steady degradation rate that did not plateau before day 28, by which time 43% degradation (oxygen consumption) had occurred. However, degradation reached 98% after 60 days. The reference substance, aniline, achieved 71% degradation after 14 days, 88% degradation aft 28 days, and 105% degradation after 60 days. The validity criteria were met, and the substance was considered not to be readily biodegradable under the conditions of the test, although the results did indicate a potential for complete mineralisation in the environment.
Ready biodegradability was tested according to the Modified OECD Screening test (OECD 301 E, EC C.4-B) in 1989 by Ciba-Geigy Ltd. (Bader U). The initial test substance concentration was equivalent to 20 mg DOC/L. The test was performed with mixed polyvalent bacteria collected from the secondary effluent of the domestic sewage treatment plant at CH-4106 Therwil, and the DOC removal was monitored over a time period of 28 days. The test substance exhibited a slow but steady degradation rate that did not plateau before the end of the study on day 28, by which time 38% degradation (DOC removal) had occurred. The reference substance, aniline, achieved 99% and 100% DOC removal after 7 days and 28 days, respectively. The validity criteria were met, and the substance was considered not to be readily biodegradable under the conditions of the test.
A supporting study conducted in accordance with the Modified MITI Test I (OECD 301 C, EU C.4-F) in 2002 is reported by the Japanese National Institute of Technology and Evaluation (NITE). Nominal initial test substance concentration was 100 mg/L, and the test was performed using 30 mg/L of activated sludge. The duration of the test was 4 weeks, after which the test substance had achieved a degradation of 5% measured by oxygen uptake and 9% measured by TOC removal. GC analysis showed 86% loss of the test substance over the course of the test and the report states that hydrolysis [of the epoxy groups] had occurred. No data to confirm the validity of the test were reported. The test substance was reported to be not readily biodegradable.
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