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Diss Factsheets
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EC number: 203-466-5 | CAS number: 107-13-1
- 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
Hydrolysis
Administrative data
Link to relevant study record(s)
- Endpoint:
- hydrolysis
- Type of information:
- other: secondary source
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Studies reviewed in EU RAR
- Qualifier:
- no guideline followed
- Version / remarks:
- The EU RAR (2004) reviews several studies which investigated the abiotic aquatic degradation of acrylonitrile.
- Principles of method if other than guideline:
- Abiotic degredation
- GLP compliance:
- not specified
- Radiolabelling:
- not specified
- Analytical monitoring:
- not specified
- Details on sampling:
- No information available
- Buffers:
- No information available
- Estimation method (if used):
- No information available
- Details on test conditions:
- See below
- Number of replicates:
- No information available
- Statistical methods:
- No information available
- Preliminary study:
- No information available
- Test performance:
- No information available
- Transformation products:
- not specified
- Details on hydrolysis and appearance of transformation product(s):
- Acrylonitrile is relatively hydrolytically stable, with no hydrolysis reported to occur in distilled water over the pH range 4-10 (Going et al., 1978).
- Remarks on result:
- other: Acrylonitrile is relatively hydrolytically stable, with no hydrolysis reported in distilled water over the pH range 4-10 (Going et al., 1978)
- Other kinetic parameters:
- No information available
- Details on results:
- Acrylonitrile is relatively hydrolytically stable, with no hydrolysis reported to occur in distilled water over the pH range 4-10.
99.0% wet air oxidation of acrylonitrile after 1 hour at 275°C and pressures of 70-140 kg/cm³. - Validity criteria fulfilled:
- not applicable
- Conclusions:
- Acrylonitrile is relatively hydrolytically stable, with no hydrolysis reported to occur in distilled water over the pH range 4-10
- Executive summary:
Acrylonitrile is relatively hydrolytically stable, with no hydrolysis reported to occur in distilled water over the pH range 4-10 (Going et al., 1978). Knoevenagel and Himmelreich (1975) reported photo-oxidation of acrylonitrile in the presence of water to occur under experimental conditions, approximately 25% degradation being reported in a 24-hour period. It appears that elevated temperatures were used in this study, and the results may be of little relevance for normal environmental conditions. The authors suggest that this process of abiotic aquatic degradation will occur in surface waters, in the layers accessible by light. Randall (1980) reported 99.0% wet air oxidation of acrylonitrile after 1 hour at 275°C and pressures of 70-140 kg/cm³. Going et al. (1978) also demonstrated decomposition of acrylonitrile over a period of 23 days at a concentration of 10 mg/l in Mississipi River water at different pHs. Concentrations of acrylonitrile in river water at unadjusted pH fell linearly to undetectable levels by day 6, decomposition was slower at pH 4.0 and pH 10.0, although levels at pH 10 were also below the limits of detection by day 23. The degradation seen in this study may be due to a combination of biodegradation and volatilisation of acrylonitrile from the test medium rather than abiotic degradation.
EU RAR (2004)
Reference
Acrylonitrile is relatively hydrolytically stable, with no hydrolysis reported to occur in distilled water over the pH range 4-10 (Going et al., 1978). Knoevenagel and Himmelreich (1975) reported photo-oxidation of acrylonitrile in the presence of water to occur under experimental conditions, approximately 25% degradation being reported in a 24-hour period. It appears that elevated temperatures were used in this study, and the results may be of little relevance for normal environmental conditions. The authors suggest that this process of abiotic aquatic degradation will occur in surface waters, in the layers accessible by light. Randall (1980) reported 99.0% wet air oxidation of acrylonitrile after 1 hour at 275°C and pressures of 70-140 kg/cm³. Going et al. (1978) also demonstrated decomposition of acrylonitrile over a period of 23 days at a concentration of 10 mg/l in Mississipi River water at different pHs. Concentrations of acrylonitrile in river water at unadjusted pH fell linearly to undetectable levels by day 6, decomposition was slower at pH 4.0 and pH 10.0, although levels at pH 10 were also below the limits of detection by day 23. The degradation seen in this study may be due to a combination of biodegradation and volatilisation of acrylonitrile from the test medium rather than abiotic degradation.
EU RAR (2004)
Description of key information
Acrylonitrile is relatively hydrolytically stable.
Key value for chemical safety assessment
Additional information
Acrylonitrile is relatively hydrolytically stable, with no hydrolysis reported to occur in distilled water over the pH range 4-10 (EU RAR, 2004). Photo-oxidation of acrylonitrile in the presence of water is reported to occur under experimental conditions, with approximately 25% degradation being reported in a 24-hour period at elevated temperature (EU RAR, 2004). However the relevance of the experimental conditions to normal environmental conditions is questioned.
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