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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
Phototransformation in air
Administrative data
Link to relevant study record(s)
- Endpoint:
- phototransformation in air
- 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 (2004)
- Qualifier:
- no guideline followed
- Version / remarks:
- The EU RAR (2004) reviews several studies which investigated the atmospheric degradation of acrylonitrile.
- Principles of method if other than guideline:
- The EU RAR refers to studies and theoretical modelling in the discussion of atmospheric degredation of acrylonitrile
- GLP compliance:
- not specified
- Estimation method (if used):
- The photooxidation of acrylonitrile by ozone and hydroxyl radicals under simulated atmospheric conditions
- Light source:
- not specified
- Details on light source:
- No information available
- Details on test conditions:
- No information available
- Preliminary study:
- No information available
- Test performance:
- No information available
- DT50:
- 84 d
- Test condition:
- Reaction with ozone
- Remarks on result:
- other: Munshi et al (1989)
- DT50:
- > 115 d
- Test condition:
- Reaction with ozone
- Remarks on result:
- other: Atkinson et al (1982)
- DT50:
- 131
- Test condition:
- Reaction with ozone
- Remarks on result:
- other: Hoechst (1994)
- DT50:
- 5
- Test condition:
- Reaction with OH radicals
- Remarks on result:
- other: Hansen et al (1982); Edney et al (1982)
- DT50:
- 4.1 d
- Test condition:
- Reaction with OH radicals
- Remarks on result:
- other: Hoechst (1994)
- Reaction with:
- ozone
- Rate constant:
- 0 cm³ molecule-1 s-1
- Remarks on result:
- other: Munshi et al (1989)
- Reaction with:
- ozone
- Rate constant:
- < 0 cm³ molecule-1 s-1
- Remarks on result:
- other: Atkinson et al (1982)
- Reaction with:
- ozone
- Rate constant:
- 0 cm³ molecule-1 s-1
- Remarks on result:
- other: Hoechst (1994)
- Reaction with:
- OH radicals
- Rate constant:
- 0 cm³ molecule-1 s-1
- Remarks on result:
- other: Hansen et al (1982); Edney et al (1982)
- Reaction with:
- OH radicals
- Rate constant:
- 0 cm³ molecule-1 s-1
- Remarks on result:
- other: Hoechst (1994)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The estimated half-life for reaction with OH. is sufficiently long to allow redistribution of acrylonitrile to the aqueous compartment and to soil, with associated exposure of populations in the vicinity of the emission source, but is unlikely to be long enough to allow redistribution to the stratosphere.
- Executive summary:
Acrylonitrile is labile in the atmosphere, due to photodegradation processes. Studies of photooxidation of acrylonitrile by ozone and hydroxyl radicals (OH.) by several groups (Atkinson et al., 1982; Hansen et al.; 1982, Edney et al., 1982; Munshi, 1989) under simulated atmospheric conditions indicate that reaction with OH.is the major loss process in the troposphere for acrylonitrile. The reaction with ozone is slow and is not likely to constitute a major route of degradation. Munshi (1989) determined a rate constant of 1.38.10-19 cm³/mol/s for the reaction of acrylonitrile with O3, giving a trophospheric lifetime of 84 days, while Atkinson et al. (1982) determined a rate constant of < 1.0 x 10-19cm³/mol/s at an O3concentration of < 2.4 x 1013mol/cm³. Both Hansen et al. (1982) and Edney et al. (1982) have published a rate constant of 3.2 x10-12cm³/mol/s for the reaction of acrylonitrile with OH., giving an estimated half-life of 5 days in the troposphere, based on an estimated hydroxyl radical concentration of 5 x105mol/cm³.
Theoretical estimation of the photo-oxidation of acrylonitrile using the AOPWINvl.55a Atmospheric Modelling Programme (Hoechst, 1994) has provided similar results, giving an overall predicted rate constant of 3.945 x10-12cm³/mol/s for the reaction of acrylonitrile with OH., and a half-life of 4.067 days, based on a hydroxyl radical concentration of 5.105 mol/cm³. The rate constant for the reaction of acrylonitrile with O3is predicted as 0.87 x 10-19cm³/mol/s, giving a half-life of 130.971 days at an O3concentration of 7.1011 mol/cm³. Both experimental results (Hashimoto et al., 1984) and theoretical modelling (Hoechst, 1994) suggest that addition of OH.to the olefinic double bond represents the initial degradation reaction. Harris and co-workers (1981) showed that the reaction of acrylonitrile with OH.was independent of temperature in the range studied but showed a small increase with increasing pressure. Formaldehyde has been demonstrated as a primary reaction product following reaction of acrylonitrile with OH.in the presence of NO by Edney at al. (1982), Hashimoto et al. (1984) and Spicer et al. (1985). CO, HCN, formyl cyanide (HCOCN) and formic acid have also been reported as degradation products (Edney et al., 1982; Hashimoto et al., 1984).
The estimated half-life for reaction with OH.is sufficiently long to allow redistribution of acrylonitrile to the aqueous compartment and to soil, with associated exposure of populations in the vicinity of the emission source, but is unlikely to be long enough to allow redistribution to the stratosphere.
Reference
Table 1. Rate constants for reaction of acrylonitrile with hydroxyl radical and ozone and dervied tropospheric lifetimes.
Species |
Rate constant cm³/mol/s |
Trophospheric lifetime/half-life (days) |
Reference |
O3 |
1.38 x 10-19 |
Lifetime 84 * |
Munshi et al (1989) |
O3 |
< 1.0 x 10-19 |
Lifetime > 115 * |
Atkinson et al (1982) |
O3 |
0.87 x 10-19 |
Half-life 131 ** |
Hoechst (1994) |
OH. |
3.2 x 10-12**** |
Half-life 5 *** |
Hansen et al (1982) Edney et al (1982) |
OH. |
3.95x 10-12 |
Half-life 4.1 *** |
Hoechst (1994) |
* Value assumes an O3concentration of 1 x 1012mol/cm³
** Value assumes an O3concentration of 0.7 x 1012mol/cm³
*** Value assumes an O3concentration of 5 x105mol/cm³
**** Value used in EUSES
Description of key information
Acrylonitrile is labile in the atmosphere, due to rapid photodegradation.
Key value for chemical safety assessment
- Half-life in air:
- 5 d
- Degradation rate constant with OH radicals:
- 0 cm³ molecule-1 s-1
Additional information
Acrylonitrile is labile in the atmosphere, due to rapid photodegradation. The EU RAR reports a rate constant of 3.2 x 10e-12 for the reaction of acrylonitrile with hydroxyl radicals, giving an estimated half life of 5 days in the troposphere. Theoretical assessment gives similar results and a predicted half life of 4 days.
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