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Diss Factsheets
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EC number: 202-547-2 | CAS number: 96-96-8
- 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
Mode of degradation in actual use
Administrative data
- Endpoint:
- mode of degradation in actual use
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 4 (not assignable)
Data source
Reference
- Reference Type:
- review article or handbook
- Title:
- Handbook of Chemical Property Estimation Methods
- Author:
- [(1) Atkinson R; (2) Meylan WM, Howard PH; (3) Lyman WJ et al
- Year:
- 2 011
- Bibliographic source:
- Environ Toxicol Chem 7: 435-62 (1988); Chemosphere 26: 2293-99 (1993) ; . Washington, DC: Amer Chem Soc pp. 7-4, 7-5 (1990)
Materials and methods
Test guideline
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- Toxnet database
- GLP compliance:
- not specified
Test material
- Reference substance name:
- 5-nitro-o-anisidine
- EC Number:
- 202-770-5
- EC Name:
- 5-nitro-o-anisidine
- Cas Number:
- 99-59-2
- IUPAC Name:
- 2-methoxy-5-nitroaniline
Constituent 1
Results and discussion
Applicant's summary and conclusion
- Executive summary:
Environmental Abiotic Degradation:
The rate constant for the vapor-phase reaction of 5-nitro-o-anisidine with photochemically-produced hydroxyl radicals has been estimated as 3.3X10-11 cu cm/molecule-sec at 25 deg C(SRC) using a structure estimation method(1). This corresponds to an atmospheric half-life of about 12 hours at an atmospheric concentration of 5X10+5 hydroxyl radicals per cu cm(2). 5-Nitro-o-anisidine is not expected to undergo hydrolysis in the environment due to the lack of hydrolyzable functional groups(3). Aromatic amines such as aniline have weak absorption bands that extend beyond 290 nm(4), therefore p-anisidine may be susceptible to direct photolysis, but the kinetics of this reaction are unknown. Aniline has been shown to undergo indirect photolysis in natural waters containing humic acids(5), therefore it is expected that p-anisidine may also undergo indirect photolysis in natural water.
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