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Diss Factsheets
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EC number: 203-404-7 | CAS number: 106-50-3
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
Biodegradation is not a primary route of degradation for this substance. The substance is neither readily nor inherently biodegradable as indicated by numerous studies utilizing activated sludge. However, abiotic degradation studies demonstrate rapid degradation in water and air via oxidative and photolytic mechanisms. The substance is predicted to undergo rapid degradation after reaction with hydroxyl radicals with a DT50 value of 0.091 days (QSAR model AOPWIN, v1.93). It is unlikely to undergo hydrolysis, since the substance is an aromatic amine and cannot behave as an electrophile unless it is metabolically activated. Under natural or simulated sunlight, direct and indirect photodegradation in water is rapid (overall t½ = 0.12 d). It indicates that the substance is very photolabile, and both direct and indirect photolysis contribute significantly to its phototransformation. Rapid photodegradation and oxidation (CSR section 5.2.2) of the substance indicate that the substance is unlikely to persist in air. In addition, the vapour pressure (0.0104 Pa) and the Henry's law constant (3.63E-5 Pa m3/mol) of the substance indicate that the substance is not likely to volatilise extensively from surfaces into air under dry conditions or from water. Therefore, any concentrations of the substance in air are considered negligible.
Abiotic degradation occurs rapidly when the substance is exposed to light and oxygen and can lead either to the formation of higher molecular weight molecules (dimer, trimer and Bandrowski’s base) or to benzoquinone depending on concentration. Degradation pathways were identified in the buffered water studies by Picardo et al. (1990), with the primary degradative pathway being oxidation to p-benzoquinonediimine and subsequent hydrolysis to benzoquinone. Oxidation of the substance to p-benzoquinonediimine in aqueous solutions was also documented with Bandrowski’s base the primary rearrangement product (Corbett, 1972). Given the rapid oxidation of the substance, storage recommendations during and prior to use include keeping the substance in well-closed containers, protected from light (Merck Index, 1996). For the adsorption property of the substance, the Koc value (33.83 L/kg) is estimated to be 33.83 L/kg (log Koc=1.53) using KOCWIN (QSAR model).
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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