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EC number: 204-616-2 | CAS number: 123-30-8
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
4-aminophenol is soluble (6500 mg/L) and is inherently biodegradable in water with pre-adapted sludge. It has a low capacity to volatilise from solution to the air (Henry's law constant of 8.954E-005 Pa m3/mol-1) and undergoes rapid phototransformation in the atmosphere (half-life of 1.7 hours in the presence of hydroxyl radicals at1.5X10+6 hydroxyl radicals per cu assuming 12 hours daylight).
The partitioning coefficient (log Kow = -0.09) indicates that 4-aminophenol does not have a high potential for adsorption to soil or sediment (log Koc = 0.59). It has a low potential for bioaccumulation in aquatic and terrestrial habitats (BCF <=0.46 L/kg). Assuming predominate emissions to the water compartment, Mackay Level III fugacity predictions estimate 1.61%, 98.2%, 0.18% and 3.24e-007 % partitioning in the soil, water, sediment and air compartments, respectively.
4 -aminophenol is amphoteric with both amine and hydroxyl functional groups; pKa values for these groups are 5.48 and 10.46, respectively. At environmental pH values from 5 to 9, the substance is expected to exist primarily as the neutral species.
The rate constant for the vapor-phase reaction of 4-aminophenol with photochemically-produced hydroxyl radicals has been estimated as 74.2471 E-12cu cm/molecule-sec at 25 deg C using a structure estimation method (aopWin v1.92). This corresponds to an atmospheric half-life of about 1.7 hours at an atmospheric concentration of 1.5X10+6 hydroxyl radicals per cu cm (aopWin v 1.92).4-Aminophenol is expected to undergo fairly rapid oxidation in the presence of air and may directly photolyze due to its absorption in the environmental UV spectrum (max= 294 nm). Hence, the substance is unlikely to persist in air. In addition, the vapour pressure (0.00053 Pa at 25°C) and the Henry's law constant (8.954E-005 Pa m3/mol) of the substance indicate that the substance is not likely to volatilize extensively from surfaces into air under dry conditions or from water. Therefore, any concentrations of the substance in air are considered negligible.
4-Aminophenol is not expected to undergo hydrolysis in the environment due to the lack of hydrolyzable functional groups. Biodegradation is not expected to be a primary route of degradation in the environment. The substance is not readily biodegradable but can be considered inherently biodegradable with pre-adapted sludge. The substance is degraded at rates of 92%, 87% and 66% after 22d, 5d and 8d respectively when exposed to pre-adapted sludge (see section 4.1.2.1.2).This is an indication that the substance has the potential for degradation under favorable conditions, such as STP or biological treatment plant.
The substance degrades primarily via abiotic processes and to a much lesser extent via biotic processes such as microbial degradation. Abiotic degradation occurs rapidly when the substance is exposed to light and oxygen.
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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