Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 200-539-3 | CAS number: 62-53-3
- 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

Long-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
Daphnia magna: NOEC (21d) = 0.016 mg/L (Hutton 1989)
Daphnia magna: NOEC (21d) = 0.004 mg/L (Kuehn et al. 1988 1989)
Daphnia magna: NOEC (21d) = 0.024 mg/L (Gersich and Milazzo 1988)
Key value for chemical safety assessment
Additional information
Hutton (1989) examined the effects of long-term exposure of Daphnia magna to aniline. The daphnids were exposed in a flow-through system at about 20°C. As dilution water hardened unfiltered fish tank water was used. During the test the daphnids were fed with trout chow and yeast daily. Five test concentrations; a DMF control and a water control were used. Nominal test concentrations were between 11 μg/l and 105 μg/l. However, weekly HPLC analysis of the test samples showed that the measured test concentration in all samples was about 50% of the nominal concentration. A 21-day NOEC related to reproduction of 16 μg/l (based on measured concentrations) was derived. The decreasing aniline concentration that was found in this flow-through study is attributed by the author to the presence of daphnid food.
In a semi-static test (three renewals per week) Kühn et al. (1988,1989) studied the long-term toxicity of aniline to Daphnia magna. The study was conducted at 25°C. During the test the daphnids were fed on fish food and activated sludge. Eight test concentrations ranging nominally from 0.1 μg/l to 316 μg/l were employed. A 21-day NOEC for reproduction of 10 μg/l based on nominal concentration was found. As it was not possible to analyse the real aniline concentrationlin the samples (detection limit of the used method was 0.1 mg/l an additional test vessel without daphnids and food but with a nominal aniline concentration of 316 μg/l was employed. After 2 days the aniline concentration in this sample was only 40 to 60% of the nominal concentration. Therefore, a NOEC value of 4 μg/l is extrapolated from this recovery rate. This extrapolation does not take into account the possibly enhanced degradation of aniline in the presence of daphnid food.
Gersich and Milazzo (1988) examined the effect of aniline to Daphnia magna in a long-term study. The daphnids were exposed under semi-static conditions at 20°C for 21 days. During the tests the daphnids were fed on green algae. Aniline concentrations ranging nominally from 10.6 μg/l to 170 μg/l were employed. The stability of aniline over the renewal period was examined by analyzing particular test solutions at 0-hour and 48-hour. A mean deviation of about 82% was found. A NOEC of 24 μg/l for reproduction based on mean analysed concentrations was reported.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
