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EC number: 218-817-8 | CAS number: 2243-62-1
- 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
Endpoint summary
Administrative data
Key value for chemical safety assessment
Additional information
1,5-Naphthylenediamine showed mutagenic properties in bacteria with (S. typhimurium TA 1537, TA 1538, TA 98 and TA 100) and without metabolic activation (S. typhimurium TA 1537, TA 98 and TA 100; Bacillus subtilis H17). A gene mutation assay with Chinese hamster V79 cells and two in vitro UDS tests with primary rat hepatocytes gave no indications for mutagenic or genotoxic effects of the compound. The results of a chromosomal aberration assay were regarded as invalid because of the strange pattern of cytotoxicity, with may be a consequence of unnoticed precipitation of the compound. An in vivo DNA binding assay showed no DNA-binding activity of 1,5-naphthylenediamine in rat liver. Overall, the mutagenic effects seen in bacteria could not be reproduced in mammalian cells. No classification for mutagenicity is proposed
Short description of key information:
In vitro:
Several in vitro genetic toxicity tests with 1,5-naphthylenediamine (Alphamin) were performed.
The test substance was tested in a Salmonella microsome test with 20-12500 µg/plate.
Doses up to 1600 µg/plate did not cause bacteriotoxic effects.
Higher doses showed bacteriotoxicity and substance precipitation occurred at the highest dose level, therefore 12500 µg/plate were not interpretable. On strains TA 1537, TA 98 and TA 100 a biologically relevant increase of revertants were found with and without metabolic activation; the effect was more pronounced with S9-mix.
The lowest effective dose was 200 µg/plate.
The genotoxicity of the test substance was found to be positive (Herbold 1988).
This result is supported by another Ames test (with and without metabolic activation):
In a preliminary experiment doses of 20-12500 µg substance/plate were tested in a Salmonella microsome test.
Doses up to 1200 µg/plate did not cause bacteriotoxic effects, higher doses revealed bacteriotoxicity and sustance precipitation occurred at doses of > 9600 µg/plate; at 12500 µg/plate the test was no longer interpretable. On strains TA 1537, TA 98 and TA 100 a biologically relevant increase in revertants was found with and without metabolic activation.
The lowest reproducible effective dose was 300 µg/plate (Herbold 1989).
Additionally the test substance was tested in 4 independent Institutes with the Salmonella typhimurium strains TA 98, TA 100, TA 1535, TA 1537, TA 1538 and Escherichia Coli WP2 uvrA. The doses used were: 0,3 and 3333,33 µg/plate and the experiments were performed with and without metabolical activation ( liver S-9 preparations from Aroclor 1254 -induced livers from rats, mice and syrian hamsters). The test substance was positive for TA 100(with and without metabolical activation), TA 1537 ( with and without metabolical activation) and TA 1538 (with metabolical activation). No pointmutagen effect was found in TA 1535 (with and without metabolical activatio...
Endpoint Conclusion:
Justification for classification or non-classification
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