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EC number: 219-372-2 | CAS number: 2425-85-6
- 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian cell study: DNA damage and/or repair
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2013
- Reliability:
- 1 (reliable without restriction)
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 013
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 486 (Unscheduled DNA Synthesis (UDS) Test with Mammalian Liver Cells in vivo)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- unscheduled DNA synthesis
Test material
- Reference substance name:
- 1-(4-methyl-2-nitrophenylazo)-2-naphthol
- EC Number:
- 219-372-2
- EC Name:
- 1-(4-methyl-2-nitrophenylazo)-2-naphthol
- Cas Number:
- 2425-85-6
- Molecular formula:
- C17H13N3O3
- IUPAC Name:
- 1-(4-methyl-2-nitrophenylazo)-2-naphthol
- Test material form:
- solid: particulate/powder
- Remarks:
- migrated information: powder
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
Administration / exposure
- Route of administration:
- oral: gavage
- Frequency of treatment:
- The study was performed in two parts, in Experiment 1 perfusion of the livers commenced approximately 16 hours after dosing and in Experiment 2 perfusion was performed approximately 4 hours after dosing.
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
0 mg/kg bw
Basis:
nominal conc.
- Remarks:
- Doses / Concentrations:
1000 mg/kg bw
Basis:
nominal conc.
- Remarks:
- Doses / Concentrations:
2000 mg/kg bw
Basis:
nominal conc.
- No. of animals per sex per dose:
- 4
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
The test item was considered to be non-genotoxic under the conditions of this study. - Executive summary:
Introduction. A study was performed to assess the potential of the test item to induce DNA repair in isolated rat hepatocytes following in vivo administration. The method used has been designed to be compatible with the OECD Guidelines for Testing of Chemicals No. 486 and follows the recommendations of the UKEMS Sub-Committee on Guidelines for Mutagenicity Testing: Report, Part II revised (Supplementary Mutagenicity Tests: UKEMS recommended procedures, 1993).
Methods. A range-finding test was performed to find suitable dose levels of the test item, route of administration and to determine if the there was any differences in toxicity in male and female rats. As there was no difference in toxicity between sexes the main test was performed using male rats only. The UDS assay was conducted using the oral route of administration using only male animals and with the test item at the maximum dose level of 2000 mg/kg, with 1000 mg/kg as the lower dose level. The study was performed in two parts, in Experiment 1 perfusion of the livers commenced approximately 16 hours after dosing and in Experiment 2 perfusion was performed approximately 4 hours after dosing. Following perfusion the liver hepatocytes were processed to give stained slides which were then scored using a microscope and an automated image analysis system. The method used for scoring the hepatocytes was an area counting method which is compatible with the UKEMS guidelines and OECD test method. Further groups of rats were given a single oral dose of arachis oil, or dosed with 2-acetylaminofluorene (2AAF) at 16 hours or N,N’-dimethylhydrazine dihydrochloride (NDHC) at 4 hours to serve as vehicle and positive controls respectively.
Results. There were no marked increases in the incidence of unscheduled DNA synthesis in animals dosed with the test item at either time point. The positive controls produced marked increases in net nuclear grain counts and in the incidence of cells in repair, and the vehicle control groups gave acceptable values for net nuclear grain counts.
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