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EC number: 229-388-1 | CAS number: 6505-28-8
- 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
Key value for chemical safety assessment
Genetic toxicity in vitro
Description of key information
The substance was not mutagenic in bacteria, not clastogenic in a chinese hamster cell line and it did not induce micronuclei in human peripheral blood lymphocytes. All studies were performed according to OECD testing guidelines and GLP.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Genetic toxicity in vivo
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Ames Tests
In a reverse gene mutation assay in bacteria, strains TA100, TA98, TA1535 and TA1537 of Salmonella typhimurium and Escherichia coli strain WP2 uvrA were exposed to the following test item concentrations in DMSO: 0, 4.88, 9.77, 19.5, 39.1, 78.1, 156, 313, 625, 1250, 2500 and 5000 µg/plate. The test was conducted in the presence and absence of Phenobarbital/5,6-benzoflavone pretreated rat liver S9 mix. However, as it had been already reported that o-dianisidine produced by the reduction of azo groups in the test substance was positive in an Ames test, an additional test exclusively on TA98 was performed by using the metabolic activation system enhancing the reduction of azo groups (Hamster S9 mix). As a result, the gene mutagenicity of the test item on bacteria was judged negative in both performed test.
In a reverse gene mutation assay in bacteria, strains TA1535, TA1537, TA102, TA98 and TA100 of S. typhimurium were treated with suspensions of the test item in dimethyl sulphoxide at concentrations 0, 50, 150, 500, 1500 and 5000 µg/plate (Experiment 1 and 2). The test was performed in the presence and absence of a hamster liver homogenate metabolising system (30 % liver S9 in modified co-factors). No significant increases in the frequency of revertant colonies were recorded for any of the bacterial strains, with any dose of the test item, either with or without metabolic activation. Therefore, the test item, was considered to be non-mutagenic under the conditions of this test.
Chromosome aberration test
In an in vitro chromosome aberration test, Chinese hamster lung cell line (CHL cells) were exposed to the test substance in carboxymethyl cellulose sodium at concentrations of 313, 625, 1250, 5000 µg/mL in the absence of S9 mix and 625, 1250, 2500, 5000 µg/mL in the presence of S9 mix. The test doses were determined according to the result of the cell growth inhibition test, and each 3 doses of 1250, 2500 and 5000 μg/ml were also subjected to the microscopic observation in the 24-hour treatment by the continuous treatment method. As a result, no induction of the chromosome aberration was found, either, similarly in the short-term treatment method, and it was thus judged negative.
MNT in vitro
The test item, dissolved in DMSO, was assessed for its potential to induce micronuclei in human peripheral blood lymphocytes (HPBL) in the absence and presence of a rat liver metabolising system (S9 mx). Based on the results of a preliminary toxicity study, the doses chosen for the micronucleus assay ranged from 0.25 to 30 μg/mL for all three treatment groups. In the micronucleus assay, the cells were treated for 4 and 24 hours in the non-activated test system and for 4 hours in the S9-activated test system. All cells were harvested 24 hours after treatment initiation. Substantial toxicity (≥ 55 ± 5 % cytotoxicity relative to the solvent control) was not observed at any dose level in all three treatment groups. The dose levels to score for micronuclei were based on visible precipitate in the treatment medium (the lowest precipitating dose and two lower doses) in all harvests. The percentage of cells with micronucleated binucleated cells in the test article-treated groups was not statistically significantly increased relative to solvent control at any dose level in the 4-hour treatment group either in the presence of or the absence of S9 or in the 24-hour treatment group in the absence of S9. The results for the positive and negative controls indicate that all criteria for a valid assay were met. Based on the findings of this study, the test item was negative for the induction of micronuclei in both non-activated and S9-activated test systems.
Justification for classification or non-classification
Classification, Labelling, and Packaging Regulation (EC) No 1272/2008
The available experimental test data are reliable and suitable for classification purposes under Regulation (EC) No 1272/2008. In none of the tests, a genotoxic response was observed. As a result the substance is not considered to be genotoxic under Regulation (EC) No 1272/2008,as amended for the seventh time in Regulation (EC) No 2015/1221.
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