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EC number: 223-754-4 | CAS number: 4051-63-2
- 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
Link to relevant study records
- Endpoint:
- in vitro gene mutation study in bacteria
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2009
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP and OECD testing guideline compliant study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- Deviations:
- no
- GLP compliance:
- yes
- Type of assay:
- bacterial reverse mutation assay
- Species / strain / cell type:
- S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
- Species / strain / cell type:
- E. coli WP2 uvr A
- Metabolic activation:
- with and without
- Metabolic activation system:
- liver S9 mix from Delor 106 (mixture of PCBs) induced rats
- Test concentrations with justification for top dose:
- 10, 100, 500, 1000, 2500 and 5000 microgramms/plate (TA 100)
50, 150, 500, 1500 and 5000 microgramms/plate (all other strains) - Vehicle / solvent:
- water
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: Sodium azide, 4-nitro-o-phenylenediamine, 9-aminoacridine hydrochloride monohydrate, 2-aminofluorene, 2-aminoanthracene, N-methyl-N'-nitro-N-nitrosoguanidine
- Details on test system and experimental conditions:
- METHOD OF APPLICATION: in medium; in agar (plate incorporation)
- Evaluation criteria:
- The main criterion for evaluation of results was modified two-fold increase rule, its using is comparable with using of statistical methods. After this rule the result is positive, when reproducible dose-effect and/or doubling of ratio Rt/Rc is reached.
- Statistics:
- Dunkel V. C.,Chu K.C. (1980): Evaluation ofmethods for analysis ofmicrobial
mutagenicity assays, in The Predictive Value of Short-Term Screening Tests in Carcinogenicity Evaluation, Elsevier North-Holland Biomedical Press, 231 - 240
Claxton L. D. et al. (1987): Guide for the Salmonella typhimurium/mammalian microsome tests far bacterial mutagenicity, Mutat. Res. 189, 83 - 91 - Key result
- Species / strain:
- S. typhimurium TA 100
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity nor precipitates, but tested up to recommended limit concentrations
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Key result
- Species / strain:
- S. typhimurium TA 98
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity nor precipitates, but tested up to recommended limit concentrations
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Key result
- Species / strain:
- S. typhimurium TA 1537
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity nor precipitates, but tested up to recommended limit concentrations
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Key result
- Species / strain:
- S. typhimurium TA 1535
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity nor precipitates, but tested up to recommended limit concentrations
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Key result
- Species / strain:
- E. coli WP2 uvr A
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity nor precipitates, but tested up to recommended limit concentrations
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- The test item precipitated on the plates. This did not hinder scoring.
- Conclusions:
- Interpretation of results (migrated information):
negative
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Additional information
The key study for mutagenicity in bacteria was performed according to OECD guideline 471 and according to GLP (Synthesia 2009b). Four Salmonella typhimurium strains TA 98, TA 100, TA 1535 and TA 1537 and Escherichia coli WP2 uvrA strain were used. The test substance was suspended in water and assayed in doses of50-5000mg which were applied
to plates in volume of 0.1mL. Two series of experiments were performed with each strain - without metabolic activation and with a supernatant of rat liver and a mixture of cofactors.
In the arrangement given above, the test substance C.I. Pigment Red 177 was non-mutagenic for all the used bacterial strains with as well as without metabolic activation.
Another Ames test was performed with only four strains and without an independent repeat experiment (Ciba-Geigy Ltd 1979). Its procedure was comparable to a guideline study with acceptable restrictions. The plate incorporation protocol was applied and the maximal evaluated concentration was 2000 µg/plate in the absence of cytotoxicity or precipitation. Liver homogenate from arochlor induced rats was used for metabolic activation. No increase in revertant frequency was induced by treatment with the pigment.
The assessment of mutagenicity in mammalian cells in vitro was performed by two GLP-compliant studies for unscheduled DNA synthesis (Ciba-Geigy Ltd. 1986a, b). The experiment without metabolic activation was performed with a human fibroblast cell line (CRL 1121), and the experiment with metabolic activation was performed with primary hepatocytes from arochlor 1254 induced rats. Both studies together fulfill the requirements of OECD testing guideline 482. In the studies, the optional inhibition of semi-conservative DNA replication was not included. However, discrimination between cells in S-phase and repairing cells was done.
The test concentrations that could be applied were limited by the solubility of the pigment: In rat hepatocytes, 0.4, 2, 10 and 50 µg/ml were applied using DMSO as vehicle. In human fibroblasts, 0.8 , 4, 20 and 100 µg/ml were scored. 2-Acetylaminof luorene at 0.2 mg/L was used as positive control for the study with metabolic activation and (4-nitroquinoline- N-oxide at 5µM was used for the study. Incubation with the pigment did not induce an increase in unscheduled DNA synthesis.
Pigment Red 177was assessed for its potential to induce structural chromosomal aberrations (clastogenic activity) and/or changes in the number of chromosomes (aneugenic activity) in V79 cells in vitro both in the absence and the presence
of a metabolizing system (BASF 2012c). The study followed OECD testing guideline 473 and was performed under GLP.
According to an initial range-finding cytotoxicity test for the determination of the experimental doses, the following concentrations were evaluated (higher concentrations were tested but not evaluated due to strong precipitation):
1st Experiment: 4-hour exposure, 18-hour sampling time, without and with S9 mix: 0;5; 10; 20μg/mL.
2nd Experiment: 18-hour exposure, 18-hour sampling time, without S9 mix
0; 2.5; 5; 10;μg/mL; 18-hour exposure, 28-hour sampling time, without S9 mix 0;10; 20μg/mL; 4-hour exposure, 28-hour sampling time, with S9 mix; 0;5; 10; 20μg/mL
A sample of 100 metaphases for each culture was analyzed for chromosomal aberrations, except for the positive control cultures where only 50 metaphases were scored due to clearly increased aberration rates.
The negative controls gave frequencies of aberrations within the range expected for the V79 cell line. Both positive control substances, EMS and cyclophosphamide, led to the expected increase in the number of cells containing structural chromosomal aberrations.
In the main experiments no clear cytotoxicity was observed after 4 or 18 hours exposure period at any experimental condition, except in the 1st Experiment in the presence of metabolic activation where all test groups scored for chromosomal damage showed a mitotic rate of about 50% of control. However, strong test substance precipitation in culture medium was observed in all experimental parts. Thus, dose selection for cytogenetic evaluation was based on the occurrence of precipitates in the test groups. No increase in the frequency of cells containing structural or numerical chromosome aberrations was demonstrated and the pigment was found to be non clastogenic in vitro.
Justification for selection of genetic toxicity endpoint
random; more than one study needed for this endpoint.
Justification for classification or non-classification
Dangerous Substance Directive (67/548/EEC)
The available studies are considered reliable and suitable for classification purposes under 67/548/EEC. As a result the substance is not considered to be classified for genotoxicity under Directive 67/548/EEC, as amended for the 28th time in Directive 2001/59/EC.
Classification, Labelling, and Packaging Regulation (EC) No. 1272/2008
The available experimental test data are reliable and suitable for classification purposes under Regulation 1272/2008. As a result the substance is not considered to be classified for genotoxicity under Regulation (EC) No. 1272/2008, as amended for the third time in Directive (EC 618/2012).
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