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EC number: 274-675-7 | CAS number: 70571-81-2
- 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
Genetic toxicity: in vitro
Administrative data
- 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:
- 2000-09-26 - 2000-10-13
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 000
- Report date:
- 2000
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.5100 - Bacterial Reverse Mutation Test (August 1998)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- bacterial reverse mutation assay
Test material
- Reference substance name:
- Sodium 4-[[3-(acetylamino)phenyl]amino]-1-amino-9,10-dihydro-9,10-dioxoanthracene-2-sulphonate
- EC Number:
- 274-675-7
- EC Name:
- Sodium 4-[[3-(acetylamino)phenyl]amino]-1-amino-9,10-dihydro-9,10-dioxoanthracene-2-sulphonate
- Cas Number:
- 70571-81-2
- Molecular formula:
- C22H17N3O6S.Na
- IUPAC Name:
- sodium 4-[(3-acetamidophenyl)amino]-1-amino-9,10-dioxo-9,10-dihydroanthracene-2-sulfonate
- Test material form:
- solid: particulate/powder
Constituent 1
Method
Species / strain
- Species / strain / cell type:
- S. typhimurium TA 1535, TA 1537, TA 98, TA 100 and TA 102
- Metabolic activation:
- with and without
- Metabolic activation system:
- rat liver S9 mix
- Test concentrations with justification for top dose:
- The test compound was suspended in deionized water and a stock solution of 50 mg/mL was prepared for the highest concentration, which provided a final concentration of 5000 µg/plate. Further dilutions of 1600, 500, 160 and 50 µg/plate were used in the first plate incorporation test.
In the second experiment with the strain TA 98 dilutions of 5000, 1600, 500, 160, 50, 16, 5 and 1.6 µg/plate were chosen.
Visible precipitation of the test compound on the plates was observed at 1600 µg/plate and above.
Because of heavy precipitation of the test compound the bacterial lawn could only be evaluated at the dose level of 1600 µg/plate and lower concentrations.
In the first plate incorporation test toxicity was observed at a concentration of 1600 µg/plate in the absence of metabolic activation with the tester strain TA 100. - Vehicle / solvent:
- Solvent: deionised water
Controlsopen allclose all
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- Positive controls:
- yes
- Remarks:
- Without metabolic activation
- Positive control substance:
- 9-aminoacridine
- 2-nitrofluorene
- sodium azide
- mitomycin C
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- Positive controls:
- yes
- Remarks:
- with metabolic activation
- Positive control substance:
- other: 2-aminoanthracene
- Details on test system and experimental conditions:
- METHOD OF APPLICATION: in medium; in agar (plate incorporation)
- Evaluation criteria:
- Assay considered valid if:
-Solvent control data are within the laboratory´s normal control range for the spontaneous mutant frequency
-Positive controls induced increases in the mutation frequency which were both statistically significant and within the laboratory´s normal range
Test compound is classified as mutagenic if has either following effects:
-it produces at least a 2-fold increase in the mean number of revertants per plate of at least one of the tester strains over the mean number of revertants per plate of the appropriate vehicle control at complete bacterial background lawn
-it induces a dose-related increase in the mean number of revertants per plate of at least one of the tester strains over the mean number of revertants per plate of the appropriate vehicle control in at least two to three concentrations of the test compound at complete bacterial background lawn.
If test substance does not achieve either of the above criteria, it is considered to show no evidence of mutagenic activity in this system
Results and discussion
Test resultsopen allclose all
- Species / strain:
- S. typhimurium TA 1535
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity, but tested up to precipitating concentrations
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Species / strain:
- S. typhimurium TA 1537
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity, but tested up to precipitating concentrations
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Species / strain:
- S. typhimurium TA 100
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Species / strain:
- S. typhimurium TA 102
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity, but tested up to precipitating concentrations
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Species / strain:
- S. typhimurium TA 98
- Metabolic activation:
- without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity, but tested up to precipitating concentrations
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Key result
- Species / strain:
- S. typhimurium TA 98
- Metabolic activation:
- with
- Genotoxicity:
- ambiguous
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity, but tested up to precipitating concentrations
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- TEST-SPECIFIC CONFOUNDING FACTORS
- Effects of pH: -
- Effects of osmolality: -
- Evaporation from medium: -
- Water solubility: > 10 g/L
- Precipitation: yes; from 1600 µg/plate onwards
- Definition of acceptable cells for analysis: -
- Other confounding effects:
HISTORICAL CONTROL DATA (with ranges, means and standard deviation and confidence interval (e.g. 95%)
- Positive historical control data: yes
- Negative (solvent/vehicle) historical control data: yes - Remarks on result:
- other: no dose-dependency observed
Applicant's summary and conclusion
- Conclusions:
- In the presence of metabolic activation, treatment of the bacterial strain with Acid Blue 324 resulted in increases in the number of revertant colonies with the strain TA 98 without showing any dose-dependency; hence not meeting the criteria for a positive result.
- Executive summary:
Acid Blue 324 was tested for mutagenicity with the strains TA 100, TA 1535, TA 1537, TA 98 and TA 102 of Salmonella typhimurium. This mutagenicity study was conducted (plate incorporation test), in the absence and in the presence of a metabolizing system derived from a rat liver homogenate. Additionally a repeat of the plate incorporation test was performed with the strain TA 98 in the presence of S9-mix.
For both studies, the compound was suspended in deionized water, and each bacterial strain was exposed to 5 dose levels, in the repetition with the strain TA 98 to 8 dose levels.
Visible precipitation of the test compound on the plates was observed at 1600 µg/plate and above. The concentrations for the first plate incorporation test were 50, 160, 500, 1600 and 5000 µg/plate. Because of the increased mutation frequencies (2.1 to 5.2 -fold without dose-dependency) observed with the strain TA 98, dose levels from 1.6 to 5000 µg/plate were chosen for the second plate incorporation test with TA98 in the presence of the metabolizing system.
Control plates without mutagen showed that the number of spontaneous revertant colonies was within the laboratory's historical control range. All the positive control compounds showed the expected increase in the number of revertant colonies.
In the first plate incorporation test toxicity was observed at a concentration of 1600 µg/plate in the absence of metabolic activation with the tester strain TA 100.
In the presence of metabolic activation, treatment of the bacterial strain with Acid Blue 324 resulted in increases in the number of revertant colonies with the strain TA 98 without showing any dose-dependency; hence not meeting the criteria for a positive result.
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