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Diss Factsheets
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EC number: - | CAS number: -
- 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 somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- other: read across from similar substance
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 985
- Report date:
- 1985
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- GLP compliance:
- not specified
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Trisodium bis[3-hydroxy-4-[(2-hydroxy-1-naphthyl)azo]-7-nitronaphthalene-1-sulphonato(3-)]chromate(3-)
- EC Number:
- 260-906-9
- EC Name:
- Trisodium bis[3-hydroxy-4-[(2-hydroxy-1-naphthyl)azo]-7-nitronaphthalene-1-sulphonato(3-)]chromate(3-)
- Cas Number:
- 57693-14-8
- Molecular formula:
- C40H20CrN6O14S2.3Na
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River GmbH, WIGA, D-8741 Sulzfeld, FRG
- Weight at study initiation: mean 26.7 g
- Assigned to test groups randomly: yes
- Housing: individually in Makrolon cages, type M I
- Diet (e.g. ad libitum): Standardized pelleted feed (Kliba Haltungsdiät, Klingentalmühle AG, CH-4303 Kaiseraugst, Switzerland); ad libitum
- Water (e.g. ad libitum): drinking water from bottles; ad libitum
- Acclimation period: about one week
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20 - 24
- Humidity (%): 30 - 70
- Photoperiod (hrs dark / hrs light): 12 / 12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: CMC (carboxymethyl cellulose)
- Concentration of test material in vehicle: 8.5, 17, 34 g/100 ml
- Amount of vehicle (if gavage or dermal): 20 ml/kg bw - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
All test substance formulations were prepared immediately before administration. The amount of substance or volume to be administered was related to the specific weight of the individual animals on the day of the experiment. - Duration of treatment / exposure:
- 16, 24, 48 h for the highest dose of test material; 24 h for all other dose groups and controls
- Frequency of treatment:
- single application
- Post exposure period:
- 16, 24, 48 h for the highest dose of test material; 24 h for all other dose groups and controls
Doses / concentrations
- Remarks:
- Doses / Concentrations:
1700, 3400, 6800 mg/kg bw
Basis:
nominal conc.
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- cyclophosphamide;
- Route of administration: oral by gavage
- Doses / concentrations: 40 mg/kg bw
Examinations
- Tissues and cell types examined:
- bone marrow of the two femora
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
In the determination of the acute oral toxicity all animals survived the high dose of 6810 mg/kg body weight without any clinical signs or symptoms. A volume as high as 20 ml/kg body weight had to be selected in order to be able do administer this amount. Higher doses suspended in an 0.5 % aqueous CMC formulation led to a viscous mass which could no longer be administered.
DETAILS OF SLIDE PREPARATION:
Smears were prepared using slides with ground edges, the preparations were dried in the air and subsequently stained. Staining in eosin and methylene blue solution for 5 minutes. Rinsed in aqua dest., then placed in fresh aqua dest. for 2 or 3 minutes. Staining in Giemsa solution for 12 minutes. After being rinsed twice in aqua dest. and clarified in xylene, the preparations were embedded in Entellan.
METHOD OF ANALYSIS:
As a rule, 1000 polychromatic erythrocytes from each of the male and female animals of every test group are evaluated and investigated for micronuclei. The normochromatic erythrocytes (= normocytes), which occur, are also scored. - Evaluation criteria:
- The increase in the micronucleus rate in polychromatic erythrocytes of treated animals as compared with the solvent control group provides an index of a chromosome breaking (clastogenic) effect or of a spindle activity of the substance tested.
- Statistics:
- Two statistical tests were used to answer the questions of whether there are significant differences between control group and dose group or between the individual dose groups concerning the rate of micronuclei in polychromatic erythrocytes: first, the exact test according to FISHER, which was applied to register significant differences between the relative frequencies of a characteristic of two groups, and, second, the asymptotic U test according to MANN-WHITNEY (rank test modified according to WILCOXON). The relative frequencies of cells with micronuclei per animal were use d
as a criterion of the rank determination for the U test.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF DEFINITIVE STUDY
- Clinical signs of toxicity in test animals: The single oral administration in doses of 6800 mg/kg, 3400 mg/kg or 1700 mg/kg body weight was tolerated by all animals without any signs of toxicity.
-Necropsy: The gross-pathological examination of the animals sacrificed at the end of the study did not reveal any changes of the internal organs which could the attributed to the test substance administered.
Any other information on results incl. tables
Results:
Substance | Dose (mg/kg bw) | Interval: 16 hours | Interval: 24 hours | Interval: 48 hours | |||||||||
Polychromatic erythrocytes investigated | Normocytes / 10000 polychromatic erythrocytes | Cells with micronuclei | Polychromatic erythrocytes investigated | Normocytes / 10000 polychromatic erythrocytes | Cells with micronuclei | Polychromatic erythrocytes investigated | Normocytes / 10000 polychromatic erythrocytes | Cells with micronuclei | |||||
per 1000 polychromatic erythrocytes | per 1000 normochromatic erythrocytes | per 1000 polychromatic erythrocytes | per 1000 normochromatic erythrocytes | per 1000 polychromatic erythrocytes | per 1000 normochromatic erythrocytes | ||||||||
vehicle control, 0.5% CMC | - | 10000 | 3485 | 1.8 | 0 | ||||||||
Säurebraun 6229 | 6800 | 10000 | 2988 | 1.4 | 1.34 | 10000 | 4349 | 1.4 | 1.61 | 10000 | 4359 | 1.3 | 1.61 |
Säurebraun 6229 | 3400 | - | 10000 | 3506 | 1.4 | 0.86 | |||||||
Säurebraun 6229 | 1700 | - | 10000 | 4307 | 1.9 | 0.46 | |||||||
Cyclophospamide | 40 | - | 10000 | 5623 | 23.4 | 1.78 |
Applicant's summary and conclusion
- Conclusions:
- The analogue substance was tested for chromosome aberration potential following OECD 476, by oral administration. The tested sample under the experimental conditions, did not induce chromosome breaking (clastogenic) effect or a spindle activity in polychromatic erythrocytes of the bone marrow of the femora mice.
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