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Reaction mass of disodium 4-amino-6-[[4-[(2,4-diaminophenyl)diazenyl]phenyl]]-3-((E)-[4-((E)-(2,4-diaminophenyl)diazenyl]phenyl )diazenyl)-5-hydroxynaphthalene-2,7-disulphonate and disodium 4-amino-6-((E)-(4-aminophenyl)diazenyl)-3-((E)-(4-((E)-(2,4-diaminophenyl)diazenyl)phenyl)diazenyl)-5-hydroxynaphthalene-2,7-disulfonate
EC number: 951-695-0 | 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: experimental resulta on similar substance
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 993
- Report date:
- 1993
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Disodium 4-amino-3,6-bis[[4-[(2,4-diaminophenyl)azo]phenyl]azo]-5-hydroxynaphthalene-2,7-disulphonate
- EC Number:
- 229-208-1
- EC Name:
- Disodium 4-amino-3,6-bis[[4-[(2,4-diaminophenyl)azo]phenyl]azo]-5-hydroxynaphthalene-2,7-disulphonate
- Cas Number:
- 6428-31-5
- Molecular formula:
- C34H29N13O7S2.2Na
- IUPAC Name:
- disodium 4-amino-3,6-bis({4-[(2,4-diaminophenyl)diazenyl]phenyl}diazenyl)-5-hydroxynaphthalene-2,7-disulfonate
- Test material form:
- solid: particulate/powder
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Mollegard Deutshland
- Number: 85 (50 male and 35 female)
- Age at study initiation: between 6 and 8 weeks
- Weight at study initiation: 27-48 g for male, 23-37 g for female
- Housing: mouse were housed in Macrolon Type 2 cages in optimal hygienic conditions.
- Diet: Granular Altromin N 1326
- Water: municipal water ad libitum
- Acclimation period:at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 2°C
- Humidity (%): 55 ± 10 %
- Air changes (per hr): 10 times/h
- Photoperiod: 12 h light / 12 h dark
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- Acqueous solution of ultra - amylopectin (0.7%) with the addiction of two drops of Tween 80 (polysorbate) per 10 ml of solution.
- Details on exposure:
- single oral administration for the tested item
single oral administration for the negative control
single intraperitoneal application for the positive control - Duration of treatment / exposure:
- one single application
- Frequency of treatment:
- single oral administration for the tested item
single oral administration for the negative control
single intraperitoneal application for the positive control - Post exposure period:
- 24 h and 48 h
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
1600 mg/kg
Basis:
nominal in water
- Remarks:
- Doses / Concentrations:
800 mg/kg
Basis:
nominal in water
- Remarks:
- Doses / Concentrations:
400 mg/kg
Basis:
nominal in water
- Remarks:
- Doses / Concentrations:
1200 mg/kg
Basis:
nominal in water
- No. of animals per sex per dose:
- Dose 1600 mg/kg: Observation time: 48 h, 5 male and 5 female
Dose 1600 mg/kg: Observation time: 24 h, 5 male and 5 female
Dose 800 mg/kg: Observation time: 24 h, 5 male and 5 female
Dose 400 mg/kg: Observation time: 24 h, 5 male and 5 female
Dose 1200 mg/kg: Observation time: 24 h, 5 male and 5 female
Positive control: Dose 80 mg/kg, Observation time: 24 h, 5 male and 5 female
- Control animals:
- yes
- Positive control(s):
- Name: cyclophosphamide
Supplier: SIGMA CHMIE Gmbh
- Route of administration: intraperitoneal
- Doses / concentrations: 80 mg/kg
- Application volume: 0.1 ml/10 g body weight
- Solvent: water for injection
The preparations of the positive control substance were freshly prepared before administration.
Examinations
- Tissues and cell types examined:
- The cells suspension was obtained from the extraction of bone marrow from the medullary canal of femurs.
- Details of tissue and slide preparation:
- The cells suspension was treated and the specimens colored following Pappenheimer's method.
2000 polychromatic erythrocytes per animal were examined microscopically in order to determine the presence and the number o micronuclei.
- Evaluation criteria:
- The classification of micronuclei was performed using the following criteria:
- Micronuclei are round, rarely oval or crescent shaped.
- They have a sharp contour.
- They are uniformly colored and are approximately from 1/20 to 1/5 of the diameter of the erythrocytes.
- It is usually only a micronucleus present.
The ratio of polychromatic to normochromatic erythrocytes was determined individually for each animal by counting a total of 1000 erythrocytes. - Statistics:
- The statistics of the test were riported in the study report.
The calculations were performed using the program MUTAI (SOP M/EDV/036) performed on a 386 AT DIGICOM. The program is written in PowerBASIC and is extensively tested.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- valid
- Positive controls validity:
- valid
Any other information on results incl. tables
No
signs of systemic intoxication were observed in female
mice for the sigle oral doses of 1600,
800 and 400 mg/kg.
The
highest
dose of
1600 mg/kg
causes the death of 2 male mice within 24h.
Conseguently the dose was lowered to 1200 mg/kg. The
other doses of 800 and 400 mg/kg were tolerate without
symptoms.
The results show no citotoxic effect of any chromosomal damages.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
No cytotoxic effect of the test substance were observed.
No potential of chromosomal damages were observed.
- Executive summary:
This end point was assessed following the OECD 474 and it was performed in GLP conditions. Micronuclei arise as a result of damage to the chromosomes or the spindle apparatus through a mutagenic active substance during the mitotic cell division in proliferating bone marrow cells. The results show no increased incidence of micronucleated polychromatic erythrocytes
The calculated frequency of the micronuleated polychromatic erythrocytes of the groups treated with the substance was between 0,17 and 0,42 %.The observed frequency corresponds to the data reported in the literature which is related to the spontaneous rate of occurrence of micronuclei in polychromatic erythrocytes.
Hence a potential of chromosomal damages or damage to the mitotic apparatus could be excluded for the tested substance.
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