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Reaction mass of lithium sodium hydrogen 4-amino-6-({5-[(5-chloro-2,6-difluoropyrimidin-4-yl)amino]-2-sulfonatophenyl}diazenyl)-5-hydroxy-3-[(4-{[2-(sulfonatooxy)ethyl]sulfonyl}phenyl)diazenyl]naphthalene-2,7-disulfonate and lithium sodium hydrogen 4-amino-6-({5-[(5-chloro-2,6-difluoropyrimidin-4-yl)amino]-2-sulfonatophenyl}diazenyl)-5-hydroxy-3-{[4-(vinylsulfonyl)phenyl]diazenyl}naphthalene-2,7-disulfonate
EC number: 941-533-7 | 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
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- test procedure in accordance with generally accepted scientific standards and described in sufficient detail
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 986
- Report date:
- 1986
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Principles of method if other than guideline:
- The test was conducted according to the method published by Salamone et al., 1980.
Salamone M, Heddle J, Stuart E and Katz M, 1980. Towards and improved micronucleus test. Studies on 3 model agents, mitomycin C, cyclophosphamide and dimethylbenzanthracene. Mutat. Res. 74:347-356. - GLP compliance:
- yes
- Type of assay:
- other: Mammalian erythrocyte micronucleus test
Test material
- Reference substance name:
- Lithium sodium hydrogen 4-amino-6-(5-(5-chloro-2,6-difluoropyrimidin-4-ylamino)-2-sulfonatophenylazo)-5-hydroxy-3-(4-(2-(sulfonatooxy)ethylsulfonyl)phenylazo)naphthalene-2,7-disulfonate
- EC Number:
- 401-560-2
- EC Name:
- Lithium sodium hydrogen 4-amino-6-(5-(5-chloro-2,6-difluoropyrimidin-4-ylamino)-2-sulfonatophenylazo)-5-hydroxy-3-(4-(2-(sulfonatooxy)ethylsulfonyl)phenylazo)naphthalene-2,7-disulfonate
- Cas Number:
- 108624-00-6
- Molecular formula:
- C28H(21-x-y)ClF2Li(x)N8Na(y)O16S5
- IUPAC Name:
- Lithium sodium hydrogen-4-amino-6-(5-(5-chloro-2,6-difluoropyrimidine-4-ylamino)-2-sulfonatophenylazo)-5-hydroxy-3-(4-(2-(sulfonatooxy)ethylsulfonyl)phenylazo)naphthalene-2,7-disulfonate
- Test material form:
- solid: particulate/powder
- Details on test material:
- Reactive Blue FC 05717
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: F. Winkelmann, Borchen
- Age at study initiation: 8 to 12 wk
- Weight at study initiation: 23-34 g
- Housing: Makrolon Type II cage
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum):ad libitum
- Acclimation period: one wk
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21-22°C
- Humidity (%): 44-50%
- Photoperiod (hrs dark / hrs light): 12:12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: 0.5% aqueous cremophor emulsion
- Justification for choice of solvent/vehicle: the test substance has a better dispersibility in this vehicle
- Amount of vehicle (if gavage or dermal): 20 mL/kg bw - Duration of treatment / exposure:
- 24, 48 and 72 h for three separate test groups dosed at 7500 mg/kg bw
24 h for negative and positive control groups - Frequency of treatment:
- Once
Doses / concentrations
- Dose / conc.:
- 7 500 mg/kg bw (total dose)
- No. of animals per sex per dose:
- Ten (five males and five females) per dose group including negative and positive control groups
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide
- Route of administration: Oral gavage
- Doses / concentrations: 20 mg/kg bw
- Dose volume: 10 mL/kg bw
Examinations
- Tissues and cell types examined:
- Bone marrow from femur was obtained and the polychromatic erythrocytes were examined.
- Details of tissue and slide preparation:
- TREATMENT AND SAMPLING TIMES:
Three groups of mice were treated with the test substance and were sacrificed at 24 h interval (i.e., at 24, 48 and 72 h) to obtain the bone marrow samples.
DETAILS OF SLIDE PREPARATION:
The bone marrow preparation was stained with Ames Hema-Tek slide stainer, followed by treatment with methanol and washing with demineralised water. Once the slides are dried, they ere observed under microscope.
METHOD OF ANALYSIS: 1000 polychromatic erythrocytes were examined per animal and the frequency of micronucleated cells among them were determined.
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- not specified
- Vehicle controls validity:
- not specified
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- - Following treatment with the test substance, no relevant increase in the number of micronucleated PCEs over the concurrent negative control was observed at the treated dose and at all the exposure intervals. A marked increase in the frequency of micronucleated PCEs was noticed in the positive control group.
- Bone marrow cell toxicity: not specified
Applicant's summary and conclusion
- Conclusions:
- Under the study conditions, the test substance did not induce micronuclei in the polychromatic erythrocytes of the treated mice.
- Executive summary:
A study was conducted to determine the in vivo genetic toxicity of the test substance in NMRI mice according to the method published by Solomone et al, 1980. The ability of the test substance to induce cytogenetic damage and/or disruption of the mitotic apparatus in rat bone marrow was investigated by measuring the induction of micronuclei in polychromatic erythrocytes. NMRI mice (5 per sex per group) were exposed to a single oral gavage dose of the test substance at 0 and 7500 mg/kg bw for 24, 48 and 72 h. A positive control group (cyclophosphamide, 20 mg/kg bw) was also tested. Following treatment with the test substance, no relevant increase in the number of micronucleated PCEs over the concurrent negative control was observed at any of the exposure interval. A marked increase in the frequency of micronucleated PCEs was noticed in the positive control group. The values for the positive and negative controls were within the expectation ranges. The experiment was therefore considered valid. Under the study conditions, the test substance did not induce micronuclei in the polychromatic erythrocytes of the treated mice (Herbold, 1986b).
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