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EC number: 279-131-2 | CAS number: 79295-99-1
- 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 cell study: DNA damage and/or repair
- Type of information:
- other: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 1991
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
- Remarks:
- The test was conducted by means of Read Across approach. Further information was attached at section 13
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 991
- Report date:
- 1991
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 486 (Unscheduled DNA Synthesis (UDS) Test with Mammalian Liver Cells in vivo)
- Deviations:
- yes
- Remarks:
- see below
- Principles of method if other than guideline:
- Two doses only of the test compound were applied: Only two test compound concentrations were required for scoring as the test substance dosed at a limit concentration is not cytotoxic in the liver. A third dose was therefore considered unnecessary.
- GLP compliance:
- yes
- Type of assay:
- unscheduled DNA synthesis
Test material
- Reference substance name:
- Disperse Blue 291 - Similar Substance 05
- IUPAC Name:
- Disperse Blue 291 - Similar Substance 05
- Test material form:
- solid
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: ICI Barriered Animal Breeding Uni (BABU), Alderley Park, Macclesfield
- Age at study initiation:
- Weight at study initiation: 180-280 g
- Assigned to test groups randomly: yes - according to the order in which they are removed from the stock cage
- Fasting period before study:
- Housing: - pre dosing: up to 5 per cage
- for dosing: up to three per cage in a fume cupboard for a total period not exceeding 24 hours
- Diet (e.g. ad libitum): Porton Combined Diet, Special Diets Services Ltd, ad libitum
- Water (e.g. ad libitum): tap water, ad libitum
- Acclimation period: Since the animals were eventually moved in a fume cupboard, acclimatisation was not considered appropriate
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 17 - 21
- Humidity (%): 40 - 60
- Air changes (per hr):
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: corn oil
- Justification for choice of solvent/vehicle: test substance in insoluble in water
- Concentration of test material in vehicle: 125 and 200 mg/mL
- Amount of vehicle (if gavage or dermal): 10 mL/kg body weight - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: Dosing suspensions of the test substance were prepared in corn oil.
- Duration of treatment / exposure:
- single dose
- Frequency of treatment:
- once
- Post exposure period:
- 4 and 12 h after treatment
Doses / concentrationsopen allclose all
- Dose / conc.:
- 1 250 mg/kg bw/day (nominal)
- Remarks:
- in corn oil
- Dose / conc.:
- 2 000 mg/kg bw/day (nominal)
- Remarks:
- in corn oil
- No. of animals per sex per dose:
- 5 males/dose/time point in treatment group
4 males/group/time point in vehicle and positive control group - only 1 animal/group/time point scored - Control animals:
- yes, concurrent vehicle
- Positive control(s):
- 2-acetylaminofluorene [2AAF] at twelve hours and N-nitrosodimethylamine [NDMA] or 6-p-dimethylaminophenylazobenzthiazole [6BT] at four hours
Examinations
- Tissues and cell types examined:
- Hepatocytes
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: Based on acute oral toxicity study in rats, in which the acute MTD for the test substance was >5000 mg/kg bw and a range finding study in 5 males at 2000 mg/kg bw
TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields): Single oral dose by oral gavage. Slides from the animals were subsequently analysed. Of the two positive and two vehicle control animals in each experiment, only one of each was scored for induction of UDS
DETAILS OF SLIDE PREPARATION: Preparation of hepatocytes were made 4 or 12 h after dosage. Hepatocytes were prepared from treated animals by a two stage collagenase perfusion technique. Hepatocyte cultures were prepared by allowing cells to attach to plastic cover slips. Medium was removed from the dishes and replaced with fresh medium containing [3H] thymidine. After 4 h incubation at 37 °C within a 5% CO2/95% air (v/v) atmosphere, the medium was removed, the cells washed three times with medium containing unlabelled thymidine and the cultures incubated overnight with the same medium. Cultures were fixed and coverslips mounted onto microscope slides. Slides were coated with photographic emulsion and left for 14 d at 4 °C in the dark. The emulsion was developed, fixed and the cell nuclei and cytoplasm stained with Meyers haemalum and eosin Y phloxine.
Slides were examined microscopically for signs of undue cytotoxicity to enable selection of those to be examined for UDS.
METHOD OF ANALYSIS: Prior to microscopic assessment, all slides were furnished with code numbers, so that the counting was blind. The following counts were made:
- at least 25 but normally 50 cells/slide of two slides for each animal. The third slide was not normaly read, unles a total of 10 cells could not be obtained from the
first two slides examined.
- The nuclear count (the number of silver grains over the nucleus) and the cytoplasmic count (the number of grains in an adjacent, nuclear sized, most heavily labelled area of cytoplasm) were measured using an automated image analyser and the data captured directly into a computer.
- The mean net grain count (nuclear count - cytoplasmic count), the mean nuclear count and cytoplasmic counts and the percent of cells in repair (net grain count of 5 or greater) to be calculated. - Evaluation criteria:
- EVALUATION CRITERIA
Criteria for a positive response:
- The criteria outlined in the ASTM Guideline are adopted, based on the mean net group grain count and the percentage of cells in repair. A treated group showing mean net nuclear grain counts of 5 or greater and 20% or greater of the cells in repair is considered to be a positive response. A compound can only be assigned as an unequivocal genotoxin in this assay if such a response is reproduced.
Criteria for a negative response:
- A negative response is obtained where the mean net nuclear grain count of the treated cultures is less than 0, and the percentage of cells in repair is also less than 20.
VALIDATION CRITERIA
Negative Controls
Cytoplasmic counts of less than 40 are considered acceptable. Mean net nuclear grain counts for the negative controls should be less than zero.
Positive Controls
Mean net grain counts for the positive control in each experiment shall be sufficient to be regarded as an unequivocal positive response; mean net nuclear grain value of 5 or greater, with at least 20% of the cells examined in repair (ie with 5 or more net grains). - Statistics:
- difference between treated and control cultures
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Remarks:
- No significant adverse reactions to treatment
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: No adverse effects at 5000 mg/kg bw in acute oral or 2000 mg/kg body weight for four days in range finding study
RESULTS OF DEFINITIVE STUDY
- Animal Toxicity: No significant signs of acute toxic effects were observed.
Others:
Test substance caused no significant increases over the vehicle control in mean net nuclear grain count, nor in percentage of cells in repair, at either dose level (1250 or 2000 mg/kg bw) or time point (4 or 14 h) investigated. Hepatocytes from test substance treated animals had mean net nuclear grain values of less than zero. These data therefore provided no evidence for induction of UDS by test substance.
Applicant's summary and conclusion
- Conclusions:
- Under the test conditions, the test substance did not induce DNA repair in rat liver in vivo up to a limit dose of 2000 mg/kg bw.
- Executive summary:
The test substance was tested for the ability to induce unscheduled DNA synthesis (UDS) in an in vivo rat hepatocyte assay. Male Fischer 344 rats were treated with a single oral doseby gavage at 1250, or 2000 mg/kg body weight. The highest test dose, 2000 mg/kg was the limit test dose for a non-toxic test agent in this assay. Animals were killed and hepatocytes prepared four hours and twelve hours following administration of the chemical. Two independent experiments were carried out for each time point.
Hepatocytes from treated rats were exposed to [³H]-thymidine and the amount of radioactivity incorporated into the nucleus [N] and an equal area of cytoplasm [C] determined by autoradiography. The cytoplasmic grain count was subtracted from that of the nucleus. The value obtained, the mean net nuclear grain count [N-C], is an index of UDS activity. In the respective testing laboratory, no negative control animal has shown a mean net nuclear grain count greater than zero. An [N-C] of more than zero in a treated animal is therefore considered indicative of a UDS response.
Each experiment was validated by concurrent control treatments of rats with corn oil, the solvent for the test substance and with the carcinogens 2-acetylaminofluorene [2AAF] at twelve hours and N-nitrosodimethylamine [NDMA] or 6-p-dimethylaminophenylazobenzthiazole [6BT] at four hours. Solvent treated rats gave rise to mean net grain counts of less than zero, whilst hepatocytes from 2AAF, 6BT or NDMA treated animals had mean net nuclear grain counts of greater than +5. These data showed that background levels of UDS were normal and that the tester animals were responsive to known carcinogens requiring metabolic activation for genotoxic activity.
Hepatocytes from treated animals were assessed for UDS at two dose levels of 1250 and 2000 mg/kg body weight. Treatments with the test substance in no case resulted in a mean net grain count greater than zero, at either time point.
It is concluded that, when tested up to a limit dose of 2000 mg/kg body weight, the test sample did not induce DNA repair (as measured by unscheduled DNA Synthesis) in hepatocytes from rats treated in vivo.
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