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EC number: 201-248-4 | CAS number: 80-08-0
- 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:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2001
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 001
- Report date:
- 2001
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:
- Dapsone
- EC Number:
- 201-248-4
- EC Name:
- Dapsone
- Cas Number:
- 80-08-0
- Molecular formula:
- C12H12N2O2S
- IUPAC Name:
- 4,4'-sulfonyldianiline
- Details on test material:
- Dapsone, batch no. 70522014, white powder, purity 99.69%, stored at 1-10 degrees C in the dark.
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- CD-1
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River-UK Ltd
- Age at study initiation: 7 weeks
- Weight at study initiation: 26-33g
- Diet (e.g. ad libitum): availabe ad-libitum
- Water (e.g. ad libitum): availabe ad-libitum
- Acclimation period: 8 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21-23 deg C
- Humidity (%): 52-61%
- Photoperiod (hrs dark / hrs light): 12-hour light/12-hour dark cycle
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- 1% methylcellulose in water
- Details on exposure:
- Groups of 8 male mice (as there was no evidence of sex-related difference in toxicity in the range finding test) were used for each dose groups and one control group. Dose levels were 0, 43.75, 87.5, 175 mg/kg bw/day in the main experiment. A positive control group of 8 male mice received 40 mg/kg cyclophosphamide once on day 2 of the experiment.
- Duration of treatment / exposure:
- 2 consecutive days
- Frequency of treatment:
- daily once
- Post exposure period:
- none
- No. of animals per sex per dose:
- 8 males per dose (as no evidence of sex-related differences in toxicity was revealed in the range finding test)
- Control animals:
- yes, concurrent no treatment
- Positive control(s):
- cyclophosphamide, 40 mg/kg bw once on day 2
Examinations
- Tissues and cell types examined:
- Bone marrow were analysed for numbers of micronucleated polychromatic erythrocytes.
- Details of tissue and slide preparation:
- femours were excised and the content washed out with a syringe into 1% fetal bovine serum in RPMI medium
- Evaluation criteria:
- - Slides had to have at least 1000 scorable cells (PCE and NCE).
Acceptance Criteria:
The assay was considered valid if the following criteria are met:
1) the incidence of micronucleated PCE in the vehicle control group falls within or close to the historical vehicle control range
2) at least seven animals out of each group are available for analysis, and
3) the positive control chemical (CPA) induces a statistically significant increase in the frequency of micronucleated PCE.
Evaluation Criteria:
A test article is considered positive in this assay if:
1) A statistically significant increase in the frequency of micronucleated PCE occurs at least at one dose, and
2) the frequency of micronucleated PCE at such point exceeds the historical vehicle control range.
the frequency of PCE is higher than the historical control range. - Statistics:
- Statistics was applied
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- Mice treated with Dapsone at all doses exhibited frequencies of micronucleated PCE which were similar to the values for the vehicle control group and also fell within the normal range. There were no instances of statistically significant increases in micronucleus frequency for any of the groups receiving Dapsone. The mean PCE to NCE ratios of the groups given Dapsone were similar to the negative control value and fell within the historical negative control range.
Applicant's summary and conclusion
- Conclusions:
- Dapsone did not introduce micronuclei in the polychromatic erythrocytes of the bone marrow in mice treated up to 175 mg/kg/day, at a dose which limited mortality and clinical signs of toxicity were observed.
- Executive summary:
Dapsone was assessed for in vivo gentoxicity in a mouse bone marrow micronucleus assay. The potential of Dapsone to induce structural chromosomal damage and aneuploidy, by determining the frequency of micronucleated polychromatic erythrocytes in mouse bone marrow after exposure to 0 (negative control), 43.75, 87.5 and 175 mg/kg bw/day given on two consecutive days by oral gavage to groups of 8 male mice.
In a range finding test, doses from 500 to 1000 mg/kg Dapsone were administered orally by gavage as a suspension in 1% methylcellulose. Groups of three male and three female out-bred, virus-free, CD-1 mice were dosed on two consecutive days (mortality permitting). Observations were made over a two day period following the first administration and signs of toxicity recorded. No difference in toxicity was seen between males and females.
Based on the results of the range finding test, doses of 0, 43.75, 87.5 and 175 mg Dapsone/kg/d were given on two consecutive days to groups of 8 male mice. All surviving animals were killed 24 hours after receiving their final dose and femoral bone marrow smears examined. Slides from all animals were analyzed from the negative control, positive control and Dapsone-treated groups.
All animals were observed after dosing, with clinical signs and mortalities recorded. In the main study, bone marrow smears were analyzed for numbers of micronucleated polychromatic erythrocytes. The ratio of polychromatic erythrocytes to normochromatic (mature) erythrocytes was also recorded.
Negative and positive control group results were all confirmed as valid. Mice treated with Dapsone at all doses exhibited frequencies of micronucleated PCE which were similar to the values for the vehicle control group, and fell into the normal range. There were no instances of statistically significant increased in micronucleus frequency for any of the groups receiving Dapsone. The mean PCE to NCE ratios of the groups given Dapsone were similar to the negative control value and fell within the historical negative control range.
Dapsone did not introduce polychromatic erythrocytes of the bone marrow in mice treated up to 175 mg/kg/day. Limited mortality and clinical signs were observed at this dose.
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