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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 / bone marrow chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- December 3, 1991 to June 9, 1992
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 992
- Report date:
- 1992
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- GLP compliance:
- yes
- Type of assay:
- mammalian bone marrow chromosome aberration test
Test material
- Reference substance name:
- Reaction mass of tris(dipentyldithiocarbamato-S,S')antimony and [bis(2-ethylhexyl)dithiocarbamato-S,S']bis(dipentyldithiocarbamato-S,S')antimony and bis[bis(2-ethylhexyl)dithiocarbamato-S,S'](dipentyldithiocarbamato-S,S')antimony and tris[bis(2-ethylhexyl)dithiocarbamato-S,S']antimony
- IUPAC Name:
- Reaction mass of tris(dipentyldithiocarbamato-S,S')antimony and [bis(2-ethylhexyl)dithiocarbamato-S,S']bis(dipentyldithiocarbamato-S,S')antimony and bis[bis(2-ethylhexyl)dithiocarbamato-S,S'](dipentyldithiocarbamato-S,S')antimony and tris[bis(2-ethylhexyl)dithiocarbamato-S,S']antimony
- Test material form:
- liquid: viscous
1
Test animals
- Species:
- mouse
- Strain:
- ICR
- Sex:
- male/female
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- Corn oil
- Details on exposure:
- Initial micronucleus assay: 5/sex/time point/group for CP (30 mg/kg bw), 0, 1250, 2500, or 5000 mg/kg groups; Confirmatory micronucleus assay: 6/sex/group for CP (30 mg/kg bw), 0, 2500, or 5000 mg/kg bw groups
- Control animals:
- yes
Results and discussion
Test results
- Key result
- Sex:
- not specified
- Genotoxicity:
- positive
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
Any other information on results incl. tables
Evaluations: No mortality or clinical signs were observed in either male or female mice in the micronucleus assay. Bone marrow cells, collected 24, 48, and 72 hours after treatment, were examined microscopically for micronucleated polychromatic erythrocytes. No reduction in the ratio of polychromatic erythrocytes to total erythrocytes was observed in the male or female treatment groups suggesting that the test article did not induce bone marrow toxicity. No significant increase in micronucleated polychromatic erythrocytes was observed at 24, 48 or 72 hours after dose administration in the male mice. However, a significant increase in micronuclcated polychromatic erythrocytes was observed at dose levels of 2500 and 5000 mg/kg in female mice, only at the 48 hour sampling time.
In order to confirm the statistical increase of micronucleated polychromatic erythrocytes observed in females at dose levels of 2500 and 5000 mg/kg bw at the 48 hour bone marrow collection time, a confirmatory micronucleus assay was initiated. Male and female ICR mice were exposed to 2500 or 5000 mg/kg bw of antimony dipentyldithiocarbamate which was administered in a total volume of 20 ml/kg as a single IP injection. No mortality or clinical signs were observed in either male or female mice in the confirmatory micronucleus assay. Bone marrow cells, collected 48 hours after dose administration, were examined microscopically for rnicronucleated polychromatic erythrocytes. No reduction in the ratio of polychromatic erythrocytes to total erythrocytes was observed in the male or female treatment groups suggesting that the test article did not induce bone marrow toxicity. No significant increase in micronucleated polychromatic erythrocytes was observed in the male mice; however, a significant increase in micrornucleated polychromatic erythrocytes was observed at dose levels of 2500 and 5000 mg/kg bw in female mice.
The results of the initial and confirmatory assay indicate that under the conditions described in this study, the test substance did induce a reproducible, significant treatment-related increase in the incidence of micronucleated polychromatic erythrocytes in the bone marrow of female mice at the 48 hour sampling time. Considerable inter-animal variability was observed in the dose groups that were significantly elevated above the vehicle control group. The test substance was concluded to be weakly positive in the mouse micronucleus assay.
Applicant's summary and conclusion
- Conclusions:
- Under the conditions of the study, the test substance was concluded to be weakly positive in the mouse micronucleus assay.
- Executive summary:
A study has been conducted on the test substance. The study conducted was a mouse micronucleus test performed under GLP conditions. Although no guidelines were stated within the study, the methodology is similar or equivalent to the standardized OECD 474; hence the study has been assigned a Klimisch score of 2.
The study was performed on ICR mice, utilizing corn oil as the vehicle. In the pilot study, antimony dipentyldithiocarbamate was administered by a single IP injection to 2 males/group at 1, 10, 100, or 1000 mg/kg bw and to 5 animals/sex at 5000 mg/kg bw in corn oil with dosing volume of 20 ml/kg bw. In the absence of mortality in the pilot study, the dose levels for the micronucleus assay were set at 1250, 2500 or 5000 mg/kg bw.
Dosing solution of the test substance in corn oil (250 mg/ml) was analyzed and confirmed the concentration using atomic absorption.
No mortality or clinical signs were observed in either male or female mice in the micronucleus assay. Bone marrow cells, collected 24, 48, and 72 hours after treatment, were examined microscopically for micronucleated polychromatic erythrocytes. No reduction in the ratio of polychromatic erythrocytes to total erythrocytes was observed in the male or female treatment groups suggesting that the test substance did not induce bone marrow toxicity. No significant increase in micronucleated polychromatic erythrocytes was observed at 24, 48 or 72 hours after dose administration in the male mice. However, a significant increase in micronuclcated polychromatic erythrocytes was observed at dose levels of 2500 and 5000 mg/kg in female mice, only at the 48 hour sampling time.
In order to confirm the statistical increase of micronucleated polychromatic erythrocytes observed in females at dose levels of 2500 and 5000 mg/kg bw at the 48 hour bone marrow collection time, a confirmatory micronucleus assay was initiated. Male and female ICR mice were exposed to 2500 or 5000 mg/kg bw of the test substance which was administered in a total volume of 20 ml/kg as a single IP injection. No mortality or clinical signs were observed in either male or female mice in the confirmatory micronucleus assay. Bone marrow cells, collected 48 hours after dose administration, were examined microscopically for rnicronucleated polychromatic erythrocytes. No reduction in the ratio of polychromatic erythrocytes to total erythrocytes was observed in the male or female treatment groups suggesting that the test article did not induce bone marrow toxicity. No significant increase in micronucleated polychromatic erythrocytes was observed in the male mice; however, a significant increase in micrornucleated polychromatic erythrocytes was observed at dose levels of 2500 and 5000 mg/kg bw in female mice.
The results of the initial and confirmatory assay indicate that under the conditions described in this study, the test substance did induce a reproducible, significant treatment-related increase in the incidence of micronucleated polychromatic erythrocytes in the bone marrow of female mice at the 48 hour sampling time. Considerable inter-animal variability was observed in the dose groups that were significantly elevated above the vehicle control group. The test substance was concluded to be weakly positive in the mouse micronucleus assay.
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