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EC number: 215-248-7 | CAS number: 1314-95-0
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
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- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
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- Solubility in organic solvents / fat solubility
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- Flash point
- Auto flammability
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- 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
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- Endpoint summary
- Stability
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- 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
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- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
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- Additional toxicological data

Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: genome mutation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2009-01-04 to 2010-03-16
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP and guideline compliant study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2011
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- , 1997
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Tin sulfide
- IUPAC Name:
- Tin sulfide
- Reference substance name:
- Tin sulphide
- EC Number:
- 215-248-7
- EC Name:
- Tin sulphide
- Cas Number:
- 1314-95-0
- Molecular formula:
- SSn
- IUPAC Name:
- stannanethione
- Test material form:
- solid: particulate/powder
- Remarks:
- migrated information: powder
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: BioTest s. r. o., Pod Zámkem 279, Konárovice, Czech Republic
- Age at study initiation: 8-10 weeks
- Weight at study initiation: Males 250 g, Females 170 g
- Assigned to test groups randomly: yes, under following basis: sorted according to the body weight and randomly allocated to the dose group taking animals from each range group
- Water: ad libitum
- Acclimation period: 7 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20-24 °C
- Humidity (%): 30-70 %
- Photoperiod (hrs dark / hrs light): 12 hrs/12 hrs
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: methylcellulose 0.5%
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
Each animal in treated groups received the appropriate dose of Test item suspension orally by gavage in the volume of 1 mL per 100 g body weight. The animals in the negative control group received the appropriate volume of saline solution by the same way. The animals in the positive control group were administered cyclophosphamide solution at the dose of 20 mg/kg by a single intraperitoneal application in the volume of 1 mL per 100 g body weight.
The following procedure was adopted for the preparation of a homogenous suspension: at first the we ighed amount of the respective substance was ground in a grinding mortar with a small volume of carrier liquid. Then the content of the mortar was transferred into a calibrated vessel. Another amount of carrier liquid was poured into the mortar, stirred and the mortar with the pestle was rinsed, the rinsing liquid was added into the same calibrated vessel. This rinsing procedure was repeated once more. Then the volume in the calibrated vessel was made up with the carrier liquid to the required volume and mixed. Immediately before the application, the suspension was again stirred by means of an electromagnetic
stirrer. - Duration of treatment / exposure:
- Duration of administration was 10-20 s
- Frequency of treatment:
- single exposure
- Post exposure period:
- One half of the animals from each group were sacrificed 24 hours after the administration and the other half of animals were sacrificed 48 hours after the administration.
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 mg/kg bw/day (actual dose received)
- Remarks:
- single exposure
- Dose / conc.:
- 500 mg/kg bw/day (actual dose received)
- Remarks:
- single exposure
- Dose / conc.:
- 1 000 mg/kg bw/day (actual dose received)
- Remarks:
- single exposure
- Dose / conc.:
- 2 000 mg/kg bw/day (actual dose received)
- Remarks:
- single exposure
- No. of animals per sex per dose:
- Number of animals per group: 10 Males + 10 Females
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- cyclophosphamide
- Route of administration: i.p.
- Doses / concentrations: 20 mg/kg
Examinations
- Tissues and cell types examined:
- bone marrow (mean number of NCPE, PCE, NCE and proportion of immature erythrocytes)
- Details of tissue and slide preparation:
- During the necropsy the bone marrow was extracted from femur using bovine serum into a labeled test tube. The cells were centrifuged (1000 rpm for 10 min). The supernatant was removed and the sediment was resuspended in approx. 4 drops of bovine serum. Smear preparations from this suspension were made in duplo for each animal and fixed with methanol for 5 min and then stained with Giemsa–Romanowski (1:10) for 15-20 min.
All the slides were independently coded before blind microscopic analysis. - Evaluation criteria:
- At least 2000 polychromatic (immature) erythrocytes per animal were scored for the incidence of micronuclei under the microscope. The proportion of polychromatic (immature) among total (immature + mature or polychromatic + normochromatic) erythrocytes were determined for each animal by counting a total of at least 200 erythrocytes.
- Statistics:
- The analyzed data were tested for normality (Kolmogorov–Smirnov test) and homogeneity of variance (Bartlett’s test).
The data for males and females were separately analyzed using ANOVA followed by Dunnett’s Multiple Comparison Test. The F-test in the ANOVA tests whether there are any significant differences amongst the means at the 95.0 % confidence level.
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
- Additional information on results:
- Tin sulphide does not produce micronuclei in the immature erythrocytes in the conditions of the test.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results: negative
Tin sulfide does not produce micronuclei in the immature erythrocytes in the conditions of the test. - Executive summary:
The potential of tin sulfide to cause cytogenetic damage was assessed in a Mammalian Erythrocyte Micronucleus Test according to OECD guideline 474.
No changes in health status and condition of the animals in any of the groups were recorded during the acclimation and during the study. No significant changes of mean body weight were observed in the animals during the study. All the values of number of NPCE in all dose groups were within the reference range for negative control group. No statistically significant higher values of number of NPCE in any of the dose groups (up to 11 of micronuclei) as compared to negative control group (up to 13 of micronuclei) were noted. Statistically significant differences were observed in the positive control group (NPCE – up to 38 of micronuclei) as compared to control group.
Tin sulfide does not induce damage to the chromosomes or the mitotic apparatus of erythroblasts.
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