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EC number: 810-388-0 | CAS number: 12067-23-1
- 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

Bioaccumulation: aquatic / sediment
Administrative data
- Endpoint:
- bioaccumulation in aquatic species: fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2014-03-26 - 2014-11-07
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: no GLP, conducted on a structural analogous read-across substance
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 014
- Report date:
- 2014
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 305 B (Bioaccumulation: Semi-static Fish Test)
- Version / remarks:
- , 14 June 1996
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 850.1730 (Fish Bioconcentration Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.13 (Bioconcentration: Flow-through fish test)
- Version / remarks:
- , (2008)
- Deviations:
- no
- GLP compliance:
- no
- Remarks:
- Test performed for another registration
Test material
- Reference substance name:
- Tin sulphide
- EC Number:
- 215-248-7
- EC Name:
- Tin sulphide
- Cas Number:
- 1314-95-0
- Molecular formula:
- SSn
- IUPAC Name:
- Tin(II) sulfide
- Reference substance name:
- Tin sulfide
- IUPAC Name:
- Tin sulfide
- Test material form:
- solid: particulate/powder
- Remarks:
- migrated information: powder
Constituent 1
Constituent 2
- Radiolabelling:
- no
Test solutions
- Vehicle:
- no
- Details on preparation of test solutions, spiked fish food or sediment:
- A supersturated solution of WAFS was used. Therefore the test item was added and stirred for 24 hours on a magnetic stirplate at 23- 25°C. After stirring was stopped test substance settled down for one hour. The aqueous part was removed and used as standard solution.
Under exposure conditions the solution was changed in interval of 96 hours (qualitiy control).Fresh test solution was prepared 24 hours in advance.
Test organisms
- Test organisms (species):
- other: Gobiocypris rarus
- Details on test organisms:
- TEST ORGANISM
- Source: Fish supplier of Institute of Hydrobiology, Chinese Academy of Sciences
- Length at study initiation (lenght definition, mean, range and SD): 2.6 +- 0.5 cm
- Weight at study initiation (mean and range, SD): 0.20 +- 0.1 g
- Food type: same as during acclimation
- Amount/feeding frequency: 1-2% of body weight per day
-
ACCLIMATION
- Acclimation period: 15 days
- Acclimation conditions (same as test or not): same as test
- Type and amount of food: proprietary fish food (Protein < 36%, Fat > 2%, Fibre < 3%, Ash < 12%, Moisture < 10.0%
- Feeding frequency: dayly
- Health during acclimation (any mortality observed): no mortality, free from diseases and abnormalities
Study design
- Route of exposure:
- aqueous
- Test type:
- semi-static
- Water / sediment media type:
- natural water: freshwater
- Total exposure / uptake duration:
- 28 d
Test conditions
- Hardness:
- 119 - 122 mg/L CaCO3
- Test temperature:
- 22.2 - 22.5°C
- pH:
- 7.76 - 7.84
- Dissolved oxygen:
- 76 - 79%
- Reference substance (positive control):
- no
- Details on estimation of bioconcentration:
- Sampling and sample treatment:
At each sampling time 7 fish were removed, were killed instantly and were weigh. For calculation of test item concentration in fish, the named 7 samples were whetted with anhydrous sodium sulfat and were digested by adding 50 ml mixture of 65% nitric acid and 70% perchloric acid. In addition samples were dried and dissolved. Final solution was injected to ICP-MS after filtering with 0.22 µm millipore membran.
Water samples were divided in to two (unfiltered sample and a filtered sample through 0.22 µm millipore membran). Water samples were analysed by ICP-MS.
Results and discussion
Bioaccumulation factor
- Type:
- BCF
- Value:
- >= 24 - <= 558 dimensionless
- Time of plateau:
- 7 d
- Calculation basis:
- steady state
- Remarks on result:
- other: Conc.in environment / dose:0.01 mg/L
- Reported statistics:
- Test Validitiy:
- temperature was maintained at 23 +-2 °C
- dissolved oxygen does not fall below 60% saturation
- less than 10% mortality or adverse effects in control/ treated group
Data Processing:
7 BCF values were calculated. After 0, 3, 7, 10, 14, 21, 28 days a sample of seven fish and water samples were used for calculation. Stady state was
calculated by plotting the concentration of test item in fish against the time. Stady state was reached, if the uptake curve become approximately asymptotic to time axis (changing extent did not exceed +- 20%).
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- During the test (28 d) the range of the BCFss value of test substance is 24 - 558, when exposed to the supersaturated solution of the test item tin sulfide.
Accordingly, also ditin trisulfide is not expected to be bioaccumulative. - Executive summary:
The bioconcentration factor of tin sulfide in fish (Gobiocypris rarus) was determined with reference to OECD Guideline 305B "Bioconcentration: Semistatic Fish-Test". Fish were exposed for 28 days. After 0, 3, 7, 10, 14, 21, 28 days of exposure (0.01 mg/L test item in solution) a sample of seven fish and water samples were used for calculation of BCF. Stady state was calculated by plotting the concentration of test item in fish against the time, if the uptake curve become approximately asymptotic to time axis (changing extent did not exceed +- 20%). The results show that BCF reach the steady state at seventh day.Therefore, the steady-state period BCFss for fish was calculated from day 7 to day 28, and the mean is 558 and 24.0, respectively, according to the solubility of 0.6 µg/L of test item tin sulfide and a messured exposure concentration of 14 µg/L.
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