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EC number: 215-252-9 | CAS number: 1315-01-1
- 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
Long-term toxicity to fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- fish early-life stage toxicity
- Data waiving:
- other justification
- Justification for data waiving:
- other:
- Endpoint:
- fish, juvenile growth test
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
1. HYPOTHESIS FOR THE ANALOGUE APPROACH
Sn(II) and SnIV) demonstrate the same (lack of) long-term ecotoxicity to fish
2. SOURCE AND TARGET CHEMICAL(S) (INCLUDING INFORMATION ON PURITY AND IMPURITIES)
Source substance: SnS
Target substance: SnS2
for both substances: no relevant impurities need to be considered
3. ANALOGUE APPROACH JUSTIFICATION
The test was performed well above the water solubility limit of SnS and also above the water solubility limit of SnS2. In the target substance SnS2, Sn(IV) will be present while the souce substance contains Sn(II). Toxicological studies show that SnS and SnS2 have a comparable toxicological profile. There is no information that Sn(IV) is more toxic when compared to Sn(II). No endocrine effects are described for one of the two substances. When SnS and SnS2 are dissolved also S2- gets into solution. Based on the results of the read across source study, there is no evidence that either S2- or one of the tin ions will cause long-term toxicity in fish at the concentrations which can be expected based on the water solubility of the source and target substance. Therefore, the results from this read across study, i.e., no long-term toxicity at the limit of water solubility, are considered relevant and reliable for the risk assessment.
4. DATA MATRIX
see attached read across justification. - Reason / purpose for cross-reference:
- read-across source
- Key result
- Duration:
- 28 d
- Dose descriptor:
- EL10
- Effect conc.:
- > 149 µg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- element
- Remarks:
- Sn
- Basis for effect:
- growth rate
- Key result
- Duration:
- 28 d
- Dose descriptor:
- EC10
- Effect conc.:
- > 104 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- In none of the the test groups, adverse effects were observed for SnS, i.e., Sn(II).
The test was performed well above the water solubility limit of SnS and also above the water solubility limit of SnS2. In the target substance SnS2, Sn(IV) will be present while the souce substance contains Sn(II). Toxicological studies show that SnS and SnS2 have a comparable toxicological profile. There is no information that Sn(IV) is more toxic when compared to Sn(II). No endocrine effects are described for one of the two substances. When SnS and SnS2 are dissolved also S2- gets into solution. Based on the results of the read across source study, there is no evidence that either S2- or one of the tin ions will cause long-term toxicity in fish at the concentrations which can be expected based on the water solubility of the source and target substance. Therefore, the results from this read across study, i.e., no long-term toxicity at the limit of water solubility, are considered relevant and reliable for the risk assessment. - Validity criteria fulfilled:
- yes
- Conclusions:
- EC10 > 104 mg/L (WAF) , 149 µg Sn/L mean measured concentration
- Executive summary:
In the K1-study from Chen Guilan (2021) the effect of a 28 day exposure on the growth of Rare Minnow (Gobiocypris rarus) to tin sulfide was investigated in a semi-static test according to OECD 215. The test solutions were set up as saturated concentrations with nominal concentrations of 1.04 mg/L, 3.31 mg/L, 10.4 mg/L, 33.1 mg/L and 104 mg test item/L After the suspensions were stirred for about 24 h, the test suspensions were filtered with 0.22 μm water phase polyether sulfone (PES) filter membranes, the filtrates of the nominal concentrations of 1.04 mg/L, 3.31 mg/L, 10.4 mg/L, 33.1 mg/L and 104 mg/L saturated solutions were obtained respectively, and about 2000 ml filtrate from each test concentration group were measured as test solutions directly. The test solutions were exchanged on a daily basis. The time-weighted mean measured concentrations of Sn were 17.6 μg/L, 44.3μg/L, 107 μg/L, 145 μg/L and 149 μg/L, respectively.
The test was performed well above the water solubility limit of SnS and also above the water solubility limit of SnS2. In the target substance SnS2, Sn(IV) will be present while the souce substance contains Sn(II). Toxicological studies show that SnS and SnS2 have a comparable toxicological profile. There is no information that Sn(IV) is more toxic when compared to Sn(II). No endocrine effects are described for one of the two substances. When SnS and SnS2 are dissolved also S2- gets into solution. Based on the results of the read across source study, there is no evidence that either S2- or one of the tin ions will cause long-term toxicity in fish at the concentrations which can be expected based on the water solubility of the source and target substance. Therefore, the results from this read across study, i.e., no long-term toxicity at the limit of water solubility, are considered relevant and reliable for the risk assessment.
Referenceopen allclose all
Description of key information
not toxic at the limit of water solutbility.
Key value for chemical safety assessment
Additional information
Information from an OECD 215 wiith SnS (read across source) are available. The test was performed well above the water solubility limit of SnS and also above the water solubility limit of SnS2. In the target substance SnS2, Sn(IV) will be present while the souce substance contains Sn(II). Toxicological studies show that SnS and SnS2 have a comparable toxicological profile. There is no information that Sn(IV) is more toxic when compared to Sn(II). No endocrine effects are described for one of the two substances. When SnS and SnS2 are dissolved also S2- gets into solution. Based on the results of the read across source study, there is no evidence that either S2- or one of the tin ions will cause long-term toxicity in fish at the concentrations which can be expected based on the water solubility of the source and target substance. Therefore, the results from this read across study, i.e., no long-term toxicity at the limit of water solubility, are considered relevant and reliable for the risk assessment.
An ELS study with SnS2 is in progress.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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