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EC number: 269-105-9 | CAS number: 68187-54-2 This substance is identified in the Colour Index by Colour Index Constitution Number, C.I. 77865.
- 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
Ecotoxicological Summary
Administrative data
Hazard for aquatic organisms
Freshwater
- Hazard assessment conclusion:
- no hazard identified
Marine water
- Hazard assessment conclusion:
- no hazard identified
STP
- Hazard assessment conclusion:
- no hazard identified
Sediment (freshwater)
- Hazard assessment conclusion:
- no hazard identified
Sediment (marine water)
- Hazard assessment conclusion:
- no hazard identified
Hazard for air
Air
- Hazard assessment conclusion:
- no hazard identified
Hazard for terrestrial organisms
Soil
- Hazard assessment conclusion:
- no hazard identified
Hazard for predators
Secondary poisoning
- Hazard assessment conclusion:
- no potential for bioaccumulation
Additional information
Conclusion on classification
Tin antimony grey cassiterite is a poorly soluble inorganic substance. In accordance with ECHA Guidance on the Application of the CLP Criteria (V 5.0, July 2017), “where the compound is sufficiently poorly soluble that the levels dissolved following normal attempts at solubilisation do not exceed the available L(E)C50, it is the rate and extent of transformation, which must be considered.”
The release of antimony, tin and vanadium in environmental media at pH 6 and 8 was determined in an OECD transformation/dissolution test (Klawonn, 2018) with the higher release at pH 8.
Short-term (acute) aquatic hazard:
In accordance with ECHA Guidance on the Application of the CLP Criteria (V 5.0, July 2017), “A poorly soluble substance is evaluated for classification by comparing the dissolved metal ion level resulting from the TDp at 7d, at a loading rate of 1 mg/l with the acute ERV as determined for the (soluble) metal ion.”
The release of antimony, tin and vanadium from the pigment at a loading of 1 mg/L at pH 8 after 7 days results in concentrations of 0.40 µg/L, 5.71 µg/L and 0.18 µg/l, respectively, and are thus significantly lower (more than hundredfold up to more than thousandfold) than the corresponding acute Ecotoxicity reference levels (ERVs) (Sb = > 1770µg/L (EU, 2008), Sn = 9800 µg/L and V = 693 µg/L (MECLAS v 5.2)). Applying the concept of additivity, the sum of the respective ratios of dissolved metal ion concentrations in the T/Dp (loading of 1 mg/L, 7 d, pH 6 and pH 8) and corresponding acute ERVs is also well below 1 (< 0.01). Thus, the pigment does not meet classification criteria for an acute aquatic hazard under CLP.
Two supporting non-GLP studies on the acute toxicity of the dispersed pigment on zebrafish (OECD TG 203) and Daphnia magna (OECD TG 202) provide further evidence on the low potential for acute aquatic toxicity since effects were not observed at 100 mg/L (nominal, dispersed) and the respective LC/EC50 values are estimated with > 100 mg/L (nominal, dispersed). Thus, according to Table 4.1.0 (a) of Regulation (EC) No 1272/2008, tin antimony grey cassiterite would also not meet criteria for an acute aquatic hazard.
Thus, in accordance with Figure IV.4 “Classification strategy for determining acute aquatic hazard for metal compounds” of ECHA Guidance on the Application of the CLP Criteria (V 5.0, July 2017) and section 4.1.2.10.2. of Regulation (EC) No 1272/2008, classification for acute (short-term) aquatic hazard is not required for tin antimony grey cassiterite.
Long-term (chronic) aquatic hazard:
The release of antimony, tin and vanadium from the pigment at a loading of 1 mg/L at pH 8 after 28 days results in concentrations of 0.61 µg/L, 8.89 µg/L and 0.21 µg/l, respectively, and are significantly lower (more than hundredfold up to more than thousandfold) than respective chronic toxicity levels (Sb = > 1000µg/L (EU, 2008), Sn = 1001 µg/L and V = 76 µg/L (MECLAS v 5.2)). Applying the concept of additivity, the sum of the respective ratios of dissolved metal ion concentrations in the T/Dp (loading of 1 mg/L, 28 d, pH 6 and pH 8) and corresponding long-term ERVs is also well below 1 (< 0.1). Thus, the pigment does not meet classification criteria for a long-term aquatic hazard under CLP.
Two supporting non-GLP studies on the acute toxicity of the dispersed pigment on zebrafish (OECD TG 203) and Daphnia magna (OECD TG 202) provide further evidence on the low potential for aquatic toxicity since effects were not observed at 100 mg/L (nominal, dispersed) and the respective LC/EC50 values are estimated with > 100 mg/L (nominal, dispersed). Thus, applying the surrogate approach according to Table 4.1.0 (b) (iii) of Regulation (EC) No 1272/2008, tin antimony grey cassiterite would also not meet criteria for any long-term aquatic hazard category.
Thus, in accordance with Figure IV.5 „Classification strategy for determining long-term aquatic hazard for metal compounds“ of ECHA Guidance on the Application of the CLP Criteria (V 5.0, July 2017) and section 4.1.2.10.2. of Regulation (EC) No 1272/2008, classification for long-term (acute) aquatic hazard is not required for tin antimony grey cassiterite.
The conclusion on a lack of an aquatic hazard potential of tin antimony grey cassiterite is in accordance with a Tier 2 assessment (using T/Dp data) performed with MECLAS version 5.2 (http://www.meclas.eu/accessed on 10.01.2019). The Metals Classification Tool (MECLAS) is a web enabled classification tool always updated to the latest classification guidance, legal ruling, information on toxicity references and available self-classifications.
In sum, it can safely be assumed that tin antimony grey cassiterite does not meet classification criteria of an acute or long-term aquatic hazard of Regulation (EC) No 1272/2008.
Reference:
EU (European Union), 2008. European Union Risk Assessment Report. Diantimony trioxide. CAS No. 1309-64-4. EINICS No. 215-175-0, November 2008). Available from https://echa.europa.eu/documents/10162/553c71a9-5b5c-488b-9666-adc3af5cdf5f
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