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EC number: 231-141-8 | CAS number: 7440-31-5
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
Description of key information
100% aged tin solution represents the maximum concentration of soluble tin ions possible at the test conditions. No significant adverse effects of growth rate or yield were seen. ABC (2010)
Key value for chemical safety assessment
Additional information
Growth inhibition tests on the unicellular green algae Pseudokirchneriella subcapitata reported by the Chilean Mining and Metallurgy Research Center (CIMM 2009) were performed on tin (IV) chloride in accordance with OECD 201 guidelines. A preliminary growth inhibition test for a broad concentration range of tin(IV) allowed the 72h-ErC50to be calculated by extrapolation. A value of 19.7 mg/L was obtained. As high nominal concentrations of tin(IV) caused significant pH drift of the test media, another set of tests was performed in the presence of 5mM HEPES buffer, pH 8.The results from the second inhibition test with P. subcapitata showed a 72h-ErC50concentration of 9.8 mg/L of tin(IV). All the total tin (IV) concentrations are nominal. However, the measured dissolved tin at the start of the test varied between 14.0 µg/L and 16.0 µg/L across the range of nominal tin concentrations. Therefore, the dose response observed was not attributable to free tin ions and this test data cannot be used to assess the toxicity of soluble tin arising from the dissolution of tin metal powder.
In order to remove the confounding effects caused by precipitation from high nominal concentrations of tin salts, the growth inhibition study on Pseudokirchneriella subcapitata was repeated using aged solutions of tin ions (ABC 2010). The protocol for ageing tin (IV) solutions used in the ABC 2010 green algal study was developed following difficulties encountered during earlier toxicity tests with a number of species with precipitation of tin hydroxides. The methodology used for preparing the aged solutions is identical as used in the ABC 2010 short term toxicity test on Pimephales promelas.
The objective of this and the other key aquatic toxicity tests is to assess any adverse effects from soluble tin released from tin metal. Attempts to investigate the potential toxicity from tin ions using salts such as tin (IV) chloride have been confounded by lack of stability of tin ions in solution. This instability produces dissolved tin concentrations of only 10 to 20 µg/L against a nominal tin concentration of 1 mg/L. The high concentrations of precipitated tin hydroxides and the associated pH effects at higher doses do not reflect the true behaviour of tin ions released from the transformation and dissolution of tin metal. Therefore, to overcome these difficulties, aged solutions containing stable tin concentrations have been prepared just prior to the testing in a consistent manner such that the solutions will all be of the same age. Even after a total of seven days of ageing the tin (IV) ions are not yet at equilibrium conditions as slow precipitation and mineralisation reactions continue to take place. However, the aged solutions are considered to represent the maximum dissolved tin that can be achieved in the test media, and therefore a worst case exposure to dissolved tin.
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