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EC number: 231-588-9 | CAS number: 7646-78-8
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
Ecotoxicity tests according to OECD Guidelines under GLP were available for the three trophic levels:
AQUATIC INVERTEBRATES:
Tin tetrachloride was investigated for acute toxicity to Daphnia magna in a static limit test according to OECD 202 under GLP. The 48-hour NOELR was determined to be >= 100 mg test item/L (nominal). The 48-hour EL50 value was determined to be > 100 mg test item/L (nominal). The validity criteria were fullfilled. It can be concluded that the EC50 is above the solubility limit of tin tetrachloride or its hydrolysis prproducts under the reported conditions. The concentration of free Tin(IV) was below the limit of detection.
ALGEA
Tin Tetrachloride was examined for toxicity on freshwater green algae Pseudokirchneriella subcapitata in a static dose-response test according to OECD Guideline 201 and ISO 14442 Water Quality - Guidelines for Algal Growth Inhibition Tests with Poorly Soluble Materials,Volatile Compounds, Metals and Waste Water. The medium was EDTA free to prevent from complexation of free tin(IV). The validity of the test desing was evaluated in a separate study with poatassium dicromate. All validity criteria were fullfilld. The 72-hour ErL50 value was observed to be >100 mg test item/L, the 72-hour EbL50 was determined to be between 1.0 and 3.2 mg test item/L and the 72-hour EyL50 was observed to be < 1.0 mg test item/L. The 72-hour NOELR were determined to be < 1.0 and the associated 72-hour LOELR are ≤ 1.0 mg/L for all endpoints. It can be concluded that the ICr50 is above the solubility limit of tin tetrachloride or its hydrolysis prproducts under the reported conditions. The concentration of free Tin(IV) was below the limit of detection.
FISH
The effects of Tin tetrachloride on Brachydanio rerio were investigated in an acute fish toxicity test with static desing at a limit dose of 1000 mg/L according to OECD 201 under GLP. The control was valid. Tin tetrachloride did not induce acute toxic effects in Brachydanio rerio at a nominal concentration of 1000 mg/L.
ADDITIONAL DATA
Further results were available in an OECD SIDS document (see table 1). Wong et al reported an IC50 of 12 mg/L for one of three examined algeal species, the other two were >5 and >50 mg/L. In summary these experiments support the thesis that toxicity from tin(IV) ions to aquatic organisms is restricted by the solubility limit of the hydrolysis products.
Table 1: Additional information from OECD SIDS
Species |
Protocol/ Method |
Duration |
Test Substance Composition |
Test System |
Observations and Conditions |
Result |
Rating |
Reference |
|
Algae |
|||||||||
Anabaena flos-aquae (Blue-green algae) |
Primary productivity |
24 h |
SnCl4 (purity unknown) |
No Data, nominal |
Test medium was buffered to pH 8. |
IC50 >5 mg Sn/L (>11 mg/L as SnCl4) |
2 |
Wong et al. 1982
|
|
Scenedesmus quadricauda(Green algae) |
Primary productivity |
24 h |
SnCl4 (purity unknown) |
No Data, nominal |
Test medium was buffered to pH 8. |
IC50 >50 mg Sn/L (>110 mg/L as SnCl4) |
2 |
Wong et al. 1982
|
|
Ankistrodesmus falcatus(Green algae) |
Primary productivity |
24 h |
SnCl4 (purity unknown) |
No Data, nominal |
Test medium was buffered to pH 8. |
IC50 = 12 mg Sn/L (26 mg/L as SnCl4) |
2 |
Wong et al. 1982
|
|
Synechocystis aquatilis(Blue-green algae) |
Growth and chlorophyll-a content |
96 h |
Stannic chloride pentahydrate (purity unknown) |
No Data, nominal |
At pH 7, no inhibiting influence on the test species noted; growth comparable to controls. |
IC50 >10 mg Sn/L (>23 mg/L as stannic chloride pentahydrate) |
2 |
Pawlik-Skowronska et al. 1997
|
|
Microorganisms |
|||||||||
OECD TG 209 | Inhibition | 30 min | No Data, nominal |
EC0 = 5400 mg/L | 2 | Höchst AG 1994 |
CONCLUSION
The solubility of tin tetrachloride, respectively its hydrolysis products is limited. Based on the observed slight signs of toxicity in the algea test it can be assumed that the solubility limits the toxic effects. Nevertheless effects on aquatic organismns can be expected by pH-shifts, as 1 mol SnCl4 releases 4 mol of HCl. Based on current guidelines and practices labelling of tin tetrachloride as acute harmful to aquatic organisms is not indicated. This is contrary to the current EU legal classification, that classifies tin tetrachloride as acute auqutic 3 and chronic aquatic 3.
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