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EC number: 213-935-6 | CAS number: 1067-55-6
- 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
The following studies have been submitted to address the repeated dose toxicity: oral endpoint:
Barnes, J. M. and Stoner, H. B. (1958). Toxic properties of some dialkyl and trialkyl tin salts. Brit. J. Industr. Med., 1958, 15, 15.
Gaunt et al (1968). Acute and Short-term Toxicity Studies on Di-n-butyltin Dichloride in Rats. Fd Cosmet. Toxicol. Vol. 6, pp. 599-608.
Penninks A. H. & Seinen W. (1982). COMPARATIVE TOXICITY OF ALKYLTIN AND ESTERTIN STABILIZERS. Fd Chem. Toxic. Vol. 20. pp. 909 to 916.
The Gaunt et al (1968) study has been allocated a Klimisch core of 2 on the basis that the study predates GLP; however, method was comparable to OECD Guideline 408. The effect of DBT exposure on the thymus of was not assessed in this study. No information on the stability or homogeneity of the test material in the DBTC-prepared diets. The study was performed with dibutyltin dichloride.
The Penninks and Seinen (1982) study has also been allocated a Klimisch score of 2 on the basis that the study is a short-term feeding study with no information on the stability of the test substance in the diet or homogeneity of the test diets provided. The purity of the test substance (dibutyltin dichloride) is not reported.
The Barnes and Stoner (1958) study has been allocated a Klimisch score of 4.
Dibutyltin chloride was the test substance employed in all the studies presented under repeated dose toxicity. Under gastric conditions, dibutyltin dimethoxystannane is anticipated to hydrolyse to dibutyltin chloride. A read-across approach from dibutyltin chloride was considered acceptable when dosing repeatedly via the oral route.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Endpoint conclusion
- Dose descriptor:
- NOAEL
- 2 mg/kg bw/day
- Study duration:
- subchronic
- Species:
- rat
Additional information
A robust review of data for organotin compounds (including dibutyltin) by the EU’s Scientific Panel on Contaminants in the Food Chain (SPCFC, 2004) appears to include the above studies. The available data for repeat-dose (subchronic) studies are restricted to rats, exposed to dibutyltin chloride. Determination of NOAELs is variable, but thymus weight is considered a critical endpoint. One study concludes effects at a dose level as low as 50 ppm in diet/2.5 mg/kg bw/day (Pennincks et al, 1982). Another study of equivalent reliability identifies 2 mg/kg bw/day as a NOAEL (Gaunt et al, 1968). As the only reliable sub-chronic study available Gaunt et al, (1968) was selected as the key study for this data requirement.
A read-across approach was considered appropriate from dibutyltin chloride to other dibutyltins. Under gastric conditions dibutyltins are hydrolysed to form dibutyltin chloride. This is demonstrated in various dibutyltin compounds presented in the TNO report V5047, (presented as individual reports as under Toxicokinetics).
Justification for classification or non-classification
The substance is classified with R48/R25 according to Directive 67/548/EEC. According to Regulation (EC) no 1272/2008 the test substance would be classified as a STOT Rep. Exp. 1 with Hazard statement: H372: Causes damage to thymus through prolonged or repeated exposure and should be accompanied with the signal word 'Danger'.
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