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Diss Factsheets
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EC number: 234-186-1 | CAS number: 10584-98-2
- 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
Bioaccumulation: aquatic / sediment
Administrative data
Link to relevant study record(s)
Description of key information
The following studies have been submitted in support of the argument for omission of further testing for the bioaccumulation aquatic/sediment end point:
No information is available for DBT (2-EHMA), however it is possible to read across from the structurally similar compound DBTC.
Tsuda et al (1986). Bioconcentration of Butyltin Compounds by Round Crucian Carp. Toxicological and Environmental Chemistry Vol. 12, pp. 137-143.
Tsuda et al (1988). BIOCONCENTRATION AND METABOLISM OF BUTYLTIN COMPOUNDS IN CARP. Wat. Res. Vol. 22, No. 5, pp. 647-651, cited in Walterson et al (1994). KEMI report: Mono and Di-Substituted Organotins Used as Plastic Additives - Volume 1: Environmental Hazard Assessment. Report no.: 11/94. Owner company: THE SWEDISH NATIONAL CHEMICALS INSPECTORATE.
All studies have been allocated a Klimisch score of 4. The studies were performed on dibutyltin dichloride, which is similarto the substance in question, a read-across approach was therefore considered suitable for assessment of the bioaccumulation potential of the substance.
Key value for chemical safety assessment
Additional information
The two studies provided in support of omitting further testing were Tsuda et al (1986) and The KEMI report (Waterson et al (1994). The Tsuda et al (1986) study was conducted to non-standard methods, and the parameters of the study were not comparable to those required for accurate assessment of this data requirement. Both studies were assigned reliability scores of 4 (not assignable), this was based on methodological deficiencies and areas lacking in detail in the reporting of the study by Tsuda et al (1986).The KEMI report (Waterson et al (1994), is a comprehensive review of mono and di-substituted organotins and encompasses a later report by Tsuda (Tsuda et al 1988). Both studies, though not sufficient for assessment indicated that the potential for bioaccumulation in aquatic species is low.
As bioaccumulation is considered to be unlikely further testing was ommitted in accordance with column 2 of REACH Annex IX. Bioaccumulation in Aquatic Species does not need to be conducted as the chemical safety assessment concluded that the substance is of no immediate concern to the environment. The available data are adequate for classification and labelling purposes and PBT assessment, so no further testing is required. Also direct and indirect exposure of the aquatic compartment is unlikely.This is further supported by the anticipated low log Kow (<3) which also points to the conclusion of a low potential for bioaccumulation.
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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