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EC number: 204-710-3 | CAS number: 124-70-9
- 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
There are no repeated dose toxicity data on dichloro(methyl)(vinyl)silane or its hydrolysis product, methyl(vinyl)silanediol, so good quality data for the related substance trimethoxyvinylsilane have been used to assess the general systemic toxicity of dichloro(methyl)(vinyl)silane.
In an oral OECD 422 study ( Hashima Labs, no date) in rats, trimethoxyvinylsilane was administered by gavage at doses up to 1000 mg/kg bw/day, for approximately 28 days. The LOAEL was 62.5 mg/kg bw/day (based on decreased relative thymus weight in females and histopathological changes in the urinary bladder of males) and the NOAEL was < 62.5 mg/kg bw/day for both sexes.
In a 14-week whole-body inhalation study (BRRC, 1990) in which rats were exposed to trimethoxy(vinyl)silane at concentrations up to 400 ppm, a concentration of 100 ppm was a LOAEC (effects included decreased urine osmolality and sodium, potassium and chloride concentrations in males and slight decrease in body weight and body weight gain in females), and 10 ppm (58 mg/m3) was a NOAEC.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Endpoint conclusion
- Dose descriptor:
- LOAEL
- 62.5 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Dose descriptor:
- NOAEC
- 58 mg/m³
- Study duration:
- subchronic
- Species:
- rat
Additional information
There are no repeated dose toxicity data on dichloro(methyl)(vinyl)silane or its hydrolysis product, methyl(vinyl)silanediol, so good quality data for the related substance trimethoxyvinylsilane have been used to assess the general systemic toxicity of dichloro(methyl)(vinyl)silane. Local effects from the other hydrolysis product, hydrogen chloride (HCl) are not addressed by these data.
Dichloro(methyl)(vinyl)silane hydrolyses rapidly in contact with water (half-life <1 minute at pH 7), generating HCl and methyl(vinyl)silanediol. Trimethoxy(vinyl)silane (CAS 2768 -02 -7) hydrolyses more slowly at pH 7 (half-life <2.4 hours at 50°C and pH7)
, but under acidic conditions such as in the stomach following ingestion, much more rapid hydrolysis can be expected based on experience with other methoxysilanes. The relevant hydrolysis products are methanol and vinylsilanetriol. The silanol hydrolysis products for the registered substance and the surrogate substance are therefore similar in chemical structure, the only difference being the replacement of -CH3 with an extra Si-OH group. Both have high water solubility and very low log Kow (log Kow -0.05 and -2.0, respectively). Acute oral toxicity data for other related silanols [e.g. dimethylsilanediol and methylsilanetriol (as the potassium salt)] indicate there are no significant toxicological differences between silanediol and silanetriol analogues. Data obtained via the oral route for trimethoxyvinylsilane are therefore considered appropriate for read-across to dichloro(methyl)(vinyl)silane.
For the inhalation route, the hydrolysis rate of trimethoxyvinylsilane in the respiratory tract and lungs is unknown, but is likely to be slower than that of dichloro(methyl)(vinyl)silane. For dichloro(methyl)(vinyl)silane, the species absorbed following inhalation exposure are mainly hydrolysis products, whereas for trimethoxyvinylsilane, absorption of the parent substance may be more significant. Trimethoxyvinylsilane has a higher log Kow value (1.08) therefore the proportion of inhaled material which is systemically absorbed is likely to be greater than for dichloro(methyl)(vinyl)silane. Nevertheless, in the absence of other data, the inhalatory NOAEL for trimethoxy(vinyl)silane is considered to represent a reasonable worst-case for read-across to dichloro(methyl)vinylsilane.
It is of note that the oral NOAEL in rats for methanol is greater (500 mg/kg bw/day) than the dose that is expected to be generated from hydrolysis of trimethoxy(vinyl)silane in the stomach. Therefore the effects of trimethoxy(vinyl)silane following a dose of 62.5 mg/kg bw/day are not thought to be attributable to methanol. Similarly, following inhalation of methanol the NOAEC is an order of magnitide greater than the NOAEC for trimethoxy(vinyl)silane, and it therefore unlikely that systemic effects observed following inhalation of trimethoxy(vinyl)silane are due to methanol.
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Repeated dose toxicity: via oral route - systemic effects (target organ) urogenital: urinary bladder
Justification for classification or non-classification
Based on the observed effects on the urinary bladder of males at all dose levels, it is appropriate to classify trimethoxyvinylsilane as STOT RE 2 (bladder) following oral exposure, according to the criteria of Regulation 1272/2008. However, at the dose levels tested, corrosive effects of trichloro(vinyl)silane would outweigh any potential systemic effects. It is therefore not considered appropriate to classify trichloro(vinyl)silane for repeated dose toxicity.
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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