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EC number: 232-263-4 | CAS number: 7803-62-5
- 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
Endpoint summary
Administrative data
Description of key information
In the key acute inhalation study (Toxic Hazard Research Unit, 1972, reliability score 2) conducted using a protocol similar to OECD Test Guideline 403 (reliability score 2) and prior to the introduction of GLP, a concentration of 9600 ppm (12611 mg/m3) silane (CAS 7803-62-5; EC No. 232-263-4) for four hours caused deaths in 4 of 10 mice. A concentration of 9600 ppm (12611 mg/m3) for 4 hours did not cause any deaths in five rats. Hence the LC50s for mice and rats were approximately 10000 ppm and >9600 ppm, respectively. There are no acute oral or dermal toxicity studies available.
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Acute toxicity: via inhalation route
Link to relevant study records
- Endpoint:
- acute toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Study conducted during the period June 1971 to May 1972
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Remarks:
- The study was well documented and meets generally accepted scientific principles, but was not conducted in compliance with GLP.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 403 (Acute Inhalation Toxicity)
- GLP compliance:
- no
- Test type:
- standard acute method
- Limit test:
- no
- Species:
- other: rat and mouse
- Strain:
- other: CFE and CF1, respectively.
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- No data.
- Route of administration:
- inhalation: vapour
- Type of inhalation exposure:
- whole body
- Vehicle:
- other: nitrogen
- Details on inhalation exposure:
- No data.
- Analytical verification of test atmosphere concentrations:
- yes
- Remarks:
- Beckman Infrared 5-A spectrophotometer
- Duration of exposure:
- 1 - 4 h
- Concentrations:
- 1000, 4000, 6000, 10000 ppm
- No. of animals per sex per dose:
- 5-50 males
- Control animals:
- yes
- Details on study design:
- No data.
- Statistics:
- No data.
- Key result
- Sex:
- male
- Dose descriptor:
- LC50
- Effect level:
- > 9 600 ppm
- Based on:
- test mat.
- Exp. duration:
- 4 h
- Remarks on result:
- other: based on 4/10 deaths at this concentration in mice
- Key result
- Sex:
- male
- Dose descriptor:
- LC50
- Effect level:
- > 9 600 ppm
- Based on:
- test mat.
- Exp. duration:
- 4 h
- Remarks on result:
- other: based on 0/5 deaths in rats (equivalent to >12611 mg/m³)
- Mortality:
- See Table 1.
- Clinical signs:
- other: No data.
- Body weight:
- No data.
- Gross pathology:
- No data.
- Other findings:
- No data.
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- In an acute inhalation study conducted using a protocol similar to OECD Test Guideline 403 prior to the introduction of GLP (reliability score 2), a concentration of 9600 ppm silane for 4 hours caused deaths in 4 of 10 mice. A concentration of 9600 ppm for 4 hours did not cause any deaths in five rats. Hence the LC50s for mice and rats were approximately 10000 ppm and >9600 ppm, respectively.
Reference
Table 1 Summary of results for acute inhalation studies in rats and mice
Species | Nominal concentration (ppm) | Measured concentration (ppm) | Measured concentration (mg/l) | Exp. time (h) | Mortality | Time to death |
Rat | 1000 | - | - | 1.25 | 0/50 | - |
Rat | 4000 | - | - | 1 | 0/5 | - |
Rat | 10000 | 9600 | 12.6 | 4 | 0/5 | - |
Mouse | 6000 | - | - | 1 | 0/5 | - |
Mouse | 10000 | 9600 | 12.6 | 4 | 4/10 | 31 -45 h |
Mouse | 10000 | 9800 | 12.8 | 2 | 0/10 | - |
The mean weight gain of the 9600 ppm group appears to have been slightly inhibited during the first post-exposure week, but fully recovered at 14 days. No gross lesions due to treatment were observed at sacrifice. A gross pathological examination of the animals that died was not conducted.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LC50
- Value:
- > 12 611 mg/m³ air
Acute toxicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
There are no acute toxicity data available for oral or dermal routes. However, in accordance with Annex XI of REACH, the acute oral and dermal toxicity studies do not need to be conducted as the substance is a gas which is spontaneously flammable in air.
For the inhalation route, the key study (Toxic Hazard Research Unit, 1972, reliability score 2) was chosen in preference to other available reliable studies as it was conducted using rats, the preferred species for acute inhalation toxicity studies. In this study the highest concentration tested was restricted by the flammability of silane. Since no deaths occurred the LC50 was >9600 ppm (>12,611 mg/m3).
Two other reliable studies provide supporting information for the inhalation route. In a well documented study (Omae, 1992) that was conducted using a similar protocol to OECD Test Guideline 403 (not to GLP; reliability score 2), male ICR mice were exposed to 1000 ppm silane for 1, 2, 4 and 8 hours. No mice died and no exposure-related changes in any organs were observed. Biochemical or haematological parameters affected included an increase in red blood cell counts in mice exposed for 8 hours, an increase in blood urea nitrogen in mice exposed for 1 hour and a decrease in the 8-hour exposure group, and a decreased white blood cell count after 1-hour exposure. The 4 hour LC50 was greater than 1000 ppm. In another well conducted acute inhalation study (Takebayashi, 1992; reliability score 2 as no information on GLP, and only males were tested) which generally exceeded the requirements of OECD Test Guideline 403, male ICR mice were exposed to 2500, 5000, 7500, or 10000 ppm for 30 minutes (n=8), one hour, or four hours (n=12). In the one and four hour groups 12 mice were divided into two subgroups; four for a two day observation and eight for a two week observation. Only animals in the group exposed to 10000 ppm for 4 hours died (9/12; all within 24 hr). At autopsy these animals had increased relative kidney weights, renal tubular necrosis, splenic atrophy, appearance of macrophages with debris of degenerated cells in bone marrow and thymus, and inflammatory changes of the nasal mucosa. In the groups exposed for 30 minutes or one hour and sacrificed at week two, changes to the kidneys were the main effects found (tubular interstitial nephrosis in 6/8 and 7/8 animals, respectively). Following exposure to 7500 ppm (only 30-min exposure), tubular nephrosis was observed in 4/8 animals. The one and four hour exposures to 5000 ppm caused tubular interstitial nephritis in 1/8 and 2/8 animals sacrificed at week 2, respectively, and acute renal tubular necrosis in 0/4 and 1/4 animals sacrificed after two days, respectively. Concerning the 2500 ppm groups, the only effect observed was acute renal tubular necrosis in 1/4 animals exposed for 4 hours. It was concluded that the LC50 was 5000-10000 ppm.
Justification for classification or non-classification
Based on the available data, silane does not require classification for acute toxicity according to Regulation (EC) 1272/2008.
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