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EC number: 700-790-3 | CAS number: -
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
Description of key information
The 72-hour EC50s for the constituents of GLS-Silane range are >100 mg/L. NOECs ranged from <6.3 mg/L to >118 mg/L.
Key value for chemical safety assessment
Additional information
There are no data for toxicity to aquatic algae and cyanobacteria for GLS-Silane. Data are available for the constituents of GLS-Silane, their hydrolysis products or structurally similar analogues.The hydrolysis half-life of chlorosilanes indicate that, under conditions relevant to the algal toxicity test, hydrolysis to a silanediol and hydrogen chloride will occur. The properties of hydrogen chloride are well characterised. Its effects on aquatic organisms are limited to those that result from changes to pH in unbuffered media.
Silanes comprise 74 -97% w/w of GLS-Silane. The remaining constiuents are hydrocarbons. Three of the hydrocarbons are liqufied gases present at <1%. The other hydrocarbon, 2 -methyl butane is present at >3 -<10% w/w. Therefore, toxicity of GLS-Silane is determined based on the toxicity of its silane constituents or their read-across compounds. EC50 values for the silanes and/or silanols are all > 100 mg/L.
No data for toxicity to aquatic algae and cyanobacteria are available for dichloro(methyl)silane. However a study of toxicity to aquatic algae is available for the related substance dimethylsilanediol. Dimethylsilanediol, 1066-42-8, is a close structural analogue of Methylsilanediol, which is the hydrolysis product of Dichloro(methyl)silane, 75-54-7. The 72-hr EC50 for dimethylsilanediol was >118 mg/L. The NOEC was also >118 mg/L.
Trimethoxysilane was used as a structural analogue for triclorosilane. Both materials break down to silanol. The Algal Growth Inhibition 72-hr EC50 with Pseudokirchnerella subcapitata for trimethoxysilane was >100 mg/L. The NOEC was <6.3 mg/L.
Trimethylsilanediol was used as a structural analogue for chloro(dimethyl)silane. The Algal Growth inhibition 72-hr EC50 with Pseudokirchnerella subcapitata for trimethylsilanediol was >1053 mg/L. The NOEC was 70 mg/L.
An algal growth inhibition study was conducted on Tetramethylsilane with a reported EC50 and NOEC of > 0.0079 mg/L. However, this was the highest concentration tested and no effects were observed at this concentration. This study was not considered in the range of algal toxicity studies for GLS-Silane because of its low value relative to all other test endpoints and the lack of effect at this, the highest concentration tested.
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