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EC number: 236-112-3 | CAS number: 13170-23-5
- 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
Stability: Hydrolysis: Key study: Read-across from experimental data on analogue propyltriacetoxysilane: Diacetoxydi-tert-butoxysilane was determined to be hydrolytically unstable, with a fast hydrolysis (very low half-life time) into acetic acid and the corresponding silanols, regardless of pH.
Biodegradation: Key study: Read-across from experimental data on analogue Methyltriacetoxysilane:
Diacetoxydi-tert-butoxysilane was determined to be readily biodegradable. According to column 2 of REACH Annex IX, the simulation testing in surface water, sediment and soil were not necessary to be conducted since the substance is readily biodegradable.
Bioaccumulation: According to the column 2 of REACH Annex IX, the study needs not to be conducted since the substance has a low potential for bioaccumulation (log Kow < 3).
Transport and distribution: According to the column 2 of REACH Annex VIII, the study does not need to be conducted since the substance is expected to have low potential for adsorption based on the low octanol-water partition coefficient (log Kow < 3).
Nevertheless, base on the KOCWIN v2.00, MCI calculation method, soil adsorption ofdiacetoxydi-tert-butoxysilanewas estimated to be: Koc = 48.95 L/kg and Log Koc = 1.69.
Additional information
It is well known that triacetoxisilane undergoes rapid hydrolysis in aqueous or moist environments to acetic acid and trisilanol.
The confirm that hydrolysis of acetoxysilanes is fast, the test of hydrolysis of propyl triacetoxysilane in water was performed. It was measured, that the process was very fast. The half-life at different pH of propyltriacetoxysilane was determined to be < 37.5 seconds since the test item was completely hydrolysed at 150 seconds after the initial contact with water.
As it is stated in different publications, silanols hydrolyse well in water and the carbon- bounded substituents can have profound effects on the rate of hydrolysis. (Arkles B., Chemtech 1977; Pluddemann E.P., Plenum Press NY, 1982; Kay, B.D. and Assink R.A, J. Non-Cryst. Solids, 1988).
The rates of hydrolysis of the alkoxy groups are generally related to their steric bulk: CH3O>C2H5O> t-C4H9O and a methoxysilane hydrolyzes at 6-10 times rate of an ethoxysilane. Smith (Smith K. J. Org. Chem 1986) proved that increased organic substitution enhances the hydrolysis rate Me3SiOMe> Me2Si(OMe)2> MeSi(OMe)3.
During the performed hydrolysis test, the condensation and polimerysation of the molecules formed in hydrolysis were observed too. It was observed as the phase separation. Unfortunately, this phase separation caused the technical difficulties of the determination of the molecular weight of larger condensation products. It was possible to determined MW of smaller condensates which still are in solutions. Their average MW were between 604-695.
This phase separation as a result of condensation was described by Arkles. The hydrolysis of propyltrimetoxysilane showed that oligomers are formed and branched structures presages phase separation (Arkles B. et al, Silanes and Coupling Agents, 1992).
Taking in account both, the hydrolysis and condensation, it is expected that the observed in the hydrolysis test phase changed product contains large chain polymers with MW>1000.
Authors showed that molecules of MW>1000 cannot be biologically available (Van Gestel et a, Reg. Toxicol. and Pharmacol., 1985, 5, 422-31 and Zitko V, Handbook of Environmental Chemistry, v. 2 221-29).
Stability: Hydrolysis: Key study: Read-across from experimental data on analogue propyltriacetoxysilane: Diacetoxydi-tert-butoxysilane was determined to be hydrolytically unstable, with a fast hydrolysis (very low half-life time) into acetic acid and the corresponding silanols, regardless of pH.
Biodegradation: Key study: Read-across from experimental data on analogue Methyltriacetoxysilane:
Diacetoxydi-tert-butoxysilane was determined to be readily biodegradable. According to column 2 of REACH Annex IX, the simulation testing in surface water, sediment and soil were not necessary to be conducted since the substance is readily biodegradable.
Bioaccumulation: According to the column 2 of REACH Annex IX, the study needs not to be conducted since the substance has a low potential for bioaccumulation (log Kow < 3).
Transport and distribution: According to the column 2 of REACH Annex VIII, the study does not need to be conducted since the substance is expected to have low potential for adsorption based on the low octanol-water partition coefficient (log Kow < 3).
Nevertheless, base on the KOCWIN v2.00, MCI calculation method, soil adsorption of diacetoxydi-tert-butoxysilane was estimated to be: Koc = 48.95 L/kg and Log Koc = 1.69.
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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