Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 211-656-4 | CAS number: 681-84-5
- 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

Ecotoxicological Summary
Administrative data
Hazard for aquatic organisms
Freshwater
- Hazard assessment conclusion:
- PNEC aqua (freshwater)
- PNEC value:
- 5 mg/L
- Assessment factor:
- 1 000
- Extrapolation method:
- assessment factor
- PNEC freshwater (intermittent releases):
- 50 mg/L
Marine water
- Hazard assessment conclusion:
- PNEC aqua (marine water)
- PNEC value:
- 0.5 mg/L
- Assessment factor:
- 10 000
- Extrapolation method:
- assessment factor
STP
- Hazard assessment conclusion:
- PNEC STP
- PNEC value:
- 1 mg/L
- Assessment factor:
- 100
- Extrapolation method:
- assessment factor
Sediment (freshwater)
- Hazard assessment conclusion:
- PNEC sediment (freshwater)
- PNEC value:
- 20 mg/kg sediment dw
- Extrapolation method:
- equilibrium partitioning method
Sediment (marine water)
- Hazard assessment conclusion:
- PNEC sediment (marine water)
- PNEC value:
- 2 mg/kg sediment dw
- Extrapolation method:
- equilibrium partitioning method
Hazard for air
Air
- Hazard assessment conclusion:
- no hazard identified
Hazard for terrestrial organisms
Soil
- Hazard assessment conclusion:
- PNEC soil
- PNEC value:
- 1.12 mg/kg soil dw
- Extrapolation method:
- equilibrium partitioning method
Hazard for predators
Secondary poisoning
- Hazard assessment conclusion:
- no potential for bioaccumulation
Additional information
The registered substance will hydrolyse very rapidly (half-life <3 min at pH 4, 7 and 9 at approximately 20°C) in contact with water and atmospheric moisture tosilicic acid and methanol. REACH guidance (ECHA 2010A, R.16) states that “for substances where hydrolytic DT50 is less than 12 hours, environmental effects are likely to be attributed to the hydrolysis product rather than to the parent itself”. TGD and ECHA guidance, (EC 2003, ECHA 2010A) also suggest that when the hydrolysis half-life is less than 12 hours, the breakdown products, rather than the parent substance, should be evaluated for aquatic toxicity. Therefore, the environmental hazard assessment, including sediment and soil compartments due to water and moisture being present, is based on the properties of the silanol hydrolysis product, in accordance with REACH guidance.
As described in Section 1.3, the silicic acid may precipitate as insoluble silica (SiO2) at high enough concentrations. Relevant low molecular weight tetra-alylsilicates are described in section 1.4.
READ-ACROSS JUSTIFICATION
In order to reduce animal testing read-across is proposed to fulfil up to REACH Annex IX requirements for the registered substance from substances that have similar structure and physicochemical properties. Ecotoxicological studies are conducted in aquatic medium or in moist environments; therefore the hydrolysis rate of the substance is particularly important since after hydrolysis occurs the resulting product has different physicochemical properties and structure.
Tetramethyl orthosilicate and tetraethyl orthosilicate are members of a group of substances that hydrolyse rapidly (<12 hours) to form silicic acid, a bioavailable form of silicate.
Silicic acid is a naturally occurring substance which is not harmful to aquatic organisms. It is the major bioavailable form of silica for aquatic organisms and plays an important role in the biogeochemical cycle of Si. Most living organisms contain at least trace quantities of silicon. For some species Si is essential element taken up actively, for example, diatoms, radiolarians, flagellates, sponges and gastropods all have silicate skeletal structures.In addition, silicic acid has been shown to be beneficial in protection against mildew formation in wheat and to not be phytotoxic in non-standard studies (Côte-Beaulieu et al. 2009).Therefore, it is not expected to be harmful to the environment nor the organisms it will be exposed to. However, methanol has the potential to cause some harmful effects at high dose levels and PNECs will be based on the properties of methanol.
In the following paragraphs the read-across approach for tetramethyl orthosilicate is assessed for the surrogate substance taking into account structure, hydrolysis rate and physico-chemical properties.
Additional information is given in a supporting report (PFA, 2013x) attached in Section 13 of the REACH IUCLID 5 dossier.
· Read-across from tetraethyl orthosilicate to tetramethyl orthosilicate
The registered substance, tetramethyl orthosilicate (CAS 681-84-5), hydrolyses rapidly (half-life <3 min at pH 4, 7 and 9 at approximately 20°C) to produce silicic acid and methanol (CAS 67-56-1). Tetraethyl orthosilicate (CAS 78-10-4) also hydrolyses rapidly (half-life 4.4 h at pH 7 and at 25°C) to silicic acid and ethanol (CAS 64-17-5).Therefore the surrogate and registered substance share the same silanol hydrolysis product and read-across is considered to be directly relevant. The non-silanol hydrolysis products are given due consideration below.
Short-term toxicity data available for the structurally-analogous substance do not report any effects below 100 mg/l.
· Considerations on the non-silanol hydrolysis products:
Ethanol is well characterised in the public domain literature and is of low toxicity at the concentrations relevant to the studies; the short-term EC50and LC50values for this substances is in excess of 1000 mg/l (OECD 2004 - SIDS for ethanol, CAS 64-17-5).
Aquatic toxicity data for propanol have been reviewed as part of a European Union Risk assessment Report (EC 2008) and show the low toxicity of the substance to aquatic organisms. The lowest available effect concentration identified was a 48-hour EC50value of 1000 mg/l for effects on the invertebrate species Gammarus pulex.
CAS Number |
681-84-5 |
78-10-4 |
Chemical Name |
Tetramethyl orthosilicate |
tetraethyl orthosilicate |
Si hydrolysis product |
Silicic acid |
Tetraethyl orthosilicate |
Non-Si hydrolysis product |
Methanol |
Ethanol |
Molecular weight (parent) |
152.22 |
208.33 |
Molecular weight (silanol hydrolysis product) |
96.1 |
96.1 |
Molecular weight (non-silanol hydrolysis product) |
32.04 |
46.07 |
log Kow(parent) |
-0.5 |
3.18 |
log Kow(silanol hydrolysis product) |
n/a |
n/a |
log Kow (non-silanol hydrolysis product) |
-0.82 |
-0.3 |
Water sol (parent) |
n/a |
approx. 1500 mg/l |
Water sol (silanol hydrolysis product)) |
1E+06 mg/l |
1E+06 mg/l |
Water sol (non-silanol hydrolysis product) |
Soluble |
Soluble |
Vapour pressure (parent) |
1800 Pa |
1.1 hPa |
Vapour pressure (silanol hydrolysis product) |
<1E-10 Pa |
<1E-10 Pa |
Vapour pressure (non-silanol hydrolysis product) |
12790 Pa |
57.3 hPa |
Hydrolysis t1/2at pH 7 and 25°C |
<3 min |
4.4 hrs |
Hydrolysis t1/2at pH 4 and 25°C |
<3 min |
0.11 hours |
Hydrolysis t1/2at pH 9 and 25°C |
<3 min |
0.22 hours |
Short-term toxicity to fish (LC50) |
>245mg/l |
>245mg/l |
Short-term toxicity to aquatic invertebrates (EC50) |
>75 mg/l |
>75 mg/l |
Algal inhibition (ErC50and NOEC) |
(72-hour) EC50: >22 mg/l; NOEC: ≥22 mg/l |
72-hour EC50: >22 mg/l; NOEC: ≥22 mg/ |
Long-term toxicity to fish (NOEC) |
n/a |
n/a |
Long-term toxicity to aquatic invertebrates (NOEC) |
n/a |
n/a |
Sediment toxicity (NOEC) |
n/a |
n/a |
Short-term terrestrial toxicity (L(E)C50) |
n/a |
n/a |
Long-term terrestrial toxicity (NOEC) |
n/a |
n/a |
The read-across data for tetraethyl orthosilicate indicate that the common hydrolysis product, tetrahydroxysilane (silicic acid), is not toxic at the loading rates used.
For the other hydrolysis product, methanol, short-term aquatic toxicity data reviewed under the OECD SIDS programme indicate that L(E)C50values for fish, invertebrates and algae exposed are all ≥10 000 mg/l. The low toxicity of methanol to aquatic organisms is confirmed by QSAR predictions for short-term L(E) C50 values of >1000 mg/l for the same three taxonomic groups with a lowest 96-hour EC50value of 5000 mg/l reported for algae. There are no long-term data for methanol.
The QSAR-predicted algal 96-hour EC50 value for methanol of 5000 mg/l is used to derive the PNECs as follows because it is the lowest available non-limit value:
· A PNECaquatic(freshwater) of 5 mg/l methanol (equivalent to 6 mg/l TMOS) is derived using an assessment factor (AF) of 1000 because short-term data are only available.
· A PNECaquatic(marine water) of 0.5 mg/l methanol (equivalent to 0.6 mg/l TMOS) is derived by applying an assessment factor 10000.
· A PNECaquatic(intermittent releases) of 50 mg/l methanol (equivalent to 60 mg/l TMOS) is derived by applying an assessment factor of 100.
PNECs for sediment and soil compartments are determined from the PNECs for the aquatic compartment using the equilibrium partitioning method.
Conclusion on classification
Tetramethyl orthosilicate hydrolyses very rapidly in contact with moisture. The hydrolysis product is inorganic silicic acid.
Tetramethyl orthosilicateis notclassifiedfor the environment in the EU according to Regulation (EC) No. 1272/2008 because short-term data available for an appropriate analogue indicate the EC and LC50 to be >100 mg/l.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.

EU Privacy Disclaimer
This website uses cookies to ensure you get the best experience on our websites.