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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
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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
Toxicological Summary
- Administrative data
- Workers - Hazard via inhalation route
- Workers - Hazard via dermal route
- Workers - Hazard for the eyes
- Additional information - workers
- General Population - Hazard via inhalation route
- General Population - Hazard via dermal route
- General Population - Hazard via oral route
- General Population - Hazard for the eyes
- Additional information - General Population
Administrative data
Workers - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 93 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- DNEL derivation method:
- other: Substance-specific
- Overall assessment factor (AF):
- 1
- Dose descriptor:
- NOAEC
- AF for dose response relationship:
- 1
- Justification:
- A NOAEC was established
- AF for differences in duration of exposure:
- 1
- Justification:
- Substance specific: local effects already very severe, unlikely to be worse with longer exposure duration
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Default (inhalation route)
- AF for other interspecies differences:
- 1
- Justification:
- Substance specific: local effects unlikely to be more severe in humans than in rats
- AF for intraspecies differences:
- 1
- Justification:
- Substance specific: local effects already very severe, including death, so unlikely to cause specific effects in sensitive populations
- AF for the quality of the whole database:
- 1
- Justification:
- Guideline, GLP study
- AF for remaining uncertainties:
- 1
- Justification:
- No remaining uncertainties
Acute/short term exposure
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.3 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 33
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 10 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- The DNEL for systemic effects via the dermal route is determined on the basis of route-to-route extrapolation from the oral NOAEL for TEOS as follows: NOAEL = 10 mg/kg bw/day No corrections were made to the NOAEL (oral).
- AF for dose response relationship:
- 1
- Justification:
- A clear NOAEL was established
- AF for differences in duration of exposure:
- 6
- Justification:
- Default (subacute to chronic)
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- The allometric scaling factor accounts for metabolic differences between the test species and humans. This factor is not considered to be relevant for tetramethyl orthosilicate on the following grounds: The hydrolysis product, silicic acid, is inorganic (the soluble form of silica) and is not susceptible to enzymatic metabolism in vivo. The observed biodegradation of the related substance tetraethylorthosilicate (see Section 5) is accounted for by the non-silanol hydrolysis product, ethanol. Toxicological effects of tetramethyl and tetraethylorthosilicate are not attributable to methanol or ethanol (see Section 7.5).
- AF for other interspecies differences:
- 2.5
- Justification:
- Default
- AF for intraspecies differences:
- 2.2
- Justification:
- The intraspecies assessment factor takes account for the variability in sensitivity between individuals. The human population is far more diverse than experimental animals that are bred to be as similar as possible, and unhealthy animals are not allowed to start the study. This AF also covers differences between ethnic groups and age groups. The default intraspecies factors are typically broken down into equal factors accounting for toxicodynamic and toxicokinetic differences, respectively. Accordingly, an interspecies factor of 10 is composed of two identical factors of √10 = 3.2. Likewise, the default for workers (AF = 5) can be split into AFs of √5 = 2.2. The conversion of tetramethyl and tetraethylorthosilicate to their excretion proceeds without enzymatic involvement. Individual genetic dispositions are therefore without effect on these processes. As a result, the toxicokinetic components (3.2 and 2.2 for general population and workers, respectively) can be eliminated from the intraspecies AF for substances that hydrolyse fast into the ultimate excretion product.
- AF for the quality of the whole database:
- 1
- Justification:
- Guideline, GLP study
- AF for remaining uncertainties:
- 1
- Justification:
- No remaining uncertainties
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.3 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 33
- DNEL extrapolated from long term DNEL
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
Additional information - workers
Short-term high exposures are considered unlikely given the high levels of control in place at sites producing and using the substance. DNELs for long-term exposure are therefore adequate to protect against short-term exposures and no separate short-term DNELs are calculated.
The critical effect for the inhalation exposure route is severe respiratory tract damage. The DNEL used for risk characterisation for the inhalation route is therefore based on the local NOAEC from the existing 28-day inhalation study with the registered substance. There were no adverse systemic effects observed in that study up to the highest dose level tested.
For the dermal exposure route, it is not appropriate to use route-to-route extrapolation from local inhalation effects. The DNEL is therefore based, as a worst case, on read-across of the subacute oral toxicity NOAEL for the related substance tetraethyl orthosilicate. Read-across is discussed in Section 7.5. In practice, the potential for systemic uptake of tetramethyl orthosilicate by the dermal route is limited.
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - General Population
There are no consumer uses of tetramethyl orthosilicate therefore DNELs for the inhalation and oral routes are not required. Humans exposed via the environment are not assessed for this substance (see Section 9 of the CSR) therefore no oral DNEL is required.
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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