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: 219-637-2 | CAS number: 2487-90-3
- 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

Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2004-05-06 to 2004-05-08
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- Guideline study with GLP but no analysis of exposure concentrations
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Principles of method if other than guideline:
- OECD. 2000. Guideline for Testing of Chemicals. Daphnia sp., Acute Immobilization Test. Revised Proposal tor Updating Guideline #202. October 2000.
U.S. EPA. 1975. Methods for Acute Toxicity Tests with Fish, Macroinvertebrates and Amphibians. Ecological Research Series (EPA-660/3-75-009). 61 pp. - GLP compliance:
- yes
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: A 100 mg a.i./L stock solution was prepared by adding 0.215 mL of trimethoxysilane to 2.0 L of dilution water (based on a purity of 97.1% and a density of 0.957 g/mL). The solution was mixed overnight with a magnetic stir plate and Teflon®-coated stir bar. Each test concentration was prepared by adding the appropriate amount of the 100 mg a.i./L stock solution to an intermediate vessel and bringing it to a final volume of 1.0 L with dilution water. - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Source: Springborn Smithers culture facility.
- Method of culture: Daphnids were cultured in 1.0-L glass vessels containing 0.80 L of water. Water used to culture the daphnids was prepared in the same manner and has the same characteristics as the dilution water. Daphnids were fed a unicellular green algae, Ankistrodesmus falcatus (4 x 10E7cells/mL) and YCT (yeast, cereal leaves and flaked fish food) suspension daily, at a rate of 2.0 mL algae and 0.5 mL YCT solution per vessel per day. Daphnids were obtained by removing all immature daphnids from the culture vessel, thus isolating mature gravid daphnids <24 hours prior to initiating the test. Young produced by these organisms were subsequently pipetted into the test beakers.
- Age at study initiation: < 24 hours - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- Total hardness and alkalinity: 180 mg/L and 110 mg/L as CaCO3
- Test temperature:
- 20 to 22ºC
- pH:
- 7.7-8.0
- Dissolved oxygen:
- 7.6-9.0 mg/L
- Salinity:
- Not applicable
- Nominal and measured concentrations:
- Nominal concentrations: 0 (Control), 13, 22, 36, 60 and 100 mg a.i./L. (nominal)
- Details on test conditions:
- TEST SYSTEM
- Test vessel: The toxicity test was conducted in 250-mL glass beakers, each containing 200 mL of test solution.
- Aeration: No aeration was provided to the test vessels.
TEST DESIGN
- Replication: Four replicate test vessels were established for each treatment lever and a dilution water control.
- Number of daphnids per treatment: Twenty daphnids were impartially selected and distributed to each concentration and the control (five daphnids per replicate vessel).
- Control group: Dilution water control
TEST MEDIUM / WATER PARAMETERS
- Dilution water source: Fortified well water based on the formula for hard water (U.S. EPA, 1975).
- Dilution water chemistry (hardness, alkalinity. pH, TOC): The dilution water had a total hardness and alkalinity as CaCO3 of 180 mg/L and 110 mg/L, respectively, a pH range of 7.9 to 8.0 and a specific conductivity of 500 umhos/cm. The TOC concentration of the dilution water source was 0.40 mg/L for the month of May 2004.
OTHER TEST CONDITIONS
- Light intensity: The test area was illuminated with fluorescent bulbs at an intensity range of 65 to 83 footcandles at the solutions' surface.
- Photoperiod: The test area received a regulated photoperiod of 16 hours of light and 8 hours of darkness. Sudden transitions from light to dark and vice versa were avoided. Light intensity was measured once during the test.
EFFECT PARAMETERS MEASURED (with observation intervals if applicable): Immobilization .
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2
- Range finding study
- Test concentrations: 1, 10 and 100 mg/L
- Results used to determine the conditions for the definitive study: No immobilisation in any treatment - Reference substance (positive control):
- no
- Key result
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- other: test substance hydrolysis products
- Basis for effect:
- mobility
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- other: test substance hydrolysis products
- Basis for effect:
- mobility
- Details on results:
- - Was control response satisfactory: Yes. No immobilization or adverse effects were observed among daphnids exposed to the control.
- Reported statistics and error estimates:
- No treatment level resulted in any immobilisation. The EC50 and NOEC values were therefore empirically estimated to be =the highest test concentration.
- Validity criteria fulfilled:
- yes
- Conclusions:
- A 48-hour EC50 of >100 mg/L and NOEC of =100 mg/L have been determined for the effects of the test substance on mobility of Daphnia magna. It is likely that the test organisms were exposed to the hydrolysis products of the substance.
Reference
The highest concentration producing 0% immobilization was 100 mg a.i./L. The lowest concentration producing 100% immobilization was > 100 mg a.i./L. Biological observations: - Number immobilized as compared to the number exposed: Number immobilized: 0, Number exposed: 120 (includes control) - Was control response satisfactory (yes/no/unknown): Yes. No immobilization or adverse effects were observed among daphnids exposed to the control.
Description of key information
48-hour EC50: >100 mg/L, mobility of Daphnia magna.
Key value for chemical safety assessment
Additional information
A 48-hour EC50 value of >100 mg/L (nominal concentration) (highest concentration tested) has been determined for the effects of trimethoxysilane (CAS 2487-90-3) on mobility of the freshwater invertebrate Daphnia magna, in accordance with Test Guideline OECD 202 and in compliance with GLP (Springborn Smithers, 2004b).
The test substance is susceptible to rapid hydrolysis and, due to the test media preparation (stirring overnight) and exposure regime (static), it is likely that the test organisms were predominantly exposed to the hydrolysis products of the substance, monosilicic acid and methanol.
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.
