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EC number: 224-221-9 | CAS number: 4253-34-3
- 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
Long-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- long-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2008-11-14 to 2008-12-05
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 211 (Daphnia magna Reproduction Test)
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- - Sampling method: One sample from the freshly prepared stock solution and duplicate samples from the freshly prepared test media of all treatments were taken taken at a pretreatment period in the first, second and third weeks of the test (days 3, 10 and 14).
The stability of the test media was determined over periods of 48 and 72 hours using sub-samples of the test media that did not contain food or daphnia.
- Sample storage conditions before analysis: Samples were analysed directly on the day of collection. - Vehicle:
- no
- Details on test solutions:
- A 100 mg/L stock suspension of the test substance was prepared by adding the test substance to dilution water. Immediately after adding the substance the pH of the water was adjusted to 8.0 - 8.1. The mixture was then stirred for 24 hours in the dark to dissolve as much test substance as possible. The resulting medium was filtered (0.45 µm cellulose nitrate filter). After filtration the pH was adjusted again to 8.0.Undiluted filtrate and 1:2, 1:4, 1:8 and 1:16 dilutions of the filtrate were tested.
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Strain/clone: Clone 5
- Source: Laboratory stock culture
- Feeding during test
- Food type: Green algae (Desmodesmus subspicatus)
- Amount: 0.10 mg TOC/daphnid on days 0 - 4, 0.15 mg TOC/daphnid on days 5-20
- Frequency: daily
ACCLIMATION
- Type and amount of food: Daily with algae (Desmodesmus subspicatus) and weekly with Tetra Min-extract - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 21 d
- Hardness:
- 250 mg/L as CaCO3
- Test temperature:
- 19 - 22ºC
- pH:
- 7.7 - 8.0 in freshly prepared media
7.6 - 8.7 in aged media - Dissolved oxygen:
- 7.0 - 9.0 mg/L in freshly prepared media
8.1 - 10.4 mg/L in aged media - Salinity:
- Not applicable
- Nominal and measured concentrations:
- Nominal treatments: 0 (Control), filtered 100 mg/L loading rate and 1:2, 1:4, 1:8 and 1:16 dilutions of the filtrate
Measured concentrations: The mean measured Total carbon content of the nominal 100 mg/L filtrate was 10 mg/L. The mean measured concentrations in the 1:2 and 1:4 dilutions of the filtrate were 5.2 and 2.9 mg/L. No analysis results were reported for the 1:8 and 1:16 dilution treatments. - Details on test conditions:
- TEST SYSTEM
- Test vessel:
- Type (delete if not applicable): open
- Material, size, headspace, fill volume: 100 mL glass beakers containing 80 mL of test medium
- Aeration: none
- Renewal rate of test solution (frequency/flow rate): every 2 or 3 days
- No. of organisms per vessel: 1
- No. of vessels per concentration (replicates): 10
- No. of vessels per control (replicates): 10
- Biomass loading rate: 1 daphnid/80 mL of test medium
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Elendt M4 medium prepared by adding analytical grade salts and additives to deionised water
- Culture medium different from test medium: no
- Intervals of water quality measurement: On the occasions of test medium renewal in fresh and old medium
OTHER TEST CONDITIONS
- Adjustment of pH: yes
- Photoperiod: 16 hours light, 8 hours dark
- Light intensity: 50-1200 lux
EFFECT PARAMETERS MEASURED (with observation intervals if applicable): Daily observations of dead parental daphnia. At the same time offspring (dead and alive) were counted and removed.
VEHICLE CONTROL PERFORMED: no
RANGE-FINDING STUDY: no - Reference substance (positive control):
- no
- Duration:
- 21 d
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Duration:
- 21 d
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Duration:
- 21 d
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 10 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- other: Total Organic Carbon
- Basis for effect:
- other: Adult survival and reproduction
- Details on results:
- - Mortality of parent animals: 0
- No. of offspring in the Control after 21 days: 60.2 per surviving parental daphnid - Reported statistics and error estimates:
- There were no effects in the highest treatment and therefore statistical analysis of the results was not required.
- Validity criteria fulfilled:
- yes
- Conclusions:
- A 21-day NOEC value of =100 mg/L has been determined for the effects of the test substance on survival and reproduction of Daphnia magna when expressed in terms of nominal concentrations. When expressed in terms of mean measured TOC concentration in the test medium the NOEC was =10 mg/L. It is likely that the test organisms were primarily exposed to the hydrolysis products of the substance.
Reference
Table 1. Analysis of test media
Nominal treatment |
Mean measured TOC concentration with (SD) (mg/L) |
<LOQ |
100 |
1:16 dilution |
Not determined |
1:8 dilution |
Not determined |
1:4 dilution |
2.87 (0.067) |
1:2 dilution |
5.23 (0.068) |
Undiluted 100 mg/L nominal concentration |
9.96 (0.048) |
Table 2. Test results
Treatment |
Percentage of surviving parental daphnia at end of test |
Average number of offspring per surviving parental daphnia at end of test |
Average number of of offspring as a percentage of Control |
0 (Control) |
100 |
60.2 |
- |
1:16 dilution |
100 |
38.4 |
63.8* |
1:8 dilution |
100 |
59.8 |
99.3 |
1:4 dilution |
100 |
69.4 |
115 |
1:2 dilution |
90 |
67.3 |
112 |
Undiluted 100 mg/L nominal concentration |
100 |
60.1 |
99.8 |
*significantly different from Control
Description of key information
Long-term toxicity to invertebrates: 21 day NOEC=100 mg/l (highest concentration tested) (OECD 211), read-across from a structurally related substance, trichloro(ethyl)silane (CAS 115-21-9). The NOEC is equivalent to=66 mg/l expressed in terms of ethylsilanetriol.
Key value for chemical safety assessment
Additional information
There are no reliable long-term invertebrate toxicity data available for methylsilanetriyl triacetate (CAS 4253-34-3), therefore good quality data for an appropriate structural analogue, trichloro(ethyl)silane (CAS 115-21-9), have been read across. Both substances have structurally similar silanol hydrolysis products, methylsilanetriol and ethylsilanetriol, respectively. The other hydrolysis products are acetic acid and hydrochloric acid, respectively.
A 21 day NOEC value of =100 mg/l (highest concentration tested) has been determined for the effects of trichloro(ethyl)silane (CAS 115-21-9) on reproduction of Daphnia magna. In view of the exposure regime it is likely that the test organisms were exposed predominantly to the hydrolysis products of the tested substance. The results may be expressed in terms of concentration of the hydrolysis product, ethylsilanetriol, by applying a molecular weight correction: (MW of silanol = 108.17 / MW of parent = 163.51) * [CONCENTRATION OF PARENT = =100 mg/l] = =66 mg/l.
Refer Section 6 endpoint summary (Section 7.0 of CSR) for further discussion of the approach to chemical safety assessment for this registration substance, and justification for read-across used.
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