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Diss Factsheets
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EC number: 221-906-4 | CAS number: 3277-26-7
- 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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2008-07-29 to 2008-08-26
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 310 (Ready Biodegradability - CO2 in Sealed Vessels (Headspace Test)
- GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic (adaptation not specified)
- Details on inoculum:
- - Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): A mixed population of sewage sludge microorganisms from the secondary treatment stage of the Severn Trent Water Plc sewage treatment plant at Loughborough, Leicestershire, UK, which treats predominantly domestic sewage.
- Preparation of inoculum for exposure: Filtered through coarse filter paper (first approximate 200 ml discarded). Filtrate sparged with CO2-free air for approximately 1 hour whilst maintaining its pH at 6.5 using concentrated orthophosphoric acid. After sparging, the pH was restored to its original value of 8.0 using 7M NaOH and the inoculum allowed to settle for approximately 1 hour prior to removal of an aliquot (2 litres) of the supernatant for use in the test. The supernatant was maintained on aeration using CO2-free air until use. - Duration of test (contact time):
- 28 d
- Initial conc.:
- 20 mg/L
- Based on:
- other: Carbon
- Parameter followed for biodegradation estimation:
- inorg. C analysis
- Parameter followed for biodegradation estimation:
- DOC removal
- Details on study design:
- TEST CONDITIONS
- Test temperature: 20±1 deg C
- Other: Constant shaking at approximately 150 rpm
TEST SYSTEM
- Culturing apparatus: 125 ml glass Wheaton bottles (total volume when full 160 ml) each containing 107 ml of solution.
- Number of culture flasks/concentration: 45 replicate vessels with concentration 20 mg carbon/l
SAMPLING
- Sampling frequency: Triplicate control, standard material and test material vessels were sacrificed on days 0, 2, 6, 8, 10, 14, 16 and 21 for IC analysis. On day 28, five replicate vessels were sacrificed for IC analysis. Triplicate toxicity control vessels were sacrificed on days 0, 8 and 14 for IC analysis.
- Sampling method: IC analysis - An aliquot (1.0 ml) of concentrated orthophosphoric acid was injected through the septum of each vessel taken for analysis in order to lower the pH of the medium to <3. The vessels were then shaken at approximately 150 rpm (INFORS Version 2 Multitron Incubator) for 1 hour at 20±1 deg C.
- Sampling method: DOC analysis - Samples filtered through Gelman 0.45 µm Acrocap filters (approximately 5 ml discarded) prior to DOC analysis.
CONTROL AND BLANK SYSTEM
- Inoculum blank: 45 replicate vessels
- Toxicity control: 11 replicate vessels. Concentration = 40 mg carbon/l
- Standard: 45 replicate vessels. Concentration = 20 mg carbon/l - Reference substance:
- benzoic acid, sodium salt
- Parameter:
- % degradation (inorg. C analysis)
- Value:
- 0
- Sampling time:
- 28 d
- Details on results:
- DOC analysis conducted on sample taken from the test material vessels on Day 0 and 28 showed that the replicate test material vessels attained 4% to 8% degradation. The higher degradation rates than those determined IC analysis were considered to be due to sampling/analytical variation.
- Results with reference substance:
- 86% degradation after 14 days and 87% degradation after 28 days. (DOC analysis showed 95-100% degradation after 28 days. The higher degradation rates than those determined by IC analyses were considered to be due to incorporation of sodium benzoate into the microbial biomass prior to degradation and hence CO2 evolution occurring.)
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- A biodegradation rate of 0% in 28 days was determined in a reliable study conducted according to an appropriate test protocol, and in compliance with GLP.
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- Refer to Endpoint Summary for justification
- Reason / purpose for cross-reference:
- read-across source
- Remarks:
- 5.2.086
- Parameter:
- % degradation (inorg. C analysis)
- Value:
- 0
- Sampling time:
- 28 d
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- A biodegradation rate of 0% in 28 days was determined in a reliable study conducted according to an appropriate test protocol, and in compliance with GLP.
Referenceopen allclose all
% degradation at sampling time (days) |
|||||||||
0 |
2 |
6 |
8 |
10 |
14 |
16 |
21 |
28 |
|
|
|
|
|
|
|||||
Toxicity control |
0 |
- |
- |
34 |
|
43 |
|
|
|
|
|
|
|
|
|
||||
Test sample |
0 |
0 |
-1 |
0 |
1 |
0 |
0 |
0 |
0 |
|
|
|
|
|
|
||||
Reference substance |
0 |
54 |
63 |
70 |
73 |
86 |
82 |
72 |
87 |
|
|
|
|
|
|
|
|
|
|
Description of key information
Biodegradation in water: screening tests: 0% biodegradation in 28 days (OECD 310), based on read-across from a structurally-related substance.
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
Additional information
There are no reliable ready biodegradation data available for H2-L2. H2-L2 hydrolyses rapidly to dimethylsilanol, and more slowly to dimethylsilanediol. Therefore, good quality data for the structurally-related substance, trimethylsilanol (1066-40-6), have been read across.
Dimethylsilanediol, dimethylsilanol, and trimethylsilanol are within an analogue group of substances. Within this analogue group, in general, the substances exhibit no evidence of any significant biodegradation once hydrolysis and subsequent biodegradation of any alkoxy/acetoxy groups has been taken into account..
It is therefore considered valid to read-across the results for trimethylsilanol to fill the data gap for the registered substance. Additional information is given in a supporting report (PFA, 2013g) attached in Section 13 of the IUCLID dossier.
0% degradation in 28d (CO2 production) was determined for trimethylsilanol.
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.