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EC number: 205-746-2 | CAS number: 149-74-6
- 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
- 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)
- Qualifier:
- according to guideline
- Guideline:
- other: ISO Guideline No 14593 (Water quality- Evaluation of ultimate aerobic biodegradability of organic compounds in aqueous medium -Method by analysis of inorganic carbon in sealed vessels (CO2 headspace test)
- GLP compliance:
- yes
- 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): Secondary treatment stage of the Severn Trent Water Plc sewage treatment plant at Loughborough, UK, which treats predominantly domestic sewage.
- Preparation of inoculum for exposure: Sample effluent filtered through coarse filter paper. Filtrate sparged with CO2-free air for approx. 1hr. Inoculum was allowed to settle for approx. 1 hr prior to removal of an aliquot of the supernatant for use in the test. - Duration of test (contact time):
- 60 d
- Initial conc.:
- 740 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- CO2 evolution
- Parameter followed for biodegradation estimation:
- DOC removal
- Details on study design:
- TEST CONDITIONS
- Solubilising agent (type and concentration if used): Parent material dispersed directly in culture medium with aid of ultrasonication for approx 60 mins.
- Test temperature: 20 ± 1°C
- Continuous darkness: yes
TEST SYSTEM
- Culturing apparatus: 125 ml glass Wheaton bottles sealed using Teflon lined silicon speta and aliminium crimp caps, each containing 107 ml solution (headspace to liquid ration of 1:2.
- Number of culture flasks/concentration: 60 replicates test substance, 39 replicates reference substance, 60 replicates control, 15 replicates toxicity control
SAMPLING
- Sampling frequency: Determination of CO2 produced on days 0, 2, 7, 10, 14, 21, 28, 35, 42, 49, 60 (0, 2, 7, 10 and 14 for toxicity control). Measurement of DOC on days 0, 21, 35, 42, 49, 60.
- Sampling method: CO2: triplicate control, reference substance and test substance vessels were sacrificed on each sampling. DOC: duplicate vessels per sampling.
CONTROL AND BLANK SYSTEM
- Inoculum blank: Yes.
- Toxicity control: Yes - Reference substance:
- benzoic acid, sodium salt
- Key result
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 1
- Sampling time:
- 28 d
- Key result
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 0
- Sampling time:
- 60 d
- Key result
- Parameter:
- % degradation (DOC removal)
- Value:
- 0
- Sampling time:
- 60 d
- Details on results:
- Toxicity control attained 40% degradation after 14 days, confirming that test substance was not toxic to the microorganisms in the study.
- Results with reference substance:
- Reference substance attained 85% degradation after 14d.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- A biodegradation rate of 0% in 28d was determined in a reliable study conducted according to an appropriate test protocol, and in compliance with GLP.
Reference
Table 1: Percent degradation values (CO2 determination)
Type of suspension |
% degradation at sampling time (days) |
|||||||||||
0 |
2 |
7 |
10 |
14 |
21 |
28 |
35 |
42 |
49 |
60 |
|
|
Reference substance |
-1 |
64 |
79 |
84 |
85 |
79 |
76 |
77 |
73 |
72 |
74 |
|
|
|
|
|
|
||||||||
Test sample |
0 |
0 |
0 |
0 |
2 |
1 |
1 |
0 |
0 |
-1 |
-1 |
|
|
|
|
|
|
||||||||
Toxicity control |
0 |
29 |
36 |
36 |
40 |
- |
- |
- |
- |
- |
- |
|
|
|
|
|
|
||||||||
|
|
|
|
|
Description of key information
Biodegradation in water (screening tests): 0% in 28 days (OECD 310), read-across from a structurally-related substance. No significant biodegradation of the silanol hydrolysis product is expected.
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 dichloro(methyl)(phenyl)silane, therefore good quality data for the structurally-related substance, trichloro(phenyl)silane (CAS 98-13-5), have been read across. Both substances hydrolyse to structurally-related hydrolysis products, methylphenylsilanediol and phenylsilanetriol respectively; the other hydrolysis product being hydrochloric acid.
Dichloro(methyl)(phenyl)silane and trichloro(phenyl)silane are within an analogue group of substances which in general, exhibit no evidence of any significant biodegradation once hydrolysis and subsequent biodegradation of alkoxy/acetoxy groups has been taken into account.
Table 4.1.6 presents ready biodegradation data available for relevant analogue substances and the closest available analogue, trichloro(phenyl)silane selected for read-across.
It is therefore considered valid to read-across the results for trichloro(phenyl)silane to fill the data gap for the registered substancesince the source and target substances generate similar silanol hydrolysis products. Additional information is given in a supporting report (PFA, 2013f) attached in Section 13.
Table 4.1.6 Ready biodegradation data available for relevant substances
CAS |
Name |
Readily biodegradable? Yes/no |
Result: Biodegradation after 28 day |
Guideline |
Reliability |
Corrected % biodegradation once alkoxy/acetoxy biodegradation is accounted for |
No CAS. EC no. 410-270-5 |
3-(3-Chloro-4-fluorophenyl)propyldimethylchlorosilane |
No |
8% |
OECD 301B |
1 |
-12 (i.e. 0) |
52301-18-5 |
Tris[(1-methylethenyl)oxy]phenylsilane |
Yes |
96% |
MITI |
1 |
90 |
98-13-5 |
Trichloro(phenyl)silane |
No |
0% after 60d |
OECD 310 and ISO Guideline 14593 |
1 |
0 |
No CAS/ EC no. |
p-(trihydroxysilyl)styrene |
No |
26% BOD; 29% TOC; 100% HPLC |
OECD 301C |
1 |
2 |
166255-23-8 |
4,6-Bis(Carbonylphenyl)-2(3(Triethoxysilyl)propyl)-1,3-Phenylenbisphenylmethanon |
No |
5% |
OECD 301D |
1 |
-20 (i.e. 0) |
17890-10-7 |
Benzenamine, N-[(dimethoxymethylsilyl)methyl]- |
yes, but not meeting 10-day window |
59-63% |
OECD 301F |
1 |
54 |
250783-08-5 |
3-[(4'-acetoxy-3'-methoxyphenyl)propyl]trimethoxysilane |
No |
30% |
OECD 301D |
1 |
13 |
In the study with trichloro(phenyl)silane (CAS 98-13-5), 0% biodegradation was observed in 28 days.
Trichloro(phenyl)silane (CAS 98-13-5), hydrolyses within the timescale of the ready biodegradation study to phenylsilanetriol and hydrochloric acid.
No significant biodegradation is expected for the silanol hydrolysis product.
Biodegradation is not relevant for the non-silanol hydrolysis product, hydrochloric acid being an inorganic substance.
Reference:
PFA (2013f). Peter Fisk Associates, Biodegradation Main Analogue Group report, PFA.300.005.007
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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