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EC number: 217-496-1 | CAS number: 1873-88-7
- 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 and sediment: simulation tests
Administrative data
Link to relevant study record(s)
Description of key information
Biodegradation in sediment: 6.91 years at 12°C (read-across)
Key value for chemical safety assessment
- Half-life in freshwater sediment:
- 6.91 yr
- at the temperature of:
- 12 °C
Additional information
There are no sediment degradation data available for H-L3; an OECD 308 study is available with the analogous substance octamethyltrisiloxane (L3, CAS 107-51-7) and has been read across to the registration substance.
The study was conducted under aerobic conditions with two aquatic freshwater sediment systems (Calwich Abbey Lake sediment: 27.1% w/w sand / 70.4% w/w silt / 2.5% w/w clay [textural class: Silt Loam]; % organic carbon: 4.7 % w/w and Emperor Lake sediment: 63.7% w/w sand / 16.1% w/w silt / 20.2% w/w clay [textural class: Sandy Clay Loam]; % organic carbon: 2.0 % w/w). A half-life of 6.91 years was estimated for transformation of L3 in the Calwich Abbey Lake sediment system. For the Emperor Lake sediment system, a half-life of 3.50 years was determined. The transformation products identified were pentamethyldisiloxanol (PMDS), trimethylsilanol (TMS) and dimethylsilanediol (DMSD); the total amount of CO2captured was very small in both systems, suggesting a low rate of mineralisation.
The target substance (H-L3) and the source substance (L3) are members of the Reconsile Siloxane Category. The Category hypothesis is that stability in sediment is linked to the organic carbon-water coefficient and hydrolysis rates, which are dependent in turn on the structural features and constituent functional groups within the molecule. A comparison of the key physicochemical properties of the two substances is presented in the table below.
Table 4.1.5 Key physicochemical properties of H-L3 and surrogate substance L3
Property |
H-L3 (1873-88-7) |
L3 (107 -51-7) |
|||
Molecular weight |
222.51 |
236.54 |
|||
Log Kow |
6.2 |
6.60 |
|||
Log Koc |
3.8 |
4.34 |
|||
Water solubility (mg/l) |
0.02 (at 22°C) |
0.034 (at 23°C) |
|||
Vapour pressure at 25°C (Pa) |
8.5E+02 |
5.3E+02 |
|||
Hydrolysis half- life at pH 7 and 25°C (d) |
2.2 |
13.7 |
H-L3and the source substance L3 are linear siloxanes with three silicon atoms, alternated by oxygen atoms. In L3, the Si atoms are fully methyl substituted, whereas in H-L3 the central silicon atom is substituted with one hydrogen atom and one methyl group. L3 and H-L3 possess similar physicochemical properties (similar vapour pressure, solubility in water, and Log Koc). Both substances have negligible biodegradability and moderate hydrolysis rates. The hydrolysis half-life for L3 is slower than the hydrolysis half-life for H-L3. Degradation in sediment is expected to be primarily abiotic, and therefore the read-across of sediment degradation data with L3 represents a worst-case scenario. Since the degradation half-life for L3 leads to a conclusion of ‘vP’ for the sediment compartment based on a worst-case half-life of 6.91 years at 12 °C, it is reasonable to read-across the conclusion of ‘vP’ in sediment for H-L3.
Available data for substances in the Category indicate that degradation of siloxanes is predominantly abiotic, with the formation of hydrolytic products. The mineralisation rate is expected to be very slow. The available data for the Category are presented in Table 4.1.6:
Table4.1.6 Reconsile Siloxane Category Simulation test data for degradation in water and sediment
CAS |
Name |
Sediment type |
Results |
Klimisch code |
Reference |
556-67-2 |
Octamethylcyclotetrasiloxane |
Natural sediment (aerobic) |
Half-life (DT50): 242 d in sediment at 24°C (pH 7.9 after acclimation) |
1 |
Dow Corning Corporation (2009b) |
556-67-2 |
Octamethylcyclotetrasiloxane |
Natural sediment (anaerobic) |
Half-life (DT50): 365 d in sediment at 24°C (pH 7.9 after acclimation) |
1 |
Dow Corning Corporation (2009c) |
541-02-6 |
Decamethylcyclopentasiloxane |
Natural sediment (aerobic and anaerobic) |
Half-life (DT50): 1200 d in sediment at 24°C (Non-sterilised. Aerobic.) 2700 d in sediment at 24°C (Sterilised. Aerobic.) Approximately 3100 d in sediment at 24°C (Non-sterilised. Anaerobic. (a good trend of degradation was not able to be established, so half-life is approximate)) 800 d in sediment at 24°C (Sterilised.. Anaerobic.) |
1 |
Dow Corning Corporation (2010b) |
107 -46 -0 |
Hexamethyldisiloxane |
Natural sediment (aerobic) |
Half-life (DT50): 192 d at 12°C (high %OC sediment); 53 d at 12°C (lower % OC sediment) |
1 |
The Dow Chemical Company (2019) |
107-51-7 |
Octamethyltrisiloxane |
Natural sediment (aerobic) |
Half-life (DT50): 6.91 years at 12°C (high %OC sediment); 3.50 years at 12°C (lower % OC sediment) |
1 |
The Dow Chemical Company (2021) |
The chemical safety assessment according to REACH Annex I indicates that it is not necessary to conduct the simulation test on ultimate degradation in surface water, because the risk characterisation ratios (RCRs) for the aquatic compartment, even with the assumption that the parent substance is not biodegradable, are <1.
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