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EC number: 208-764-9 | CAS number: 541-02-6
- 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)
Description of key information
Biodegradation in water: screening tests: 0.14% in 28d (OECD 310)
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
Additional information
A biodegradation rate of 0.14% in 28d, i.e. no biodegradation observed under test conditions, was determined in a reliable study conducted according to an appropriate test protocol, and in compliance with GLP.
Itrich and Federle (2007) conducted a study to investigate the biodegradation of D5 by activated sludge microorganisms. The D5 used in the study was 14C-labelled on the methyl groups. The activated sludge sample used in the experiment was taken from a primarily domestic waste-water treatment plant in Ohio, USA (solids content 2228 mg/l).
The test method used was optimised to account for the volatile and adsorptive behaviour of D5. A stock solution of the test substance was prepared in tetrahydrofuran and then mixed with a concentrated solution of surfactant (a C45 alkyl sulfate) prior to dispersion in water. This dosing system was chosen to simulate domestic ‘grey water’.
The test flasks were sealed.
The final concentrations of D5 and the surfactant in the test vessel were 7.2 μg/l and 3 mg/l, respectively, and the pH of the solution was 7.1
The test vessels were incubated at 22°C for 28 days. During the test the headspace was continuously purged with CO2- free air, and the sludge was continuously mixed using a stirrer.
Traps were used to collect volatiles and CO2 evolved. Samples of the sludge solids were also collected and analysed for both 14C and the parent compound.
Overall recovery of 14C from the test chambers was good (average 102.1% in biotic vessels and 99.2% in abiotic vessels over the 28 days).
No significant formation of 14CO2 was observed during the study.
Some of the tetrahydrofuran extracts from the sludge solids (where most of the radioactivity was found to be distributed) were also analysed for the parent compound. These showed that the majority (88-99%) of the radioactivity in these extracts from both the biotic treatment and the abiotic controls was parent compound. No evidence for metabolites was apparent in these analyses.
Overall the results of this study show that no significant biodegradation or other transformation (e.g. hydrolysis) or loss process (e.g. volatilisation) occurred under the conditions of this study. This supports the result of the key study.
Itrich N R and Federle T W, 2007, Biotransformation of Decamethylcyclopentasiloxane (D5)
in Activated Sludge Waste Water Treatment. Experimental Summary, Environmental Science
Laboratory. Cincinnati, OH: Miami Valley Laboratories.
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