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EC number: 932-185-7 | CAS number: 1187742-72-8
- 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
Key value for chemical safety assessment
Additional information
According to the REACH regulation Annex IX column 2, studies on the biodegradation in water and sediment do not need to be conducted if the test item is readily biodegradable.
However, additional data obtained from different wastewater simulation tests conducted in accordance of OECD guideline 314 are available. The results of these studies were used to calculate the degradation kinetic constant k for STP, surface water and soil.
In three die-away studies performed in accordance with OECD guideline 314 A and 314 B the biodegradation potential of AES (C14, 3EO) within wastewater was investigated. For testing raw sewage and activated sludge (collected on different dates) from a municipal waste water treatment plant receives predominantly domestic wastewater was used. The removal of AES (C14, 3EO) in raw sewage was 98.8% after 24 h and 98.0% in activated sludge after approx. 5 h.
Using raw sewage as inoculum the test substance was converted to metabolites and incorporated into solids. Mineralisation did not occur. Using activated sludge as inoculum the test substances was mineralized, converted to metabolites and incorporated into solid (P&G, 1988).
In a further wastewater simulation study Marks (P&G, 1994) investigated the degradation of AES (C14, 3EO) under aerobic conditions in accordance with OECD 314 B. Using activated sludge of a sewage treatment plant fed predominately with domestic sewage AES (C14, 3EO) was mineralized to 88.3% after 28 days of exposure.
In a test conducted similar to OECD 314 C AES (C14, 3EO) was incubated in anaerobic digester sludge. After 21 h 91% of the radiolabelled test substance was mineralized. The half-life for primary degradation was determined as 2.6 h while the half-life of ultimate degradation was 3 h (P&G, 1994).
This result was supported by a similar test with AES (C14, 3EO) according to OECD 314 C. After 14 days 88% of the applied radioactivity was recovered in evolving gases. The half-life was determined to be 0.67 d (P&G, 1994).
Biodegradation of the AES (C14, 3EO) directly discharged into surface water was simulated in a test following the procedures of OECD guideline 314 D. In surface water (89% river water, 10% sewage treatment plant effluent and 1% activated sludge) 39.7% of AES (C14, 3EO) were mineralized after 48 hours. Remained parent compounds and metabolites were not found. However, 60.3% were determined as non-extractable residues (P&G, 1996).
In another simulation test in surface water in accordance to OECD guideline 314 D a mineralization rate > 87% was observed after 28 days of exposure (P&G, 1994).
Taking into account all available results obtained from the different simulation tests conducted according to OECD guideline 314 it was demonstrated, that alkylethoxysulfates are not persistent in water and are ultimately removed under aerobic and anaerobic conditions.
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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