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EC number: 293-170-2 | CAS number: 91052-13-0
- 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
Not readily biodegradable: 24% (CO2 evolution) in 28 days (OECD 301B)
Key value for chemical safety assessment
Additional information
One study investigating the ready biodegradability of Glycerides, C8-18 and C18-unsatd. mono- and di-, acetates (CAS No. 91052 -13 -0) is available (Clarke, 2009). The GLP study is conducted over 28 days according to OECD guideline 301B (CO2 evolution test) using activated sludge from a treatment plant treating predominantly domestic sewage. The test substance concentration tested was 10 mg/L carbon content (15.1 mg test substance/L). After 28 days 24% were biodegraded. Thus, Glycerides, C8-18 and C18-unsatd. mono- and di-, acetates was not readily biodegradable under the chosen test conditions.
Nevertheless, the components of Glycerides, C8-18 and C18-unsatd. mono- and di-, acetates are aliphatic fatty acids esters with glycerol. There are adequate biodegradability data in the scientific literature which support the premise that free fatty acids, would be expected to be rapidly and extensively biodegraded in aerobic systems in the environment (e.g. Swisher, 1987). Also for fatty acid salts with chain lengths up to and including C18 it is reported a complete metabolism under aerobic conditions, so that this substances can be considered to be readily biodegradable (HERA, 2003). Consequently, it can be assumed that the components of Glycerides, C8-18 and C18-unsatd. mono- and di-, acetates should be biodegraded faster than shown in the screening test mentioned above. This assumption is supported by two QSAR estimations which have been calculated for the two main fatty acid components of the described UVCB (C12 mono/diacetate and C14 mono/diacetate) using the program KOCWIN, v2.00 (Gebhardt 2013).
Swisher RD (1987). Surfactant Biodegradation, Marcel Dekker, New York. Biodegradability of fatty acids, pp. 826-827
HERA (2003). Fatty Acid Salts (Soap) Environmental Risk Assessment
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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