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EC number: 292-951-5 | CAS number: 91031-48-0
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
No acute toxicity effects to aquatic invertebrates up to the limit of water solubility.
Key value for chemical safety assessment
Additional information
In general, all EC/EL50(48h) values derived with different invertebrate species for various test substances in the SCAE C2 -C8 category were above the limit of water solubility, so that no toxicity of dissolved substance was found (chemical toxicity). There were, however, several studies describing indirect toxicity by means of physical effects of the test substance at concentrations between 1 and 100 mg/L.
No studies are available for Fatty acids, C16-18, 2 -ethylhexyl esters. Therefore, results are taken from the read-across substances 2-ethylhexyl oleate (CAS 26399-02-0), Fatty acids, C8 -16, 2 -ethylhexyl esters (CAS 135800-37-2) and Fatty acids, C16-18 and C18-unsatd., 2-ethylhexyl esters (CAS 85049-37-2).
One key study investigated the effects of the read across 2-ethylhexyl oleate to the freshwater invertebrate Daphnia magna (Kuech and Wierich 1995). The study was performed according to the EU-method C.2 considering the VCI concept draft for the acute testing of poorly soluble substances from 1994-01-31 for 48 h. The first approach without removal of the insoluble particles resulted in immobilization rates between 0 and 100% (mean: 25%). After removal of insoluble particles (filtration) no effects to Daphnia magna were observed. Thus, it can be stated that the insoluble particles of the test substance resulted in negative physical effects to the test species (e.g. agglutination of gills). No effects in the range of water solubility were observed. This resulted in an EC50 (48h) > 100 mg/L (nominal).
The second key study determined the acute toxicity of the read across substance Fatty acids, C8 -16, 2 -ethylhexyl esters to Daphnia magna according to the EU method C.2 under GLP conditions (Wierich 1998). Different mixing methods of test solution with dilution water were applied. Effects on mobility of the daphnids (about 50 %) were reported for the medium which contained 100 mg/L test substance without further separation of the undissolved test substance (measured concentration at the start of the test: 12.41 mg/L). After filtration of the test solution no effect on mobility was stated (measured concentration at the start of the test: 0.04 mg/L). Similarly to the first read across, these results confirmed the statement, that the observed effects are most likely physical and not systemic effects. The resulting EC50(48h) was reported as >100 mg/L (nominal).
A supporting study on the marine species Acartia tonsa as category read-across from Fatty acids, C16-18 and C18-unsatd., 2-ethylhexyl esters (CAS 85049-37-2), tested as WAF, reported an EL50(48h) > 2047 (1646 -2470) mg/L (Hudson 2000).
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