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EC number: 287-636-4 | CAS number: 85566-26-3
- 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

Endpoint summary
Administrative data
Description of key information
Additional information
The UVCB Fatty acids, C8-10, Me esters (CAS 85566-26-3) is assumed to be not toxic to fish, but toxic to aquatic invertebrates and algae based on a short-term fish study and on results from the main components of the UVCB for aquatic invertebrates and algae. The result of the fish study (Benijts, 1999) determined LC50 (96h) of 100 mg/L indicating the test substance is not toxic to fish. Methyl decanoate (CAS 110-42-9) and methyl octanoate (CAS 111-11-5) were used as read across for Fatty acids, C8-10, Me esters (CAS 85566-26-3) for short-term toxicity to aquatic invertebrates and toxicity to algae, as these both substances are the main components of Fatty acids, C8-10, Me esters. For methyl decanoate (CAS 110-42-9), a SCAE-Me with a C10 chain length, an EC50 of 1.1 mg/L was determined for Daphnia magna. Two QSAR-calculations for methyl octanoate (CAS 111-11-5), with a C8 chain length of the fatty acid, determined an EC50 of 5.6 mg/L (ECOSAR, 2010) and EC50 = 11.6 mg/L (Ohe, 2005) for aquatic invertebrates. The toxicity to algae was evaluated via QSAR-calculation for both main components of Fatty acids, C8-10, Me esters. For methyl decanoate (CAS 110-42-9) the QSAR-calculation yielded an EC50 of 1.35 mg/L (ECOSAR, 2008) and for methyl octanoate (CAS 111-11-5) an EC50 of 4.76 mg/L (ECOSAR, 2008). All QSAR-calculations are assumed to be valid due to good conformities of the EC50-values for structurally related substances in this category with experimental data.
Due to the ready biodegradability of Fatty acids, C8-10, Me esters no toxicity could be expected for microorganisms and the inhibition of the degradation activity of activated sludge is not anticipated.
A long term exposure of the test substance to the aquatic environment is not expected as only low concentrations of the test substance can be expected in the aquatic environment due to the low water solubility and ready biodegradability. In addition, should the substance be taken up, Fatty Acid Methyl Ester will be extensively metabolized by carboxylesterase enzymes.
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