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Diss Factsheets
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EC number: 943-007-2 | CAS number: -
- 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
Experimental data on the toxicity of Fatty acids, C12-18, even numbered, 3-methylbutyl esters (CAS 1314763-50-2) to terrestrial organisms are not available. In order to fulfil the standard information requirements set out in Annex IX, in accordance with Annex XI, 1.5, of Regulation (EC) No 1907/2006, read-across to a structurally related source substance was conducted.
In accordance with Article 13 (1) of Regulation (EC) No 1907/2006, "information on intrinsic properties of substances may be generated by means other than tests, provided that the conditions set out in Annex XI are met.” In particular for human toxicity, information shall be generated whenever possible by means other than vertebrate animal tests, which includes the use of information from structurally related substances (grouping or read-across).
Having regard to the general rules for grouping of substances and
read-across approach laid down in Annex XI, Item 1.5, of Regulation (EC)
No 1907/2006 whereby substances may be predicted as similar provided
that their physicochemical, toxicological and ecotoxicological
properties are likely to be similar or follow a regular pattern as a
result of structural similarity.The target and the source substances are
esters of abranched alcoholwith a carboxylic fatty acid chain.. The
fatty acid moiety of the target substance comprises linear carbon chain
lengths of C12-C18 esterified with isopentanol. The source substance is
a C14 linear fatty acid esterified with branched C3 alcohol. Target and
source substancesare characterised by a low water solubility, low vapour
pressure and high log Koc. Thus, the substances are expected to have a
similar environmental fate and ecotoxicity profile.
Based on the ecotoxicological profile of Fatty acids, C12-18, even
numbered, 3-methylbutyl esters toxicity of the substance to terrestrial
organisms is considered as unlikely. The substance is characterised by a
low water solubility (WS <0.05 mg/L). The Guidance on information
requirements and chemical safety assessment, Chapter R7.b (ECHA, 2014)
states that once insoluble chemicals enter a standard STP, they will be
extensively removed in the primary settling tank and fat trap and thus,
only limited amounts will get in contact with activated sludge
organisms. Consequently a significant release to the environment of the
substance via STP effluents is not expected and thus an exposure of
terrestrial organisms is unlikely.
However, when terrestrial organisms are exposed to the substance toxic effects are not expected as demonstrated by a short-term toxicity study with earthworms available for the analogue substance isopropyl myristate (CAS 110-27-0). The toxicity of isopropyl myristate (CAS 110-27-0) to earthworms was evaluated by Steber (1999). Eisenia fetida was exposed to the test substance for 14 days at a concentration of 20,000 mg/kg dw (limit test). No effects on survival during the exposure period were reported, leading to a LC50 (14 d) > 20,000 mg/kg dw.
As stated by ECHA Guidance R.7c the absence of chronic or long-term toxicological effects in aquatic organisms up to the substance solubility limit, can be used as part of a Weight of Evidence argument to modify/waive the data requirements of Annex IX and X. Since no effects on Daphnia were observed up to the limit of water solubility in the available chronic toxicity study it is assumed that long term tests on terrestrial organisms will not result in a different outcome. Furthermore, bioaccumulation or biomagnification through the food chain of the substance is not likely. Though the high log Pow value (log Pow >5) indicates a potential of the substance to bioaccumulate a relevant uptake is not likely. Due to a metabolization via enzymatic hydrolysis a relevant uptake and bioaccumulation in terrestrial organisms is not expected. This is supported by low BCF values (0.325 - 2.087 L/kg; BCFBAF v3.01, Arnot-Gobas, including biotransformation, upper trophic), calculated for the main substance components, indicating a low bioaccumulation potential.The available read across study on the toxicity of the target and source substances to aquatic microorganisms determined no inhibition of microorganisms. The Guidance Document (ECHA, 2014) states that a test on soil microbial activity will only be additionally necessary for a valid PNEC derivation if inhibition of sewage sludge microbial activity has occurred. Further evidence on the lack of toxicity is available from literature data. These data show that soil microorganism communities are well capable of degrading fatty acid esters (Hita et al., 1996 and Cecutti et al., 2002) and use them as energy source (Banchio & Gramajo, 1997). Overall, the substance is unlikely to pose a risk to terrestrial organisms based on a) the lack of exposure and b) the lack of adverse effects and low bioaccumulation potential.
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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