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EC number: 266-936-9 | CAS number: 67701-12-6 This substance is identified by SDA Substance Name: C14-C18 and C16-C18 unsaturated alkyl carboxylic acid zinc salt and SDA Reporting Number: 04-006-09.
- 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
Phototransformation in air
Administrative data
Link to relevant study record(s)
Description of key information
The assessment entity “Ol” is a mixture of naturally occurring C14-18 saturated and C16-18 unsaturated fatty acids. Therefore, the endpoint is addressed with publicly available data on fatty acids with the same or similar structure, including conservatively fatty acids with a shorter chain if relevant and appropriate in accordance with previously applied read-across approaches (U.S. EPA Fact Sheet, 2008).
A registration dossier shall contain information on the environmental hazard assessment (Regulation 1907/2006, Article 10). For the environmental hazard assessment of C14-18 and C16-18-unsatd. fatty acids, the standard testing regime set out in Annexes VII to IX is adapted in accordance with Section 1.2 and 1.3 of Annex XI so that “testing does not appear to be scientifically necessary” as follows:
(I) The ecotoxic potential of C14-18 saturated and C16-18-unsatd. fatty acids is assumed to be negligible. Fatty acids are generally not considered to represent a risk to the environment, which is reflected in their exemption from the obligation to register (Annex V, Section 9 and Regulation (EC) No 987/2008). Non-branched aliphatic fatty acids (C5-24) “are expected to be of low toxicity by their nature”, i.e. they “are not considered PBT/vPvB, […] degrade rapidly and have a low potential for bioaccumulation” (ECHA, 2020: Integrated Regulatory Strategy Annual Report May 2020).
(II) Fatty acids can enter air (particulate and vapour phases) but would breakdown very quickly by hydroxyl radical reaction and/or be removed by wet and dry deposition (e.g. particulate-phase fatty acids) (Health Canada, 2017). Based on the hydroxyl radical reaction at 25°C (AOPWin v1.92; EPI Suite v4.1; 12-hr day; 1.5E6 OH/cm3), half-live times of 7.63, 6.53, 5.71, 1.77, ≤1.70 (cis/trans), ≤1.0 (cis/trans) and ≤0.71 (cis/trans) hours were estimated for tetradecanoic acid (C14), hexadecanoic acid (C16), octadecanoic acid (C18), cis-9-hexadecenoic acid (C16 unsatd.), 9-octadecenoic acid (C18 unsatd.), 9,12-octadecadienoic acid (C18 unsatd.) and 9,12,15-octadecatrienoic acid (C18 unsatd.), respectively. In addition, half-live times of 2.12, ≤2.12 (cis/trans), ≤1.06 (cis/trans), and ≤0.71 (cis/trans) hours were determined based on the ozone reaction at 25°C (AOPWin v1.92; EPI Suite v4.1; at 7E11 mol/cm3) for cis-9-hexadecenoic acid (C16 unsatd.), 9-octadecenoic acid (C18 unsatd.), 9,12-octadecadienoic acid (C18 unsatd.) and 9,12,15-octadecatrienoic acid (C18 unsatd.), respectively. Estimates were not provided for the ozone reaction at 25°C for tetradecanoic, hexadecanoic and octadecanoic acid. However, previous QSAR-based estimations with C8 to C18 fatty acids generally pointed to an increased stability with decreasing alkyl chain length with half-life values ranging from 0.6 to 17.5 hours for e.g. C18 and C8 fatty acids, respectively (OECD SIDS, 2014).
(III) Level III fugacity modelling (EPI Suite v4.10) indicates that “aliphatic acids will distribute primarily to soil and water, with lesser amounts to air and sediment. With increasing chain length, the percent distributions to soil and sediment generally increase and the percent distributions to water and air generally decrease” (OECD SIDS, 2014). In summary, available data point to a fast photodegradation of C14-18 saturated and C16-18-unsatd. fatty acids with half-live times in air of < 1 day. Taking into account that C14-18 saturated and C16-18-unsatd. fatty acids are expected to be readily biodegradable under aerobic conditions, further tests on the photodegradation of C14-18 saturated and C16-18-unsatd. fatty acids are not considered to be scientifically necessary.
References:
European Chemicals Agency (ECHA, 2020). Grouping speeds up regulatory action. Integrated Regulatory Strategy Annual Report May 2020.
OECD SIDS initial assessment profile- aliphatic acids (2014), CoCAM 6 September 30-October 3, Italy/ICCA, p. 41
Health Canada’s PMRA, Pest Management Regulatory Agency (2017). Ammonium Salt of Fatty Acid Proposed Registration Decision PRD2017-04, p. 36
Key value for chemical safety assessment
Additional information
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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