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EC number: 273-295-9 | CAS number: 68955-98-6
- 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
Long-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
No toxicological effects on aquatic invertebrates were observed up to the limit of water solubility of Fatty acids, C16-18 and C18-unsatd., branched and linear regarding mortality and reproduction (NOELR >= 5 mg/L Daphnia magna).
Key value for chemical safety assessment
Additional information
One study is available on the long-term toxicity of Fatty acids, C16-18 and C18-unsaturated, branched and linear, “Monomer acid” (CAS No. 68955-98-6) to aquatic invertebrates. The study was conducted according to the OECD guideline 211 under GLP conditions. As the test substance is a UVCB and poorly soluble in water, the test solutions were prepared as water accommodated fractions (WAF) with differential loadings. The test organism Daphnia magna was exposed to the test substance at loadings of 0.1, 0.5, 1.25 and 5.0 mg/L for 21 days. The analytical monitoring of the test concentrations showed that the test substance was present in the test solutions and that the WAFs were stable. Based on preliminary media preparation trials, 5.0 mg/L was the highest concentration at which a stable WAF could be obtained. However, as the test substance is a poorly soluble UVCB substance, the fatty acid cluster of the original test item differs from the soluble part in the WAF fraction, due to the different solubilities of the constituents. Therefore, as the analytical concentrations do not reflect the concentration of the original test substance, they cannot be used to derive effect values.
No significant effect on reproduction was observed in any of the treatment groups. The NOELR for both cumulative number of offspring and age at first brood was determined to be ≥ 5.0 mg/L.
The effect of the test substance on the length of the daphnids was significant at the three highest test concentrations. However, the observed reduction in growth was very small and obviously only turned out to be significant due to the very consistent length of the animals (low standard deviation) from the lowest treatment and the control groups. Additionally, as stated in the ECHA guidance, the purpose of the test is to determine the effect of the test substance on the reproductive output and the ecologically most relevant response variable is the total number of living offspring produced per parent animal. The hazard assessment is therefore based on the NOELR for reproduction. Moreover, the EC10 for length is also > 1 mg/L and thus does not influence classification.
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