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EC number: 429-270-1 | CAS number: 136210-30-5
- 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 fish
Administrative data
Link to relevant study record(s)
Description of key information
The acute toxicity of aspartic acid, N,N'-[methylenebis(2-methyl-4,1-cyclohexanediyl)]bis-, 1,1',4,4'-tetraethyl ester towards fish (Brachydanio rerio) was determined according to the OECD-Guideline 203 yielding a LC0(96 h) ≥ 5 mg/L as no adverse effects were observed at testing concentrations up to the water solubility limit of the test item.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 5 mg/L
Additional information
As the concentration of the test item decreased below 80 % of the nominal concentration, analytical values based on the arithmetic mean of the measured concentrations, were used for the effect evaluation. The losses might be assigned to hydrolytic degradation processes as the stability of the test item in aqueous media at pH 7 and a temperature of 25 °C is characterised by a dissipation half-life of 25.4 h. Therefore, the observed effects cover both, the toxicity of the parent substance as well as the toxicity of the hydrolysis products, although the test media was renewed daily.
To produce the test solutions the test item was weighed daily into water and treated with an ultra-turrax for a selected period. The solution was not filtrated prior to use causing the presence of undissolved particles in the test vessels. Consequently, it cannot be excluded that the observed effects are caused by undissolved particles rather than the dissolved (bioavailable) fraction of the test item. These facts are confirmed by the findings that all of the effective concentrations reported were above the water solubility limit of 5 mg/L.
The investigated concentration range covered concentrations below as well as above the water solubility limit. Even at the first concentration exceeding the water solubility limit, assuming a saturated solution containing the maximal achievable concentration, no adverse effects were observed. Based on these findings it can be concluded that there are no effects up to the water solubility limit of aspartic acid, N,N'-[methylenebis(2-methyl-4,1-cyclohexanediyl)]bis-, 1,1',4,4'-tetraethyl ester and the toxicity toward fish is preferably characterised by a LC0 ≥ 5 mg/L. Therefore, the reported LC50(96 h) of 66 mg/L was not used for the hazard assessment.
Study was performed with aspartic acid, N,N'-[methylenebis(2-methyl-4,1-cyclohexanediyl)]bis-, 1,1',4,4'-tetraethyl ester which is a structural analogue to aspartic acid, N,N'-(methylenedi-4,1-cyclohexanediyl)bis-, 1,1',4,4'-tetraethyl ester. Both substances are diethyl esters of aspartic acid linked to a dicyclohexylmethyldiamine moiety. The difference between these two substances is merely the presence of two methyl groups connected to the cyclohexane rings. This structural analogy was confirmed by the Member State responsible for the notification of both substances under the NONS regulation. The Member State decided that test results obtained for one substance can be transferred to the other substance and that testing of both substances is usually not required. This decision is in accordance with the grouping of substances and read-across approach in Annex XI, 1.5 of the REACH Regulation.
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