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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
Adsorption / desorption
Administrative data
Link to relevant study record(s)
Description of key information
The potential of the structural analogue aspartic acid, N,N’-[methylenebis(2-methyl-4,1-cyclohexanediyl) ]bis-,1,1',4,4'-tetraethyl ester to sorb or sediment was determined according to EU-Method C.19 (HPLC-Method) yielding a logKoc between 4.2 and 5.1. The sorption coefficient was determined at pH 6 and pH 8 showing that the sorption behaviour does not depend on the prevailing pH. For environmental assessment a mean log Koc value of 4.7 (Koc 44668) was used (Bayer, 2003).
According to the classification of Swann et al. (1983), the structural analogue aspartic acid, N,N’-[methylenebis(2 -methyl-4,1-cyclohexanediyl) ]bis-,1,1',4,4'-tetraethyl ester has a high potential to sorb on soil.
Key value for chemical safety assessment
- Koc at 20 °C:
- 44 668
Additional information
The applied HPLC method as stipulated in the EU-method C.19 method is suitable to determine sorption coefficients for mixtures having logKoc values up to a value of 5. As the test substance is a mixture of stereoisomeric components, only an unresolved elution band was obtained. Consequently, a logKoc range was reported rather than a single value.
In the underlying method, the calibration was based on standards with a maximal logKoc of 4. Thus, the logKoc of the test substance could solely be evaluated by linear extrapolation beyond the prescribed calibration range.
To comply with the requirements of the EU-guideline C.19 for the measurement of ionisable substances, the sorption coefficient was determined at pH 6 and pH 8.Aspartic acid, N,N'-[methylenebis(2 -methyl-4,1 -cyclohexanediyl)]bis-, 1,1',4,4'-tetraethyl ester as an organic base, is partly ionized at pH 6 and non-ionised at pH 8. The pKa of the test substance was estimated prior to the experiment by the means of the software ACD/pKa v 6.0 to select the required pH values.
The determined sorption coefficient (logKoc) at pH 6 (ionised form) covers the range between 4.3 and 5.1, whereas the logKoc of the non-ionised form of this organic base ranges between 4.2 and 5.1. Based on theses results it can be seen, that the sorption behaviour does not depend on the prevailing pH.
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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