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EC number: 629-735-0 | CAS number: 1226892-50-7
- 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
Biodegradation in water and sediment: simulation tests
Administrative data
Link to relevant study record(s)
Description of key information
Chemically related fatty amine derivatives as for instance tall oil, reaction products with N-(2-aminoethyl)piperazine (AkzoNobel 2010b) has been assessed in a CAS test. Comparable biodegradation pathways of fatty amine derivatives i.e. oxidation of the alkyl hain (primary degradation) and the bioavailability are the keys to justification of the use of read-across of the results obtained CAS unit fed with domestic wastewater.
Key value for chemical safety assessment
Additional information
The Kpsed was determined as 47000 L/kg. The suggested maximum half-life for a readily degradable substance with a Kpsed in the range >10000 L/kg is 30000 days (at 12 ºC). These values are considered as extremely conservative but in the absence of measured data will be used in the exposure assessment as a worst-case. The half-life of the bioavailable fraction of Fatty acids C18 unsaturated diethylenetriamine imidazoline in the water phase of sediments is expected to be in the order of a few days, which is based on experiments with dialkyldimethylammonium salts (van Ginkel et al, 2003).
Biological wastewater treatment
Fatty acids C18 unsaturated diethylenetriamine imidazoline has not been tested in the continuously-fed activated sludge (CAS) test. However, the fate of a number of chemically related fatty amine derivatives as for instance tall oil, reaction products with N-(2-aminoethyl)piperazine(AkzoNobel 2010a) have been assessed in a CAS test. Comparable biodegradation pathways of fatty amine derivatives i.e. oxidation of the alkyl chain (primary degradation) and the bioavailability are the keys to justification of the use of read-across of the results obtained CAS unit fed with domestic wastewater spiked. Removal percentages of the parent compounds from the influent and removal by biodegradation in the CAS unit are given below.
Surfactant |
Removal from wastewater (%) |
Removal by biodegradation (%) |
Tall oil, reaction products with N-(2-aminoethyl)piperazine(CAS no.: 92062-17-4) |
>99.999 |
99.96 |
The removal of Fatty acids C18 unsaturated diethylenetriamine imidazoline from wastewater in biological wastewater systems through read-across is assumed to be >99.999%. The removal by biodegradation in biological wastewater treatment is expected to be >99.8%.
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