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EC number: 800-029-6 | CAS number: 1290049-56-7
- 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
A waste water treatment simulation test was performed with ethanol, 2,2’-[[3-[2-hydroxyethyl]amino]propyl]-iminobis-, N-(hydrogenated tallow alkyl) derivatives. A removal of >99.97% was observed using specific chemical analyses (LC-MS/MS) of the effluent. Also the sorption to sludge was measured and this accounted for 3.8 % of the total removal. Biodegradation is therefore responsible for 96.2% of the removal.
Key value for chemical safety assessment
- Half-life in freshwater sediment:
- 30 000 d
- at the temperature of:
- 12 °C
Additional information
The removal of ethanol, 2,2’-[[3-[2-hydroxyethyl]amino]propyl]-iminobis-, N-(hydrogenated tallow alkyl) derivatives in biological treatment plants was simulated in a continuously-fed activated sludge (CAS) unit fed with domestic wastewater. Ethanol, 2,2’-[[3-[2-hydroxyethyl]amino]propyl]-iminobis-, N-(hydrogenated tallow alkyl) derivatives were spiked at a nominal influent concentration of 28.3 mg/L (20.0 mg/L carbon; calculated) for a period of 62 days and included a control fed with domestic wastewater only. The immediate high carbon removal percentages can be attributed to adsorption and probably biodegradation. The mean carbon removal percentage of ethanol, 2,2’-[[3-[2-hydroxyethyl]amino]propyl]-iminobis-, N-(hydrogenated tallow alkyl) derivatives calculated over 15 measurements obtained from day 47 to 62 of the test was 99 ± 2% (95% confidence interval). These high removal percentages strongly indicate that ethanol, 2,2’-[[3-[2-hydroxyethyl]amino]propyl]-iminobis-, N-(hydrogenated tallow alkyl) derivatives is biodegraded completely. Formation of water soluble compounds during biological treatment of ethanol, 2,2’-[[3-[2-hydroxyethyl]amino]propyl]-iminobis-, N-(hydrogenated tallow alkyl) derivatives can be excluded. An accurate assessment of the removal of 2,2’-[[3-[2-hydroxyethyl]amino]propyl]-iminobis-, N-(hydrogenated tallow alkyl) derivatives was established with specific analyses. A removal percentage of >99.97 was observed for ethanol, 2,2’-[[3 -[2-hydroxyethyl]amino]propyl]-iminobis-, N-(hydrogenated tallow alkyl) derivatives in a waste water treatment simulation test. Adsorption accounted for only 3.8% of the total removal whereas biodegradation was responsible for 96.2% of the observed removal from the wastewater
In conclusion, the CAS test demonstrates that ethanol, 2,2’-[[3-[2-hydroxyethyl]amino]propyl]-iminobis-, N-(hydrogenated tallow alkyl) derivatives is almost completely removed from the wastewater in conventional biological wastewater treatment plants. Ethanol, 2,2’-[[3-[2-hydroxyethyl]amino]propyl]-iminobis-, N-(hydrogenated tallow alkyl) derivatives is primarily removed by biodegradation.
This test result of ethanol, 2,2’-[[3-[2-hydroxyethyl]amino]propyl]-iminobis-, N-(hydrogenated tallow alkyl) derivatives can be used for the other ethanol, 2,2’-[[3-[2-hydroxyethyl]amino]propyl]iminobis-, N-alkyl derivativesas a worst-case because all ethoxylated alkyl-1,3-diaminopropanes tested are readily biodegradable and the reduced sorption is expected for fatty amine derivatives with shorter alkyl chains is compensated by higher removal by biodegradation.
The Kpsed was determined as 43274 L/kg. The suggested maximum half-life for a readily degradable substance with a Kpsed in the range >10000 and < 100000 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 ethoxylated diamines in the water phase of soils is expected to be in the order of a few days,which is based on experiments with dialkyldimethylammonium salts (van Ginkel et al, 2003).
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