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Diss Factsheets
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EC number: 905-898-6 | CAS number: -
- 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
Partition coefficient
Administrative data
Link to relevant study record(s)
Description of key information
The log pow was determined by QSAR calculation to -1.0
Key value for chemical safety assessment
- Log Kow (Log Pow):
- -1
- at the temperature of:
- 25 °C
Additional information
The log pow values are used for for risk assessment to estimate distribution into environmental compartments, and the estimation of biocencentration factor, BCF. For Classification and Labelling high log pow values are relevant to determine long-term effects in environment. For this substance the log pow values estimated are low for all three constituents. This is consistent with their high water solubility. The impact of any deviations from measured values on risk assessment will be insignificant. In this range there is no impact on Classification and Labelling
The estimated values are therefore considered adequate.
In a multiconstituent substance one could consider to calculate a mean value of the contribution of each constituent to an overall log pow value for the substance. This is not really meaningful, since each constituent will partition to organic phase or water individually.
In this case since the log pow value measured for the most abundant constituent 2,2',2''-nitrilotriethanol in the training set of the model is the highest value and represents the worst case of partitioning to organic phase this value will be taken as representative for the substance “Reaction mass of 2,2',2''-nitrilotriethanol and 2,2'-[[2-[(2-hydroxyethyl)amino]ethyl]imino]bisethanol and 2,2'-iminodiethanol”.
Since the pKa value of the most abundant constituent 2,2',2''-nitrilotriethanol is 7.86, one can expect both charged and neutral species of this component to be present at environmentally relevant pH ( 4 – 9). Since the log pow of the charged species are expected to be lower than for the neutral, the log pow of the neutral constituent will be reported for the substance as a worst case.
Conclusion
The log pow ofReaction mass of 2,2',2''-nitrilotriethanol and 2,2'-[[2-[(2-hydroxyethyl)amino]ethyl]imino]bisethanol and 2,2'-iminodiethanol is -1.00 at pH ~8. This value will also be considered applicable for the environmentally relevant pH range ( 4 – 9) in the risk assessment.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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