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Diss Factsheets
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EC number: 931-341-1 | CAS number: 68955-55-5
- 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
Partition coefficient
Administrative data
Link to relevant study record(s)
Description of key information
The log Pow is estimated conservatively to be < 2.7.
Key value for chemical safety assessment
- Log Kow (Log Pow):
- 2.7
- at the temperature of:
- 20 °C
Additional information
The log Pow for C12 -18 AO has been estimated using the approximate solubility in n-octanol and water [Younis, S]. The value obtained was -0.04. The same author also measured the log Pow using an HPLC method, resulting in a log Pow of 1.05. This result has been disregarded as the HPLC method is not appropriate for surfactants.
The log Pow of C12 -14 AO has been estimated on the basis of experimental data for the solubility of this substance in n-octanol and literature data for the critical micelle concentrations of the C12 and C14 alkyl dimethylamine oxides. The result was log Pow < 2.7. This is considered to be a worse case value for the following reasons:
Surfactants can form different types of solutions in water (e.g. mono-molecular-, micellar-, hexagonal or lamellar solutions) depending on concentration and temperature. The mono-molecular solubility of a surfactant is defined by the critical micelle concentration (cmc). If cmc data are available, they may be used as a worst-case approach in cases where the resulting log Pow is not critical. However, from a physico-chemical point of view, the cmc is not a good descriptor for the water solubility, as the micelles themselves completely dissolve in water. The rationale behind using the octanol/water solubility ratio as a measure for the octanol/water partitioning coefficient is that material insoluble in octanol would be “pushed” into the water phase while material insoluble in water would be “pushed” into the octanol phase. With micelles, this is definitely not true. Micelles form an isotropic, homogeneous solution in water and cannot partition into an organic phase due to their hydrophilic nature. Further, the typical lifetime of surfactant micelles is only a few milliseconds, and the lifetime of micelle/bulk exchange of surfactant molecules is only a few µs, i.e. there is a very rapid exchange between mono-molecular dissolved and micellar dissolved surfactant molecules. This is in stark contrast to classical undissolved material, which has molecular lifetimes of several seconds or longer. Thus, the cmc underestimates the total solubility of a surfactant and hence overestimates the partition coefficient.
Taking all the available evidence together it has been concluded that it is valid to use the same limit value of log Pow < 2.7 for C12 -18 AO, as this is still likely to overestimate the partition coefficient.
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