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EC number: 203-058-7 | CAS number: 102-82-9
- 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
Log Pow = 3.34 at 25 °C and pH 9.35(measured; Laus, 2010)pH was measured with 9.35. The following result was obtained: Log Pow = 3.338 ± 0.046 (25 °C; pH 9.35) RSD (relative standard variation) = 1.4%
The draw-back of the study is, that Pow was not determined for each ionisation state (protonated / not protonated):
Given the pKa of tributylamine at 25 °C (10.89) at pH of determination (pH 9.35), approximately 97% will be present as tertiary ammonium ion, while ca. 3% will be in the neutral, non-protonated form.
In consequence, log Kow will be lower than 3.34 in the environmentally relevant neutral pH-range, while the log Kow value for the neutral molecule will be higher and could only be determined at very high pH values (pronouncedly higher than pKa of 10.89 at 25 °C).
This fits with the results determined in the supporting study (BASF
Key value for chemical safety assessment
- Log Kow (Log Pow):
- 3.34
- at the temperature of:
- 25 °C
Additional information
In the reliable (with restrictions) key study (LAUS, 2010), the log Pow was determined for the submission substance tributylamine according to OECD 123 (Slow-Stirring Method) compliant with GLP. pH was measured with 9.35. The following result was obtained:
Log Pow = 3.338 ± 0.046 (25 °C; pH 9.35)
RSD (relative standard variation) = 1.4%
The draw-back of the study is that Pow was not determined for each ionisation state of the ionisable tributylamine: given a pKa at 25°C of 10.89, at pH 9.35 as determined within the study approximately 3% of tributylamine will be present in the neutral state, while ca. 97% will be present as tertiary ammonium ion.
In conclusion, log Pow will be lower in the environmentally relevant neutral pH range around pH 7, while log Pow will be higher for the neutral, non-protonated form. Pow for the latter could only be determined at very high pH-values significantly above pKa.
This fits with the data from the supporting study (BASF, 1988): a lower log Pow of 2.4 at 25°C was determined at the pH of 9.0. Because pH was less alkaline in this study, a higher fraction of tributylamine was protonated (neutral state ca. 1.27%, i.e. less than half the fraction at pH 9.35) and thus log Pow was lower.
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