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Diss Factsheets
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EC number: 701-028-2 | 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
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Partition coefficient
Administrative data
Link to relevant study record(s)
Description of key information
Key value for chemical safety assessment
- Log Kow (Log Pow):
- 14
Additional information
All of the available information on TNPP, indicated that it will have a very high octanol-water partition coefficient, with log Kow estimates ranging from 6 to >20. This range takes into account both the highest result obtained using QSAR models and the fact that this substance was expected to have a high log Kow based on its structure.
Considering the high hydrophobic potential of TNPP which contains 27 aliphatic and 18 aromatic carbons, this would be expected for this compound. The draft EU Risk Assessment Report (October 2008) considered this endpoint in detail in a senstivity analysis that was provided in Annex 1 of that assesment. The assesment concluded that a log Kow of 14 is appropriate for TNPP.
Reimer (2001d) concluded that it was not appropriate to conduct the partition coefficient measurement because the solubility of TNPP in water was too low and the reaction of TNPP with octanol does not allow the measurement of adequate TNPP concentrations in octanol. Jakupca (2007) determined that a more appropriate approach at estimating the Kow was an HPLC method based on OECD guidelines 117. The analysis of TNPP was conducted with gradient HPLC. Butyl benzene, diethylhexyl phthalate (DEHP), diisononylphthalate (DINP) and diisodecylphthalate (DIDP) were used as standards with known Kow’s to develop a calibration curve. Based on this approach, TNPP was estimated with a log Kow of 14 or greater. A standard could not be found that had a Kow of 14 to test the calibration.
Modelled data results are provided for comparison, though it appears that the models have limitation to be able to accurately predict the octanol-water coefficient.
Kow calculations for TNPP along with the validity domain of the calculation method used
Program | Valid Kow Range* | TNPP value | Remark |
CLOGP | 0-5 | 19.918 | Very high LogP unrealistic in nature (this remark was associated to the result of the model) In general, CLOGP gives also better estimates with log Kow < 0. |
KOWWIN Version 1.67 | 0-5 (clear estimates in this range most of the time) | 20.05 |
|
SPARC | >5 | 19.02 | Better than KOWWIN and CLOGP for Kow >5. |
* all estimates for Kow around 10 or above should be considered rather as qualitative than quantitative information.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
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