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EC number: - | 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)
- Endpoint:
- partition coefficient
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 15 March 2013 to 21 August 2014
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 117 (Partition Coefficient (n-octanol / water), HPLC Method)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- HPLC method
- Partition coefficient type:
- octanol-water
- Key result
- Type:
- log Pow
- Partition coefficient:
- > 6.5
- Temp.:
- 20 °C
- pH:
- 7
- Details on results:
- The Partition Coefficient is log Pow >6.5.
- Conclusions:
- According the TG OECD 117 and GLP study, the partition coefficient of the test item is greater than > 3.16 x 106, log10 Pow > 6.5, based on the reference standard with the highest log10 Pow tested.
- Executive summary:
A study was conducted in accordance with GLP and OECD Testing Guideline No. 117 to determine the Partition Coefficient of the test item. The chromatography of the test item showed several peaks with well-defined and reproducible retention times. The HPLC method was therefore considered to be suitable for the purpose of the study. The partition coefficient of the test item has been determined to be greater than 3 .16 x 106 (log10 P ow > 6.5).
Reference
Based on the composition of the test material, , the test item contained multiple components and the partition coefficient was expected to be high; therefore, the HPLC method was the most suitable for determination of partition coefficient for this test material.
The method guidelines for the HPLC method state that methanol is the preferred solvent for mobile phase; however, the test material demonstrated insufficient solubility in methanol for this to be practical. Therefore, THF was used in place of methanol in preparing the mobile phase for the testing.
Preparation of reference standard solution :
Solutions of reference standards (see following table) were prepared in THF.
Standard | Purity (%) | Concentration (mg/L) |
2-Butanone | >99.7 | 5.13x 103 |
Toluene | >99 | 3.59 X 103 |
Naphthalene | 99 | 438 |
Phenanthrene | 97 | 28.0 |
Triphenylamine | 99+ | 199 |
DDT | 98 | 207 |
The dead time and the retention times, capacity factors (k') and log10 Pow values for the reference standards are shown in the following tables:
Standard | Retention Time (min) | Mean Retention Time (min) | Capacity Factor (k') | Log10 k’ | Log10 Pow | ||
Injection 1 | Injection 2 | ||||||
2-Butanone | 1.922 | 1.924 | 1.923 | 0.253 | -0.597 | 0.3 | |
Toluene | 3.383 | 3.386 | 3.385 | 1.21 | 8.10 x 10-2 | 2.7 | |
Naphthalene | 3.331 | 3.334 | 3.333 | 1.17 | 6.86 x 10-2 | 3.6 | |
Phenanthrene | 3.575 | 3.574 | 3.575 | 1.33 | 0.123 | 4.5 | |
Triphenylamine | 4.972 | 4.972 | 4.972 | 2.24 | 0.350 | 5.7 | |
DDT | 6.647 | 6.648 | 6.648 | 3.33 | 0.523 | 6.5 |
The chromatography of the test item showed several peaks with well-defined and reproducible retention times. Based on the chromatographic data, the test item was considered to be stable during the test procedure.
Partition coefficient of sample :
The retention times, capacity factors and log10 Pow values determined for the sample are shown in the following table
Peak | Injection | Retention Time | Capacity Factor (k') | Log10 k' | Log10 Pow |
1 | 1 | 22.008 | 13.3 | 1.13 | > 6.5 |
2 | 22,017 | 13.3 | 1.13 | >6.5 | |
2 | 1 | 25.088 | 15.3 | 1.19 | > 6.5 |
2 | 25.151 | 15.4 | 1.19 | >6.5 | |
3 | 1 | 28.478 | 17.6 | 1.24 | > 6.5 |
2 | 28.513 | 17.6 | 1.25 | >6.5 | |
4
| 1 | 32.064 | 19.9 | 1.30 | > 6.5 |
2 | 32.164 | 20.0 | 1.30 | >6.5 | |
5 | 1 | 36.504 | 22.8 | 1.36 | > 6.5 |
2 | 36.516 | 22.8 | 1.36 | >6.5 | |
6 | 1 | 41.421 | 26.0 | 1.42 | >6.5 |
2 | 41.435 | 26.0 | 1.42 | >6.5 | |
7 | 1 | 47.163 | 29.7 | 1.47 | > 6.5 |
2 | 47.082 | 29.7 | 1.47 | >6.5 | |
8 | 1 | 53.339 | 33.7 | 1.53 | > 6.5 |
2 | 53.372 | 33.8 | 1.53 | >6.5 | |
9 | 1 | 60.687 | 38.5 | 1.59 | > 6.5 |
2 | 60.758 | 38.6 | 1.59 | >6.5 | |
10 | 1 | 68.510 | 43.6 | 1.64 | > 6.5 |
2 | 68.197 | 43.4 | 1.64 | > 6.5 | |
11 | 1 | 77.988 | 49.8 | 1.70 | > 6.5 |
2 | 77.067 | 49.2 | 1.69 | >6.5 |
Description of key information
In an OECD 117 study conducted according to GLP, the Partition Coefficient of the test material is log Pow greater than 6.5.
Key value for chemical safety assessment
- Log Kow (Log Pow):
- 6.5
- at the temperature of:
- 20 °C
Additional information
Key Study:
In an OECD 117 study, conducted on the registered substance according to GLP, the Partition Coefficient of the test material is log Pow greater than 6.5.
Supporting Studies:
In an EU Method A8 study, not conducted according to GLP, the Partition Coefficient of the structurally similar read across substance is greater than 5.7 at 23°.
In an EU Method A8, not conducted according to GLP, the Partition Coefficient of the structurally similar read across substance is log Pow greater than 5.7 at 23°.
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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