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EC number: 200-624-5 | CAS number: 66-25-1
- 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
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- 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
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- 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:
- 2018-02-19 - 2018-10-24
- 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)
- Version / remarks:
- 13 April 2004
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: A.25: 'Partition Coefficient (n-Octanol/water), high performance liquid chromatography (HPLC) method'
- Version / remarks:
- 7 December 2015
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- HPLC method
- Partition coefficient type:
- octanol-water
- Analytical method:
- high-performance liquid chromatography
- Type:
- log Pow
- Partition coefficient:
- 2.3
- Temp.:
- 25 °C
- pH:
- 5
- Details on results:
- The following deviation from the study plan was observed:
No Laser pointer was used during this study due to an error. This was stated as uncritical, because the prepared solutions were visually clear.
The deviation was assessed and stated by the study director on 15. Nov. 2018. - Conclusions:
- With the calibration function log k versus log POW, the corresponding log POW value of the test item peak was determined with: 2.3 ± 0.0.
- Executive summary:
The study was performed according to OECD 117 and EU method A.24 under GLP using a HPLC with a C18 column. Eight reference items with different retention times and thiourea for the determination of the dead time were used to produce a calibration curve, since retention time on hydrophobic columns and POW are correlated. The reference items were chosen based on the results of the pre-test.
One vial was filled with the reference item mix and one vial with the test item solution. The vials were analysed using the HPLC with the program described below. First one injection from the solvent blank methanol/water 75/25 (v/v) was made. Then three injections were measured from the reference item mix, three injections from the test item and again three injections from the reference item mix.
For each reference item, the capacity factor k was calculated from the retention time of thiourea and the retention time of the respective reference item.
A calibration function (log k versus log POW, linear fit) was determined using the literature values for POW of the reference items and the retention times in the six determinations.
The chromatogram of the test item gave one peak. With the calibration function log k versus log POW, the corresponding log POW value of the test item peak was determined with: 2.3 ± 0.0. This value is the mean ± standard deviation of three independent determinations.
Reference
The retention times of the test item are for
measurement 1: 2.792 min
measurement 2: 2.792 min
measurement 3: 2.792 min.
log POW was calculated from the capacity factor
Using the correlation log k / log POW, the log POW of the peak of test item was calculated as 2.3 ± 0.0 (mean ± standard deviation). Validity criteria are fullfilled.
Description of key information
The study was performed according to OECD 117 and EU method A.24 under GLP using a HPLC with a C18 column. Eight reference items with different retention times and thiourea for the determination of the dead time were used to produce a calibration curve, since retention time on hydrophobic columns and POWare correlated. The reference items were chosen based on the results of the pre-test.
One vial was filled with the reference item mix and one vial with the test item solution. The vials were analysed using the HPLC with the program described below. First one injection from the solvent blank methanol/water 75/25 (v/v) was made. Then three injections were measured from the reference item mix, three injections from the test item and again three injections from the reference item mix.
For each reference item, the capacity factor k was calculated from the retention time of thiourea and the retention time of the respective reference item.
A calibration function (log k versus log POW, linear fit) was determined using the literature values for POWof the reference items and the retention times in the six determinations. The chromatogram of the test item gave one peak. With the calibration function log k versus log POW, the corresponding log POWvalue of the test item peak was determined with:
2.3 ± 0.0. This value is the mean ± standard deviation of three independent determinations.
Key value for chemical safety assessment
- Log Kow (Log Pow):
- 2.3
- at the temperature of:
- 25 °C
Additional information
Octanol-water partitition coefficient of hexanal is reported as log Pow = 1.78 based on handbook data. This handbook data is supported by calculation with EPI Suite Log Kow version 1.68 according to the fragments of the molecule. Calculated value is log Pow = 1.7985.
CRC Handbook:
log Pow = 1.78 at 25 °C
EPI Suite:
1.7985
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