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EC number: 947-696-0 | 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 January 2016 to 07 December 2017
- 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:
- yes
- Remarks:
- The results from the two tests do not agree within ± 0.1 log units as specified in the OECD 117 guideline; however it is felt that these results are acceptable based on the chromatography obtained and the nature of the test material.
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- HPLC method
- Partition coefficient type:
- octanol-water
- Analytical method:
- high-performance liquid chromatography
- Key result
- Type:
- log Pow
- Partition coefficient:
- 1.15
- Temp.:
- 25 °C
- pH:
- 7
- Key result
- Type:
- log Pow
- Partition coefficient:
- 1.99
- Temp.:
- 25 °C
- pH:
- 7
- Key result
- Type:
- log Pow
- Partition coefficient:
- 2.36
- Temp.:
- 25 °C
- pH:
- 7
- Key result
- Type:
- log Pow
- Partition coefficient:
- 4.85
- Remarks on result:
- other: The acid: KOWWIN model
- Key result
- Type:
- log Pow
- Partition coefficient:
- 5.167
- Remarks on result:
- other: The monoester: KOWWIN model
- Key result
- Type:
- log Pow
- Partition coefficient:
- 10.936
- Remarks on result:
- other: The diester: KOWWIN model
- Details on results:
- Distribution Coefficient:
- The test material gave three peaks. The mean log Pow values from the two runs were 1.15, 1.99 and 2.36.
- The results from the two tests do not agree within ± 0.1 log units as specified in the OECD 117 guideline; however it is felt that these results are acceptable based on the chromatography obtained and the nature of the test material.
- Calculated Values: Calculated values for partition coefficient were estimated using the KOWWIN model:
The acid: Hydrophobic, predicted partition coefficient (log Kow) 4.8504.
The monoester: Hydrophobic, predicted partition coefficient (log Kow) 5.1671.
The diester: Partition coefficient (Kow) is difficult to measure experimentally, predicted partition coefficient (log Kow) 10.9361. - Conclusions:
- Under the conditions of this study, the test material gave three peaks. The mean log Pow values from the two runs were 1.15, 1.99 and 2.36.
Calculated values for partition coefficient were estimated using the KOWWIN model:
The acid: Hydrophobic, predicted partition coefficient (log Kow) 4.8504.
The monoester: Hydrophobic, predicted partition coefficient (log Kow) 5.1671.
The diester: Partition coefficient (Kow) is difficult to measure experimentally, predicted partition coefficient (log Kow) 10.9361. - Executive summary:
The partition coefficient of the test material was investigated in accordance with the standardised guideline OECD 117, under GLP conditions.
Due to issues with getting acceptable validation results for the analytical procedure, in aqueous pH buffers saturated with n-octanol and n-octanol saturated with aqueous pH 7 buffers, a suitable validated analytical method could not be obtained. As a result, the partition coefficient could not be carried out using the shake flask method so testing was done following the HPLC method as specified in OECD guideline 117. Testing was done at pH 7 only.
Under the conditions of this study, the test material gave three peaks. The mean log Pow values from the two runs were 1.15, 1.99 and 2.36. The results from the two tests do not agree within ± 0.1 log units as specified in the OECD 117 guideline; however it is felt that these results are acceptable based on the chromatography obtained and the nature of the test material.
Calculated values for partition coefficient were estimated using the KOWWIN model:
The acid: Hydrophobic, predicted partition coefficient (log Kow) 4.8504.
The monoester: Hydrophobic, predicted partition coefficient (log Kow) 5.1671.
The diester: Partition coefficient (Kow) is difficult to measure experimentally, predicted partition coefficient (log Kow) 10.9361.
Reference
Analytical Procedure
- Due to the issues with the validation for the analytical method for water solubility it was decided, in consultation with the Sponsor, that the partition coefficient would only be done at one pH level. As the pH level selected for the water solubility test was pH 7 it was decided that this pH would also be used for the partition coefficient test. Based on this, method validation was only carried out at pH 7.
- Four validation batches were analysed as follows:
Log P Val 1: Method validation for pH 7 buffer saturated with n-octanol.
Log P Val 2: Method validation for n-octanol saturated with pH 7 buffer.
Log P Val 3: Method validation for pH 7 buffer saturated with n-octanol and n-octanol saturated with pH 7 buffer using re-dilutions of samples used for the previous two validation batches.
Log P Val 4: Method validation for pH 7 buffer saturated with n-octanol and n-octanol saturated with pH 7 buffer using freshly prepared samples.
- A successful validation could not be achieved with percent recovery and percent relative standard deviations (%RSD) falling outside the acceptance criteria at different points in each batch. As a result, the analytical method was not used and the partition coefficient was carried out using the OECD guideline 117 HPLC method which method that does not require a validated method.
- A summary of the validation results is given below but because the validation was not successful, full results of each validation batch have not been reported.
- The method was assessed against the criteria detailed in the following sections:
Specificity:
Diluting solvent and blank control solutions were generally free of any components that interfered with the analysis of the test material. However, there were a few instances where the responses were > 30 % of the responses for the limit of quantification samples as follows:
First validation (Log P Val 1) for the pH 7 buffer saturated with n-octanol control sample had a response of 47 % of the lowest LOQ sample response for the diester.
Second validation (Log P Val 3) for the pH 7 buffer saturated with n-octanol control sample had a response of 40 % of the lowest LOQ sample response for the diester.
Third Validation (Log P Val 4) for pH 7 buffer saturated with n-octanol control sample had a response of 40 % of the lowest LOQ sample response for the acid.
Based on this it cannot be claimed that the analytical method is totally specific for the test material. However, as the analysis was done using a LC-MS/MS TOF instrument with specific ions being monitored it is more likely that the peaks in the controls were due to carryover of the test material rather than interferences from other substances.
Sensitivity:
The lowest calibration standard was 0.001 µg/mL (0.00037 µg/mL as the acid, 0.000190 µg/mL as the monoester and 0.000439 µg/mL as the diester which demonstrated sufficient sensitivity.
The limit of quantification (LOQ) was defined as the lowest validation level that gave acceptable mean recoveries and percent relative standard deviation (%RSD).
Matrix |
LOQ for the acid (µg/mL) |
LOQ for the monoester (µg/mL) |
LOQ for the diester (µg/mL) |
pH 7 buffer saturated with n-octanol |
Could not be defined as none of the validation batches passed for this constituent |
0.190 |
0.439 |
n-octanol saturated with pH 7 buffer |
979.81 |
501.79 |
1121.56* |
Linearity:
Response of the LC-MS/MS TOF system to the test material was linear with a 1/X weighting, over the range 0.001 to 0.1 μg/mL (0.000371 to 0.0371 µg/mL as the acid, 0.000190 to 0.0190 µg/mL as the monoester and 0.000439 to 0.0439 µg/mL as the diester, with correlation coefficients of > 0.99. However it should be noted that for three of the validation batches (Log P Val 1, Log P Val 2 and Log P Val 3) the calibration failed for the diester (correlation coefficients of 0.91076, 0.90273 and 0.96639, respectively).
Accuracy (Recovery):
The accuracy mean recovery values varied between batches with no one batch showing acceptable mean recoveries at all validation levels for all three constituents.
The summary of the acceptability of the accuracy mean recovery results is as follows:
Matrix |
Validation batch |
Constituent |
Acceptable mean recoveries |
||
Low level |
Mid-level |
High level |
|||
pH 7 buffer saturated with |
Log P Val 1 |
Acid |
No |
No |
No |
Monoester |
No |
No |
Yes |
||
Diester |
No* |
No* |
No* |
||
Log P Val 3 |
Acid |
No |
No |
No |
|
Monoester | Yes |
No |
Yes |
||
Diester |
No* |
No* |
Yes* |
||
Log P Val 4 |
Aid |
No |
Yes |
No |
|
Monoester |
Yes |
Yes |
No |
||
Diester |
Yes |
Yes |
Yes |
||
n-Octanol saturated with pH 7 buffer |
Log P Val 2 |
Acid |
Yes |
No |
No |
Monoester |
Yes |
No |
No |
||
Diester |
Yes* |
Yes* |
Yes* |
||
Log P Val 3 |
Acid |
Yes |
No |
Yes |
|
Monoester |
No |
No |
No |
||
Diester |
No* |
No* |
No* |
||
Log P Val 4 |
Acid |
Yes |
Yes |
Yes |
|
Monoester |
No |
No |
Yes |
||
Diester |
Yes |
Yes |
Yes |
Precision (Repeatability):
The precision %RSD values varied between batches with no one batch showing acceptable recoveries at all validation levels for all three constituents.
The summary of the acceptability of the precision %RSD results is as follows:
Matrix |
Validation batch |
Constituent |
Acceptable %RSD |
||
Low level |
Mid-level |
High level |
|||
pH 7 buffer saturated with |
|
|
|
|
|
Log P Val 1 |
Acid |
Yes |
Yes |
Yes |
|
Monoester |
Yes |
Yes |
Yes |
||
Diester |
No* |
No* |
No* |
||
Log P Val 3 |
Acid |
Yes |
Yes |
Yes |
|
Monoester |
Yes |
Yes |
Yes |
||
Diester |
No* |
No* |
Yes* |
||
Log P Val 4 |
Acid |
No |
No |
No |
|
Monoester |
Yes |
No |
No |
||
Diester |
Yes |
Yes |
Yes |
||
n-Octanol saturated with pH 7 buffer |
Log P Val 2 |
Acid |
Yes |
Yes |
Yes |
Monoester |
Yes |
Yes |
Yes |
||
Diester |
No* |
Yes* |
No* |
||
Log P Val 3 |
Acid |
Yes |
Yes |
Yes |
|
Monoester |
Yes |
Yes |
Yes |
||
Diester |
Yes* |
Yes* |
Yes* |
||
Log P Val 4 |
Acid |
Yes |
Yes |
Yes |
|
Monoester |
Yes |
Yes |
Yes |
||
Diester |
Yes |
Yes |
Yes |
*The calibration lines for the diester failed (correlation coefficients < 0.99) for batches Log P Val 1, Log P Val 2 and Log P Val 3.
- Due to the poor validation results for this method it was considered not possible to successfully validate the analytical method for partition coefficient. This meant that the shake flask and slow stir methods for partition coefficient could not be used. As a consequence so, the OECD 117 HPLC method was used instead.
Interpreting Results
The KOWWIN model uses a "fragment constant" method to predict the partition coefficient (Kow usually reported as the logarithm log Kow). In the "fragment constant" method, a molecule is divided into fragments (atoms or larger functional groups) and the assigned coefficient values for each fragment are added to give the Kow estimate, which is reported as log Kow.
The predicted partition coefficients are interpreted as follows:
For log Kow< 1 – the substance is classified as highly soluble in water (hydrophilic).
For log Kow> 4 – the substance is classified as not very soluble in water (hydrophobic).
For log Kow> 8 – the substance is classified as not readily bioavailable.
For log Kow> 10 – the substance is classified as not bioavailable – partitioning properties are difficult to measure experimentally.
The EPI suite has no statistical test that can be used to judge the reliability of the predicted values. The KOWWIN model is a fragment approach so a surrogate method to judge the reliability of the predictions is to check that all the substructures in the compound of interest are represented in the calculations. If all the substructures are in the model domain, and are accounted for, then this increases the confidence in the predictions and the model result may be assumed to provide relevant information.
Method
Stock solutions were prepared by weighing out the standards and dissolving in methanol as follows:
Reference Substance |
Weight of Reference Substance Used (mg) |
Final Volume of Solution in Methanol (mL) |
Final Concentration, Corrected for Purity (µg/mL) |
Formamide |
212.78 |
10 |
21129.05 |
Acetanilide |
41.45 |
10 |
4136.71 |
Benzonitrile |
70.21 |
10 |
7018.19 |
Methyl benzoate |
53.88 |
10 |
5382.61 |
Ethyl benzoate |
59.57 |
10 |
5951.04 |
Bromobenzene |
69.63 |
10 |
6949.07 |
Naphthalene |
17.61 |
10 |
1759.24 |
Phenanthrene |
13.90 |
10 |
1363.59 |
These solutions were then diluted further to give working solutions:
Reference Substance |
Concentration of Stock Solution (µg/mL) |
Volume of Stock Solution Used (mL) |
Final Volume in Mobile Phase Diluent (mL) |
Final Concentration, Corrected for Purity (µg/mL) |
Formamide |
21129.05 |
0.10 |
10 |
211.79 |
Acetanilide |
4136.71 |
0.05 |
10 |
20.68 |
Benzonitrile |
7018.19 |
0.05 |
10 |
35.09 |
Methyl benzoate |
5382.61 |
0.05 |
10 |
26.91 |
Ethyl benzoate |
5951.04 |
0.10 |
10 |
59.51 |
Bromobenzene |
6949.07 |
0.05 |
10 |
34.75 |
Naphthalene |
1759.24 |
0.10 |
10 |
17.59 |
Phenanthrene |
1363.59 |
0.25 |
10 |
34.09 |
The amounts of the reference substance and test substance injected on the HPLC-UV system were as follows:
Reference Substance |
Concentration of Working Solution used (µg/mL) |
Volume of Solution Injected (µL) |
Amount of Reference Substance Injected (µg) |
Formamide |
211.79 |
10 |
2.11 |
Acetanilide |
20.68 |
10 |
0.21 |
Benzonitrile |
35.09 |
10 |
0.35 |
Methyl benzoate |
26.91 |
10 |
0.27 |
Ethyl benzoate |
59.51 |
10 |
0.60 |
Bromobenzene |
34.75 |
10 |
0.35 |
Naphthalene |
17.59 |
10 |
0.18 |
Phenanthrene |
34.09 |
10 |
0.34 |
Test material |
394.20 |
10 |
3.942 |
Description of key information
Under the conditions of this study, the test material gave three peaks. The mean log Pow values from the two runs were 1.15, 1.99 and 2.36.
For the chemical safety assessment, a weighted average log Pow of 1.84 (at 25 °C) was derived, based on the constituents’ experimentally derived log Pow values and their proportion (%) in the substance (see table below).
Constituent |
Percentage in substance |
Log Pow |
Log Pow component |
The acid |
37.1 |
1.15 |
0.43 |
The monoester |
19 |
1.99 |
0.38 |
The diester |
43.9 |
2.36 |
1.04 |
Weighted average Log Pow Component |
|
1.84 |
Key value for chemical safety assessment
- Log Kow (Log Pow):
- 1.84
- at the temperature of:
- 25 °C
Additional information
The partition coefficient of the test material was investigated in accordance with the standardised guideline OECD 117, under GLP conditions. The study was awarded a reliability score of 1 in accordance with the criteria set forth by Klimisch et al. (1997).
Due to issues with getting acceptable validation results for the analytical procedure, in aqueous pH buffers saturated with n-octanol and n-octanol saturated with aqueous pH 7 buffers, a suitable validated analytical method could not be obtained. As a result, the partition coefficient could not be carried out using the shake flask method so testing was done following the HPLC method as specified in OECD guideline 117. Testing was done at pH 7 only.
Under the conditions of this study, the test material gave three peaks. The mean log Pow values from the two runs were 1.15, 1.99 and 2.36. The results from the two tests do not agree within ± 0.1 log units as specified in the OECD 117 guideline; however it is felt that these results are acceptable based on the chromatography obtained and the nature of the test material.
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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