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EC number: 203-378-7 | CAS number: 106-25-2
- 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:
- 7 January 2012 - 10 March 2012
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- This study was considered as reliable with restrictions because it was not conducted under GLP and there are some lack of details in the study report.
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.8 (Partition Coefficient)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 117 (Partition Coefficient (n-octanol / water), HPLC Method)
- Version / remarks:
- (13 April 2004)
- Deviations:
- no
- GLP compliance:
- not specified
- Type of method:
- HPLC method
- Partition coefficient type:
- octanol-water
- Analytical method:
- high-performance liquid chromatography
- Key result
- Type:
- log Pow
- Partition coefficient:
- ca. 2.76
- Temp.:
- 30 °C
- pH:
- ca. 6.5
- Remarks on result:
- other: +/-0.01
- Conclusions:
- Using the HPLC method, log Pow of nerol was determined to be 2.76 ± 0.01
- Executive summary:
Partition coefficient of nerol was determined at 30°C by the HPLC method, according to EC A8 guideline and OECD guideline 117.
log Pow = 2.76 ± 0.01 (Mean retention time: 5.03 min). This value was the mean ± standard deviation of three independent determinations.
Calibration was appropriately performed between 2.13 and 5.44, in buffered mobile phase at pH=6.5, with 8 references substances. These reference items were chosen in relation to the expected retention time of the test item. For each reference item, two determinations were performed. The capacity factor k was calculated from the retention time of acetone (dead time) and the retention time of the respective reference item. A calibration function (log k versus log Pow, linear fit) was determined based on literature values of Pow for the reference items. Despite the purity of the references substances was missing, the regression equation shows a good linearity. The correlation between log k and log Pow was satisfactory according to the coefficient of determination r² of 0.986. This value was considered as sufficiently high to use the calibration function for the determination of the log Pow of test item nerol. Variations in the retention times of reference items and test item were very small. Therefore a stable configuration of the HPLC-column can be assumed.
A second measurement was carried out on another C18 silica column and gave similar results.
As no observations were made which might cause doubts concerning the validity of the study outcome, the study was considered as reliable without restriction.
The log Pow of nerol being below 3, a low potential for bioaccumulation was shown.
Reference
REFERENCE ITEMS :
Retention times and capacity factors
The retention times of the reference items and calculated capacity factors are presented in the following table.
Compound | tR1(min) | tR2(min) | Mean (min) | Standard deviation (min) | Relative standard deviation | k |
Benzene | 3.77 | 3.77 | 3.77 | 0.00 | 0.00% | 0.47 |
Trichloroethylene | 4.42 | 4.43 | 4.43 | 0.01 | 0.16% | 0.73 |
Toluene | 4.79 | 4.77 | 4.78 | 0.01 | 0.30% | 0.86 |
M-Xylene | 6.58 | 6.57 | 6.58 | 0.01 | 0.11% | 1.56 |
1,2,4-trimethylbenzene | 9.17 | 9.15 | 9.16 | 0.01 | 0.15% | 2.57 |
Benfuracarb | 10.51 | 10.47 | 10.49 | 0.03 | 0.27% | 3.02 |
Butralin | 19.50 | 19.49 | 19.50 | 0.01 | 0.04% | 6.60 |
Heptachlor | 27.13 | 27.13 | 27.13 | 0.00 | 0.00% | 9.58 |
The relative standard deviations of the retention times of the reference items laid all below 0.3%.
Dead times t0:
- 2.56 and 2.57 min (HPLC analysis of reference items mix)
- 2.61 and 2.61 min (HPLC analysis of Benfuracarb).
The mean value is used for calculation of k.
log Pow/log k
log Pow (literature data) and calculated log k of the reference items are presented in the following table.
Compound | log k | log Pow |
Benzene | -0,33 | 2,13 |
Trichloroethylene | -0,14 | 2,4 |
Toluene | -0,06 | 2,69 |
M-Xylene | 0,19 | 3,16 |
1,2,4-trimethylbenzene | 0,41 | 3,65 |
Benfuracarb | 0,48 | 4,22 |
Butralin | 0,82 | 4,93 |
Heptachlor | 0,98 | 5,44 |
log k versus log Pow and Correlation Results
The logarithms of the mean capacity factors, log k, are plotted as a function of log Pow and the linear regression equation is obtained as follows :
log k = (0.383 x log Pow) - 1.075
with a coefficient of determination r2 = 0.986
TEST ITEM NEROL
Retention times and capacity factors
The retention times of the test item are presented in the following table.
tR1(min) | tR2(min) | tR3(min) | Mean (min) | Relative standard deviation | |
Test item | 5,03 | 5,03 | 5,03 | 5,03 | 0,00% |
Dead time | 2,57 | 2,57 | 2,58 | 2,57 | 0,22% |
log Pow/log k
Log Pow is calculated using the regression equation obtained from the reference items.
Capacity factor k, log k and log Pow for the test item are presented in the following table.
Measurement No. | k | log k | log Pow |
1 | 0,96 | -0,02 | 2,76 |
2 | 0,96 | -0,02 | 2,76 |
3 | 0,95 | -0,02 | 2,75 |
Mean | 2,76 | ||
Standard deviation | 0,01 |
Results obtained with another HPLC Column
The retention times and capacity factors of the reference items obtained with a different C18 bonding are presented in the table below.
Compound | tR(min) | k | log k |
Benzene | 4,09 | 0,83 | -0,08 |
Trichloroethylene | 5,13 | 1,3 | 0,11 |
Toluene | 5,63 | 1,52 | 0,18 |
M-Xylene | 8,35 | 2,74 | 0,44 |
1,2,4-trimethylbenzene | 12,19 | 4,47 | 0,65 |
Benfuracarb | 20,17 | 8,04 | 0,91 |
Butralin | 37,29 | 15,72 | 1,2 |
Heptachlor | 47,55 | 20,32 | 1,31 |
The linear regression of the plot log k versus log Pow gives the following equation:
log k = (0.425 x log Pow) – 0.931
with a coefficient of determination r² = 0.992
The retention time of the test item was 6.59 min, corresponding to a log k of 0.29. According to the previous equation, the log Pow can be estimated to 2.88 with this column.
This result is not significantly different from the one obtained previously (2.76). It can be concluded that a change in the C18 silica bonding chemistry has no significant effects on log Pow results.
Description of key information
Using the HPLC method, log Pow of nerol was determined to be 2.76 ± 0.01.
Therefore, nerol shows a low potential for bioaccumulation.
Key value for chemical safety assessment
- Log Kow (Log Pow):
- 2.76
- at the temperature of:
- 30 °C
Additional information
The partition coefficient of nerol was determined by High Performance Liquid Chromatography method according to guidelines OECD 117 and EC A8. No observations were made which might cause doubts concerning the validity of the study outcome. Therefore, the well described result can be used as key value for the partition coefficient of nerol.
Based on the log Kow result, nerol shows a low potential for bioaccumulation.
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