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EC number: 946-442-6 | 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
- Data waiving:
- study technically not feasible
- Justification for data waiving:
- other:
- Justification for type of information:
- The substance is a complex mixture, which contains a large number of constituents, which are mostly unkown and which have different solubility (often low solubility) and volatility. In addition its physical state leads to difficulties for physico-chemical testing: It is described as brown to brown red not flowable very hard sticky paste like a resin.
A GLP study has been conducted on another labdanum resinoid substance according to OECD 117 showing a non reliable result (the major peak of the test item detected with a logKow < 0.3 while the substance is mainly insoluble in water)(see disregarded study on labdanum resinoid(ethanol). In addition a feasibiliity studies conducted on other natural complex substances showed that this method is difficult to applicate for this kind of substances due to the very low response of the test items with the HPLC detectors tested (Diode Array Detector and Mass Spectrometry).
Another strategy based on the application of the OECD 123 method and the quantification of the test item in both octanol and water phases by a GC-FID analytical method was considered. However, this approach does not allow to detect the totality of the test item constituents and was not considered as appropriate to define a range of logKow for the whole substance.
Finally the standard tests for partition coefficient endpoint are intended for single substances and are not appropriate for such complex substances because of the limited knowledge of composition and the physical state of the substance. - Reason / purpose for cross-reference:
- data waiving: supporting information
- Endpoint:
- partition coefficient
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Study period:
- run on 2017
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with limited documentation / justification
- Justification for type of information:
- QSAR prediction : The values obtained on known constituents of the substance are not experimental results, however the QSAR model is recommended by the ECHA guidance document on information requirements, is well documented with regard to validation parameters according to OECD principles. Moreover, the constituents of the substance are fully characterised towards the applicability domain.
- Reason / purpose for cross-reference:
- reference to other study
- Principles of method if other than guideline:
- QSAR estimation
- Partition coefficient type:
- octanol-water
- Type:
- log Pow
- Partition coefficient:
- >= 2.29 - <= 15.57
- Remarks on result:
- other: Temperature and pH not provided (QSAR estimation)
- Remarks:
- Range of logKow estimated on a the known constituents of the substance
- Conclusions:
- Log Kow of known constituents of the substance, representing a limited fraction of the composition, were estimated to be between 2.29 and 15.57 (estimated by QSAR)
- Executive summary:
The partition coefficient of the known constituents of the substance were estimated using the recommended QSAR model KOWWIN v1.68, based on Atom/Fragment Contribution (AFC) method. The constituents of the test item were within the applicability domain (MW, descriptors).
This range of logKow was estimated between 2.29 and 15.57, with a standard deviation provided by the model of 0.48.
- Endpoint:
- partition coefficient
- Type of information:
- experimental study
- Adequacy of study:
- disregarded due to major methodological deficiencies
- Study period:
- 06-11 March 2014
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- significant methodological deficiencies
- Justification for type of information:
- A study has been conducted according to OECD 117 leading to a non reliable result (logKow < 0.3 while the substance is mainly insoluble in water) and showing that the conventional standard tests for partition coefficient endpoint are intended for single substances and are not appropriate for such complex substances because of the limited knowledge of composition and the physical state of the substance.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 117 (Partition Coefficient (n-octanol / water), HPLC Method)
- Version / remarks:
- 2004
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.8 (Partition Coefficient - HPLC Method)
- Version / remarks:
- 2008
- Deviations:
- no
- Principles of method if other than guideline:
- not applicable
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- inspected on 29 and 30 November 2010 / signed on 11 April 2011
- Type of method:
- HPLC method
- Partition coefficient type:
- octanol-water
- Type:
- log Pow
- Partition coefficient:
- < 0.3
- Temp.:
- 25 °C
- pH:
- ca. 6
- Remarks on result:
- not determinable because of methodological limitations
- Remarks:
- Assuming that the test item consists mainly of one peak, calculation of logKow, mean and standard deviation of the major component of test item was not possible because the retention time of measurements lay below the retention time of thiourea. So the log POW of the test item is stated as < 0.3.
- Executive summary:
The partition coefficient of the test substance was measured according to the OECD 117/EU A8 guideline, HPLC method. The system was calibrated with seven different references substances.
The measurements of the test item solution were very reproducible ( very small variations in the retention times of reference items and test item) and correlation log K/Log POW is good (r² = 0.9616).
Nevertheless, the log POW of the major peak of test item was not calculable, because during the measurements its retention time lies below the retention time of thiourea and thus not within the range of log Kows of the reference items. The corresponding log Kow is stated as < 0.3 (log POW of 2-Butanone, the reference item with the lowest log POW).
Referenceopen allclose all
Temperature and pH values are not considered in this model.
The estimation is based on the non-ionised form of the molecule.
No Experimental Value Adjustment was made.
The molecular weight of the constituents are between 150.17 and 436.84 g/mol, hence within the estimation domain of the validation set (27.03 -991.15 g/mol), all the functional groups are included in the list of descriptors, and, the occurence of each fragment is below or very closed to the maximum number in the training/validation sets (Appendix D), such as:
Training Set | Validation Set | ||||
Fragment Descriptor & Correction Factor Descriptor | Coef | Max | Number | Max | Number |
-CH3 [aliphatic carbon] | 0,5473 | 13 | 1401 | 20 | 7413 |
-CH2- [aliphatic carbon] | 0,4911 | 18 | 1083 | 28 | 7051 |
-CHO [aldehyde, aliphatic attach] | -0,9422 | 1 | 8 | 2 | 30 |
-CH [aliphatic carbon] | 0,3614 | 16 | 460 | 23 | 3864 |
=CH- or =C< [olefinc carbon] | 0,3836 | 10 | 239 | 10 | 1847 |
-COOH [acid, aliphatic attach] | -0,6895 | 3 | 126 | 3 | 672 |
-tert Carbon [3 ot more carbon attach] | 0,2676 | 4 | 130 | 8 | 1381 |
Fused aliphatic ring unit correction | -0,3421 | 8 | 41 | 8 | 684 |
-OH [hydroxy, aliphatic attach] | -1,4086 | 6 | 187 | 9 | 1525 |
-O- [oxygen, aliphatic attach] | -1,2566 | 5 | 108 | 12 | 1235 |
Aromatic carbon | 0,294 | 24 | 1790 | 30 | 8792 |
-O- [oxygen, one aromatic attach] | -0,4664 | 3 | 203 | 5 | 1770 |
-OH [hydroxy, aromatic attach] | -0,4802 | 3 | 193 | 4 | 611 |
Ketone in a ring [olefin, aromatic attach] -0,5497 | -0,5497 | 2 | 11 | 2 | 104 |
Ortho-Hydroxy to misc. -C(=O)- correction | 0,777 | 2 | 11 | 2 | 82 |
-C(=O)O [ester, aliphatic attach] | -0,9505 | 3 | 113 | 6 | 1178 |
-C(=O)- [carbonyl, aliphatic attach] | -1,5586 | 2 | 54 | 2 | 241 |
Cyclic ester correction | -1,0577 | 1 | 14 | 2 | 144 |
Results:
Reference item:
For each reference item, the retention times, the calculated capacity factors K, logK and log Kow were presented in the following table:
Compound | Mean Retention Time (min) | K | log K | log POW |
Thiourea | 1,482 | 0 | ||
2-Butanone | 1,981 | 0,3369 | -0.4726 | 0.30 |
Benzylalcohol | 2,407 | 0,6241 | -0.2047 | 1.10 |
Acetophenone | 3,016 | 1,0355 | 0.0152 | 1.70 |
Nitrobenzene | 3,645 | 1,4599 | 0.1643 | 1.90 |
Benzene | 5,286 | 2,567 | 0.4094 | 2.10 |
Toluene | 8,596 | 4,8008 | 0.6813 | 2.70 |
Naphthalene | 12,367 | 7,346 | 0.8660 | 3.60 |
Dead time is 1.482 ± 0.002 minutes, with RSD 0.1%.
The RSD of the retention times of the reference items lay all below 0.5 %.
Equation of the regression:
log k = 0.4399 * log POW – 0.6337 with a coefficient of determination r2 = 0.9616
Test item:
Retention Times Test Item
Measurement |
RT 1 |
RT 2 |
RT 3 |
|
min. |
min. |
min. |
Measurement 1 |
1.365 |
1.936 |
5.412 |
Measurement 2 |
1.36 |
1.946 |
5.405 |
Measurement 3 |
1.361 |
1.930 |
5.407 |
Mean |
1.362 |
1.937 |
5.408 |
Standard Deviation |
0.003 |
0.008 |
0.004 |
Areas Test Item
Measurement |
Area Peak 1 |
Rel. |
Area Peak 2 |
Rel. |
Area Peak 3 |
Rel. Area |
|
mAU*min |
% |
mAU*min |
% |
mAU*min |
% |
Measurement 1 |
17.4385 |
95.64 |
0.2898 |
1.59 |
0.1424 |
0.78 |
Measurement 2 |
17.4690 |
94.60 |
0.3843 |
2.08 |
0.1925 |
1.04 |
Measurement 3 |
17.3221 |
94.25 |
0.4228 |
2.30 |
0.1481 |
0.81 |
Mean |
17.4099 |
94.83 |
0.3656 |
1.99 |
0.1610 |
0.88 |
Standard Deviation |
0.45% |
0.76% |
18.73% |
18.31% |
17.05% |
16.48% |
As peaks 2 and 3, showed a relative area < 5%, they were considered as minor peaks.
The calculated values are presented in the following table:
Capacity Factor, log Capacity Factor, log POWTest Item Peaks
Peak |
Measurement No. |
K |
log K |
log POW |
1 |
1 |
-0.0788 |
Not calculable* |
Not calculable* |
2 |
-0.0822 |
Not calculable* |
Not calculable* |
|
3 |
-0.0815 |
Not calculable* |
Not calculable* |
|
Mean |
|
Not calculable* |
Not calculable* |
|
Stand. Dev. |
|
Not calculable* |
Not calculable* |
|
2 |
1 |
0.3065 |
-0.5136 |
0.273 |
2 |
0.3132 |
-0.5041 |
0.295 |
|
3 |
0.3024 |
-0.5194 |
0.260 |
|
Mean |
|
|
0.276 |
|
Stand. Dev. |
|
|
0.017 |
|
3 |
1 |
2.6522 |
0.4236 |
2.403 |
2 |
2.6475 |
0.4228 |
2.402 |
|
3 |
2.6489 |
0.4231 |
2.402 |
|
Mean |
|
|
2.402 |
|
Stand. Dev. |
|
|
0.001 |
*As the retention time of peak 1 lies below the retention time of thiourea, the log POWof peak 1 is not calculable.
log POWwas calculated from the capacity factor as follows:
log POW= (log K + 0.6337) / 0.4399
Description of key information
No range of logKow representative of the test item can be determined (neither with an experimental approach nor with an estimation approach)
Key value for chemical safety assessment
Additional information
The substance is a complex mixture, which contains a large number of constituents, which are mostly unkown but which have different solubility (often low solubility) and volatility. In addition its physical state leads to difficulties for physico-chemical testing: It is described as brown to brown red not flowable very hard sticky paste like a resin.
For such complex substances, the standard tests for partition coefficient endpoint are considered as not appropriate because of the limited knowledge of composition and the physical state of the substance. That is why the test has been waived.
In addition calculated values were provided on known constituents of the substance. However, only a range of logKow on a limited part of the composition of the substance can be calculated using QSAR estimations.
Therefore it is considered that no range logKow representative of the whole test item can be determined (neither with an experimental approach nor with an estimation approach).
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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