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EC number: 239-593-8 | CAS number: 15545-97-8
- 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:
- 27.07.-28.07.16
- 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:
- 2004
- Deviations:
- no
- 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:
- 2.3
- Temp.:
- 25 °C
- Remarks on result:
- other: HPLC screening; pH not determined
- Conclusions:
- Variations in the retention times of reference items and test item are very small. Therefore a stable configuration of the HPLC-column can be assumed.
The correlation log K/log POW is good: the coefficient of determination r2 was calculated with 0.9582. This value was considered as sufficiently high to use the calibration function for the de-termination of the log POW of the test item 2,2'-Azobis (4-methoxy-2,4-dimethyl valeronitrile).
As peaks 1, 3 and 4 showed a relative area < 5 %, they were considered as minor peaks. Alt-hough area is not necessarily correlated to absolute concentration if UV detection is used, it is assumed that the test item 2,2'-Azobis (4-methoxy-2,4-dimethyl valeronitrile) consists mainly of the second peak, indicating that the log POW should be regarded as 2.3.
No observations were made which might cause doubts concerning the validity of the study outcome. - Executive summary:
The study was performed using a HPLC with a C18 column. Seven 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 65/35 %(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 major and three minor peaks. With the calibration function log K versus log POW, the corresponding log POWs of the major peaks were determined with:
Peak
Mean Area
[mAU*min][1]Relative Area
[%]Mean Retention Time
[min]log POW
±Standard Deviation1
0.151
1.24
2.319
1.1 ± 0.0
2
10.917
89.65
4.257
2.3 ± 0.0
3
0.161
1.32
4.808
2.5 ± 0.0
4
0.292
2.40
7.888
3.1 ± 0.0
[1]mAU = milli absorbance units
These values are the means ± standard deviations of three independent determinations
As peaks 1, 3 and 4 showed a relative area < 5 %, they were considered as minor peaks. Although area is not necessarily correlated to absolute concentration if UV detection is used, it is assumed that the test item2,2'-Azobis (4-methoxy-2,4-dimethyl valeronitrile) consists mainly of the second peak, indicating that the log POWshould be regarded as 2.3.
Reference
Capacity factor, log Capacity Factor, log Pow test item peaks
Peak |
Measurement No. |
K |
log K |
log POW |
1 |
1 |
0.6984 |
-0.1559 |
1.133 |
2 |
0.6968 |
-0.1569 |
1.131 |
|
3 |
0.6977 |
-0.1563 |
1.132 |
|
Mean |
|
|
1.132 |
|
Standard Deviation |
|
|
0.001 |
|
2 |
1 |
2.1164 |
0.3256 |
2.273 |
2 |
2.1154 |
0.3254 |
2.273 |
|
3 |
2.1165 |
0.3256 |
2.274 |
|
Mean |
|
|
2.273 |
|
Standard Deviation |
|
|
0.000 |
|
3 |
1 |
2.5204 |
0.4015 |
2.453 |
2 |
2.5202 |
0.4014 |
2.453 |
|
3 |
2.5173 |
0.4009 |
2.452 |
|
Mean |
|
|
2.453 |
|
Standard Deviation |
|
|
0.001 |
|
4 |
1 |
4.7732 |
0.6788 |
3.110 |
2 |
4.7691 |
0.6784 |
3.109 |
|
3 |
4.7800 |
0.6794 |
3.111 |
|
Mean |
|
|
3.110 |
|
Standard Deviation |
|
|
0.001 |
Description of key information
Based on the findings in the available guideline study the value of 2.3 is selected as key value for the further chemical safety assessment.
Key value for chemical safety assessment
- Log Kow (Log Pow):
- 2.3
- at the temperature of:
- 25 °C
Additional information
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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