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EC number: 226-195-4 | CAS number: 5324-84-5
- 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:
- weight of evidence
- Study period:
- 16 January 2018 - 12 March 2018
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- accepted calculation method
- Remarks:
- Study was conducted in accordance with international guidelines and in accordance with GLP. All guideline validity criteria were met.
- Qualifier:
- according to guideline
- Guideline:
- other: EU Method A.8. (Partition Coefficient - Estimation Method (Solubility Ratio))
- Version / remarks:
- Regulation (EC) 440/2008 of 30 May 2008
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- estimation method (solubility ratio)
- Partition coefficient type:
- octanol-water
- Analytical method:
- other: Not applicable
- Key result
- Type:
- log Pow
- Partition coefficient:
- < -2.25
- Temp.:
- 19.8 °C
- Remarks on result:
- other: Estimated value.
- Remarks:
- Estimation method using solubility ratios.
- Conclusions:
- The partition coefficient of the test item was estimated to be Log Pow = < - 2.25 at a temperature of 20 ± 1.0 °C.
- Executive summary:
EU Method A.8. – The partition coefficient of the test item was determined using the estimation method (solubility ratio). The procedures employed were designed to be compatible with Method A.8., partition coefficient, of Commission Regulation (EC) No 440/2008 of 30 May 2008.
An aliquot of test item (31.5 mg) was placed in a glass vessel, n-octanol was added in a stepwise manner. After each addition of n-octanol, the vessel was shaken for at least 10 min. The sample was then visually checked for undissolved test item. If the test item was not dissolved further n-octanol was added in the manner previously described. The test was performed at 19.8 ℃.
For the test item an estimated partition coefficient of log Pow < - 2.25 was determined. As the limit of the log Pow of the shake flask method is – 2, further dilution of the test item was not pursued.
- Endpoint:
- partition coefficient
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- 16 January 2018 - 28 February 2018
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- unsuitable test system
- Remarks:
- Whilst the study has been conducted according to the guideline method under GLP conditions. The test item is a complex substance that has been determined to be surface active. As such this study must be regarded as not reliable. The nature of the test item means that there is the potential for secondary column interactions to occur, leading to a potential overestimation of the partition coefficient. To mitigate against this phenomenon, this study is being used as a part of a weight of evidence for this endpoint.
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.8 (Partition Coefficient - HPLC Method)
- Version / remarks:
- Regulation (EC) 440/2008 of 30 May 2008
- Deviations:
- yes
- Remarks:
- The study was conducted on a surface active substance.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 117 (Partition Coefficient (n-octanol / water), HPLC Method)
- Version / remarks:
- April 2004
- Deviations:
- yes
- Remarks:
- The study was conducted on a surface active substance.
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- HPLC method
- Partition coefficient type:
- octanol-water
- Analytical method:
- other: N/A - Partition coefficient determined by HPLC method.
- Key result
- Type:
- log Pow
- Partition coefficient:
- < 0
- Temp.:
- 20 °C
- Remarks on result:
- other: Limit Value
- Remarks:
- Worst case limit.
- Type:
- log Pow
- Partition coefficient:
- < 0
- Temp.:
- 20 °C
- Remarks on result:
- not determinable
- Remarks:
- Test 1 - Test item eluted from the column quicker than the unretained reference substance, i.e. tr < t0
- Type:
- log Pow
- Partition coefficient:
- < -1.31
- Temp.:
- 20 °C
- Remarks on result:
- not determinable because of methodological limitations
- Remarks:
- Test 2 - The determined Log Pow value is below the determination limit of the method (Log Pow = 0.0 according to OECD 117 and EC method A.8).
- Details on results:
- Data Evaluation
Calculation of log k – The corresponding logarithms of the capacity factors, log k, were calculated from the retention times and the dead time.
Calibration Graph – A correlation graph of log k versus log Pow was plotted.
Sample Results – The log Pow was below the determination limit of this method (log Pow = 0.0), the log Pow was stated as < 0. - Conclusions:
- The test item was determined to have a partition coefficient (Log Pow) of < 0.0 at a mean temperature of 20 ± 1.0 °C.
- Executive summary:
EU Method A.8. – The partition coefficient of the test item was determined using the HPLC method. The procedures employed were designed to be compatible with Method A.8., partition coefficient, of Commission Regulation (EC) No 440/2008 of 30 May 2008.
Analysis was performed using a solid phase of long hydrocarbon chains chemically bound onto silica (Luna 5µ C18(2) 100A; 250 x 3.0 mm), with a mobile phase mixture of 60 % methanol and 40 % ultra-pure water. A PDA detector was used at 270 nm (reference solution), 223 nm (test item). Reference items were used to determine column dead time and regression coefficients.
For the test item a measured partition coefficient of log Pow < 0.0 was determined. The measured log Pow was below the limit of the method as the test item eluted from the column before the unretained organic substance selected to determine the deadtime of the column. As the log Pow value of the test item is below the limit of detection for the method, repeatability could not be determined.
Referenceopen allclose all
Data Evaluation:
The partition coefficient is estimated from the ratio of the solubilities of the test item in the pure solvents.
POW estimate = saturation cn-octanol/ saturation cwater
Table 1: Solubility in n-octanol (at 19.8 °C)
Weight of Test Item (mg) |
Volume n-octanol |
Duration of Shaking |
Remarks |
31.5 mg |
25 ml |
10 min |
not dissolved |
50 ml |
10 min |
not dissolved |
|
125 ml |
10 min |
not dissolved |
|
250 ml |
10 min |
not dissolved |
|
500 ml |
10 min |
not dissolved |
|
550 ml |
overnight |
not completely dissolved, (therefore solubility < 55.3 mg/L) |
The critical micelle concentration of the test item was measured using ISO 4311:1979 and mean measured value of 9,836 mg/l was determined(1). As the test item is surface active(2), the critical micelle concentration of the test item is used as a surrogate value for water solubility.
The POW is estimated as "max possible saturation conc. n-octanol/saturation conc. water"
i.e. POW = < 55.3 mg/L/9800 mg/L = < 0.0058.
The log POW is calculated to be < log 0.0058 = < - 2.24.
As the limit of the log Pow of the shake flask method is - 2, the log POW of the test item can therefore be stated as < 2.
(1)Anon (2017): "Use of processor Tensiometer K100 in combination with the double dosing unit for characterization of cristical micelle concentrations", Source: KRÜSS GmbH, Borsteler Chaussee 85, 22453 Hamburg, Germany. Unpublished report, Report No.: Not Applicable.
(2) Anderson, D. (2018): “Surface Tension Determination of Sodium octane-1-sulphonate” Source: ECOLAB, 370 Wabasha Street North, St. Paul, MN 55102-1390, USA. Unpublished report, Report No.: Not Applicable.
Table 3: Retention time and log Pow of the test item (mean of two runs)
|
Retention time [min] |
Mean retention time [min] |
Mean retention time of two runs [min] |
Absolute deviation [min] |
Log POWdetermined |
Mean log POW |
Mean log Powof two runs |
Absolute deviation of log Pow |
Run 1, Injection 1 |
1.536 |
1.54 |
1.63 |
0.16 |
Not determined.
tR< t0 |
< 0.0* |
< 0.0* |
N/A |
Run 1, Injection 2 |
1.540 |
|||||||
Run 1, Injection 3 |
1.545 |
|||||||
Run 1, Injection 4 |
1.552 |
|||||||
Run 2, Injection 1 |
1.706 |
1.71 |
-1.314 |
< 0.0* |
||||
Run 2, Injection 2 |
1.705 |
-1.319 |
||||||
Run 2, Injection 3 |
1.707 |
-1.308 |
||||||
Run 2, Injection 4 |
1.710 |
-1.292 |
*: below determination limit of the method (0.0 according to OECD 117 and EC method A.8). The log Pow values were below the limit of the method (log Pow < 0). Therefore the repeatability could not be determined.
Table 4: Calibration parameter obtained from first run
|
Slope |
x |
Intercept |
Log Pow = |
2.205795 |
log k |
+ 1.278437 |
R = |
0.9983 |
Table 5: Calibration parameter obtained from second run
|
Slope |
x |
Intercept |
Log Pow = |
2.205313 |
log k |
+ 1.278914 |
R = |
0.9983 |
Table 6: Values for determination of Pow, dead time and calibration graph obtained from 1st run
Name |
Log Pow |
RT [min]** |
Mean RT [min] |
SD [min]** |
log k |
Log Pow determined |
Mean log Pow |
SD log Pow |
|
Test Item |
--- |
1.536 |
1.543 |
0.007 |
N/A: tR< t0 |
< 0.0* |
< 0.0* |
N/A |
Log k not determinable. |
1.540 |
N/A: tR< t0 |
< 0.0* |
|||||||
1.545 |
N/A: tR< t0 |
< 0.0* |
|||||||
1.552 |
N/A: tR< t0 |
< 0.0* |
|||||||
Thiourea** |
--- |
1.626 |
1.627 |
0.001 |
--- |
--- |
--- |
|
Dead time |
1.626 |
|||||||||
1.628 |
|||||||||
1.626 |
|||||||||
2-Butanone |
0.3 |
2.266 |
2.265 |
0.001 |
-0.406 |
0.38 |
0.38 |
0.00 |
Reference Items |
2.264 |
-0.407 |
0.38 |
|||||||
2.266 |
-0.406 |
0.38 |
|||||||
2.264 |
-0.407 |
0.38 |
|||||||
Acetanilide |
1.0 |
2.789 |
2.790 |
0.001 |
-0.146 |
0.96 |
0.96 |
0.00 |
|
2.789 |
-0.146 |
0.96 |
|||||||
2.791 |
-0.145 |
0.96 |
|||||||
2.789 |
-0.146 |
0.96 |
|||||||
Nitrobenzene |
1.9 |
4.794 |
4.793 |
0.002 |
0.289 |
1.92 |
1.92 |
0.00 |
|
4.791 |
0.289 |
1.92 |
|||||||
4.795 |
0.289 |
1.92 |
|||||||
4.792 |
0.289 |
1.92 |
|||||||
Atrazine |
2.6 |
7.193 |
7.187 |
0.005 |
0.534 |
2.46 |
2.46 |
0.00 |
|
7.182 |
0.533 |
2.45 |
|||||||
7.185 |
0.534 |
2.46 |
|||||||
7.186 |
0.534 |
2.46 |
|||||||
Diphenylamine |
3.4 |
17.296 |
17.280 |
0.020 |
0.984 |
3.45 |
3.45 |
0.00 |
|
17.262 |
0.983 |
3.45 |
|||||||
17.263 |
0.983 |
3.45 |
|||||||
17.299 |
0.984 |
3.45 |
|||||||
Benzylbenzoate |
4.0 |
30.792 |
30.757 |
0.031 |
1.253 |
4.04 |
4.04 |
0.00 |
|
30.721 |
1.252 |
4.04 |
|||||||
30.745 |
1.253 |
4.04 |
|||||||
30.771 |
-0.406 |
0.38 |
*tR< t0: Retention time of the test item (tR) below retention time of thiourea (t0). Therefore Log Pow of the test item is below determination limit of the method (0.0 according to OECD 117 and EC method A.8)
**Thiourea was used for determination of the dead time; RT = retention time; SD = standard deviation
Table 7: Values for determination of Pow, dead time and calibration graph obtained from 2nd run
Name |
Log Pow |
RT [min] |
Mean RT [min] |
SD [min] |
log k |
Log Pow determined |
Mean log Pow |
SD log Pow |
|
Test Item
|
--- |
1.706 |
1.707 |
0.002 |
-1.314 |
< 0.0* |
< 0.0* |
N/A |
|
1.705 |
-1.319 |
< 0.0* |
|||||||
1.707 |
-1.308 |
< 0.0* |
|||||||
1.710 |
-1.292 |
< 0.0* |
|||||||
Thiourea**
|
--- |
1.627 |
1.627 |
0.001 |
--- |
--- |
--- |
--- |
Dead time |
1.626 |
|||||||||
1.627 |
|||||||||
1.627 |
|||||||||
2-Butanone
|
0.3 |
2.265 |
2.265 |
0.001 |
-0.407 |
0.38 |
0.38 |
0.00 |
Reference Items |
2.266 |
-0.406 |
0.38 |
|||||||
2.264 |
-0.407 |
0.38 |
|||||||
2.265 |
-0.407 |
0.38 |
|||||||
Acetanilide
|
1.0 |
2.789 |
2.789 |
0.002 |
-0.146 |
0.96 |
0.96 |
0.01 |
|
2.791 |
-0.145 |
0.96 |
|||||||
2.787 |
-0.147 |
0.95 |
|||||||
2.788 |
-0.147 |
0.95 |
|||||||
Nitrobenzene
|
1.9 |
4.795 |
4.794 |
0.003 |
0.289 |
1.92 |
1.92 |
0.00 |
|
4.797 |
0.290 |
1.92 |
|||||||
4.790 |
0.289 |
1.92 |
|||||||
4.792 |
0.289 |
1.92 |
|||||||
Atrazine
|
2.6 |
7.192 |
7.187 |
0.007 |
0.534 |
2.46 |
2.46 |
0.01 |
|
7.192 |
0.534 |
2.46 |
|||||||
7.179 |
0.533 |
2.45 |
|||||||
7.183 |
0.533 |
2.45 |
|||||||
Diphenylamine
|
3.4 |
17.294 |
17.280 |
0.021 |
0.984 |
3.45 |
3.45 |
0.00 |
|
17.302 |
0.984 |
3.45 |
|||||||
17.259 |
0.983 |
3.45 |
|||||||
17.265 |
0.983 |
3.45 |
|||||||
Benzylbenzoate |
4.0 |
30.757 |
30.746 |
0.027 |
1.253 |
4.04 |
4.04 |
0.00 |
|
30.771 |
1.253 |
4.04 |
|||||||
30.707 |
1.252 |
4.04 |
|||||||
30.747 |
1.253 |
4.04 |
*Log Pow of the test item is below determination limit of the method (0.0 according to OECD 117 and EC method A.8)
**Thiourea was used for determination of the dead time; RT = retention time; SD = standard deviation
Description of key information
Partition coefficient: Log Pow= < -2.25 at 20.0°C ± 1.0 °C; EU Method A.8. (Estimation Method (Solubility Ratio)); C Bär (2018)
Partition coefficient: Log Pow= < 0.0 at 20.0°C ± 1.0 °C; EU Method A.8. (HPLC Method); C Bär (2018)
Key value for chemical safety assessment
- Log Kow (Log Pow):
- -2.25
- at the temperature of:
- 19.8 °C
Additional information
EU Method A.8. – The partition coefficient of the test item was determined using the HPLC and calculation methods. The procedures employed were designed to be compatible with Method A.8., partition coefficient, of Commission Regulation (EC) No 440/2008 of 30 May 2008. As part of the wider testing programme it was determined experimentally that the test item is surface active (D. Anderson, EU Method A.5. (2018)). As per EU Method A.8., neither the shake-flask method nor the HPLC method is applicable to surface active substances. Potentially misleading results may arise due to emulsification (flask method) or secondary column interactions (HPLC Method). As such the HPLC Method should be regarded as supplementary information as part of a weight of evidence based on the calculation method.
HPLC Method: Analysis was performed using a solid phase of long hydrocarbon chains chemically bound onto silica (Luna 5µ C18(2) 100A; 250 x 3.0 mm), with a mobile phase mixture of 60 % methanol and 40 % ultra-pure water. A PDA detector was used at 270 nm (reference solution), 223 nm (test item). Reference items were used to determine column dead time and regression coefficients.
For the test item a measured partition coefficient of log Pow < 0.0 was determined. The measured log Pow was below the limit of the method as the test item eluted from the column before the unretained organic substance selected to determine the dead time of the column. As the log Pow value of the test item is below the limit of detection for the method, repeatability could not be determined.
Estimation Method (Solubility Ratio): An aliquot of test item was placed in a glass vessel, n-octanol was added in a stepwise manner. After each addition of n-octanol, the vessel was shaken for at least 10 min. The sample was then visually checked for undissolved test item. If the test item was not dissolved further n-octanol was added in the manner previously described. The test was performed at 19.8 ℃.
For the test item an estimated partition coefficient of log Pow < - 2.25 was determined. As the limit of the log Pow of the shake flask method is – 2, further dilution of the test item was not pursued.
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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