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EC number: 212-757-6 | CAS number: 867-13-0
- 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:
- From 16 December 2011 to 3 September 2012
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- The study was conducted according to internationally recognised guidelines, and under GLP. No deviation affected the quality of the study.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 117 (Partition Coefficient (n-octanol / water), HPLC Method)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.8 (Partition Coefficient)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- 2011-08-31
- Type of method:
- HPLC method
- Partition coefficient type:
- octanol-water
- Analytical method:
- high-performance liquid chromatography
- Type:
- log Pow
- Partition coefficient:
- 1.23
- Remarks on result:
- other: estimated value obtained by a QSAR (KOWWIN)
- Type:
- Pow
- Partition coefficient:
- 13.4
- Temp.:
- 30 °C
- Remarks on result:
- other: value obtained by HPLC method
- Type:
- log Pow
- Partition coefficient:
- 1.13
- Temp.:
- 30 °C
- Remarks on result:
- other: value obtained by HPLC method
- Conclusions:
- The partition coefficient of the test item has been determined to be 13.4 at 30°C, log Pow 1.13. Although the test item was identified as being surface active, no interference in the HPLC estimation method was evident for this non-ionic test item. The experimental value was in strong agreement with the KOWWIN predicted value of log Pow 1.23. Although the validation of computer estimated values is beyond the scope of the Principles of GLP, assessment with literature values of log Pow for chemically similar substances indicated an accuracy of within ± 0.5 log units.
- Executive summary:
The determination was carried out using an HPLC estimation method, according to Method A8 Partition Coefficient of Commission Regulation (EC) No 440/2008 of 30 May 2008, Method 117 of the OECD Guidelines for testing of Chemicals, 13 April 2004 and GLP. No deviation from the guideline was observed during the test.
Although the test item was identified as being surface active, no interference in the HPLC estimation method was evident for this non-ionic test item. The partition coefficient (Pow) of the test item is determined from its elution time, in comparison with recommended reference items, using a reverse phase column. Chemicals injected onto such a column move along by partitioning between the mobile phase, which is partly aqueous, and the hydrocarbon stationary phase. Elution time will depend of the hydrocarbon/water partition coefficient.
A preliminary assessment of the partition coefficient was calculated using KOWWIN v1.68a (Sept 2012)©2000 U.S Environmental Protection Agency. In the definitive test,a calibration curve was constructed from the retention time data of the dead time and reference standard solutions. With the log k' of the test item and the equation of the calibration curve of reference standard solutions, log Pow of the test item was calculated.
The KOWWIN predicted value of log Pow is 1.23. The experimental value at 30°C obtained by HPLC method (log Pow 1.13) is very close to the predicted value.
Reference
Preliminary estimate:
The log Pow was estimated to be 1.23 using KOWWIN. The full calculation is presented below:
Log Kow(version 1.68 estimate): 1.23
SMILES : O=P(OCC)(OCC)CC(=O)OCC
Chemical Name : Acetic acid, (diethoxyphosphinyl)-, ethyl ester
Molecular Formula: C8 H17 O5 P1
Molecular Weight : 224.20
TYPE |
NUM |
LOGKOW FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
3 |
-CH3 [aliphatic carbon] |
0.5473 |
1.6419 |
Frag |
4 |
-CH2- [aliphatic carbon] |
0.4911 |
1.9644 |
Frag |
1 |
-C(=O)O [ester, aliphatic attach] |
-0.9505 |
-0.9505 |
Frag |
2 |
-O-P [aliphatic attach] |
-0.0162 |
-0.0324 |
Frag |
1 |
O=P |
-2.4239 |
-2.4239 |
Factor |
1 |
-P(=O)-C-C(=O)- correction |
0.8000** |
0.8000 |
Const |
|
Equation Constant |
|
0.2290 |
NOTE |
|
An estimated coefficient (**) used |
|
|
Log Kow = 1.2285 |
Calibration results:
The retention times of the dead time and the retention times, capacity factor (k') and log Pow values for the reference standards are shown in the following tables :
Dead time |
Retention time (min) |
Mean retention time (min) |
|
Injection 1 |
Injection 2 |
||
Thiourea |
1.559 |
1.559 |
1.559 |
Dead time |
Retention time (min) |
Mean retention time (min) |
Capacity factor (k’) |
Log k’ |
Log Kow |
|
Injection 1 |
Injection 2 |
|||||
2-butanone |
2.061 |
2.061 |
2.061 |
0.322 |
-0.492 |
0.3 |
Aniline |
2.315 |
2.313 |
2.314 |
0.484 |
-0.315 |
0.9 |
Benzyl alcohol |
2.623 |
2.632 |
2.628 |
0.685 |
-0.164 |
1.1 |
Benzonitrile |
3.067 |
3.065 |
3.066 |
0.967 |
-1.47*10-2 |
1.6 |
Benzene |
6.642 |
6.64 |
6.641 |
3.260 |
0.513 |
2.1 |
Toluene |
12.001 |
11.983 |
11.992 |
6.692 |
0.826 |
2.7 |
The parameters A and B from equation B were determined by the calibration curve of these reference standards :A = -0.775 and B -0.575. The calibration curve is shown on the attached illustration.
Partition coefficient of sample:
The retention times, capacity factor (k') and log Pow value determined for the sample are shown in the following table :
Injection |
Retention Time (min) |
Capacity factor (k’) |
Log k’ |
Log Pow |
1 |
2.725 |
0.748 |
-0.126 |
1.13 |
2 |
2.723 |
0.747 |
-0.127 |
1.13 |
Mean log Pow: 1.13
Partition coefficient 13.4
Discussion:
Regulatory guidance documents raise caution for the use of the HPLC estimation method for the determination of partition coefficient for surface active substances, as possible secondary interactions may occur between the test item and the HPLC column stationary phase. The absence of any such secondary interactions for this non-ionic surface active substance was strengthened in this case by the consistency between the computer estimated value of partition coefficient and that determined experimentally. Additional validation data in support of the computer estimated value of partition coefficient is presented the following section (Overall, remarks, attachments). Estimation of the partition coefficient from the saturation solubility of the test item in the individual solvents of n-octanol and water was not considered valid for this test item. The miscibility of the test item in at least one of the solvents prevented obtaining any meaningful saturation concentrations, such that the estimation calculation process could not be completed.
In absence of any dissociating functional groups, no specific manipulation of the mobile phase pH was required. Therefore the determination was performed at an approximately neutral pH.
Description of key information
Experimental value Log Pow for the test item at 30°C: 1.13
Calculated value for Log Pow for the test item (QSAR): 1.23
Key value for chemical safety assessment
- Log Kow (Log Pow):
- 1.13
- at the temperature of:
- 30 °C
Additional information
The determination was carried out using an HPLC estimation method, according to Method A8 Partition Coefficient of Commission Regulation (EC) No 440/2008 of 30 May 2008, Method 117 of the OECD Guidelines for testing of Chemicals, 13 April 2004 and according to GLP. No deviation from the guideline was observed.
In absence of any dissociating functional groups, no specific manipulation of the mobile phase pH was required. Therefore the determination was performed at an approximately neutral pH.
Regulatory guidance documents raise caution for the use of the HPLC estimation method for the determination of partition coefficient for surface-active substances, as possible secondary interactions may occur between the test item and the HPLC column stationary phase. The absence of any such secondary interactions for this non-ionic surface-active substance was strengthened in this case by the consistency between the computer-estimated value of the partition coefficient and that determined experimentally. Estimation of the partition coefficient from the saturation solubility of the test item in the individual solvents of n-octanol and water was not considered valid for this test item. The miscibility of the test item in at least one of the solvents prevented obtaining any meaningful saturation concentrations, such that the estimation calculation process could not be completed.
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