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EC number: 200-641-8 | CAS number: 67-03-8
- 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:
- 12 May 2015 to 16 July 2015
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 107 (Partition Coefficient (n-octanol / water), Shake Flask Method)
- Version / remarks:
- 1995
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.8 (Partition Coefficient - Shake Flask Method)
- Version / remarks:
- 2008
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- flask method
- Partition coefficient type:
- octanol-water
- Analytical method:
- high-performance liquid chromatography
- Key result
- Type:
- Pow
- Partition coefficient:
- < 0.001
- Temp.:
- 22.5 °C
- pH:
- 7.08
- Key result
- Type:
- log Pow
- Partition coefficient:
- < -3.04
- Temp.:
- 22.5 °C
- pH:
- 7.08
- Details on results:
- PRELIMINARY TEST
- Estimated log10 Pow: -3.93
MAIN TEST
- The mean peak areas obtained for the standard, stock and sample solutions were:
Organic Phase:
Standard 1.04 mg/L: 1.5057 x 10^6
Standard 1.06 mg/L: 1.8245 x 10^6
Organic phase matrix blank (comparable to sample areas): 1.1515 x 10^6
Sample 1: 1.0890 x 10^6
Sample 2: 1.1858 x 10^6
Sample 3: 1.0014 x 10^6
Sample 4: 1.1517 x 10^6
Sample 5: 1.2301 x 10^6
Sample 6: 1.2914 x 10^6
Aqueous Phase:
Standard 15.7 mg/L: 1.4242 x 10^7
Standard 15.9 mg/L: 1.4491 x 10^7
Aqueous phase matrix blank: -
Sample 1: 1.0601 x 10^7
Sample 2: 1.0149 x 10^7
Sample 3: 1.0139 x 10^7
Sample 4: 1.0287 x 10^7
Sample 5: 9.9992 x 10^6
Sample 6: 1.0413 x 10^7
Stock solution A: 1.0697 x 10^7
Stock solution B: 1.0243 x 10^7
- The total weights (mg) and analysed concentration (mg/L) of the respective phases are shown in Table 2. pH of stock solution : 7.08. Temperature : 22.5 ± 0.5 °C.
- The partition coefficient for each sample is shown in Table 3. Overall Pow : <9.12 x 10^-4. Overall log10 Pow : <-3.04
- Validation: The linearity of the detector response with respect to concentration was assessed over the nominal concentration range of 0.8 to 2 mg/L in organic matrix and 5 to 30 mg/L in aqueous matrix. The results were satisfactory, with a goodness of fit (r2) of 0.9866 and 0.9997 being obtained for the organic and aqueous matrices, respectively.
DISCUSSION
- The determination of partition coefficient was performed using the shake flask method. This choice was supported by the estimated partition coefficient obtained in the preliminary estimation.
- The stock solution was prepared in n-octanol saturated water in place of water saturated n-octanol due to the insolubility of the test material in the organic phase. This deviation to the guidelines has been considered to have a negligible impact on the overall result, as it was more appropriate to use this solvent to obtain a more realistic partition coefficient value. The stock solution was adjusted to neutral pH, since it was not possible to avoid the ionization of the test material in solution.
- All glassware used for the test was silanised, and low adsorption HPLC vials were used, in an attempt to minimise any test material adsorption to the glassware.
- The limit value used for the concentration of the organic phases (<2 mg/L) was derived from the nominal concentration of the standards (1 mg/L), which produced a response greater than the corresponding matrix blank, corrected for the dilution factor (2).
- The responses of the duplicate standards prepared for the analysis of the organic phases were significantly different. However, this inconsistency had no negative effect on the results, since the concentration of the organic phases was given as a limit value; therefore, it was sufficient to prove that the peak areas of all organic samples and matrix blank were lower than the peak areas of the respective standards. - Conclusions:
- Under the conditions of this study, the partition coefficient of the test material has been determined to be less than 9.12 x 10^-4 at 22.5 ± 0.5 °C, log10 Pow less than -3.04, at 22.5 °C pH 7.08.
- Executive summary:
The partition coefficient of the test material was determined in accordance with the standardised guidelines OECD 107 and EU Method A.8, under GLP conditions using the shake flask method.
The test system consisted of an aqueous and an n-octanol phase in the same vessel. A defined amount of test item was added (pre-dissolved in the appropriate phase). Partitioning of the test item between both phases was achieved by inversion of the mixture. The test temperature was in the range of 20 °C to 25 °C and kept constant (± 1 °C).
Under the conditions of this study, the partition coefficient of the test material has been determined to be less than 9.12 x 10^-4 at 22.5 ± 0.5 °C, log10 Pow less than -3.04, at 22.5 °C pH 7.08.
Reference
Table 2: The total weights (mg) and analysed concentration (mg/L) of the respective phases during the study.
Sample Number |
Total Weight (mg) |
Organic Phase |
|
% Recovery |
|||
Analysed Concentration (mg/L) |
Weight (mg) |
Analysed Concentration (mg/L) |
Weight (mg) |
pH |
|||
1 |
57.4 |
<2 |
<0.1 |
2.33 x 10^3 |
58.1 |
6.91 |
>101 |
2 |
62.0 |
<2 |
<0.1 |
2.23 x 10^3 |
60.1 |
6.88 |
>97.0 |
3 |
91.8 |
<2 |
<8x10^-2 |
2.22 x 10^3 |
89.0 |
7.08 |
>96.9 |
4 |
91.8 |
<2 |
<8x10^-2 |
2.26 x 10^3 |
90.2 |
7.05 |
>98.3 |
5 |
129 |
<2 |
<6x10^-2 |
2.19 x 10^3 |
123 |
7.32 |
>95.5 |
6 |
129 |
<2 |
<6x10^-2 |
2.28 x 10^3 |
128 |
7.34 |
>99.5 |
Table 3: Determination of the Partition Coefficient
Sample Number |
Organic/Aqueous Volume Ratio |
Partition Coefficient |
Log10 Pow |
Overall Partition Coefficient |
1 |
2:1 |
<8.60 x 10-4 |
<-3.07 |
<8.99 x 10^-4 |
2 |
<8.99 x 10-4 |
<-3.05 |
||
3 |
1:1 |
<8.99 x 10-4 |
<-3.05 |
<8.99 x 10^-4 |
4 |
<8.87 x 10-4 |
<-3.05 |
||
5 |
1:2 |
<9.12 x 10-4 |
<-3.04 |
<9.12 x 10^-4 |
6 |
<8.76 x 10-4 |
<-3.06 |
Description of key information
Under the conditions of this study, the partition coefficient of the test material has been determined to be less than 9.12 x 10^-4 at 22.5 ± 0.5 °C, log10 Pow less than -3.04, at 22.5 °C pH 7.08.
Key value for chemical safety assessment
- Log Kow (Log Pow):
- -3.04
- at the temperature of:
- 22.5 °C
Additional information
The partition coefficient of the test material was determined in accordance with the standardised guidelines OECD 107 and EU Method A.8, under GLP conditions using the shake flask method. The study was awarded a reliability score of 1 in accordance with the criteria set forth by Klimisch et al. (1997).
The test system consisted of an aqueous and an n-octanol phase in the same vessel. A defined amount of test item was added (pre-dissolved in the appropriate phase). Partitioning of the test item between both phases was achieved by inversion of the mixture. The test temperature was in the range of 20 °C to 25 °C and kept constant (± 1 °C).
Under the conditions of this study, the partition coefficient of the test material has been determined to be less than 9.12 x 10^-4 at 22.5 ± 0.5 °C, log10 Pow less than -3.04, at 22.5 °C pH 7.08.
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