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EC number: 849-166-3 | CAS number: 83841-00-3
- 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
- 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
- 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:
- log Pow
- Partition coefficient:
- < -3
- Temp.:
- 20 °C
- pH:
- 4.7
- Key result
- Type:
- log Pow
- Partition coefficient:
- < -3
- Temp.:
- 20 °C
- pH:
- 6.8
- Key result
- Type:
- log Pow
- Partition coefficient:
- < -3
- Temp.:
- 20 °C
- pH:
- 9
- Conclusions:
- A log Kow <-3.0 was determined for the test substance under relevant environmental pH conditions (pH value ranging from 5 to 9) at a test temperature of 20 °C using the shake flask method.
- Executive summary:
The octanol-water partition coefficient of the substance was determined under GLP in accordance with OECD TG 107, by using the shake flask method. For the determinations at specified pH conditions, individual buffer solutions were prepared and mutually saturated with n-octanol. Stock solutions of the test substance in the buffers were produced by diluting aliquots of 0.2549 g (pH 5), 0.2507 g (pH 7) and 0.2510 g (pH 9) in 250 mL of n-octanol saturated buffer solution. These were used as the aqueous phase in the test. The organic phase for the specific pH determinations was the relevant buffer solution saturated n-octanol. For each test conditions, six partitions were tested according to the following setup at a test temperature varying from 20 to 20.4 °C.
In each test, the combined volume of both phases occupied not less than 90% of the total volume of the test vessel. The organic and aqueous phases were equilibrated to the test temperature for a minimum of one hour before partitioning, which was performed by inversion of the flasks through approximately 180 °C over a five minute period. The test temperature was measured and confirmed at the time of partitioning and the flasks then returned to the 20 °C conditions to allow initial phase separation prior to decanting the individual phases for centrifugation. Individual aliquots of each phase from each vessel were taken and phase separation ensured by centrifugation at at leas 13000 rpm for 15 minutes. Aliquots of both phases from each vessel and each stock solution were taken for analysis by HPLC. The analysis of the organic phase sample solutions showed that the concentration of test substance was below the limit of quantification of the applied method (0.5 mg/L). A limit value of <1.0 mg/L in the organic phase was used in the calculation of Kow values (corrected for the dilution factor of 2). The Kow value at all tested pH values was <0.001. The resulting log Kow was thus <-3.0 at pH 5, 7 and 9 at a temperature of 20 °C.
Reference
Table 1: Analysed concentrations, aqueous phase pH and resulting test item weights – pH 5
Sample number |
Total weight (mg) |
Organic phase |
Aqueous phase |
Mass recovery (%) |
|||
Analysed concentration (mg/L) |
Weight (mg) |
Analysed concentration (mg/L) |
Weight (mg) |
pH |
|||
1 |
27.6 |
<1.0 |
<0.054 |
996 |
26.9 |
4.7 |
97.5 |
2 |
27.6 |
<1.0 |
<0.054 |
1010 |
27.3 |
4.7 |
99.1 |
3 |
40.9 |
<1.0 |
<0.04 |
1020 |
40.7 |
4.7 |
99.5 |
4 |
40.9 |
<1.0 |
<0.04 |
1010 |
40.6 |
4.7 |
99.2 |
5 |
55.2 |
<1.0 |
<0.027 |
1020 |
55.0 |
4.7 |
99.7 |
6 |
55.2 |
<1.0 |
<0.027 |
1020 |
55.2 |
4.7 |
100.0 |
Table 2: Analysed concentrations, aqueous phase pH and resulting test item weights – pH 7
Sample number |
Total weight (mg) |
Organic phase |
Aqueous phase |
Mass recovery (%) |
|||
Analysed concentration (mg/L) |
Weight (mg) |
Analysed concentration (mg/L) |
Weight (mg) |
pH |
|||
1 |
26.7 |
<1.0 |
<0.054 |
996 |
26.9 |
6.8 |
100.7 |
2 |
26.7 |
<1.0 |
<0.054 |
995 |
26.9 |
6.8 |
100.6 |
3 |
39.6 |
<1.0 |
<0.04 |
1000 |
40.1 |
6.8 |
101.3 |
4 |
39.6 |
<1.0 |
<0.04 |
994 |
39.8 |
6.8 |
100.4 |
5 |
53.5 |
<1.0 |
<0.027 |
993 |
53.6 |
6.8 |
100.3 |
6 |
53.5 |
<1.0 |
<0.027 |
991 |
53.5 |
6.8 |
100.1 |
Table 3: Analysed concentrations, aqueous phase pH and resulting test item weights – pH 9
Sample number |
Total weight (mg) |
Organic phase |
Aqueous phase |
Mass recovery (%) |
|||
Analysed concentration (mg/L) |
Weight (mg) |
Analysed concentration (mg/L) |
Weight (mg) |
pH |
|||
1 |
26.8 |
<1.0 |
<0.054 |
997 |
26.9 |
9.0 |
100.7 |
2 |
26.8 |
<1.0 |
<0.054 |
1000 |
27.0 |
9.0 |
101.0 |
3 |
39.7 |
<1.0 |
<0.04 |
999 |
40.0 |
9.0 |
100.7 |
4 |
39.7 |
<1.0 |
<0.04 |
994 |
39.8 |
9.0 |
100.3 |
5 |
53.6 |
<1.0 |
<0.027 |
995 |
53.7 |
9.0 |
100.2 |
6 |
53.6 |
<1.0 |
<0.027 |
1000 |
54.0 |
9.0 |
100.7 |
Description of key information
log Kow <-3.0 at pH 5, 7, 9 and 20 °C (GLP, OECD TG 107, shake flask method)
Key value for chemical safety assessment
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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