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EC number: 807-130-4 | CAS number: 53716-82-8
- 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:
- 09 Apr - 21 Jun 2014
- 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:
- 27 July 1995
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.8 (Partition Coefficient)
- Version / remarks:
- 30 May 2008
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- The Department of Health of the Government of the United Kingdom
- Type of method:
- flask method
- Partition coefficient type:
- octanol-water
- Analytical method:
- gas chromatography
- Key result
- Type:
- Pow
- Partition coefficient:
- 0.031
- Temp.:
- 22 °C
- pH:
- ca. 5.18 - ca. 5.24
- Key result
- Type:
- log Pow
- Partition coefficient:
- -1.52
- Temp.:
- 22 °C
- pH:
- ca. 5.18 - ca. 5.24
- Conclusions:
- A log Kow value of -1.52 at 22.0 ± 1.0°C and pH 5.18 to 5.24 was determined for the substance using a relevant test method and in compliance with GLP. The result is considered to be reliable.
Reference
Preliminary estimate:
The preliminary estimation of partition coefficient was a log Kow value of -0.28 (KOWWIN v1.68)
Definitive test:
The determination of partition coefficient was performed using the shake-flask method. This was due to the expected partition coefficient obtained in the preliminary assessment.
The mean peak areas obtained for the standard, stock and sample solutions are shown in the following two tables:
Organic phase:
Solution |
Mean peak area |
Standard 25.3 mg/L |
1.2326E+06 |
Standard 25.6 mg/L |
1.2854E+06 |
Organic phase matrix blank |
< LOD |
Sample 1 |
7.0305E+05 |
Sample 2 |
6.3135E+05 |
Sample 3 |
7.8620E+05 |
Sample 4 |
7.8007E+05 |
Sample 5 |
6.9707E+05 |
Sample 6 |
7.9389E+05 |
Aqueous phase:
Solution |
Mean peak area |
Standard 501 mg/L |
2.6059E+07 |
Standard 523 mg/L |
2.7407E+07 |
Aqueous phase matrix blank |
< LOD |
Sample 1 |
1.0110E+07 |
Sample 2 |
9.9981E+06 |
Sample 3 |
1.0213E+07 |
Sample 4 |
1.0485E+07 |
Sample 5 |
9.7851E+06 |
Sample 6 |
9.9685E+06 |
Stock solution A |
1.0560E+07 |
Stock solution B |
1.0492E+07 |
The total weights and analyzed concentration of the respective phases are shown in the following table:
Sample no. |
Total weight [mg]* |
Organic phase |
Aqueous phase |
% Recovery |
|||
Analyzed concentration [mg/L] |
Weight [mg]** |
Analyzed concentration [mg/L] |
Weight [mg]** |
pH |
|||
1 |
85.6 |
28.4 |
2.41 |
967 |
82.2 |
5.24 |
98.9 |
2 |
85.6 |
25.5 |
2.17 |
957 |
81.3 |
5.23 |
97.5 |
3 |
115 |
31.8 |
1.81 |
977 |
111 |
5.18 |
98.6 |
4 |
115 |
31.5 |
1.80 |
1003 |
114 |
5.19 |
101.2 |
5 |
57.4 |
28.2 |
3.21 |
936 |
53.4 |
5.21 |
98.6 |
6 |
62.4 |
32.1 |
3.98 |
954 |
59.1 |
5.22 |
101.1 |
* from analysis of the stock solution; ** from analysis of the respective phase
pH of n-octanol saturated water: 6.16
pH of stock solution: 5.57
Temperature: 22.0 ± 0.5°C
The partition coefficient determined for each sample is shown in the following table:
Sample no. |
Organic/Aqueous volume ratio |
Partition coefficient |
Log Pow |
Mean partition coefficient |
1 |
1:1 |
2.94E-02 |
-1.53 |
2.80E-02 |
2 |
2.67E-02 |
-1.57 |
||
3 |
1:2 |
3.25E-02 |
-1.49 |
3.20E-02 |
4 |
3.14E-02 |
-1.50 |
||
5 |
2:1 |
3.01E-02 |
-1.52 |
3.19E-02 |
6 |
3.36E-02 |
-1.47 |
Pow standard deviation: 2.48E-03
The typical chromatograms are attached.
Validation:
The linearity of the detector response with respect to concentration was assessed over the nominal concentration range of 125.1 to 2002 mg/L for aqueous samples. This was satisfactory with a correlation coefficient of 1.00 being obtained. The linearity of the detector response with respect to concentration was assessed over the nominal concentration range of 10.23 to 102.3 mg/L for organic samples. This was satisfactory with a correlation coefficient of 0.999 being obtained.
Description of key information
log Kow [CyreneTM/Gem Diol]: -1.52 at 22.0 ± 1.0°C and pH 5.18 to 5.24 (OECD 107)
Key value for chemical safety assessment
- Log Kow (Log Pow):
- -1.52
- at the temperature of:
- 22 °C
Additional information
In contact with water, the ketone group of Cyrene™ ((1S,5R)-6,8 -dioxabicyclo[3.2.1]octan-4-one) hydrates to form the Gem Diol form. The hydration is fully reversible and a dynamic equilibrium is established (see attached document in Section 13 for further details).
At the concentrations used in the log Kow study, the Gem Diol form would have been the major species present. A log Kow value of -1.52 at 22.0 ± 1.0°C and pH 5.18 to 5.24 was determined for Cyrene™/Gem Diol using a flask method in accordance with OECD Test Guideline 107 and in compliance with GLP. The result is considered to be reliable.
Therefore, the measured value is considered representative of the Gem Diol form. At concentrations relevant for the environment and in vivo, the Gem Diol form also predominates. Therefore, the measured value may be used for both the environment and human health chemical safety assessment. It is not possible or useful to measure a log Kow for Cyrene™ itself but the measured value has been reported for completeness.
The measured value is supported by a calculated value for the Gem Diol form of -1.0. This result was obtained using the algorithm from the WSKOWWIN v.1.43 program (part of Epi Suite v.4.11) with the measured water solubility of 560 g/L and molecular weight of 146.14 g/mol as inputs. KOWWIN v1.69 gives a prediction of 0.6 for the Gem Diol form; however, this is not considered reliable because multiple, poorly supported correction factors are applied. Any remaining uncertainty in the value of log Kow is not considered to be important for the chemical safety assessment as the log Kow is very low.
Calculation of log Kow
Equation from WSKOWWIN: log S (mol/L) = 0.796 - 0.854 log Kow - 0.00728 MW +ΣCorrections
No correction factors are applicable to Gem Diol
MW = 146.14 g/mol
WS = 560 g/L
Solubility, S = 3.83 mol/L
Log S (mol/L) = 0.583
Log Kow = [log S (mol/L) + 0.00728 MW -0.796] / -0.854 = -1.0
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