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EC number: 240-597-7 | CAS number: 16529-65-0
- 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
Water solubility
Administrative data
Link to relevant study record(s)
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2017-09-19 to 2017-11-02
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Version / remarks:
- 1995
- Deviations:
- yes
- Remarks:
- Exclusion of CO2 and O2, two vessels was set up in a parallel design at 20 ± 1 °C, each vessel was sampled several times instead of sampling one vessel at every time point.
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.6 (Water Solubility)
- Version / remarks:
- 2008
- Deviations:
- yes
- Remarks:
- Exclusion of atmospheric CO2 and O2, two vessels was set up in a parallel design at 20 ± 1 °C, each vessel was sampled several times instead of sampling one vessel at every time point.
- GLP compliance:
- yes
- Type of method:
- flask method
- Specific details on test material used for the study:
- Conditions of storage: Tightly closed and dry, room temperature (10 °C – 30 °C), in original container
Handling: Please handle the substance as far as possible under inert gas. - Water solubility:
- 1.1 µg/L
- Conc. based on:
- test mat.
- Loading of aqueous phase:
- 1.15 mg/L
- Incubation duration:
- <= 9 d
- Temp.:
- 20 °C
- pH:
- >= 6.5 - <= 6.7
- Remarks on result:
- other: LOQ < 13.3 µg / L
- Conclusions:
- Under the conditions of this test (under exclusion of CO2 and O2, under inert gas; flask method; loadings of 1.14 and 1.16 mg test substance/L), a solubility equilibrium was reached during the first three days of testing. The mean measured amount of dissolved zinc on day 1, 2, 7, 8 and 9 at 20.0 ± 1.0 °C is 0.1 µg/L (determined as dissolved zinc, separated by filtration from undissolved test item). This corresponds to a water solubility of dissolved zinc didocosanoate of 1.1 µg/L, calculated on a zinc content of 9.3 %. Solution pH in samples containing the test item remained at 6.5 – 6.7 while the pH in method blanks ranged from 6.5 – 6.6.
Reference
Preliminary test
The preliminary test showed a water solubility of zinc didocosanoate lower than the expected limit of quantification of approximately 0.1 mg / L at 20 °C after measuring the content of zinc in the filtered solutions outside GLP.
Therefore the sponsor decided to carry out the main test with a loading rate of approximately 1 mg test item / L.
Main test
The temperature of the water bath was 20 ± 1 °C.
The pH of the test solutions and blanks were in the range between 6.5 and 6.7.
In each replicate run the water solubility of the test substance was less than the limit of quantification (LOQ < 13.3 µg / L) of the analytical method.
Measured dissolved zinc concentrations of solutions containing the test item do not continuously increase during the test but vary from 3.6 to 4.5 µg zinc / L. Measured dissolved zinc concentrations of control solutions (i.e. background concentrations) vary from 3.6 to 4.3 µg zinc / L.
A t-test (unpaired, one-sided) was conducted to compare daily mean measured dissolved zinc concentrations of solutions containing the test item with measured zinc concentrations of controls (t-value 0.26). The p-value of the t-test statistic of 0.60 indicates that zinc concentrations of solutions containing the test item are not significantly different from zinc concentrations of controls.
Though statistically not significant, dissolved zinc concentrations of solutions containing the test item are estimated with 0.1 µg zinc/L, i.e. the calculated overall mean background- corrected zinc concentration of solutions containing the test item. Based on the zinc content of zinc didocosanoate of 9.3 %, water solubility is estimated with 1.1 µg zinc didocosanoate/ L.
Measured concentrations of zinc in the solutions
Equilibration time (Days) | Measured concentration in µg zinc / L | ||||
Blank | 1st | 2nd | Mean (1st & 2nd) | Mean (1st & 2nd) – blank corrected |
|
1 | 3.7 | 4.0 | 3.8 | 3.9 | 0.2 |
2 | 3.7 | 3.6 | 3.8 | 3.7 | 0.0 |
7 | 3.6 | 4.1 | 4.0 | 4.0 | 0.5 |
8 | 4.2 | 4.5 |
4.1 |
4.3 |
0.0 |
9 |
4.3 |
4.0 |
4.5 |
4.3 |
0.0 |
Mean |
3.9 |
4.0 |
4.0 |
4.0 |
0.1 |
Standard deviation |
0.3 |
0.3 |
0.3 |
0.2 |
0.2 |
Relative standard deviation (%) |
8.6 |
7.3 |
7.7 |
6.0 |
167.4 |
Description of key information
Zinc didocosanoate has a water solubility of 1.1 µg/L at 20 °C.
Key value for chemical safety assessment
- Water solubility:
- 1.1 µg/L
- at the temperature of:
- 20 °C
Additional information
Under the conditions of this test (under exclusion of CO2 and O2, under inert gas; flask method; loadings of 1.14 and 1.16 mg test substance/L), a solubility equilibrium was reached during the first three days of testing. The mean measured amount of dissolved zinc on day 1, 2, 7, 8 and 9 at 20.0 ± 1.0 °C is 0.1 µg/L (determined as dissolved zinc, separated by filtration from undissolved test item). This corresponds to a water solubility of dissolved zinc didocosanoate of 1.1 µg/L, calculated on a zinc content of 9.3 %. Solution pH in samples containing the test item remained at 6.5 – 6.7 while the pH in method blanks ranged from 6.5 – 6.6.
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