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EC number: 233-593-1 | CAS number: 10254-57-6
- 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

Hydrolysis
Administrative data
Link to relevant study record(s)
- Endpoint:
- hydrolysis
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 28 December 2006 to 13 June 2007
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 111 (Hydrolysis as a Function of pH)
- Deviations:
- no
- GLP compliance:
- yes
- Radiolabelling:
- not specified
- Analytical monitoring:
- yes
- Details on sampling:
- - Sampling method: About 40 mg of the test substance were dissolved in 2 mL solubilizer (acetone, acetonitrile and ethanol) and filled up to 100 mL with the respective buffer solution (pH 4.0, pH 7.0 and pH 9.0). Each mixture was ultrasonified and submitted to a 0.2 μm filtration. To obtain a test solution of not more than half the water solubility, one part of the solution was diluted with one part of the respective buffer.
- Buffers:
- - pH: 4.0, 7.0 and 9.0
- Details on test conditions:
- None stated
- Number of replicates:
- None stated
- Positive controls:
- not specified
- Negative controls:
- not specified
- Statistical methods:
- None stated
- Preliminary study:
- The solubility of the test substance in the buffer solutions pH 4, pH 7.0 and pH 9.0 is very low, therefore a test with different solubilizer was performed to increase the solubility of the test substance.
It was not possible to increase the solubility of the test item with the use of different solubilizers. Peaks obtained, if any, were too small to allow quantification or even to follow a degradation curve.
According to the EEC Directive 92/69 Section C.7, the method is applicable only to water soluble substances. The test item shows no significant solubility in the different solvent systems. Therefore, no further testing could be performed on the substance at pH 4, pH 7 and pH 9. - Transformation products:
- not specified
- Details on hydrolysis and appearance of transformation product(s):
- No information on hydrolysis was acheived in the test due to solubility.
- Remarks on result:
- other: No information on hydrolysis was acheived in the test due to solubility.
- Remarks on result:
- not measured/tested
- Remarks:
- The solubility of the test substance in the buffer solutions pH 4, pH 7.0 and pH 9.0 is very low, therefore a test with different solubilizer was performed to increase the solubility of the test substance. It was not possible to increase the solubility of the test item with the use of different solubilizers. Peaks obtained, if any, were too small to allow quantification or even to follow a degradation curve. According to the EEC Directive 92/69 Section C.7, the method is applicable only to water soluble substances. The test item shows no significant solubility in the different solvent systems. Therefore, no further testing could be performed on the substance at pH 4, pH 7 and pH 9.
- Details on results:
- The solubility of the test substance in the buffer solutions pH 4.0, pH 7.0 and pH 9.0 was very low. It was not possible to increase the solubility of the test substance with the use of different solubilizers (acetone, acetonitrile and ethanol).
Peaks obtained, if any, were too small to allow quantification or even to follow a degradation curve.
According to the EEC Directive 92/69 Section C.7, the method is applicable only to water soluble substances. The test item shows no significant solubility in the different solvent systems. Therefore, no further testing could be performed on the substance at pH 4, pH 7 and pH 9. - Validity criteria fulfilled:
- yes
- Conclusions:
- In an OECD 111 study conducted to GLP, the solubility of the test item in the buffer solutions pH 4.0, pH 7.0 and pH 9.0 was very low. It was not possible to increase the solubility of the test substance with the use of different solubilizers (acetone, acetonitrile and ethanol). Peaks obtained, if any, were too small to allow quantification or even to follow a degradation curve.
According to the EEC Directive 92/69 Section C.7, the method is applicable only to water soluble substances. The test item shows no significant solubility in the different solvent systems. Therefore, no further testing could be performed on the substance at pH 4, pH 7 and pH 9. (RCC Ltd, 2007).
Reference
The solubility of the test substance in the buffer solutions pH 4, pH 7.0 and pH 9.0 is very low, therefore a test with different solubilizer was performed to increase the solubility of the test substance.
It was not possible to increase the solubility of the test item with the use of different solubilizers. Peaks obtained, if any, were too small to allow quantification or even to follow a degradation curve.
According to the EEC Directive 92/69 Section C.7, the method is applicable only to water soluble substances. The test item shows no significant solubility in the different solvent systems. Therefore, no further testing could be performed on the substance at pH 4, pH 7 and pH 9.
Description of key information
In an OECD 111 study conducted to GLP, the solubility of the test item in the buffer solutions pH 4.0, pH 7.0 and pH 9.0 was very low. It was not possible to increase the solubility of the test substance with the use of different solubilizers (acetone, acetonitrile and ethanol). Peaks obtained, if any, were too small to allow quantification or even to follow a degradation curve.
According to the EEC Directive 92/69 Section C.7, the method is applicable only to water soluble substances. The test item shows no significant solubility in the different solvent systems. Therefore, no further testing could be performed on the substance at pH 4, pH 7 and pH 9. (RCC Ltd, 2007).
Key value for chemical safety assessment
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