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EC number: 931-468-2 | CAS number: 1190625-94-5
- 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)
Description of key information
Not technically possible to determine hydrolysis as a function of pH; OECD 111, EU Method C.7 and EPA OPPTS 835.2120
Key value for chemical safety assessment
Additional information
The hydrolysis as a function of pH of the test material was investigated in accordance with the standardised guidelines OECD 111, EU Method C.7 and EPA OPPTS 835.2120 under GLP conditions. The study was awarded a reliability score of 1 in accordance with the principles for assessing data quality set forth by Klimisch et al. (1997).
The rate of hydrolysis of the test material as a function of pH was investigated at buffer solutions at pH values normally found in the environment (pH 4, 7 and 9).
The buffer solutions were filter-sterilised and transferred into a sterile vessel. To exclude oxygen, nitrogen gas was purged through the solution for 5 minutes. The test material was spiked to the solutions at a target concentration of 13 µg/L using a spiking solution in methanol. For each sampling time (5 and 12 days), duplicate sterile PET vessels under vacuum were filled with 6 mL test solution and placed in the dark in a temperature controlled environment at 50.1 ± 0.3 °C.
After 5 days, a relative concentration decrease of 90, 84 and 79 % was observed at pH 4, pH 7, and pH 9, respectively. No hydrolysis was expected based on the molecular structure of the test material, therefore, to test whether this concentration decrease is caused by adsorption of test material on the wall of the test tube, additional samples were taken at t = 12 days. From duplicate vessels, one subsample was diluted as described above. The remaining volume was transferred into a glass vial and the vessels walls were flushed with an equal amount methanol.
This experiment indicates that the test material adsorbs to the container wall since the test material concentration analysed after flushing with methanol is higher than the concentration analysed in the subsample. This, along with the low test material concentrations used as a result of the low water solubility of the test material, results in the definitive test for hydrolysis not being technically possible.
Under the conditions of this study, hydrolysis as a function of pH cannot be determined.
In accordance with section 2 of Annex XI of Regulation (EC) No 1907/2006, it is considered justified to omit the full hydrolysis as a function of pH study (required in section 9.2.2.1 of Annex VIII) on the grounds that testing is not technically feasible.
An attempt was made to determine the hydrolysis as a function of pH in a screening study; however, no value could be determined. The test material concentrations employed during the hydrolysis test were very low, since the guideline requires that initial solution concentrations are less than half the water solubility (water solubility 0.000026 g/L) and that the test material is analytically measureable at 10 % of the initial test concentration (i.e. the LOQ is 0.001 mg/L).
A large test material decrease was observed during the preliminary test. Experiments have indicated that adsorbance to container walls causes significant test material loss at these low concentration levels. Together, these factors result in the definitive test for hydrolysis not being technically possible.
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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