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EC number: 204-794-1 | CAS number: 126-58-9
- 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
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 111 (Hydrolysis as a Function of pH)
- Deviations:
- not specified
- GLP compliance:
- not specified
- Radiolabelling:
- not specified
- Analytical monitoring:
- yes
- Details on sampling:
- Concentrations were determined after 5 days for each of the 3 buffer systems using HPLC analysis.
- Buffers:
- - pH: 4.0
- Type and final molarity of buffer:
- Composition of buffer: citric acid: 0.056 M; sodium hydroxide: 0.068 M; sodium chloride: 0.044 M
- pH: 7.0
- Type and final molarity of buffer:
- Composition of buffer: potassium dihydrogen phosphate: 0.026 M; disodium hydrogen phosphate 0.041 M
- pH: 9.0
- Type and final molarity of buffer:
- Composition of buffer: sodium tetraborate: 0.013 M; hydrochloric acid 0.0046 M - Details on test conditions:
- Buffer solutions containing the test substance were inclubated in the dark at 50 degrees celcius.
- Duration:
- 5 d
- pH:
- 4
- Temp.:
- 50 °C
- Initial conc. measured:
- 0.035 mol/L
- Duration:
- 5 d
- pH:
- 7
- Temp.:
- 50 °C
- Initial conc. measured:
- 0.035 mol/L
- Duration:
- 5 d
- pH:
- 9
- Temp.:
- 50 °C
- Initial conc. measured:
- 0.035 mol/L
- Transformation products:
- no
- % Recovery:
- > 99
- St. dev.:
- 0.7
- pH:
- 4
- Temp.:
- 50 °C
- Duration:
- 5 d
- Remarks on result:
- other: di-pentaerythritol cannot be considered to be rapidly hydrolysed and the results suggest that abiotic removal by hydrolysis will not be an important pathway of degradation for di-pentaerythritol in the envrionment. This study result indicates that di-pent
- % Recovery:
- > 99
- St. dev.:
- 0.7
- pH:
- 7
- Temp.:
- 50 °C
- Duration:
- 5 d
- Remarks on result:
- other: di-pentaerythritol cannot be considered to be rapidly hydrolysed and the results suggest that abiotic removal by hydrolysis will not be an important pathway of degradation for di-pentaerythritol in the envrionment. This study result indicates that di-pent
- % Recovery:
- > 99
- St. dev.:
- 0.7
- pH:
- 9
- Temp.:
- 50 °C
- Duration:
- 5 d
- Remarks on result:
- other: di-pentaerythritol cannot be considered to be rapidly hydrolysed and the results suggest that abiotic removal by hydrolysis will not be an important pathway of degradation for di-pentaerythritol in the envrionment. This study result indicates that di-pent
- Key result
- Remarks on result:
- not measured/tested
- Remarks:
- Study from 1992.
- Conclusions:
- Original substance concentration changed by less than 1% after 5 days. Therefore, it is concluded that the test substance is not sensitive to pH dependant hydrolysis.
- Executive summary:
A test was conducted according to OECD 111 to assess abiotic hydrolytic transformations of di-pentaerythritol in aquatic systems at pH values normally found in the environment (pH 4 – 9).
The rate of hydrolysis of the test substance as a function of pH and the identity or nature and rates of formation and decline of hydrolysis products will dictate the degree to which organisms may be exposed due to surface water emissions of the test substance.
Sterile aqueous buffer solutions of different pH values (pH 4, 7 and 9) were treated with the test substance and incubated in the dark under controlled laboratory conditions (at a constant temperature of 50oC). After the appropriate time interval (5 days), the buffer solutions were analysed for the test substance and for hydrolysis products. After 5 days, no significant transformation was observed. As such di-pentaerythritol cannot be considered to be rapidly hydrolysed and the results suggest that abiotic removal by hydrolysis will not be an important pathway of degradation for di-pentaerythritol in the envrionment. This study result indicates that di-pentaerythritol will have a hydrolytic half life of greater than 1 year at envrionmentally relevant pH`s (4 -9) and temperatures.
Reference
Results suggested that no significant hyrolysis took place in any of the buffer systems.
Description of key information
Di-pentaerythritol is stable to hydrolysis at environmentally relevant pH ranges, i.e. half life of greater than 1 year.
Key value for chemical safety assessment
Additional information
A test was conducted according to OECD 111 to assess abiotic hydrolytic transformations of di-pentaerythritol in aquatic systems at pH values normally found in the environment (pH 4 – 9). After 5 days, no significant transformation was observed. As such di-pentaerythritol cannot be considered to be rapidly hydrolysed and the results suggest that abiotic removal by hydrolysis will not be an important pathway of degradation for di-pentaerythritol in the environment. It is therefore estimated that di-pentaerythritol will have a hydrolytic half life of greater than 1 year at environmentally relevant pH`s (4 -9) and temperatures (20 °C).
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