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EC number: 236-526-4 | CAS number: 13419-67-5
- 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)
- Endpoint:
- hydrolysis
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From March 06, 2000 to March 21, 2000
- 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:
- no
- Analytical monitoring:
- yes
- Details on sampling:
- Preparation of the buffer solutions:
The buffer solutions were filtered through a 0.2 µm membrane filter to ensure they were sterile before commencement of the test. Also these solutions were subjected to ultrasonication and degassing with nitrogen to minimise dissolved oxygen content.
Preparation of the samples:
Sample solutions were prepared in stoppered glass flasks at a nominal concentration of 0.5 g/L in the three buffer solutions.
In an attempt to minimise oxidation, individual aliquots, sealed in vessels containing an inert nitrogen gas headspace, were incubated at the test temperature for each time point to eliminate the need to expose the test solution to air when sampled. The solutions were shielded from light whilst maintained at the test temperature. - Details on test conditions:
- Preliminary Test/Test 1
Sample solutions at pH 4, 7 and 9 were maintained at 50.0 ± 0.5 °C for a period of 120 hours.
Analysis of sample solutions:
Aliquots of the sample solutions were taken from the flasks at various times and the pH of each solution recorded. The concentration of the sample solution was determined by high performance liquid chromatography (HPLC).
Samples
Duplicate aliquots (A and B) of sample solution were diluted by a factor of five using reverse osmosis water for pH 7 and pH 9 samples and using pH 9 buffer for pH 4 samples. All diluting solvents were degassed with nitrogen prior to use.
Standards
Duplicate standard solutions of the test substance 70 % were prepared in the required sample matrix at a nominal concentration of 100 mg/L. A single marker standard of DADTL was prepared in reverse osmosis water at a nominal concentration of 200 mg/L for the 120 hour analysis only. - Transformation products:
- yes
- No.:
- #1
- Key result
- pH:
- 4
- Temp.:
- 25 °C
- DT50:
- > 1 yr
- Key result
- pH:
- 7
- Temp.:
- 25 °C
- Remarks on result:
- other: The test substance 70 % could not be prevented from oxidising
- Key result
- pH:
- 9
- Temp.:
- 25 °C
- Remarks on result:
- other: The test substance 70 % could not be prevented from oxidising
- Validity criteria fulfilled:
- yes
- Conclusions:
- Under the study conditions, the estimated hydrolytic half-life of the test substance at pH 4 (25 °C) was determined to be >1 year. Estimation of half-life at pH 7 and 9 could not be made because the test substance could not be prevented from oxidizing.
- Executive summary:
A study was conducted to determine the hydrolytic stability of the test substance solution according to OECD Guideline 111. Sample solutions were prepared in stoppered glass flasks at a nominal concentration of 0.5 g/L in the three buffer solutions pH 4, 7 and 9 and were maintained at 50.0 ± 0.5 °C for a period of 120 hours. To minimise oxidation, individual aliquots were sealed in vessels containing an inert nitrogen gas headspace. Aliquots of the sample solutions were taken from the flasks at various times and the pH of each solution recorded. The concentration of the sample solution was determined by high performance liquid chromatography (HPLC). Under the study conditions, the estimated hydrolytic half-life of the test substance at pH 4 (25 °C) was determined to be >1 year. Estimation of half-life at pH 7 and 9 could not be made because the test substance could not be prevented from oxidizing (O'Connor, 2000).
Reference
The test substance concentrations at the given time points:
pH 4 at 50.0 ± 0.5 °C
Time (h) |
0 |
2.4 |
24 |
120 |
Conc. (g/L) |
0.490 |
0.479 |
0.471 |
0.419 |
% of initial |
100 |
97.8 |
96.2 |
85.4 |
There has been some loss of test substance due to oxidation. Therefore, an estimation has been done of approximately 10 % hydrolysis after 5 days at 50 °C, equivalent to a hydrolytic half-life greater than 1 year at 25 °C.
pH 7 at 50.0 ± 0.5 °C
Time (h) |
0 |
2.4 |
24 |
120 |
Conc. (g/L) |
0.571 |
0.479 |
0.444 |
0.231 |
% of initial |
100 |
96.3 |
85.9 |
44.6 |
No estimation of hydrolytic half-life can be obtained due to oxidation of the test substance.
pH 9 at 50.0 ± 0.5 °C
Time (h) |
0 |
2.4 |
24 |
120 |
Conc. (g/L) |
0.515 |
0.490 |
0.355 |
0.156 |
% of initial |
100 |
95.2 |
69.0 |
30.2 |
No estimation of hydrolytic half-life can be obtained due to oxidation of the test substance.
Description of key information
Key value for chemical safety assessment
- Half-life for hydrolysis:
- 1 yr
- at the temperature of:
- 25 °C
Additional information
A study was conducted to determine the hydrolytic stability of the test substance solution according to OECD Guideline 111. Sample solutions were prepared in stoppered glass flasks at a nominal concentration of 0.5 g/L in the three buffer solutions pH 4, 7 and 9 and were maintained at 50.0 ± 0.5 °C for a period of 120 hours. To minimise oxidation, individual aliquots were sealed in vessels containing an inert nitrogen gas headspace. Aliquots of the sample solutions were taken from the flasks at various times and the pH of each solution recorded. The concentration of the sample solution was determined by high performance liquid chromatography (HPLC). Under the study conditions, the estimated hydrolytic half-life of the test substance at pH 4 (25 °C) was determined to be >1 year. Estimation of half-life at pH 7 and 9 could not be made because the test substance could not be prevented from oxidizing (O'Connor, 2000).
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