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EC number: 470-180-7 | CAS number: 61196-40-5
- 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:
- 2004-10-13 to 2005-03-21
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.7 (Degradation: Abiotic Degradation: Hydrolysis as a Function of pH)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 111 (Hydrolysis as a Function of pH)
- Deviations:
- no
- GLP compliance:
- yes
- Radiolabelling:
- no
- Analytical monitoring:
- yes
- Buffers:
- - pH: 4, 7 and 9
Composition of buffer:
-pH 4: 21.01 g citric acid monohydrate were dissolved in 200 mL sodium hydroxide solution (c = 1 mol/L). This solution was filled up to a volume of 1000 mL with distilled water. 44 mL of hydrochloric acid (c = 1 mol/L) were added to 560 mL of this solution and filled up to a volume of 1000 mL with distilled water. The pH value was adjusted to pH 4 for each hydrolysis temperature.
-pH 7: 13.61 g potassium dihydrogen phosphate were dissolved in 1000 mL distilled water. 30 mL of sodium hydroxide solution (c = 1 mol/L) were added to 500 mL of this solution and filled up to a volume of 1000 mL with distilled water. The pH value was adjusted to pH 7 for each hydrolysis temperature.
-pH 9: 7.46 g potassium chloride and 6.18 g boric acid were dissolved in 1000 mL distilled water. 21 mL of sodium hydroxide solution (c = 1 mol/L) were added to 500 mL of this solution and filled up to a volume of 1000 mL with distilled water. The pH value was adjusted to pH 9 for each hydrolysis temperature. - Positive controls:
- no
- Negative controls:
- no
- Transformation products:
- not measured
- % Recovery:
- > 90
- pH:
- 4
- Temp.:
- 50 °C
- Duration:
- 5 d
- % Recovery:
- > 90
- pH:
- 7
- Temp.:
- 50 °C
- Duration:
- 5 d
- Key result
- pH:
- 4
- Temp.:
- 25 °C
- DT50:
- > 1 yr
- Key result
- pH:
- 7
- Temp.:
- 25 °C
- DT50:
- > 1 yr
- Results with reference substance:
- not applicable
- Validity criteria fulfilled:
- yes
- Conclusions:
- The test substance may be considered as hydrolytically stable.
- Executive summary:
Abiotic degradation of the test item was assessed by means of hydrolysis monitoring as a function of pH in accordance with OECD TG 111. The concentration of the test item in buffered solutions at pH 4, 7 and 9 was analytically monitored over 5 days in a pre-test at 50 °C. At pH 4 and pH 7 less than 10 % of the reaction is observed after 5 days at 50 DC (t 14 > 1 year). Thus the test substance may be considered hydrolytically stable and according to the guidelines no additional testing is required. At pH 9 experiments were done at 50 DC, 65 °C and 75 DC. A calculation respectively extrapolation was not possible. At 50 °C an equilibrium was observed at approximately 20 % degradation. A 50 % degradation was not reached. A graphically calculation was not possible. For the experiments at 65 °C and 75 °C no linear relationship between -log (ct/c0) and t could be observed. The calculation of t1/2 was done graphically. As a result the test item may be considered hydrolytically stable.
Reference
At pH 4 and pH 7 less than 10 % of the reaction is observed after 5 days at 50 DC (t 14 > 1 year). Thus the test substance may be considered hydrolytically stable and according to the guidelines no additional testing is required.
At pH 9 experiments were done at 50 DC, 65 °C and 75 DC. A calculation respectively extrapolation was not possible. At 50 °C an equilibrium was observed at approximately 20 % degradation. A 50 % degradation was not reached. A graphically calculation was not possible.
For the experiments at 65 °C and 75 °C no linear relationship between -log (ct/c0) and t could be observed. The calculation of t1/2was done graphically.
Table 1 Results of the hydrolysis pre-test
pH |
Duration |
c0 in mg/L |
ct in mg/L |
Ct/C0 |
Decomposition in % |
4 |
2.4 h |
502.4 |
496.2 |
0.9877 |
1.2 |
2.4 h |
697.6 |
652.3 |
0.9351 |
6.5 |
|
5d |
502.4 |
493.2 |
0.9817 |
1.8 |
|
5d |
697.6 |
655.5 |
0.9397 |
6.0 |
|
7
|
2.4 h |
619.6 |
608.9 |
0.9823 |
1.7 |
2.4 h |
651.2 |
647.9 |
0.9950 |
0.5 |
|
5d |
619.6 |
615.6 |
0.9936 |
0.6 |
|
5d |
651.2 |
647.4 |
0.9942 |
0.6 |
|
9 |
2.4 h |
648.0 |
629.7 |
0.9717 |
2.8 |
2.4 h |
380.0 |
362.2 |
0.9531 |
4.7 |
|
5d |
648.0 |
555.6 |
0.8575 |
14.3 |
|
5d |
380.0 |
316.9 |
0.8333 |
16.6 |
Description of key information
The test item is hydrolytically stable according to results of an OECD TG 111 compliant study (reference 5.1.2-1).
Key value for chemical safety assessment
Additional information
Abiotic degradation of the test item was assessed by means of hydrolysis monitoring as a function of pH in accordance with OECD TG 111. The concentration of the test item in buffered solutions at pH 4, 7 and 9 was analytically monitored over 5 days in a pre-test at 50 °C. At pH 4 and pH 7 less than 10 % of the reaction is observed after 5 days at 50 DC (t 14 > 1 year). Thus the test substance may be considered hydrolytically stable and according to the guidelines no additional testing is required. At pH 9 experiments were done at 50 DC, 65 °C and 75 DC. A calculation respectively extrapolation was not possible. At 50 °C an equilibrium was observed at approximately 20 % degradation. A 50 % degradation was not reached. A graphically calculation was not possible. For the experiments at 65 °C and 75 °C no linear relationship between -log (ct/c0) and t could be observed. The calculation of t1/2 was done graphically. As a result the test item may be considered hydrolytically stable.
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