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EC number: 200-073-0 | CAS number: 50-97-5
- 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:
- 07 June 2018 to 10 July 2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- Study was conducted in accordance with international guidelines and in accordance with GLP
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 111 (Hydrolysis as a Function of pH)
- Deviations:
- no
- 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:
- EPA OPPTS 835.2120 (Hydrolysis of Parent and Degradates as a Function of pH at 25°C)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Date of Inspection: 18 July 2017 - 20 July 2017 Date on Certfiicate: 28 November 2017
- Radiolabelling:
- no
- Analytical monitoring:
- yes
- Details on sampling:
- - Sampling intervals for the parent/transformation products: 24 and 120 hours
- Sampling intervals/times for pH measurements: 24 and 120 hours - Buffers:
- - pH: 4.0, 7.0 and 9.0
- Composition of buffer:
pH 4.0: Components - citric acid (0.06 mol dm-3), sodium chloride (0.04 mol dm-3), sodium hydroxide (0.07 mol dm-3)
pH 7.0: Components - disodium hydrogen orthophoshate (0.03 mol dm-3), potassium hydrogogen orthophosphate (0.02 mol dm-3), sodium chloride (0.02 mol dm-3)
pH 9.0: Components - disodium tetraborate (0.01 mol dm-3), sodium chloride (0.02 mol dm-3)
The buffer solutions were passed through a 0.2 μm membrane filter to sterilise and subjected to ultrasonication and degassing with nitrogen to minimise dissolved oxygen. - Details on test conditions:
- TEST SYSTEM
- Type, material and volume of test flasks, other equipment used: Sealed glass vessels with minimal headspace
- Lighting: N/A - sample solutions were shielded from light
- Measures taken to avoid photolytic effects: As above - sample solutions were shieded from light and for analysis were transferred to amber vials
- Measures to exclude oxygen: Vessels are sealed and the buffer solutions were passed through a 0.2 μm membrane filter to sterilise and subjected to ultrasonication and degassing with nitrogen to minimise dissolved oxygen.
- Temperature: 50.0 ± 0.5 °C - Duration:
- 120 h
- pH:
- 4
- Temp.:
- 50 °C
- Initial conc. measured:
- 73.9 mg/L
- Duration:
- 120 h
- pH:
- 7
- Temp.:
- 50 °C
- Initial conc. measured:
- 72.9 mg/L
- Duration:
- 120 h
- pH:
- 9
- Temp.:
- 50 °C
- Initial conc. measured:
- 74.1 mg/L
- Number of replicates:
- 2
- Positive controls:
- no
- Negative controls:
- yes
- Preliminary study:
- The test item was determined to be hydrolytically stable therefore only a preliminary study is required. Results for the preliminary study are presented below.
- Transformation products:
- not specified
- % Recovery:
- 98.2
- pH:
- 4
- Temp.:
- 50 °C
- Duration:
- 120 h
- % Recovery:
- 99.3
- pH:
- 7
- Temp.:
- 50 °C
- Duration:
- 120 h
- % Recovery:
- 97.7
- pH:
- 9
- Temp.:
- 50 °C
- Duration:
- 120 h
- Key result
- pH:
- 4
- Temp.:
- 25 °C
- DT50:
- > 1 yr
- Key result
- pH:
- 7
- Temp.:
- 25 °C
- DT50:
- > 1 yr
- Key result
- pH:
- 9
- Temp.:
- 25 °C
- DT50:
- > 1 yr
- Details on results:
- TEST CONDITIONS
- pH, sterility, temperature, and other experimental conditions maintained throughout the study: Yes
- Validity criteria fulfilled:
- yes
- Conclusions:
- The half-lives at 25 °C of the test item were estimated to be > 1 year for pH 4, 7 and 9.
- Executive summary:
Assessment of hydrolytic stability was carried out using a procedure designed to be compatible with Method C.7 Abiotic Degradation, Hydrolysis as a Function of pH of Commission Regulation (EC) No 440/2008 of 30 May 2008, Method 111 of the OECD Guidelines for Testing of Chemicals, 13 April 2004 and Method 835.2120 of the OCSPP Guidelines. The results are as follows:
pH
Estimated half-life at 25°C
4
> 1 year
7
> 1 year
9
> 1 year
Reference
The mean peak areas relating to the standard and sample solutions for the initial time, 24 hour and 120 hour time points for pH 4, 7 and 9 are shown in the following tables:
Table 1 Initial
Solution |
Mean peak area |
Standard pH 4, 70.8 mg/L |
4.8004 x 107 |
Standard pH 4, 70.5 mg/L |
5.1345 x 107 |
Sample A pH 4, initial |
2.5940 x 107 |
Sample B pH 4, initial |
2.6013 x 107 |
Standard pH 7, 70.8 mg/L |
5.0283 x 107 |
Standard pH 7, 70.5 mg/L |
5.1186 x 107 |
Sample A pH 7, initial |
2.6223 x 107 |
Sample B pH 7, initial |
2.6097 x 107 |
Standard pH 9, 70.8 mg/L |
4.9184 x 107 |
Standard pH 9, 70.5 mg/L |
5.0771 x 107 |
Sample A pH 9, initial |
2.6244 x 107 |
Sample B pH 9, initial |
2.6194 x 107 |
Table 2 24 Hour*
*Note: standard response replication, see Discussion of Standard 71.1 mg/L
Solution |
Mean peak area |
Standard pH 4, 70.9 mg/L |
4.9976 x 107 |
Standard pH 4, 71.1 mg/L |
4.5112 x 107 |
Sample A pH 4, 24-hour |
2.6075 x 107 |
Sample B pH 4, 24-hour |
2.5615 x 107 |
Standard pH 7, 70.9 mg/L |
5.0858 x 107 |
Standard pH 7, 71.1 mg/L |
4.4549 x 107 |
Sample A pH 7, 24-hour |
2.5906 x 107 |
Sample B pH 7, 24-hour |
2.5876 x 107 |
Standard pH 9, 70.9 mg/L |
5.0134 x 107 |
Standard pH 9, 71.1 mg/L |
4.4712 x 107 |
Sample A pH 9, 24-hour |
2.5943 x 107 |
Sample B pH 9, 24-hour |
2.6012 x 107 |
Table 3 120 Hour
Solution |
Mean peak area |
Standard pH 4, 70.8 mg/L |
5.0926 x 107 |
Standard pH 4, 70.6 mg/L |
5.0458 x 107 |
Sample A pH 4, 24-hour |
2.5978 x 107 |
Sample B pH 4, 24-hour |
2.6015 x 107 |
Standard pH 7, 70.8 mg/L |
5.0794 x 107 |
Standard pH 7, 70.6 mg/L |
5.1180 x 107 |
Sample A pH 7, 24-hour |
2.6336 x 107 |
Sample B pH 7, 24-hour |
2.5907 x 107 |
Standard pH 9, 70.8 mg/L |
5.1368 x 107 |
Standard pH 9, 70.6 mg/L |
5.0602 x 107 |
Sample A pH 9, 24-hour |
2.6095 x 107 |
Sample B pH 9, 24-hour |
2.6113 x 107 |
The test item concentrations at the given time points are shown in the following tables:
Table 4 - pH 4 at 50.0 ± 0.5 °C
Time (hours) |
Concentration (mg/L) |
Percentage of mean initial concentration |
||
A |
B |
A |
B |
|
0 |
73.8 |
74.0 |
- |
- |
24 |
77.8 |
76.5 |
105 |
104 |
120 |
72.4 |
72.5 |
98.1 |
98.2 |
Less than 10% hydrolysis after 5 days at 50 °C, equivalent to half-life > 1 year at 25°C.
Table 5 - pH 7 at 50.0 ± 0.5 °C
Time (hours) |
Concentration (mg/L) |
Percentage of mean initial concentration |
||
A |
B |
A |
B |
|
0 |
73.0 |
72.7 |
- |
- |
24 |
77.1 |
77.0 |
106 |
106 |
120 |
73.0 |
71.8 |
100 |
98.6 |
Less than 10% hydrolysis after 5 days at 50 °C, equivalent to half-life > 1 year at 25°C.
Table 6 - pH 9 at 50.0 ± 0.5 °C
Time (hours) |
Concentration (mg/L) |
Percentage of mean initial concentration |
||
A |
B |
A |
B |
|
0 |
74.2 |
74.0 |
- |
- |
24 |
77.7 |
77.9 |
105 |
105 |
120 |
72.4 |
72.4 |
97.6 |
97.7 |
Less than 10% hydrolysis after 5 days at 50 °C, equivalent to half-life > 1 year at 25°C.
Validation
The linearity of the detector response with respect to concentration was assessed over the nominal concentration range of 2.5 to 100 mg/L. The plot was found to be 1storder with a correlation coefficient (r) of 1.000.
Discussion
The concentration of each solution did not exceed the lesser of 0.01 mol/L or half the water solubility.
No significant peaks were observed at the approximate retention time of the test item on analysis of any matrix blank solutions.
The pH of all the test solutions remained stable throughout testing (< ±0.1 pH unit) of the target pH 4, 7 and 9.
Standard solutions were prepared at approximately twice the concentration of the sample solutions in error, i.e. 70 mg/L, whereas the sample solutions were nominally 35 mg/L. The detector response was linear over the working concentration range and there was no significant effect on the study.
Standard solutions for the 24-Hour sample analysis demonstrated poor replication resulting in an increase in the measured test item concentration in the sample solutions (approximately 105% of initial concentration). Analysis of the 120-Hour sample solutions were consistent with the initial assay and demonstrated that there was no significant hydrolysis of the test item at pH 4, 7 and 9 (approximately 98% of initial concentration). Therefore, it was considered that the overall results were acceptable.
Description of key information
The half-lives at 25 °C of the test item were estimated to be > 1 year for pH 4, 7 and 9.
Key value for chemical safety assessment
- Half-life for hydrolysis:
- 1 yr
- at the temperature of:
- 25 °C
Additional information
Assessment of hydrolytic stability was carried out using a procedure designed to be compatible with Method C.7 Abiotic Degradation, Hydrolysis as a Function of pH of Commission Regulation (EC) No 440/2008 of 30 May 2008, Method 111 of the OECD Guidelines for Testing of Chemicals, 13 April 2004 and Method 835.2120 of the OCSPP Guidelines. The results are as follows:
pH |
Estimated half-life at 25°C |
4 |
> 1 year |
7 |
> 1 year |
9 |
> 1 year |
As the minimum estimated half life, 1 year is selected as the key value for chemical safety assessment.
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