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Diss Factsheets
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EC number: 415-070-1 | CAS number: -
- 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:
- 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)
- GLP compliance:
- yes
- Radiolabelling:
- no
- Analytical monitoring:
- yes
- Details on sampling:
- The concentration of the substance was determined using HPLC method. The conditions were:
-Sample pre-treatment preliminary test
Immediately after samples were taken, they were cooled down to room temperature. Then, each pH 4 and pH 7 sample was diluted, in duplicate, 40 times with Milli-Q water, prior to analysis. Each pH 9 sample was diluted 66.67 times with Milli-Q water, prior to analysis.
-Sample pre-treatment test 1
Immediately after samples were taken, they were cooled down to room temperature. Then, each sample was diluted, in duplicate, 80 or 100 times with Milli-Q water, prior to analysis.
-Blank solutions
At the first day of each test, blank buffer solutions were pre-treated in a similar fashion to the corresponding test solutions. - Buffers:
- A sterile 0.05 M acetate buffer pH 4; sodium acetate (p.a., Merck, Darmstadt, FRG)/acetic acid (p.a., Merck) in Milli-Q water (Millipore Corp., Bedford, MA., USA);
A sterile 0.05 M phosphate buffer pH 7; Potassium dihydrogenphosphate (p.a., Merck)/sodium hydroxide (p.a., Merck) in Milli-Q water;
A sterile 0.05 M borate buffer pH 9; bore acid (p.a., Merck)/potassium chloride (p.a,, Merck)/sodium hydroxide in Milli-Q water. - Details on test conditions:
- -Preparation of the test Solutions
Prior to the performance of each test, the test solutions were freshly prepared. Therefore, an accurately weighed amount of between 46 - 80 mg test substance was added to 50.0 ml buffer solution pH 4, pH 7 or pH 9. The resultant solutions were filter-sterilized through a 0.2 µm membrane filter (FP 030/3, Schleicher & Schuell, 's-Hertogenbosch, The Netherlands) and transferred into sterile glass vessels.
To exelude oxygen, nitrogen gas was bubbled through each solution for 5 minutes. Thereafter, each vessel was tightly sealed with a septum-crimpcap.
-Preliminary test
After preparation, the test solutions at pH 4, 7 and 9 were placed in a thermostatically controlled waterbath at 50.0 ± 0.5°C in the dark. The concentration of the test substance was determined immediately after preparation (T=:0), after 2.4 hours and after 5 days.
-Test 1
During the preliminary test, significant hydrolysis was observed at pH 4 and 9. Therefore, test 1 was carried out at these pH values.
After preparation, the test solutions pH 4 and 9 were placed in a thermostatically controlled waterbath at 60.0 ± 0.5°C in the dark. The concentration of the test substance at pH 4 was determined immediately after preparation (T=0) and 120.5, 144.5, 168, 214.6, and 287.4 hours after T=0.
The concentration of the test substance at pH 9 was determined immediately after preparation (T=0) and 120.1, 144.1, 168, 214.2, and 287 hours after T=0.
-pH measurements
For each test solution, the pH value at room temperature was determined at the beginning and at the end of the test (preliminary test) or at the beginning of the test. - Duration:
- 5 d
- pH:
- 4
- Temp.:
- 50 °C
- Initial conc. measured:
- 716 mg/L
- Remarks:
- preliminary test
- Duration:
- 5 d
- pH:
- 7
- Temp.:
- 50 °C
- Initial conc. measured:
- 972 mg/L
- Remarks:
- preliminary test
- Duration:
- 5 d
- pH:
- 9
- Temp.:
- 50 °C
- Initial conc. measured:
- 1 569 mg/L
- Remarks:
- preliminary test
- Duration:
- 12 d
- pH:
- 4
- Temp.:
- 60 °C
- Initial conc. measured:
- 848 mg/L
- Remarks:
- test 1
- Duration:
- 12 d
- pH:
- 9
- Temp.:
- 60 °C
- Initial conc. measured:
- 1 317 mg/L
- Remarks:
- test 1
- Number of replicates:
- The test concentration was measured in duplicate
- Preliminary study:
- At pH 7, a decrease in concentration < 10% was observed after 5 days (half-life time > 1 year).
At pH 4 and 9, a decrease in concentration < 50% after 2.4 hours and a decrease 1n concentration > 10% after 5 days was observed. Therefore, no further testing was necessary at pH 7. Test 1 had to be performed at pH 4 and 9. - Transformation products:
- no
- % Recovery:
- 93
- pH:
- 7
- Temp.:
- 50 °C
- Duration:
- ca. 5 d
- Remarks on result:
- other: preliminary test
- % Recovery:
- 82
- pH:
- 4
- Temp.:
- 60 °C
- Duration:
- ca. 12 d
- Remarks on result:
- other: test 1
- % Recovery:
- 88
- pH:
- 9
- Temp.:
- 60 °C
- Duration:
- ca. 12 d
- Remarks on result:
- other: test 1
- Key result
- Remarks on result:
- hydrolytically stable based on preliminary test
- Validity criteria fulfilled:
- yes
- Conclusions:
- The substance is hydrolytically stable at pH 7, and hydrolytically unstable at pH 4 and 9, under the conditions of the test.
- Executive summary:
The purpose of the study was to examine the hydrolysis behaviour of the test substance at pH values normally found in the environment (pH 4-9), according to the method C.7 of EEC-Directive 92/69 EEC. During the preliminary test, significant hydrolysis was observed at pH 4 and 9. Therefore, test was carried out at these pH values. After 287 hours the amount of hydrolysis was still below 20 % at both pH 4 and 9. As after an initial drop in the test substance the concentration started to fluctuate, it was not probable that a larger decrease will be found if test was continued for a longer time period. Therefore, no more samples were taken.
The substance was found to be hydrolytically stable at pH 7, and hydrolytically unstable at pH 4 and 9, under the conditions of the test.
Reference
According to the guideline, at least 4 samples covering the range 20 to 70 % of hydrolysis should be analysed during test 1 in order to test for pseudo-first order behaviour. However in this case even after 287 hours the amount of hydrolysis was still below 20% at both pH 4 and 9. After an initial drop in the test substance concentration the concentration started to fluctuate. For this reason, it is not probable that a larger decrease will be found if test 1 is continued for a longer time period.
Therefore, no more samples were taken.
Description of key information
hydrolytically stable at pH 7 and hydrolytically unstable at pH 4 and 9
Key value for chemical safety assessment
Additional information
The purpose of the study was to examine the hydrolysis behaviour of the test substance at pH values normally found in the environment (pH 4-9), according to the method Directive 92/69 EEC, Annex V. Part C, 7.
The substance was found to be hydrolytically stable at pH 7, and hydrolytically unstable at pH 4 and 9, under the conditions of the test.
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