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EC number: 433-180-8 | 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
- Endpoint:
- hydrolysis
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1999-02-24 to 1999-03-26
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP study according to EU method C7
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 999
- Report date:
- 1999
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.7 (Degradation: Abiotic Degradation: Hydrolysis as a Function of pH)
- GLP compliance:
- yes
Test material
- Details on test material:
- - Name of test material (as cited in study report): Reaktiv-Orange DYPR934
Constituent 1
Study design
- Analytical monitoring:
- yes
- Details on sampling:
- PREPARATION OF TEST SAMPLE:
Solutions of the test substance were prepared by weighing between 10 and 11 mg of the test substance in a 50 mL volumetric flask and dissolving in the relevant buffer. The resulting solution was subjected immediately to the hydrolytically procedure.
PREPARATION OF THE STANDARDS
The calculation standards were freshly prepared by weighing between 5 and 11 mg of the standard test substance in a 50 mL volumetric flask and dissolving in the relevant buffer or in a buffer in which the test substance is hydrolytically stable. - Buffers:
- pH 4:
COMPOSITION OF THE BUFFER:
21.008 g citric acid were dissolved in 200 mL sodium hydroxide solution (1 mole/L). The solution was filled up to a volume of 1000 mL with water. 560 mL were taken and 44 mL of hydrochloric acid (1 mole/L) were added and filled up to a volume of 1000 mL with distilled water.
pH 7:
COMPOSITION OF THE BUFFER:
13.61 g potassium dihydrogen phosphate were dissolved in 100 mL distilled water. 29.63 mL of sodium hydroxide (1mole/L) were added to 500 mL of this solution and filled up to a volume of 1000 mL with destilled water.
pH 9:
COMPOSITION OF THE BUFFER:
7.46 g of potassium chloride and 6.184 g of boric acide were dissolved in 1000 mL water. 500 mL of this solution were added to 21.3 mL sodium hydroxide (1mole/L) and filled up to a volume of 1000 mL with water. - Details on test conditions:
- Hydrolysis test procedure
The flask containing the hydrolysis mixture was placed in a thermostatically mixture controlled water bath at the selected temperature for the specified time. Thereafter it was cooled immediately. The pH was controlled. The HPLC analysis of the unhydrolysed test substance (both main compounds) was peroformed without any delay.
Duration of testopen allclose all
- Duration:
- 9 d
- pH:
- 4
- Temp.:
- 25 °C
- Initial conc. measured:
- >= 196 - <= 224 mg/L
- Duration:
- 11.4 d
- pH:
- 4
- Temp.:
- 25 °C
- Initial conc. measured:
- >= 196 - <= 224 mg/L
- Duration:
- 5.8 d
- pH:
- 7
- Temp.:
- 25 °C
- Initial conc. measured:
- >= 196 - <= 224 mg/L
- Duration:
- 9 d
- pH:
- 7
- Temp.:
- 25 °C
- Initial conc. measured:
- >= 196 - <= 224 mg/L
- Duration:
- 2.4 h
- pH:
- 9
- Temp.:
- 25 °C
- Initial conc. measured:
- >= 196 - <= 224 mg/L
- Positive controls:
- not specified
- Negative controls:
- no
Results and discussion
- Preliminary study:
- Yes see tables and comments "any other results incl. tables"
- Test performance:
- Preliminary test. A preliminary test was performed on the substance at 50 ± 0.1 °C at each of pH 4.0, 7.0 and 9.0.
The decomposition at pH 9 was higher than 50 % after 2.4 hours at 50 °C for the main compound (I) as well as for the main component (II).
REMARKS: According to the guideline, if less than 10 per cent of the reaction is observed after 5 days
(t1/2 > 1 year), the chemical is considered hydrolytically stable and no additional testing is required. If the substance is known to be unstable at environmentally relevant temperatures, the preliminary test is not required. The analytical method must be sufficiently precise and sensitive to detect a reduction of 10 per cent in the initial concentration. In the Study the substance (Component (I) and component (II)) is considered INSTABLE at pH 9. According to the guideline a half-life period of less than one day under environmental conditions (25 °C) may be estimated. No further test was necessary. - Transformation products:
- not measured
Dissipation DT50 of parent compoundopen allclose all
- pH:
- 4
- Temp.:
- 50 °C
- Hydrolysis rate constant:
- 0.03 s-1
- DT50:
- 22.2 h
- pH:
- 4
- Temp.:
- 60 °C
- Hydrolysis rate constant:
- 0.08 s-1
- DT50:
- 8.5 h
- pH:
- 4
- Temp.:
- 70 °C
- Hydrolysis rate constant:
- 0.16 s-1
- DT50:
- 4.3 h
- pH:
- 4
- Temp.:
- 25 °C
- DT50:
- 231.3 h
- pH:
- 7
- Temp.:
- 50 °C
- Hydrolysis rate constant:
- 0.12 s-1
- DT50:
- 5.7 h
- pH:
- 7
- Temp.:
- 35 °C
- Hydrolysis rate constant:
- 0.02 s-1
- DT50:
- 36.3 h
- pH:
- 7
- Temp.:
- 25 °C
- DT50:
- 138.6 h
- Details on results:
- TEST CONDITIONS
- pH, sterility, temperature, and other experimental conditions maintained throughout the study: Yes
- Anomalies or problems encountered (if yes):None
Any other information on results incl. tables
Remarks:
Due to the fact that the test substance contains two main components the hydrolysis rates were calculated separately for each main component in the following way:
The initial concentration (c (0)) of the test substance and the concentration of the standard (c (standard)) were calculated from the sample weights. The concentration during the test process (c (t)) was calculated from the HPLC peak area of the respective main component in comparison with the HPLC peak area of the respective component in the standard solution using the formula:
C=(C (standard) Peak Area (sample))/(Peak Area (standard))
In the case of pseudo first reaction, according to the following relationships a linear dependence of l is expected for log (c (t)/c(0))
log (c(t)/c(0) = -(k/2.303).t
-log (c(t)/c(0))= (k/2.303).t
The experimental data of test 1 were checked graphically for the approximate fulfilling of this relationship. The constant Kobs was determined by linear regression of -log (c (t)/c (0) to t. The half-life period t1/2=ln2/kobs
The Arrhenius Equation
logk=-A/T + B was used to extrapolate the rate constants at higher temperatures to room temperature.
Applicant's summary and conclusion
- Conclusions:
- At pH 9 the decomposition is higher than 50% after 2.4 hours at 50°C for both main components. Thus the test substance may be considered hydrolytically instable at pH 9. According to the guideline a half-life period or less than one day under environmental conditions (25°C) may be estimated.
- Executive summary:
At pH 9 the decomposition is higher than 50% after 2.4 hours at 50°C for both main components. Thus the test substance may be considered hydrolytically instable at pH 9. According to the guideline a half-life period or less than one day under environmental conditions (25°C) may be estimated.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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