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A mixture of: disodium 6-[3-carboxy-4,5-dihydro-5-oxo-4-sulfonatophenyl)pyrazolin-4-yl-azo]-3-[2-oxido-4-(ethensulfonyl)-5-methoxyphenylazo]-4-oxidonaphthalene-2-sulfonate copper (II) complex; disodium 6-[3-carboxy-4,5-dihydro-5-oxo-4-sulfonatophenyl)pyrazolin-4-yl-azo]-3-[2-oxido-4-(2-hydroxyethylsulfonyl)-5-methoxyphenylazo]-4-oxidonaphthalene-2-sulfonate copper (II) complex
EC number: 423-940-7 | CAS number: 85585-91-7 PACIFIED REACTIVE BLACK 31
- 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
![](https://echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_environmental-fate-and-pathways.png)
Hydrolysis
Administrative data
- Endpoint:
- hydrolysis
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1996
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 996
- Report date:
- 1996
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.7 (Degradation: Abiotic Degradation: Hydrolysis as a Function of pH)
- Deviations:
- no
- GLP compliance:
- yes
Test material
- Reference substance name:
- A mixture of: disodium 6-[3-carboxy-4,5-dihydro-5-oxo-4-sulfonatophenyl)pyrazolin-4-yl-azo]-3-[2-oxido-4-(ethensulfonyl)-5-methoxyphenylazo]-4-oxidonaphthalene-2-sulfonate copper (II) complex; disodium 6-[3-carboxy-4,5-dihydro-5-oxo-4-sulfonatophenyl)pyrazolin-4-yl-azo]-3-[2-oxido-4-(2-hydroxyethylsulfonyl)-5-methoxyphenylazo]-4-oxidonaphthalene-2-sulfonate copper (II) complex;
- EC Number:
- 423-940-7
- EC Name:
- A mixture of: disodium 6-[3-carboxy-4,5-dihydro-5-oxo-4-sulfonatophenyl)pyrazolin-4-yl-azo]-3-[2-oxido-4-(ethensulfonyl)-5-methoxyphenylazo]-4-oxidonaphthalene-2-sulfonate copper (II) complex; disodium 6-[3-carboxy-4,5-dihydro-5-oxo-4-sulfonatophenyl)pyrazolin-4-yl-azo]-3-[2-oxido-4-(2-hydroxyethylsulfonyl)-5-methoxyphenylazo]-4-oxidonaphthalene-2-sulfonate copper (II) complex;
- Cas Number:
- 85585-91-7
- IUPAC Name:
- 4-[2-(7-{2-[4-(ethenesulfonyl)-2-hydroxy-5-methoxyphenyl]diazen-1-yl}-8-hydroxy-6-sulfonaphthalen-2-yl)diazen-1-yl]-5-oxo-1-(4-sulfophenyl)-4,5-dihydro-1H-pyrazole-3-carboxylic acid 4-[2-(8-hydroxy-7-{2-[2-hydroxy-4-(2-hydroxyethanesulfonyl)-5-methoxyphenyl]diazen-1-yl}-6-sulfonaphthalen-2-yl)diazen-1-yl]-5-oxo-1-(4-sulfophenyl)-4,5-dihydro-1H-pyrazole-3-carboxylic acid dicopper tetrasodium hydride
- Test material form:
- solid
Constituent 1
- Specific details on test material used for the study:
- Identification: Pacified Reactive Black 31
Description: Dark blue crystals
Batch: 9T-55
Purity: 89%
Storage: At room temperature in the dark
Stability under storage conditions: Stable - Radiolabelling:
- no
Study design
- Analytical monitoring:
- yes
- Details on sampling:
- Test 1
Suring the preliminary tests, significant hydrolysis was observed at pH 9. For pH 4 and 7, no conclusions for the rate of hydrolysis could be made. Therefore, Test 1 was carried out at all the pH values in duplicate.
After preparation, the test solutions pH 4, 7 and 9 were placed in a thermostatically controlled waterbbath at 70°C (for pH 4 and 7) and at 60°C for pH 9 in the dark.
The concentration of the test substance at pH 4 was determined immediately after preparation (T=0) and 39.5 and 163 hours after T=0.
The concentration of the test substance at pH 7 was determined immediately after preparation (T=0) and 39.5, 63.0, 70.0, 90.5, 163, 187, 211, 236 and 260 hours after T=0.
The concentration of the test substance at pH 9 was determined immediately after preparation (T=0) and 24.0, 28.0, 34.0, 51.0 and 72.5 hours after T=0.
In addition, the lines from Test 1 for pH's 4, 7 and 9 were also used for the estimation of K 50°C (for pH 4) and K 25°C (for pH's 7 and 9). Therefore, the logarithms of all reactive concentrations were plotted against time for these pH values.
Test 3
Because the resultant line from Test 1 was a straight line for pH's 4, 7 and9, Test 3 was carried out.
Because Test 1 at pH 4 and pH 7 was performed at 70°C, Test 3 was performed at only one temperature >50°C; i.e. 80°C. Because Test 1 at pH 9 was conducted at 60°C, Test 3 was performed at only one temperature >50°C; i.e. 70°C.
After preparation, each test solution was placed in a thermostatically controlled waterbath at the specified temperature, and in the dark.
For pH 4, the concentration of the test substance was determined immediately after preparation (T=0) and 16.0, 39.5, 63.0, 70.0 and 163 hours after T=0.
For pH 7, the concentration of the test substance was determined immediately after preparation (T=0) and 16.0, 39.5, 43.5, 51.5, 63.0, 70.0, 90.0 and 163 hours after T=0.
For pH 9, the concentration of the test substance was determined immediately after preparation (T=0) and 13.3, 24.0 and 28.0 hours after T=0.
The logarithms of all relative concentrations wre plotted against time for these pH values. - 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 approximately 276 - 316 mg test substance was added to 50.0 ml buffer solution at pH 4, pH 7 or pH 9. The resultant solutions were filter sterilized through a 0.2 µm membrane filter and transferred into sterilised glass vessels.
To exclude oxygen, nitrogen gas was bubbled through each solution for approximately 5 minutes. Thereafter, each vessel was tightly sealed with a septum-crimcap.
Preliminary test
After preparation, the test solutions at pH 4, 7 and 9 were placed in a thermostatically controlled waterbath at 50°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.
The repeatability of the chromatograhoic method might have been insufficient to be able to determine changes in the test substance concentration of a few percent relative, to nominal. Therefore, it could not be assured that the decrease in concentration at pH 4 and 7 after 120 hours was really >10%. for this reason, the preliminary test for pH 4 and pH 7 was performed a second time.
Duration of testopen allclose all
- Duration:
- 5 d
- pH:
- 4
- Temp.:
- 50 °C
- Initial conc. measured:
- >= 3.98 - <= 5.2 g/L
- Remarks:
- Preliminary test
- Duration:
- 5 d
- pH:
- 7
- Temp.:
- 50 °C
- Initial conc. measured:
- ca. 6.23 - <= 6.78 g/L
- Remarks:
- Preliminary test
- Duration:
- 5 d
- pH:
- 9
- Temp.:
- 50 °C
- Initial conc. measured:
- 6.86 g/L
- Remarks:
- Preliminary test
- Duration:
- 163 h
- pH:
- 4
- Temp.:
- 70 °C
- Initial conc. measured:
- >= 5.08 - <= 6.1 g/L
- Remarks:
- Test 1
- Duration:
- 260 h
- pH:
- 7
- Temp.:
- 70 °C
- Initial conc. measured:
- >= 5.77 - <= 6.12 g/L
- Remarks:
- Test 1
- Duration:
- 72.5 h
- pH:
- 9
- Temp.:
- 60 °C
- Initial conc. measured:
- >= 5.52 - <= 5.97 g/L
- Remarks:
- Test 1
- Duration:
- 163 h
- pH:
- 4
- Temp.:
- 80 °C
- Initial conc. measured:
- 6.33 g/L
- Remarks:
- Test 3
- Duration:
- 163 h
- pH:
- 7
- Temp.:
- 80 °C
- Initial conc. measured:
- 5.75 g/L
- Remarks:
- Test 3
- Duration:
- 28 h
- pH:
- 9
- Temp.:
- 70 °C
- Initial conc. measured:
- >= 5.87 - <= 6.21 g/L
- Remarks:
- Test 3
- Number of replicates:
- Upto three
- Positive controls:
- no
- Negative controls:
- no
Results and discussion
- Preliminary study:
- For pH 4 and pH 7, no conclusions for the rate of hydrolysis could be made. At pH 9, a decrease in concentration <50% after 2.4 hours and a decrease in concentration >10% after 5 days was observed,
Therefore, Test 1 had to be performed at pH 4, 7 and 9. - Transformation products:
- no
Dissipation DT50 of parent compoundopen allclose all
- Key result
- pH:
- 7
- Temp.:
- 25 °C
- DT50:
- 120 000 h
- Type:
- (pseudo-)first order (= half-life)
- Key result
- pH:
- 9
- Temp.:
- 25 °C
- DT50:
- 10 000 h
- Type:
- (pseudo-)first order (= half-life)
- Details on results:
- The half-life times were 3.3E+02 hours at 70°C, 1.1E+02 hours at 80°C at pH7 and 58 hours (60°C), 16 hours (70°C) at pH 9.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- Pacified Reactive Black 31 is hydrolytically stable at pH 4, and hydrolytically unsable at pH 7 and 9, under the conditions of the test.
- Executive summary:
The determination of the hydrolysis as a function of pH was based on the EEC-Directive 92/69 EEC, Part C, Metjods for the determination of Ecotoxicity, C.7: "Abiotic degradation: Hydrolysis as a function of pH".
Pacified Reactive Black was determined to be hydrolytically stable at pH4, and hydrolytically unstable at pH 7 and 9, under the conditions of the test.
The half-life times were 3.3E+02 hours at 70°C, 1.1E+02 hours at 80°C at pH7 and 58 hours (60°C), 16 hours (70°C) at pH 9.
From these values the half-life times at 25°C were estimated: 1.2E+05 hours at pH 7 and 1.0E+04 hours at pH 9.
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