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EC number: 235-473-4 | CAS number: 12239-15-5
- 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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Data is from peer reviewed journal
- Justification for type of information:
- Data is from peer reviwed journal
- Qualifier:
- according to guideline
- Guideline:
- other: refer principle below
- Principles of method if other than guideline:
- Biodegradability of test chemical 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid was determined by analyzing percent recovery of test chemical from primary effluent.
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- - Name of test material: 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid / Acid Yellow 49
- IUPAC name: 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid
- Molecular formula: C16H13Cl2N5O3S
- Molecular weight: 426.283 g/mole
- Smiles :n1(c2ccccc2)c(c(\N=N\c2c(cc(S(O)(=O)=O)c(c2)Cl)Cl)c(n1)C)N
- Inchl: 1S/C16H13Cl2N5O3S/c1-9-15(16(19)23(22-9)10-5-3-2-4-6-10)21-20-13-7-12(18)14(8-11(13)17)27(24,25)26/h2-8H,19H2,1H3,(H,24,25,26)/b21-20+
- Substance type: Organic
- Physical state: Solid powder (yellow) - Oxygen conditions:
- not specified
- Inoculum or test system:
- activated sludge (adaptation not specified)
- Details on inoculum:
- Screened raw waste water from greater Cincinnati Mill Creek sewage treatment plant was used as influent (INF).
- Initial conc.:
- 1 mg/L
- Based on:
- test mat.
- Initial conc.:
- 5 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- test mat. analysis
- Remarks:
- By HPLC
- Details on study design:
- Test System:
Screened raw waste water from greater Cincinnati Mill Creek sewage treatment plant was used as influent (INF) to three pilot scale activated sludge biological treatment systems (Two experimental and one control). Each system consists of primary clarifier complete mix aeration basin and secondary clarifier.
Dye analytical studies were conducted by purified dye compound in organic free influent waste water and mixed liquor. Then influent, primary influent filtrate was passed through column packed with resin. The filter paper and resin were soaked in an ammonia – acetonitrile solution and then soxhlet extracted with ammonia – acetonitrile. The extract was concentrated and brought upto 50 ml volumn with methanol/dimethyl formamaide solution. All extracted samples were analyzed by HPLC with ultraviolet detector.
Sampling: All samples spiked with test compound held at 4 oC for 24 hrs before recovery was accessed. - Parameter:
- % degradation (test mat. analysis)
- Remarks:
- By HPLC
- Value:
- 25
- Remarks on result:
- other: % recovery was 75
- Parameter:
- % degradation (test mat. analysis)
- Remarks:
- By HPLC
- Value:
- 32
- Remarks on result:
- other: % recovery was 68
- Details on results:
- Percent biodegradation of test chemical 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid was observed to be 25 and 32 % by test material analysis by HPLC parameter.
- Validity criteria fulfilled:
- not specified
- Interpretation of results:
- inherently biodegradable
- Conclusions:
- Percent biodegradation of test chemical 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid was observed to be 25 % and 32 % by test material analysis by HPLC parameter. On the basis of percent degradation it is concluded that this test material is inherently biodegradable.
- Executive summary:
Biodegradability of test chemical 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid (Acid yellow 49) was determined by analyzing percent recovery of test material. This test material is dye and inoculums used for biodegradation was obtained from Screened raw waste water from greater Cincinnati Mill Creek sewage treatment plant was used as influent (INF) to three pilot scale activated sludge biological treatment systems (Two experimental and one control). Each system consists of primary clarifier, complete mix aeration basin and secondary clarifier. Influent was spiked with test material at concentration of1 mg/L and 5 mg/L. Then Dye analytical studies were conducted by purified dye compound in organic free influent waste water and mixed liquor. Then influent, primary influent filtrate was passed through column packed with resin. The filter paper and resin were soaked in an ammonia – acetonitrile solution and then soxhlet extracted with ammonia – acetonitrile. The extract was concentrated and brought upto 50 ml volume with methanol/dimethyl formamaide solution. All extracted samples were analyzed by HPLC with ultraviolet detector.
Percent recovery from mass balance data determined was 75 % in low spiked and 68 % in high spiked. On the basis of percent recovery value biodegradation of 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid was 25% and 32 %by test material analysis by HPLC parameter. On the basis of percent degradation it is concluded that this test material is inherently biodegradable.
Reference
Table 1. Percent recovery of test dyes from sample matrices.
Dye compound name |
Sample matrix |
|||||
4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid (Acid yellow 49) |
Organic free water |
Waste water |
Mixed liquor |
|||
1 mg/L |
5 mg/L |
1 mg/L |
5 mg/L |
1 mg/L |
5 mg/L |
|
90 |
93 |
99 |
100 |
99 |
99 |
Table 2 Dye concentration data summary
Dye compound name |
Low spike |
High spike |
||||||||
4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid (Acid yellow 49) |
INF |
PE |
ASE |
SOL |
RES |
INF |
PE |
ASE |
SOl |
RES |
1.14 |
1.14 |
0.84 |
0.86 |
0.14 |
5.17 |
5.42 |
3.59 |
3.79 |
0.44
|
INF- Influent
PE- Primary effluent
ASE- Activated sludge effluent
SOL- soluble Fraction
RES- Residue Fraction
Table 3. Mass Balance Data Summary
Dye Compound Name |
Low Spike |
High Spike
|
||
4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid (Acid yellow 49) |
% Recovered |
% Adsorbed |
% Recovered |
%Adsorbed
|
75 |
1 |
68 |
1 |
Description of key information
Percent biodegradation of test chemical 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid was observed to be 25 % and 32 % by test material analysis by HPLC parameter. On the basis of percent degradation it is concluded that this test material is inherently biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- inherently biodegradable
Additional information
Biodegradability of test chemical 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid (Acid yellow 49) was determined by analyzing percent recovery of test material. This test material is dye and inoculums used for biodegradation was obtained from Screened raw waste water from greater Cincinnati Mill Creek sewage treatment plant was used as influent (INF) to three pilot scale activated sludge biological treatment systems (Two experimental and one control). Each system consists of primary clarifier, complete mix aeration basin and secondary clarifier. Influent was spiked with test material at concentration of1 mg/L and 5 mg/L. Then Dye analytical studies were conducted by purified dye compound in organic free influent waste water and mixed liquor. Then influent, primary influent filtrate was passed through column packed with resin. The filter paper and resin were soaked in an ammonia – acetonitrile solution and then soxhlet extracted with ammonia – acetonitrile. The extract was concentrated and brought upto 50 ml volume with methanol/dimethyl formamaide solution. All extracted samples were analyzed by HPLC with ultraviolet detector.
Percent recovery from mass balance data determined was 75 % in low spiked and 68 % in high spiked. On the basis of percent recovery value biodegradation of 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid was 25% and 32 %by test material analysis by HPLC parameter. On the basis of percent degradation it is concluded that this test material is inherently biodegradable.
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