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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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with limited documentation / justification
- Justification for type of information:
- Data is from OECD QSAR toolbox version.3.3 and QMRF report has been attached.
- Qualifier:
- according to guideline
- Guideline:
- other: Predicted data
- Principles of method if other than guideline:
- Prediction is done using QSAR Toolbox version 3.3 with log kow as the primary discriptors.
- 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) - Analytical monitoring:
- not specified
- Vehicle:
- not specified
- Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 72 h
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 121.927 mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: not toxic
- Conclusions:
- Based on the prediction done using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the closest read across substances, the toxicity to aquatic algae was predicted 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid (CAS: 12239-15-5). EC50 growth rate was estimated to be 121.927 mg/l for Desmodesmus subspicatus for 72 hrs duration. It was concluded that 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid (CAS: 12239-15-5) was likely to be not toxic to aquatic algae.
- Executive summary:
Based on the prediction done using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the closest read across substances, the toxicity to aquatic algae was predicted 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid (CAS: 12239-15-5). EC50 growth rate was estimated to be 121.927 mg/l for Desmodesmus subspicatus for 72 hrs duration. It was concluded that 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid (CAS: 12239-15-5) was likely to be not toxic to aquatic algae.
Reference
The
prediction was based on dataset comprised from the following
descriptors: EC50
Estimation method: Takes average value from the 5 nearest neighbours
Domain logical expression:Result: In Domain
((((((("a"
or "b" or "c" )
and "d" )
and "e" )
and ("f"
and (
not "g")
)
)
and "h" )
and ("i"
and (
not "j")
)
)
and ("k"
and "l" )
)
Domain
logical expression index: "a"
Referential
boundary: The
target chemical should be classified as Acid moiety OR Anilines
(Unhindered) OR Pyrazoles/Pyrroles by Aquatic toxicity classification by
ECOSAR ONLY
Domain
logical expression index: "b"
Referential
boundary: The
target chemical should be classified as SNAr OR SNAr >> Nucleophilic
aromatic substitution OR SNAr >> Nucleophilic aromatic substitution >>
Activated halo-benzenes by Protein binding by OECD ONLY
Domain
logical expression index: "c"
Referential
boundary: The
target chemical should be classified as SN1 OR SN1 >> Nitrenium Ion
formation OR SN1 >> Nitrenium Ion formation >> Primary (unsaturated)
heterocyclic amine OR SN1 >> Nitrenium Ion formation >> Unsaturated
heterocyclic azo by DNA binding by OECD ONLY
Domain
logical expression index: "d"
Referential
boundary: The
target chemical should be classified as Class 3 (unspecific reactivity)
by Acute aquatic toxicity classification by Verhaar (Modified) ONLY
Domain
logical expression index: "e"
Referential
boundary: The
target chemical should be classified as Acid moiety AND Anilines
(Unhindered) AND Pyrazoles/Pyrroles by Aquatic toxicity classification
by ECOSAR ONLY
Domain
logical expression index: "f"
Referential
boundary: The
target chemical should be classified as Halogens AND Non-Metals by
Groups of elements
Domain
logical expression index: "g"
Referential
boundary: The
target chemical should be classified as Transition Metals by Groups of
elements
Domain
logical expression index: "h"
Referential
boundary: The
target chemical should be classified as Bioavailable by Lipinski Rule
Oasis ONLY
Domain
logical expression index: "i"
Referential
boundary: The
target chemical should be classified as Aliphatic Amine, primary AND
Aryl AND Aryl halide AND Azo AND Overlapping groups AND Pyrazole AND
Sulfonic acid by Organic Functional groups (nested)
Domain
logical expression index: "j"
Referential
boundary: The
target chemical should be classified as Nitrobenzene by Organic
Functional groups (nested)
Domain
logical expression index: "k"
Parametric
boundary:The
target chemical should have a value of log Kow which is >= -2.08
Domain
logical expression index: "l"
Parametric
boundary:The
target chemical should have a value of log Kow which is <= 2.04
Description of key information
Based on the prediction done using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the closest read across substances, the toxicity to aquatic algae was predicted 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid (CAS: 12239-15-5). EC50 growth rate was estimated to be 121.927 mg/l for Desmodesmus subspicatus for 72 hrs duration. It was concluded that 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid (CAS: 12239-15-5) was likely to be not toxic to aquatic algae.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 121.927 mg/L
Additional information
Following studies of target chemical and structurally similar read across includes predicted data and experimental data to conclude the toxicity extent of 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid (CAS: 12239-15-5) towards aquatic algae is summarized as follows:
Based on the prediction done using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the closest read across substances, the toxicity to aquatic algae was predicted 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid (CAS: 12239-15-5). EC50 growth rate was estimated to be 121.927 mg/l for Desmodesmus subspicatus for 72 hrs duration. It was concluded that 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid (CAS: 12239-15-5) was likely to be not toxic to aquatic algae.
The above predicted data of target chemical is supported by the experimental study of structurally similar read across Ammonium 3-amino-2,5-dichlorobenzoate (CAS: 1076-46-6) from the publication Hyacinth control journal 1972, suggests that the Toxicity to aquatic algae and cyanobacteria test was carried out to study the effects of Ammonium 3-amino-2,5-dichlorobenzoate on aquatic algae. Decreasing trend ofPopulation growth rate was measured during the test.
Effective concentration to 50% of Dunaliella tertiolecta when exposed to Ammonium 3-amino-2,5-dichlorobenzoate for 10 days is 4000 mg/L. It can be concluded from the value that the Ammonium 3-amino-2,5-dichlorobenzoate (CAS: 1076-46-6) is not toxic to the aquatic algaecan be considered as “not classified” as per the classification criteria for aquatic environment.
Another supporting experimental study for the structurally similar read across 4 -aminobenzenesulfonic acid (CAS no. 121 -57 -3) from the High Production Volume (HPV) Challenge Program 2016, also suggests that the Short term toxicity to Scenedesmus subspicatus(green algae) study was carried out for 72 hrs. The study was performed according to other guideline DIN 38412 Part 9, 1992. The study was based on the effects of the test compound 4 -aminobenzenesulfonic acid (CAS no. 121 -57 -3) onScenedesmus subspicatus(green algae) in a static fresh water system. Scenedesmus subspicatuswas used as a test organism. Based on effect on growth rate of the test organismScenedesmus subspicatus(green algae), the 72 hr EC10 and EC50 value was determined to be 2.7 and 375 mg/l, respectively. Thus, based on the EC50 value, it can be concluded that the substance 4 -aminobenzenesulfonic acid can be considered as non-toxic to aquatic organisms and thus cannot be classified as hazardous as per the CLP classification criteria.
Thus based on the effect concentrations which is in the range 121.927 mg/l to 4000 mg/l give the conclusion that test substance 4-[(5-amino-3-methyl-1-phenyl-1H-pyrazol-4-yl)azo]-2,5-dichlorobenzenesulphonic acid (CAS: 12239-15-5) was likely to be not toxic to aquatic algae at environmentally relevant concentrations and can be considered to be “not classified” as per the CLP classification criteria.
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