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EC number: 233-418-9 | CAS number: 10149-98-1
- 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:
- QMRF report has been attached
- Qualifier:
- according to guideline
- Guideline:
- other: Estimated data
- Principles of method if other than guideline:
- Prediction was done using the OECD QSAR toolbox version 3.3.
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- - Name of test material : 4,5-dihydro-5-oxo-4-[[4-[[2-(sulphooxy)ethyl]sulphonyl]phenyl]azo]-1-(4-sulphophenyl)-1H-pyrazole-3-carboxylic acid
- Molecular formula : C18H16N4O12S3
- Molecular weight : 576.538 g/mol
- Smiles notation : O=C(O)C1=NN(C(=O)[C@@H]1\N=N\c1ccc(S(=O)(=O)CCOS(=O)(=O)O)cc1)c1ccc(S(=O)(=O)O)cc1
- InChl : 1S/C18H16N4O12S3/c23-17-15(16(18(24)25)21-22(17)12-3-7-14(8-4-12)36(28,29)30)20-19-11-1-5-13(6-2-11)35(26,27)10-9-34-37(31,32)33/h1-8,15H,9-10H2,(H,24,25)(H,28,29,30)(H,31,32,33)/b20-19+
- Substance type: Organic
- Physical state: - Analytical monitoring:
- not specified
- Vehicle:
- not specified
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 72 h
- Hardness:
- 32.1mg/L as Ca CO3
- Test temperature:
- 24.8°C and 28°C
- pH:
- 6.95 and 11.14
- Nominal and measured concentrations:
- Estimated data
- Reference substance (positive control):
- not specified
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 24.269 mg/L
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- The EC50 was 24.268 mg/l
- Validity criteria fulfilled:
- not specified
- Conclusions:
- Based on the growth rate inhibition of green algae due to the chemical 4,5-dihydro-5-oxo-4-[[4-[[2-(sulphooxy)ethyl]sulphonyl]phenyl]azo]-1-(4-sulphophenyl)-1H-pyrazole-3-carboxylic acid, the EC50 was 24.268 mg/l
- 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 five closest read across substances, toxicity on Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) was predicted for 4,5-dihydro-5-oxo-4-[[4-[[2-(sulphooxy)ethyl]sulphonyl]phenyl] azo]-1-(4-sulphophenyl)-1H-pyrazole-3-carboxylic acid (10149-98-1). Based on the growth rate inhibition of algae, the EC50 value was estimated to be 24.268 mg/l when 4,5-dihydro-5-oxo-4- [[4-[[2-(sulphooxy)ethyl]sulphonyl]phenyl]azo]-1-(4-sulphophenyl)-1H-pyrazole-3-carboxylic acid exposed toPseudokirchneriella subcapitatafor 72hrs. Based on this value it can be concluded that the substance 4,5-dihydro-5-oxo-4-[[4-[[2-(sulphooxy) ethyl]sulphonyl]phenyl]azo]-1-(4-sulphophenyl)-1H-pyrazole-3-carboxylic acid is considered to be toxic to aquatic environment and can be classified as aquatic chronic 3 category per the criteria mentioned in CLP regulation.
Reference
The
prediction was based on dataset comprised from the following
descriptors: EC50
Estimation method: Takes average value from the 6 nearest neighbours
Domain logical expression:Result: In Domain
(((((("a"
or "b" or "c" or "d" or "e" )
and ("f"
and (
not "g")
)
)
and "h" )
and "i" )
and "j" )
and ("k"
and "l" )
)
Domain
logical expression index: "a"
Referential
boundary: The
target chemical should be classified as Vinyl Sulfones by US-EPA New
Chemical Categories
Domain
logical expression index: "b"
Referential
boundary: The
target chemical should be classified as Acid moiety OR Amides OR
Hydrazines by Aquatic toxicity classification by ECOSAR ONLY
Domain
logical expression index: "c"
Referential
boundary: The
target chemical should be classified as Acylation OR Acylation >> Direct
Acylation Involving a Leaving group OR Acylation >> Direct Acylation
Involving a Leaving group >> Acetates OR SN2 OR SN2 >> SN2 reaction at
sp3 carbon atom OR SN2 >> SN2 reaction at sp3 carbon atom >> Alkyl diazo
by Protein binding by OECD ONLY
Domain
logical expression index: "d"
Referential
boundary: The
target chemical should be classified as Schiff base formation OR Schiff
base formation >> Pyrazolones and Pyrazolidinones derivatives OR Schiff
base formation >> Pyrazolones and Pyrazolidinones derivatives >>
Pyrazolones and Pyrazolidinones by Protein binding by OASIS v1.3 ONLY
Domain
logical expression index: "e"
Referential
boundary: The
target chemical should be classified as SN1 OR SN1 >> Nitrenium Ion
formation OR SN1 >> Nitrenium Ion formation >> Aromatic azo OR SN1 >>
Nitrenium Ion formation >> Unsaturated heterocyclic azo by DNA binding
by OECD ONLY
Domain
logical expression index: "f"
Referential
boundary: The
target chemical should be classified as Not possible to classify
according to these rules (GSH) by Protein binding potency
Domain
logical expression index: "g"
Referential
boundary: The
target chemical should be classified as Moderately reactive (GSH) OR
Moderately reactive (GSH) >> Substituted 1-Alken-3-ones (MA) by Protein
binding potency
Domain
logical expression index: "h"
Referential
boundary: The
target chemical should be classified as Class 5 (Not possible to
classify according to these rules) by Acute aquatic toxicity
classification by Verhaar (Modified) ONLY
Domain
logical expression index: "i"
Referential
boundary: The
target chemical should be classified as Reactive unspecified by Acute
aquatic toxicity MOA by OASIS ONLY
Domain
logical expression index: "j"
Referential
boundary: The
target chemical should be classified as Acid moiety AND Amides AND
Hydrazines by Aquatic toxicity classification by ECOSAR ONLY
Domain
logical expression index: "k"
Parametric
boundary:The
target chemical should have a value of log Kow which is >= -5.49
Domain
logical expression index: "l"
Parametric
boundary:The
target chemical should have a value of log Kow which is <= 0.446
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 five closest read across substances, toxicity on Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) was predicted for 4,5-dihydro-5-oxo-4- [[4-[[2-(sulphooxy)ethyl] sulphonyl] phenyl] azo]-1-(4-sulphophenyl)-1H-pyrazole-3-carboxylic acid (10149-98-1). Based on the growth rate inhibition of algae, the EC50 value was estimated to be 24.268 mg/l when 4,5-dihydro-5-oxo-4- [[4-[[2-(sulphooxy)ethyl]sulphonyl]phenyl]azo]-1-(4-sulphophenyl)-1H-pyrazole-3-carboxylic acid exposed to Pseudokirchneriella subcapitata for 72hrs. Based on this value it can be concluded that the substance 4,5-dihydro-5-oxo-4-[[4-[[2-(sulphooxy) ethyl]sulphonyl]phenyl]azo]- 1-(4-sulphophenyl)-1H-pyrazole-3-carboxylic acid is considered to be toxic to aquatic environment and can be classified as aquatic chronic 3 category per the criteria mentioned in CLP regulation.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 24.26 mg/L
Additional information
Various predicted data for the target compound 4,5-dihydro-5-oxo-4-[[4-[[2-(sulphooxy)ethyl]sulphonyl] phenyl]azo]-1-(4-sulphophenyl)-1H-pyrazole-3-carboxylic acid (10149-98-1) and experimental data for supporting weight of evidence studies for its closest read across substance with log Kow as the primary descriptor and on the basis of structural and functional similarity study were reviewed for the toxicity on the aquatic algae end point which are summarized as below:
In a prediction done by SSS (2017), based on the prediction done using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the five closest read across substances, toxicity on Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum) was predicted for 4,5-dihydro-5-oxo-4- [[4-[[2-(sulphooxy)ethyl]sulphonyl]phenyl] azo]-1-(4-sulphophenyl)-1H-pyrazole-3-carboxylic acid (10149-98-1). Based on the growth rate inhibition of algae, the EC50 value was estimated to be 24.268 mg/l when 4,5-dihydro-5-oxo-4- [[4-[[2-(sulphooxy)ethyl]sulphonyl]phenyl]azo]-1-(4-sulphophenyl)-1H-pyrazole-3-carboxylic acid exposed to Pseudokirchneriella subcapitata for 72hrs. Based on this value it can be concluded that the substance 4,5-dihydro-5-oxo-4-[[4-[[2-(sulphooxy) ethyl]sulphonyl]phenyl]azo]- 1-(4-sulphophenyl)-1H-pyrazole-3-carboxylic acid is considered to be toxic to aquatic environment and can be classified as aquatic chronic 3 category per the criteria mentioned in CLP regulation.
First predicted study was supported by the structurally similar read across chemical (12225-21-7) from ABITEC report. Freshwater algal growth inhibition test was carried out on Desmodesmus subspicatus with the substance aluminum tris(4-{[3-carboxy-5-oxo-1-(4-sulfophenyl)-4,5-dihydro -1H-pyrazol-4-yl]diazenyl}benzenesulfonate). Test was performed according to OECD Guideline 201. The stock solution 130 mg/l was prepared by dissolving dark yellow powder in OECD growth medium. The test solution was kept for 30 min in ultrasonic bath. Test solutions of required concentration were prepared by mixing the stock solution of the test sample with OECD growth medium and inoculum culture. Tested conducted at the concentrations 0, 2.6, 5.6, 12, 27, 59, 130 mg/l. Effects on the growth rate of the organism were studied. The median effective concentration (ErC50) for the test substance, aluminum tris(4-{[3-carboxy-5-oxo-1-(4-sulfophenyl)-4,5-dihydro -1H-pyrazol-4-yl]diazenyl} benzenesulfonate), in Desmodesmus subspicatus was determined to be 74.2 mg/L on the basis of growth rate inhibition. This value indicates that the substance is likely to be hazardous to aquatic algae and can be classified as aquatic chronic 3 category as per the CLP criteria.
Similarly by considering another functional similar RA chemical N,N,N-trimethyl-3-[(3-methyl-5-oxo-1-phenyl-4,5-dihydro-1H-pyrazol-4-yl)diazenyl]anilinium chloride (Basic yellow 57) (68391-31-1) from ABITEC report 2016 toxicity was measured. Freshwater algal growth inhibition test was carried out on Desmodesmus subspicatus with the substance N,N,N-trimethyl-3-[(3-methyl-5-oxo-1-phenyl-4,5-dihydro-1H- pyrazol-4-yl) diazenyl]anilinium chloride (Basic yellow 57) according to OECD Guideline 201. The test substance was dissolved in OECD growth medium and tested at the concentrations 0, 10, 17, 29, 50 and 85 mg/L. Effects on the growth rate of the organism were studied. The median effective concentration (ErC50) for the test substance, N,N,N-trimethyl-3-[(3-methyl-5-oxo-1-phenyl-4,5-dihydro-1H-pyrazol-4-yl)diazenyl]anilinium chloride (Basic yellow 57), in Desmodesmus subspicatus was determined to be 67.9 mg/L and also the substance was not rapidly degradable. Thus considering the CLP criteria for aquatic classification of the substance, it is concluded that N,N,N-trimethyl-3-[(3-methyl-5-oxo-1-phenyl-4,5-dihydro-1H- pyrazol-4-yl)diazenyl] anilinium chloride (Basic yellow 57) exhibits toxicity to aquatic algae (Desmodesmus subspicatus) in the chronic 3 classification category.
In the fourth weight of evidence study from ABITEC report for the read across chemical (2519-30-4) it can be consider that the chemical was toxic to aquatic algae. Freshwater algal growth inhibition test was carried out on Desmodesmus subspicatus with the substance tetrasodium 1-acetamido-2-hydroxy-3-(4-((4-sulphonatophenylazo) -7- sulphonato-1 -naphthylazo))naphthalene-4,6-disulphonate. Test was performed according to OECD Guideline 201. The stock solution 100 mg/l was prepared by dissolving black powder in OECD growth medium. Test solutions of required concentration were prepared by mixing the stock solution of the test sample with OECD growth medium and inoculum culture. Tested conducted at the nominal concentrations 0, 12, 20, 35, 60, 100 mg/l. Effects on the growth rate of the organism were studied. The median effective concentration (ErC50) for the test substance, tetrasodium 1-acetamido-2-hydroxy-3-(4-((4-sulphonatophenylazo) -7-sulphonato-1-naphthylazo)) naphthalene- 4,6-disulphonate (2519-30-4) in Desmodesmus subspicatus was determined to be 74.2 mg/L on the basis of growth rate inhibition. This value indicates that the substance is likely to be hazardous to aquatic algae and can be classified as aquatic chronic 3 category as per the CLP classification criteria.
On the basis of above results for target chemical 4,5-dihydro-5-oxo-4-[[4-[[2-(sulphooxy)ethyl]sulphonyl] phenyl]azo]-1-(4-sulphophenyl)-1H-pyrazole-3-carboxylic acid (10149-98-1) (from OECD QSAR toolbox version 3.3) and for its read across substance from ABITEC reports 2016, it can be concluded that the test substance chemical 4,5-dihydro-5-oxo-4-[[4-[[2- (sulphooxy)ethyl] sulphonyl] phenyl]azo]-1-(4-sulphophenyl)-1H-pyrazole-3-carboxylic acid is toxic to aquatic environment and can classified as aquatic chronic 3 category per the criteria mentioned in CLP regulation.
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