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EC number: 278-189-6 | CAS number: 75314-27-1
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- 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 predicted using OECD QSAR toolbox version 3.3 and QMRF report has been attached
- Qualifier:
- according to guideline
- Guideline:
- other: estimated data
- Principles of method if other than guideline:
- Prediction was done by using OECD QSAR toolbox v3.3,
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- - Name of test material: Disodium [6-amino-5-[(2-hydroxy-4-nitrophenyl)azo]-N-methylnaphthalene-2-sulphonamidato(2-)] [6-amino-5- [(2-hydroxy-4-nitrophenyl) azo]naphthalene-2-sulphonato(3-)]cobaltate(2-)
- IUPAC name: Disodium [6-amino-5-[(2-hydroxy-4-nitrophenyl)azo]-N-methylnaphthalene-2-sulphonamidato(2-)][6-amino-5-[(2-hydroxy-4-nitrophenyl) azo]naphthalene-2-sulphonato(3-)]cobaltate(2-)
- Molecular formula: C33H22CoN9O11S2. 2 Na
- Molecular weight: 890 g/mole
- Smiles :Cc1cc(N(=O)=O)c2c(c1)N=N1c3c4ccc(S(O)(=O)=O)cc4ccc3N[Co]{2+}113(Nc4ccc5cc(S(=O)(=O)N C)ccc5c4N1=Nc1ccc(N(=O)=O) cc1O{-}.3).O{-}2Na
- Substance type: Organic
- Physical state: Solid - Analytical monitoring:
- not specified
- Vehicle:
- not specified
- Test organisms (species):
- Daphnia magna
- Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 48 h
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 15.149 mg/L
- Nominal / measured:
- not specified
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The EC50 was estimated to be 15.14 mg/l when Daphnia magna was exposed with Disodium [6-amino-5-[(2-hydroxy-4-nitrophenyl)azo]-N-methylnaphthalene-2-sulphonamidato(2-)] [6-amino-5- [(2-hydroxy-4-nitrophenyl) azo]naphthalene-2-sulphonato(3-)]cobaltate(2-)
- Executive summary:
In a prediction done by SSS (2018) using the OECD QSAR toolbox with log kow as the primary descriptor, the short term aquatic toxicity to invertebrates was estimated for Disodium [6-amino-5-[(2-hydroxy-4-nitrophenyl)azo]-N-methylnaphthalene-2-sulphonamidato(2-)] [6-amino-5- [(2-hydroxy-4-nitrophenyl) azo]naphthalene-2-sulphonato(3-)]cobaltate(2-). The EC50 was estimated to be 15.14 mg/l when Daphnia magna was exposed with Disodium [6-amino-5-[(2-hydroxy-4-nitrophenyl)azo]-N-methylnaphthalene-2-sulphonamidato(2-)] [6-amino-5- [(2-hydroxy-4-nitrophenyl) azo]naphthalene-2-sulphonato(3-)]cobaltate(2-).
On the basis of the effect concentration the test chemical is considered toxic and can be classified in the category "Aquatic chronic 3" as per CLP classification.
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" )
and ("c"
and (
not "d")
)
)
and "e" )
and ("f"
and (
not "g")
)
)
and ("h"
and (
not "i")
)
)
and ("j"
and "k" )
)
Domain
logical expression index: "a"
Referential
boundary: The
target chemical should be classified as Radical OR Radical >> Radical
mechanism via ROS formation (indirect) OR Radical >> Radical mechanism
via ROS formation (indirect) >> Diazenes OR Radical >> Radical mechanism
via ROS formation (indirect) >> Nitro Azoarenes OR SN1 OR SN1 >>
Nucleophilic attack after reduction and nitrenium ion formation OR SN1
>> Nucleophilic attack after reduction and nitrenium ion formation >>
Nitro Azoarenes by DNA binding by OASIS v.1.3 ONLY
Domain
logical expression index: "b"
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 >> Aromatic nitro by DNA binding by OECD ONLY
Domain
logical expression index: "c"
Referential
boundary: The
target chemical should be classified as Non binder, MW>500 by Estrogen
Receptor Binding
Domain
logical expression index: "d"
Referential
boundary: The
target chemical should be classified as Non binder, impaired OH or NH2
group OR Non binder, without OH or NH2 group OR Strong binder, OH group
OR Very strong binder, OH group by Estrogen Receptor Binding
Domain
logical expression index: "e"
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: "f"
Referential
boundary: The
target chemical should be classified as Not classified by Aquatic
toxicity classification by ECOSAR
Domain
logical expression index: "g"
Referential
boundary: The
target chemical should be classified as Acrylamides OR Amides by Aquatic
toxicity classification by ECOSAR
Domain
logical expression index: "h"
Referential
boundary: The
target chemical should be classified as Not classified by Aquatic
toxicity classification by ECOSAR
Domain
logical expression index: "i"
Referential
boundary: The
target chemical should be classified as Imides OR Not Related to an
Existing ECOSAR Class by Aquatic toxicity classification by ECOSAR
Domain
logical expression index: "j"
Parametric
boundary:The
target chemical should have a value of Molecular weight which is >= 839
Da
Domain
logical expression index: "k"
Parametric
boundary:The
target chemical should have a value of Molecular weight which is <= 913
Da
Description of key information
Short-term toxicity to aquatic invertebrates:
In a prediction done by SSS (2018) using the OECD QSAR toolbox with log kow as the primary descriptor, the short term aquatic toxicity to invertebrates was estimated forDisodium [6-amino-5-[(2-hydroxy-4-nitrophenyl)azo]-N-methylnaphthalene-2-sulphonamidato(2-)] [6-amino-5- [(2-hydroxy-4-nitrophenyl) azo]naphthalene-2-sulphonato(3-)]cobaltate(2-). The EC50 was estimated to be 15.14 mg/l when Daphnia magna was exposed withDisodium [6-amino-5-[(2-hydroxy-4-nitrophenyl)azo]-N-methylnaphthalene-2-sulphonamidato(2-)] [6-amino-5- [(2-hydroxy-4-nitrophenyl) azo]naphthalene-2-sulphonato(3-)]cobaltate(2-).
On the basis of the effect concentration the test chemical is considered toxic and can be classified in the category "Aquatic chronic 3" as per CLP classification.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 15.14 mg/L
Additional information
Short-term toxicity to aquatic invertebrates:
In a prediction done by SSS (2018) using the OECD QSAR toolbox with log kow as the primary descriptor, the short term aquatic toxicity to invertebrates was estimated forDisodium [6-amino-5-[(2-hydroxy-4-nitrophenyl)azo]-N-methylnaphthalene-2-sulphonamidato(2-)] [6-amino-5- [(2-hydroxy-4-nitrophenyl) azo]naphthalene-2-sulphonato(3-)]cobaltate(2-). The EC50 was estimated to be 15.14 mg/l when Daphnia magna was exposed withDisodium [6-amino-5-[(2-hydroxy-4-nitrophenyl)azo]-N-methylnaphthalene-2-sulphonamidato(2-)] [6-amino-5- [(2-hydroxy-4-nitrophenyl) azo]naphthalene-2-sulphonato(3-)]cobaltate(2-).
On the basis of the effect concentration the test chemical is considered toxic and can be classified in the category "Aquatic chronic 3" as per CLP classification.
The above prediction for target was suppported by experimental result for structurally similar read across substance sodium 4-[(2-hydroxy-1-naphthyl) diazenyl]benzenesulfonate (CAS: 633 -96 -5) summarized in Journal of Hazardous Materials, Vol. 276, Pg. no. 332–338, 2014.
Short term toxicity study toDaphnia similiswas carried out for 48 hrs. Neonates of less than 24 h old isolated from Daphnia culture were used for the study. Five test organisms were placed in each screw cap tubes, filled with 10 mL solution, and then incubated at 21±0.3°C in the dark. After 48 h of exposure, the number of immobile organisms was recorded. Jspear software was used to calculate the median 50% immobilization concentration (EC50). Based on immobilization of test organism by test chemical Acid Orange 7, the EC50 value was determine to be 87 mg/l along with confidence interval (p – 0.05) of 76-99 mg/l.
The above experiental data for read across substance was further supported by another experimental study for structurally similar read across substance Disodium 8-(phenylamino)-5-[[4-[(5 sulphonatonaphthyl) azo]naphthyl] azo]naphthalene sulphonate (CAS: 3071 -73 -6).
Disodium 8-(phenylamino)-5-[[4-[(5 sulphonatonaphthyl) azo]naphthyl] azo]naphthalene sulphonate was used to evaluate short term toxicity on 24 h old neonates Daphnia magna as per OECD guideline 202. Untreated ISO formulation freshwater and potassium dichromate (0.32 – 3.2 mg/L) were used as negative and positive controls respectively. The effect concentration (LC50) with Daphnia magna at 48 h was observed to be 58.22 mg/l
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