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EC number: 278-093-4 | CAS number: 75173-68-1
- 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: As mention below
- Principles of method if other than guideline:
- Prediction is done using QSAR Toolbox version 3.3
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- - Name of test material : [μ-[[3,3'-[azoxybis[(2-hydroxy-p-phenylene)azo]]bis[4-hydroxynaphthalene-2,7-disulphonato]](8-)]]dicopper, tetrasodium salt
- Molecular weight : 1101.8036 g/mol
- Smiles notation : [Na+].[Na+].[Na+].[Na+].O=N(=Nc1ccc2N=Nc3c4O[Cu-2]5(Oc2c1)OS(=O)(=O)c6ccc4c(c6)cc3S(=O)(=O)O5)c7ccc8N=Nc9c%10O[Cu-2]%11(Oc8c7)OS(=O)(=O)c%12ccc%10c(c%12)cc9S(=O)(=O)O%11
- InChl : 1S/C32H22N6O17S4.2Cu.4Na/c39-25-13-17(1-7-23(25)33-35-29-27(58(50,51)52)11-15-9-19(56(44,45)46)3-5-21(15)31(29)41)37-38(43)18-2-8-24(26(40)14-18)34-36-30-28(59(53,54)55)12-16-10-20(57(47,48)49)4-6-22(16)32(30)42;;;;;;/h1-14,39-42H,(H,44,45,46)(H,47,48,49)(H,50,51,52)(H,53,54,55);;;;;;/q;2*+2;4*+1/p-8/b35-33+,36-34+,38-37+;;;;;;
- Substance type : Organic
- Physical state : Liquid - 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:
- 150-200 mg/mL
- Test temperature:
- 21°C
- pH:
- 7.1
- Nominal and measured concentrations:
- Estimated data
- Reference substance (positive control):
- not specified
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 38.69 mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- not specified
- Basis for effect:
- growth rate
- Remarks on result:
- other: Other details not known
- Validity criteria fulfilled:
- not specified
- Conclusions:
- Based on the growth rate inhibition of algae Pseudokirchneriella subcapitata by the chemical [μ-[[3,3'-[azoxybis[(2-hydroxy-p-phenylene)azo]]bis[4-hydroxynaphthalene-2,7-disulphonato]](8-)]] dicopper, tetrasodium salt, the EC50 was estimated to be 38.68 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 [μ-[[3,3'-[azoxybis[(2-hydroxy-p-phenylene)azo]]bis[4-hydroxynaphthalene-2,7-disulphonato]](8-)]] dicopper, tetrasodium salt (75173-68-1). Based on the growth rate inhibition of algae Pseudokirchneriella subcapitata by the chemical [μ-[[3,3'-[azoxybis[(2-hydroxy-p-phenylene)azo]]bis[4-hydroxynaphthalene-2,7-disulphonato]](8-)]] dicopper, tetrasodium salt, the EC50 was estimated to be 38.68 mg/l. Based on this value it can be concluded that the substance [μ-[[3,3'-[azoxybis[(2-hydroxy-p-phenylene)azo]]bis[4-hydroxynaphthalene-2,7-disulphonato]](8-)]] dicopper, tetrasodium salt (75173-68-1) is considered to be toxic to aquatic environment and can be classified as aquatic chronic 3 as 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 5 nearest neighbours
Domain logical expression:Result: In Domain
(((((((((((((((("a"
or "b" or "c" or "d" )
and "e" )
and "f" )
and ("g"
and (
not "h")
)
)
and ("i"
and (
not "j")
)
)
and ("k"
and (
not "l")
)
)
and ("m"
and (
not "n")
)
)
and ("o"
and (
not "p")
)
)
and ("q"
and (
not "r")
)
)
and ("s"
and (
not "t")
)
)
and ("u"
and (
not "v")
)
)
and ("w"
and (
not "x")
)
)
and ("y"
and (
not "z")
)
)
and ("aa"
and (
not "ab")
)
)
and ("ac"
and (
not "ad")
)
)
and ("ae"
and "af" )
)
Domain
logical expression index: "a"
Referential
boundary: The
target chemical should be classified as Anion OR Aromatic compound OR
Azo compound OR Cation OR Hydroxy compound OR Phenol OR Sulfonic acid
derivative by Organic functional groups, Norbert Haider (checkmol) ONLY
Domain
logical expression index: "b"
Referential
boundary: The
target chemical should be classified as Alcohol, olefinic attach [-OH]
OR Aliphatic Nitrogen, one aromatic attach [-N] OR Aromatic Carbon [C]
OR Azo [-N=N-] OR Hydroxy, aromatic attach [-OH] OR Miscellaneous
sulfide (=S) or oxide (=O) OR Olefinic carbon [=CH- or =C<] OR Oxygen,
one aromatic attach [-O-] OR Suflur {v+4} or {v+6} OR Sulfonate,
aromatic attach [-SO2-O] by Organic functional groups (US EPA) ONLY
Domain
logical expression index: "c"
Referential
boundary: The
target chemical should be classified as Aryl OR Azo OR Azoxy OR Fused
carbocyclic aromatic OR Overlapping groups OR Phenol OR Sulfonic acid by
Organic Functional groups (nested) ONLY
Domain
logical expression index: "d"
Referential
boundary: The
target chemical should be classified as Aryl OR Azo OR Azoxy OR Fused
carbocyclic aromatic OR Naphtalene OR Phenol OR Sulfonic acid by Organic
Functional groups ONLY
Domain
logical expression index: "e"
Referential
boundary: The
target chemical should be classified as Reactive unspecified by Acute
aquatic toxicity MOA by OASIS ONLY
Domain
logical expression index: "f"
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: "g"
Referential
boundary: The
target chemical should be classified as Acid moiety AND Phenols, Poly
AND Salt by Aquatic toxicity classification by ECOSAR
Domain
logical expression index: "h"
Referential
boundary: The
target chemical should be classified as Hydrazines by Aquatic toxicity
classification by ECOSAR
Domain
logical expression index: "i"
Referential
boundary: The
target chemical should be classified as Acid moiety AND Phenols, Poly
AND Salt by Aquatic toxicity classification by ECOSAR
Domain
logical expression index: "j"
Referential
boundary: The
target chemical should be classified as Inorganic Compound by Aquatic
toxicity classification by ECOSAR
Domain
logical expression index: "k"
Referential
boundary: The
target chemical should be classified as Acid moiety AND Phenols, Poly
AND Salt by Aquatic toxicity classification by ECOSAR
Domain
logical expression index: "l"
Referential
boundary: The
target chemical should be classified as Not Related to an Existing
ECOSAR Class by Aquatic toxicity classification by ECOSAR
Domain
logical expression index: "m"
Referential
boundary: The
target chemical should be classified as Alkali Earth AND Non-Metals by
Groups of elements
Domain
logical expression index: "n"
Referential
boundary: The
target chemical should be classified as Halogens by Groups of elements
Domain
logical expression index: "o"
Referential
boundary: The
target chemical should be classified as Group 1 - Alkali Earth
Li,Na,K,Rb,Cs,Fr AND Group 14 - Carbon C AND Group 15 - Nitrogen N AND
Group 16 - Oxygen O AND Group 16 - Sulfur S by Chemical elements
Domain
logical expression index: "p"
Referential
boundary: The
target chemical should be classified as Group 12 - Trans.Metals Zn,Cd,Hg
by Chemical elements
Domain
logical expression index: "q"
Referential
boundary: The
target chemical should be classified as Group 1 - Alkali Earth
Li,Na,K,Rb,Cs,Fr AND Group 14 - Carbon C AND Group 15 - Nitrogen N AND
Group 16 - Oxygen O AND Group 16 - Sulfur S by Chemical elements
Domain
logical expression index: "r"
Referential
boundary: The
target chemical should be classified as Group 2 - Alkaline Earth
Be,Mg,Ca,Sr,Ba,Ra by Chemical elements
Domain
logical expression index: "s"
Referential
boundary: The
target chemical should be classified as Group 1 - Alkali Earth
Li,Na,K,Rb,Cs,Fr AND Group 14 - Carbon C AND Group 15 - Nitrogen N AND
Group 16 - Oxygen O AND Group 16 - Sulfur S by Chemical elements
Domain
logical expression index: "t"
Referential
boundary: The
target chemical should be classified as Group 8 - Trans.Metals Fe,Ru,Os
OR Group 9 - Trans.Metals Co,Rh,Ir by Chemical elements
Domain
logical expression index: "u"
Referential
boundary: The
target chemical should be classified as Alkali Earth AND Non-Metals by
Groups of elements
Domain
logical expression index: "v"
Referential
boundary: The
target chemical should be classified as Metals by Groups of elements
Domain
logical expression index: "w"
Referential
boundary: The
target chemical should be classified as Aryl AND Azo AND Azoxy AND Fused
carbocyclic aromatic AND Naphtalene AND Phenol AND Sulfonic acid by
Organic Functional groups
Domain
logical expression index: "x"
Referential
boundary: The
target chemical should be classified as Alkene by Organic Functional
groups
Domain
logical expression index: "y"
Referential
boundary: The
target chemical should be classified as Aryl AND Azo AND Azoxy AND Fused
carbocyclic aromatic AND Naphtalene AND Phenol AND Sulfonic acid by
Organic Functional groups
Domain
logical expression index: "z"
Referential
boundary: The
target chemical should be classified as Unsaturated heterocyclic
fragment by Organic Functional groups
Domain
logical expression index: "aa"
Referential
boundary: The
target chemical should be classified as Aryl AND Azo AND Azoxy AND Fused
carbocyclic aromatic AND Naphtalene AND Phenol AND Sulfonic acid by
Organic Functional groups
Domain
logical expression index: "ab"
Referential
boundary: The
target chemical should be classified as Alkyl arenes by Organic
Functional groups
Domain
logical expression index: "ac"
Referential
boundary: The
target chemical should be classified as Anion AND Aromatic compound AND
Azo compound AND Cation AND Hydroxy compound AND Phenol AND Sulfonic
acid derivative by Organic functional groups, Norbert Haider (checkmol)
Domain
logical expression index: "ad"
Referential
boundary: The
target chemical should be classified as Carbonic acid derivative OR CO2
derivative (general) OR No functional group found by Organic functional
groups, Norbert Haider (checkmol)
Domain
logical expression index: "ae"
Parametric
boundary:The
target chemical should have a value of log Kow which is >= 0.0785
Domain
logical expression index: "af"
Parametric
boundary:The
target chemical should have a value of log Kow which is <= 1.6
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 [μ-[[3,3'-[azoxybis[(2-hydroxy-p-phenylene)azo]]bis[4-hydroxynaphthalene-2,7-disulphonato]](8-)]] dicopper, tetrasodium salt (75173-68-1). Based on the growth rate inhibition of algae Pseudokirchneriella subcapitata by the chemical [μ-[[3,3'-[azoxybis[(2-hydroxy-p-phenylene)azo]]bis[4-hydroxynaphthalene-2,7-disulphonato]](8-)]] dicopper, tetrasodium salt, the EC50 was estimated to be 38.68 mg/l. Based on this value it can be concluded that the substance [μ-[[3,3'-[azoxybis[(2-hydroxy-p-phenylene)azo]]bis[4-hydroxynaphthalene-2,7-disulphonato]](8-)]] dicopper, tetrasodium salt (75173-68-1) is considered to be toxic to aquatic environment and can be classified as aquatic chronic 3 as per the criteria mentioned in CLP regulation.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 38.68 mg/L
Additional information
Based on the various predicted data for the target chemical and experimental data for structurally and functionally similar read across chemicals study have been reviewed to determine the toxic nature of target chemical [μ-[[3,3'-[azoxybis[(2-hydroxy-p-phenylene)azo]]bis[4-hydroxynaphthalene-2,7-disulphonato]](8-)]]dicopper, tetrasodium salt (75173-68-1) on the growth of algae. The studies are as mentioned below:
The first predicted study for the target chemical (100-07-2) 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 [μ-[[3,3'-[azoxybis[(2-hydroxy-p-phenylene)azo]]bis[4-hydroxynaphthalene-2,7-disulphonato]](8-)]] dicopper, tetrasodium salt (75173-68-1). Based on the growth rate inhibition of algae Pseudokirchneriella subcapitata by the chemical [μ-[[3,3'-[azoxybis[(2-hydroxy-p-phenylene)azo]]bis[4-hydroxynaphthalene-2,7-disulphonato]](8-)]] dicopper, tetrasodium salt, the EC50 was estimated to be 38.68 mg/l. Based on this value it can be concluded that the substance [μ-[[3,3'-[azoxybis[(2-hydroxy-p-phenylene)azo]]bis[4-hydroxynaphthalene-2,7-disulphonato]](8-)]] dicopper, tetrasodium salt (75173-68-1) is considered to be toxic to aquatic environment and can be classified as aquatic chronic 3 as per the criteria mentioned in CLP regulation.
First predicted study was supported by the second experimental weight of evidence study for the read across chemical Brilliant black 1 (2159-30-4) from UERL lab report. Aim of this study was to assess the effect of test item tetrasodium 1-acetamido-2-hydroxy-3-(4-((4-sulphonatophenylazo)-7-sulphonato-1-naphthylazo))naphthalene-4,6-disulphonate, CAS No. 2519-30-4 on the growth of fresh water green alga Chlorella vulgaris. The study was conducted following OECD guideline 201- Alga, growth inhibition test. The chemical was analytically evaluated by using spectrophotometer, the absorbance values of each test vessel and control vessel was noted at 680nm.The BBM was taken as blank for both control and test vessels. The absorbance value of each vessel was in line with the average specific growth rate. The test solution was prepared in aseptic condition. The test item tetrasodium 1-acetamido-2-hydroxy-3-(4-((4-sulphonatophenyl azo)-7-sulphonato-1-naphthylazo))naphthalene-4,6-disulphonate was prepared by adding 21 mg of test item in 200ml of BBM to get the final concentration of 105 mg/L. This stock solution was kept for stirring for 30 minutes to obtain a homogenous solution for the experiment. The concentrations were chosen according to the available data of the test item. The remaining test solutions were prepared by dilution from the above stock solution. To have a better growth and visibility of cells, the initial cell density of the culture was kept 1 X 104cells/ml. Care was taken to have a homogeneous solution for the experiment. Test organism green alga Chlorella vulgaris were collected from National Environmental Engineering Research Institute (NEERI), Nagpur and cultivate in Bold’s Basal Medium (BBM). For the assessment of algal growth, the study was conducted in replicates. The control vessel was maintained in triplicates as recommended in the OECD guideline and the test concentrations were selected in geometric series which were maintained in duplicates. After the exposure of chemical effect were measured. To obtain a quantitative concentration-response relationship by regression analysis, a linearizing transformation of the response data into probit was performed. Using the same, effective concentration (EC) was determined. The microscopic observations were also noted in each of the test vessel. All the cells appeared healthy, round and green throughout the study duration in the control and in the test vessels cells appeared shrinked and black dotted rings observed in concentrations of 0.96mg/l, 3.072mg/l, 9.830mg/l, 31.457mg/l & 100.663mg/l. After 72 hours of exposure to test item tetrasodium 1-acetamido-2-hydroxy-3-(4-((4-sulphonatophenylazo)-7-sulphonato-1-naphthylazo))naphthalene-4,6-disulphonate (CAS No. 2519-30-4) to various nominal test concentrations, EC50 was determine to be 24.342 mg/l graphically and through probit analysis. Thus based on the EC50, chemical was concluded as toxic and can be consider to be classified as aquatic chronic 3 category as per the CLP classification criteria.
Similarly for another read across chemical (3567-69-9) from UERL lab study was conducted. The objective of the test was to determine the effects of Disodium 4-hydroxy-3-[(4-sulphonatonaphthyl)azo]naphthalene sulphonate CAS No. 3567-69-9 on the growth of freshwater microalgae Chlorella vulgaris. The algae were exposed to various concentrations of the test item under static conditions over a period of 72h. The growth rate relative to the control in a 72h test was taken as a parameter to observe the algal growth inhibition. Sample analytically motorized by spectrophotometer. The absorbance values of each test vessel and control vessel was noted at 680nm.TheBBM was taken as blank for both control and test vessels. The absorbance value of each vessel was in line with the average specific growth rate. The test solution was prepared in aseptic condition. The test item Disodium 4-hydroxy-3-[(4-sulphonatonaphthyl)azo] naphthalene sulphonate was prepared by adding 50 mg of test item in 250 ml of BBM to get the final concentration of 200mg/L. This stock solution was kept for stirring for 30 minutes to obtain a homogenous solution for the experiment. The test concentrations were chosen according to the available data of the test item. The remaining test solutions were prepared by dilution from the above stock solution. To have a better growth and visibility of cells, the initial cell density of the culture was kept 1 X 104cells/ml. Care was taken to have a homogeneous solution for the experiment. Test organism green alga Chlorella vulgaris were collected from National Environmental Engineering Research Institute (NEERI), Nagpur and cultivate in Bold’s Basal Medium (BBM). For the assessment of algal growth, the study was conducted in replicates. The control vessel was maintained in triplicates as recommended in the OECD guideline and the test concentrations were selected in geometric series which were maintained in duplicates. To obtain a quantitative concentration-response relationship by regression analysis, a linearizing transformation of the response data into probit was performed. Using the same, effective concentration (EC) was determined. After 72 hours of exposure to test item Disodium 4-hydroxy-3-[(4-sulphonatonaphthyl)azo]naphthalene sulphonate (CAS No. 3567-69-9) to various nominal test concentrations, EC50 was determine to be 34.823 mg/l graphically and through probit analysis. Thus based on the EC50, chemical was concluded as toxic and can be consider to be classified as aquatic chronic 3 category as per the CLP classification criteria.
The fourth study was used from the UERL report for the structurally and functionally similar read across chemicals (4548-53-2) which supports the classification of target chemical. The effect of the test item disodium 3-[(2,4-dimethyl-5-sulphonatophenyl)azo]-4-hydroxynaphthalene-1-sulphonate, CAS No. 4548-53-2 was studied on the growth of fresh water green alga Chlorella vulgaris. The study was conducted following OECD guideline 201- Alga, growth inhibition test. The test concentration chosen for the study were 6.25mg/l, 12.5mg/l, 25mg/l, 50mg/l, 100mg/l and 200mg/l. The test concentrations were prepared using stock solution of the test item using mineral media. The green alga was exposed to the test concentration for a period of 72 hours to observe average specific growth rate and % growth inhibition under the effect of the test item. After 72 hours of exposure to test item disodium 3-[(2,4-dimethyl-5-sulphonatophenyl)azo]- 4-hydroxynaphthalene-1-sulphonate (CAS No. 4548-53-2) to various nominal test concentrations, EC50 was determine to be 17.321mg/l graphically and through probit analysis. Based on the EC50, chemical was consider as toxic and can be consider to be classified as aquatic chronic 3 category as per the CLP classification criteria.
Based on the predicted data for the target chemical [μ-[[3,3'-[azoxybis[(2-hydroxy-p-phenylene)azo]] bis[4-hydroxynaphthalene-2,7-disulphonato]](8-)]]dicopper, tetrasodium salt (75173-68-1) and for the read across chemical from experimental lab reports (UERL lab), it can be concluded that the [μ-[[3,3'-[azoxybis[(2-hydroxy-p-phenylene)azo]]bis[4-hydroxynaphthalene-2,7-disulphonato]](8-)]]dicopper, tetrasodium salt (75173-68-1) is considered to be toxic to aquatic environment (aquatic algae and cyanobacteria) and can be classified as chronic 3 category as per the CLP classification criteria.
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