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EC number: 612-023-9 | CAS number: 607724-37-8
- 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:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Remarks:
- Experimental data of read across chemical
- Justification for type of information:
- Data for the target chemical is summarized based on the structurally similar read across chemicals.
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- according to guideline
- Guideline:
- other: Refer below principle
- Principles of method if other than guideline:
- WoE report is prepared based on toxicity to aquatic invertebrates study:1st, 2nd and 3rd study
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- - Name of test material: 2-Naphthalenesulfonic acid, 7-amino-4-hydroxy-3-[2-[4-[[2-(sulfooxy)ethyl]sulfonyl]phenyl]diazenyl]-8-[2-[2-sulfo-4-[[2-(sulfooxy)ethyl]sulfonyl]phenyl]diazenyl]-, sodium salt (1:4)- Molecular formula: C26H25N5O19S6.4Na- Molecular weight: 995.85 g/mole- Smiles : [Na][Na][Na][Na]Nc1ccc2c(cc(S(O)(=O)=O)c(N=Nc3ccc(S(=O)(=O)CCOS(O)(=O)=O)cc3)c2O)c1N=Nc1ccc(S(=O)(=O)CCOS(O)(=O)=O) cc1S(O)(=O)=O- Substance type: Organic- Physical state: Solid powder
- Analytical monitoring:
- not specified
- Vehicle:
- yes
- Details on test solutions:
- 1. The stock solution 100 mg/l was prepared by dissolving red powder in reconstituted water. Test solutions of required concentrationas were prepared by mixing the stock solution of the test sample with reconstituted test water.2. The solution 100 mg/l was prepared by dissolving red powder in reconstituted water. The solution was kept 30 min in ultrasonic bath.3. The solution 100 mg/l was prepared by dissolving brown powder in reconstituted water.
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM- Common name: Water flea- Strain: Straus- Source: Own breeding at University of Chemistry and Technology, Prague- Age at study initiation (mean and range, SD): The animals used for the test shall be less than 24 h old and should not be first brood progeny- Feeding during test: No feedingACCLIMATION - No data available- Acclimation period:- Acclimation conditions (same as test or not):- Type and amount of food:- Feeding frequency:- Health during acclimation (any mortality observed):
- Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 48 h
- Remarks on exposure duration:
- ± 1 hr
- Test temperature:
- 20±1°C
- pH:
- 1. Test: 7.8 (changed to 7.7 during test)Control: 7.8 (no change during test)2. Test: 7.7 (changed to 7.8 during test)Control: 7.8 (change to 7.7during test)3.Test: 7.8 (changed to 7.6 during test)Control: 7.7 (change to 7.5 during test)
- Dissolved oxygen:
- 1. higher than 7.8 mg/L at the end of test2. higher than 7.6 mg/L at the end of test3. higher than 7.9 mg/L at the end of test
- Nominal and measured concentrations:
- 1. 0, 5, 10, 20, 40, 80, 160 mg/l nominal concentration2. 100 mg/l nominal concentration
- Details on test conditions:
- TEST SYSTEM- Test vessel: 50 ml glass vessel- fill volume: 25 ml- No. of organisms per vessel: 5- No. of vessels per concentration (replicates): 4TEST MEDIUM / WATER PARAMETERS- Source/preparation of dilution water: Natural water (surface or ground water), reconstituted water or dechlorinated tap water are acceptable as culturing and dilution water if D. magna survives in it for the duration of the culturing, acclimation and testing without showing signs of stress. Waters in the range pH 6 to pH 9, with hardness between 140 mg/l and 275 mg/l (as CaCO3) are recommended.As an example, the preparation of dilution water meeting the requirements is described below.Dissolve known quantities of reagents in water. The dilution water prepared shall have a pH of 7.8 ± 0.5, a hardness of (225 ± 50) mg/l (expressed as CaCO3), a molar Ca + Mg ratio close to 4 + 1 and a dissolved oxygen concentration above 7 mg/l.Prepare the solutions specified below:- Calcium chloride solution: Dissolve 117.6 g of calcium chloride dihydrate (CaCl2.2H2O) in water (4.2) and make up to 1 l with water (4.2).- Magnesium sulfate solution: Dissolve 49.3 g of magnesium sulfate heptahydrate (MgSO4.7H2O) in water (4.2) and make up to 1 l with water (4.2).- Sodium bicarbonate solution: Dissolve 25.9 g of sodium bicarbonate (NaHCO3) in water (4.2) and make up to 1 l with water (4.2).- Potassium chloride solution: Dissolve 2.3 g of potassium chloride (KCI) in water (4.2) and make up to 1 l with water (4.2).MixingMix 2.5 ml of each of the four solutions and make up to 1 l with water.The dilution water shall be aerated until the dissolved oxygen concentration has reached saturation and the pH has stabilized. If necessary, adjust the pH to 7.8 ± 0.5 by adding sodium hydroxide (NaOH) solution or hydrochloric acid (HCI). The dilution water prepared in this way shall not be further aerated before use.- Sodium hydroxide solution, e.g. [NaOH] : 1 mol/l.- Hydrochloric acid, e.g. [HCl] : 1 mol/l.Reference substance: Dissolve 600 mg of potassium dichromate (K2Cr2O7) in water and make up to 1 l with water (4.2).OTHER TEST CONDITIONS- Adjustment of pH: no adjustment done- Photoperiod: No - Darkness- Light intensity:CALCULATION:EC50 was calculated using non linear regression by the software Prism 4.02nd and 3rd study: TEST SYSTEM- Test vessel: 50 ml glass vessel- fill volume: 25 ml- No. of organisms per vessel: 5- No. of vessels per concentration (replicates): 5
- Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate (K2Cr2O7)
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 900 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 1st study
- Duration:
- 48 h
- Dose descriptor:
- other: IC
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: Only 8% inhibition was observed at 100 mg/l.
- Remarks:
- 2nd and 3rd study
- Details on results:
- 100 mg/l of test chemical was used at which 8% daphnia inhibited after the exposure of 48 hrs.
- Results with reference substance (positive control):
- - Results with reference substance valid- EC50: 0.79 mg/L (24 hours)
- Reported statistics and error estimates:
- EC50 was calculated using non linear regression by the software Prism 4.0
- Validity criteria fulfilled:
- not specified
- Conclusions:
- 1. Based on the immobility of daphnia magna, the median effective concentration (EC50) for the test substance, in Daphnia magna was determined to be > 900 mg/L for immobilisation effects.2. Based on the immobility of daphnia magna due to the test chemical, the inhibitory concentration at which only 8% immobility observed was 100 mg/l in a 48 hour study.3. The effective concentration (EC8) for the test substance, in Daphnia magna was determined to be 100 mg/L on the basis of mobiity inhibition effects in a 48 hour study.Thus based on the above studies, 2-Naphthalenesulfonic acid, 7-amino-4-hydroxy-3-[2-[4-[[2-(sulfooxy)ethyl]sulfonyl]phenyl]diazenyl]-8-[2-[2-sulfo-4-[[2-(sulfooxy)ethyl]sulfonyl]phenyl]diazenyl]-, sodium salt (1:4) consider to be nontoxic and not classified as per the CLP classification criteria.
- Executive summary:
Various studies available for the test chemical were reviewed to determine the toxic nature of 2-Naphthalenesulfonic acid, 7-amino-4-hydroxy-3-[2-[4-[[2-(sulfooxy)ethyl]sulfonyl]phenyl]diazenyl]-8-[2-[2-sulfo-4-[[2-(sulfooxy)ethyl]sulfonyl]phenyl]diazenyl]-, sodium salt (1:4) (CAS no 607724 -37 -8) on the mobility of aquatic invertebrates. The studies are as mentioned below:
Aim of the study was to assess the effect of chemical on the mobility of daphnia magna. Test was conducted according to OECD Guideline 202. The stock solution 100 mg/l was prepared by dissolving red powder in reconstituted water. Test solutions of required concentration as were prepared by mixing the stock solution of the test sample with reconstituted test water. The test substance was tested at the 0, 5, 10, 20, 40, 80, 160 mg/l nominal concentration. Potassium dichromate (K2Cr2O7) were used as a reference positive control. Effects on immobilisation were observed for 48 hours by using non linear regression by the software Prism 4.0. After the exposure of chemical for 48 hrs 50 % immobility was observed. Based on the immobility of daphnia magna, the median effective concentration (EC50) for the test substance, in Daphnia magna was determined to be > 900 mg/L for immobilisation effects. This value indicates that the substance is likely to be non-hazardous to aquatic invertebrates and cannot be classified as toxic as per the CLP classification criteria.
An acute immobilisation test was used to test how a range of concentrations of test chemical exerts different degrees of toxic effects on the swimming capability of Daphnia magna under otherwise identical test conditions. The test was performed in close resemblance to OECD guideline 202. The testing aim was to determine a EC50 after 48 hours of exposure to D. magna. Daphnids were exposed to test chemical in 50 ml beakers in a volume of 25 ml of liquid solution containing both the chemical and media as specified in OECD 202. The beakers were placed in a temperature controlled room at 20±1 degrees Celsius. The D. magna (age ≤24) used. The breeding stock of D. Magna originated from University of Technology in Prague. The animals were exposed to medium (i.e. a beaker containing only medium) and/or the tested chemical during 48 hours (±1 hour). None of the exposed animal’s immobilization were affected by exposure to only medium. The nominal concentrations used were: 100 mg/L (limit test). There were 5 Daphnia per test vessels and 5 replicates per concentration. The pH in test vessels were 7.7-7.8 mg/L. The positive control/ reference substance used in the tested showed an expected result and gave an EC50 that corresponded to previous exposures with this chemical in D. magna. The IC50 was defined as a concentration that immobilizes 50% of the exposed D. magna. Eight percent immobilization in D. magna was observed after 48 hours of exposure to 100 mg/L of test chemical. The IC8 was therefore estimated to be 100 mg/L. Based on the IC8, it can be concluded that the chemical was nontoxic and can be consider to be not classified as per CLP classification criteria.
Determination of the inhibition of the mobility of daphnids was carried out with the substance according to OECD Guideline 202. The limit test was performed at 100 mg/l. Effects on immobilisation were observed for 48 hours. The solution 100 mg/l was prepared by dissolving brown powder in reconstituted water. The effective concentration (EC8) for the test substance, in Daphnia magna was determined to be 100 mg/L on the basis of mobility inhibition effects in a 48 hour study. This value indicates that the substance is likely to be non-hazardous to aquatic invertebrates and cannot be classified as toxic as per the CLP criteria.
Thus based on the above studies, 2-Naphthalenesulfonic acid, 7-amino-4-hydroxy-3-[2-[4-[[2-(sulfooxy)ethyl]sulfonyl]phenyl]diazenyl]-8-[2-[2-sulfo-4-[[2-(sulfooxy)ethyl]sulfonyl]phenyl]diazenyl]-, sodium salt (1:4)(CAS no 607724 -37 -8) consider to be nontoxic and not classified as per the CLP classification criteria.
Reference
Description of key information
1. Based on the immobility of daphnia magna, the median effective concentration (EC50) for the test substance, in Daphnia magna was determined to be > 900 mg/L for immobilisation effects.
2. Based on the immobility of daphnia magna due to the test chemical, the inhibitory concentration at which only 8% immobility observed was 100 mg/l in a 48 hour study.
3. The effective concentration (EC8) for the test substance, in Daphnia magna was determined to be 100 mg/L on the basis of mobiity inhibition effects in a 48 hour study.
Thus based on the above studies, 2-Naphthalenesulfonic acid, 7-amino-4-hydroxy-3-[2-[4-[[2-(sulfooxy)ethyl]sulfonyl]phenyl]diazenyl]-8-[2-[2-sulfo-4-[[2-(sulfooxy)ethyl]sulfonyl]phenyl]diazenyl]-, sodium salt (1:4) consider to be nontoxic and not classified as per the CLP classification criteria.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 900 mg/L
Additional information
Various studies available for the test chemical were reviewed to determine the toxic nature of 2-Naphthalenesulfonic acid, 7-amino-4-hydroxy-3-[2-[4-[[2-(sulfooxy)ethyl]sulfonyl]phenyl]diazenyl]-8-[2-[2-sulfo-4-[[2-(sulfooxy)ethyl]sulfonyl]phenyl]diazenyl]-, sodium salt (1:4) (CAS no 607724 -37 -8) on the mobility of aquatic invertebrates. The studies are as mentioned below:
Aim of the study was to assess the effect of chemical on the mobility of daphnia magna. Test was conducted according to OECD Guideline 202. The stock solution 100 mg/l was prepared by dissolving red powder in reconstituted water. Test solutions of required concentration as were prepared by mixing the stock solution of the test sample with reconstituted test water. The test substance was tested at the 0, 5, 10, 20, 40, 80, 160 mg/l nominal concentration. Potassium dichromate (K2Cr2O7) were used as a reference positive control. Effects on immobilisation were observed for 48 hours by using non linear regression by the software Prism 4.0. After the exposure of chemical for 48 hrs 50 % immobility was observed. Based on the immobility of daphnia magna, the median effective concentration (EC50) for the test substance, in Daphnia magna was determined to be > 900 mg/L for immobilisation effects. This value indicates that the substance is likely to be non-hazardous to aquatic invertebrates and cannot be classified as toxic as per the CLP classification criteria.
An acute immobilisation test was used to test how a range of concentrations of test chemical exerts different degrees of toxic effects on the swimming capability of Daphnia magna under otherwise identical test conditions. The test was performed in close resemblance to OECD guideline 202. The testing aim was to determine a EC50 after 48 hours of exposure to D. magna. Daphnids were exposed to test chemical in 50 ml beakers in a volume of 25 ml of liquid solution containing both the chemical and media as specified in OECD 202. The beakers were placed in a temperature controlled room at 20±1 degrees Celsius. The D. magna (age ≤24) used. The breeding stock of D. Magna originated from University of Technology in Prague. The animals were exposed to medium (i.e. a beaker containing only medium) and/or the tested chemical during 48 hours (±1 hour). None of the exposed animal’s immobilization were affected by exposure to only medium. The nominal concentrations used were: 100 mg/L (limit test). There were 5 Daphnia per test vessels and 5 replicates per concentration. The pH in test vessels were 7.7-7.8 mg/L. The positive control/ reference substance used in the tested showed an expected result and gave an EC50 that corresponded to previous exposures with this chemical in D. magna. The IC50 was defined as a concentration that immobilizes 50% of the exposed D. magna. Eight percent immobilization in D. magna was observed after 48 hours of exposure to 100 mg/L of test chemical. The IC8 was therefore estimated to be 100 mg/L. Based on the IC8, it can be concluded that the chemical was nontoxic and can be consider to be not classified as per CLP classification criteria.
Determination of the inhibition of the mobility of daphnids was carried out with the substance according to OECD Guideline 202. The limit test was performed at 100 mg/l. Effects on immobilisation were observed for 48 hours. The solution 100 mg/l was prepared by dissolving brown powder in reconstituted water. The effective concentration (EC8) for the test substance, in Daphnia magna was determined to be 100 mg/L on the basis of mobility inhibition effects in a 48 hour study. This value indicates that the substance is likely to be non-hazardous to aquatic invertebrates and cannot be classified as toxic as per the CLP criteria.
Thus based on the above studies, 2-Naphthalenesulfonic acid, 7-amino-4-hydroxy-3-[2-[4-[[2-(sulfooxy)ethyl]sulfonyl]phenyl]diazenyl]-8-[2-[2-sulfo-4-[[2-(sulfooxy)ethyl]sulfonyl]phenyl]diazenyl]-, sodium salt (1:4)(CAS no 607724 -37 -8) consider to be nontoxic and not classified as per the CLP classification criteria.
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