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EC number: 274-493-8 | CAS number: 70239-77-9
- 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 fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to fish
- 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:
- of read across substance
- 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
- Qualifier:
- according to guideline
- Guideline:
- other: as mentioned below
- Principles of method if other than guideline:
- WoE report is based on two short term toxicity study of fish for the test chemical :
1.To evaluate short term toxicity of test material on fish
2.To evaluate the acute toxicity of test material on Fathead Minnow fish. - GLP compliance:
- not specified
- Details on sampling:
- 2. composite stored a t 20 C in dark.Stock solution refrigerated
- Vehicle:
- not specified
- Test organisms (species):
- other: 1.Bruchydunio rerio , 2.Pimephales promelas
- Details on test organisms:
- 2.TEST ORGANISM
- Common name: Fathead Minnow
- Source: Berry water gardens , windmill fish hatcheries , North Carolina
- Length at study initiation : 5.2 cm
- Weight at study initiation: 1.3 g
- Feeding during test: starved 48 hrs before test
ACCLIMATION
- Acclimation period: 10 days
- Acclimation conditions : maintained in plastic stock tank in continuously running charcoal –sand filtered Chapel Hill tap water
- Type and amount of food: protein enriched fish food
- Feeding frequency: 5-7 times per week - Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 96 h
- Hardness:
- 2) 32mg/l
- Test temperature:
- 2)15°C
- pH:
- 2)6.8-8.5
- Nominal and measured concentrations:
- 2)0, 0.1, 1.8, 3.2, and 5.6, 10.0 mg/l
- Details on test conditions:
- 2. Test vessel: 5-gallon wide mouth glass jar
- No. of organisms per vessel: 10 - Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- not specified
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: Read across 1
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 12 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: Read across 2
- Details on results:
- 2. Before death, fish tended to become very slow moving at higher concentration. Dead fish were dyed on heads and fins . Surviving fish were dyed dark green in concentration above 1mg/l
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The test chemical 4-[(3-aminobenzoyl)amino]-5-hydroxynaphthalene-1,7-disulphonic acid is likely to be toxic to fish atleast in the concentration range 12-100 mg/l
- Executive summary:
Data available for the structurally and functionally similar read across chemicals has been reviewed to determine the short term toxicity of fish of the test chemical 4-[(3-aminobenzoyl)amino]-5-hydroxynaphthalene-1,7-disulphonic acid (70239 -77 -9).The studies are as mentioned below:
1.Test material was used to evaluate the short term toxicity onBruchydunio rerio. The effect concentration (EC50 was considered to be less the 100 mg/l.
2.Test material was used as a test material to evaluate its acute toxicity effect on Fathead Minnow (Pimephales promelas)
10 Fathead Minnow (Pimephales promelas) were acclimatized in 5-gallon wide mouth glass jar for 10 days before the test in the test temperature 17°C. The test organisms were pre-treated with tetracycline .
Test material was subjected in the test vessel upto the concentration of 12 mg/l . Toxic effect were observed after 96 hrs. Hence the effect concentration was considered to be >12 mg/l
Before death, fish tended to become very slow moving at higher concentration. Dead fish were dyed on heads and fins . Surviving fish were dyed dark green in concentration above 1mg/l.
Thus, based on the above summarised studies, 4-[(3-aminobenzoyl)amino]-5-hydroxynaphthalene-1,7-disulphonic acid and it’s structurally and functionally similar read across substance, it can be concluded that effect concetration value is in the range of 12 -100 mg/ L. Thus, comparing this value with the criteria of CLP regulation, 4-[(3-aminobenzoyl)amino]-5-hydroxynaphthalene-1,7-disulphonic acid can be classified for short term toxicity of fish as " acute Aquatic 3" .Hence,based on the data available for the structurally and functionally similar read across, test chemical 4-[(3-aminobenzoyl)amino]-5-hydroxynaphthalene-1,7-disulphonic acid is likely to be toxic atleast in the concentration range 12 -100mg/L .
Reference
Description of key information
Short-term toxicity to fish:
Data available for the structurally and functionally similar read across chemicals has been reviewed to determine the short term toxicity of fish of the test chemical 4-[(3-aminobenzoyl)amino]-5-hydroxynaphthalene-1,7-disulphonic acid (70239 -77 -9).The studies are as mentioned below:
1.Test material was used to evaluate the short term toxicity onBruchydunio rerio. The effect concentration (EC50 was considered to be less the 100 mg/l.
2.Test material was used as a test material to evaluate its acute toxicity effect on Fathead Minnow (Pimephales promelas)
10 Fathead Minnow (Pimephales promelas) were acclimatized in 5-gallon wide mouth glass jar for 10 days before the test in the test temperature 17°C. The test organisms were pre-treated with tetracycline .
Test material was subjected in the test vessel upto the concentration of 12 mg/l . Toxic effect were observed after 96 hrs. Hence the effect concentration was considered to be >12 mg/l
Before death, fish tended to become very slow moving at higher concentration. Dead fish were dyed on heads and fins . Surviving fish were dyed dark green in concentration above 1mg/l.
Thus, based on the above summarised studies, 4-[(3-aminobenzoyl)amino]-5-hydroxynaphthalene-1,7-disulphonic acid and it’s structurally and functionally similar read across substance, it can be concluded that effect concetration value is in the range of 12 -100 mg/ L. Thus, comparing this value with the criteria of CLP regulation, 4-[(3-aminobenzoyl)amino]-5-hydroxynaphthalene-1,7-disulphonic acid can be classified for short term toxicity of fish as " acute Aquatic 3" .Hence,based on the data available for the structurally and functionally similar read across, test chemical 4-[(3-aminobenzoyl)amino]-5-hydroxynaphthalene-1,7-disulphonic acid is likely to be toxic atleast in the concentration range 12 -100mg/L .
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 100 mg/L
Additional information
Short-term toxicity to fish:
Data available for the structurally and functionally similar read across chemicals has been reviewed to determine the short term toxicity of fish of the test chemical 4-[(3-aminobenzoyl)amino]-5-hydroxynaphthalene-1,7-disulphonic acid (70239 -77 -9).The studies are as mentioned below:
1.Test material was used to evaluate the short term toxicity onBruchydunio rerio. The effect concentration (EC50 was considered to be less the 100 mg/l.
2.Test material was used as a test material to evaluate its acute toxicity effect on Fathead Minnow (Pimephales promelas)
10 Fathead Minnow (Pimephales promelas) were acclimatized in 5-gallon wide mouth glass jar for 10 days before the test in the test temperature 17°C. The test organisms were pre-treated with tetracycline .
Test material was subjected in the test vessel upto the concentration of 12 mg/l . Toxic effect were observed after 96 hrs. Hence the effect concentration was considered to be >12 mg/l
Before death, fish tended to become very slow moving at higher concentration. Dead fish were dyed on heads and fins . Surviving fish were dyed dark green in concentration above 1mg/l.
Thus, based on the above summarised studies, 4-[(3-aminobenzoyl)amino]-5-hydroxynaphthalene-1,7-disulphonic acid and it’s structurally and functionally similar read across substance, it can be concluded that effect concetration value is in the range of 12 -100 mg/ L. Thus, comparing this value with the criteria of CLP regulation, 4-[(3-aminobenzoyl)amino]-5-hydroxynaphthalene-1,7-disulphonic acid can be classified for short term toxicity of fish as " acute Aquatic 3" .Hence,based on the data available for the structurally and functionally similar read across, test chemical 4-[(3-aminobenzoyl)amino]-5-hydroxynaphthalene-1,7-disulphonic acid is likely to be toxic atleast in the concentration range 12 -100mg/L .
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