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Reaction mass of disodium 4-amino-6-[[4-[(2,4-diaminophenyl)diazenyl]phenyl]]-3-((E)-[4-((E)-(2,4-diaminophenyl)diazenyl]phenyl )diazenyl)-5-hydroxynaphthalene-2,7-disulphonate and disodium 4-amino-6-((E)-(4-aminophenyl)diazenyl)-3-((E)-(4-((E)-(2,4-diaminophenyl)diazenyl)phenyl)diazenyl)-5-hydroxynaphthalene-2,7-disulfonate
EC number: 951-695-0 | CAS number: -
- 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 plants other than algae
Administrative data
- Endpoint:
- toxicity to aquatic plants other than algae
- Type of information:
- other: experimetal study on similar substance
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study well documented, test procedure in accordance with OECD 221 methodes, meets generally accepted scientific principles, acceptable for assessment. GLP compliant with certificate.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 012
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 221 (Lemna sp. Growth Inhibition Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- Disodium 4-amino-3,6-bis[[4-[(2,4-diaminophenyl)azo]phenyl]azo]-5-hydroxynaphthalene-2,7-disulphonate
- EC Number:
- 229-208-1
- EC Name:
- Disodium 4-amino-3,6-bis[[4-[(2,4-diaminophenyl)azo]phenyl]azo]-5-hydroxynaphthalene-2,7-disulphonate
- Cas Number:
- 6428-31-5
- Molecular formula:
- C34H29N13O7S2.2Na
- IUPAC Name:
- disodium 4-amino-3,6-bis({4-[(2,4-diaminophenyl)diazenyl]phenyl}diazenyl)-5-hydroxynaphthalene-2,7-disulfonate
- Test material form:
- solid: particulate/powder
Constituent 1
Sampling and analysis
- Analytical monitoring:
- no
Test solutions
- Vehicle:
- yes
Test organisms
- Test organisms (species):
- Lemna minor
- Details on test organisms:
- Exponential growing plant monocolture of Lemna Minor (Umweltbundesamt, D-06813 Dessau-Rosslau, Germany
Study design
- Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 7 d
Test conditions
- Test temperature:
- 25 ± 1 °C
- pH:
- 5,5 ± 0,2
- Nominal and measured concentrations:
- The test were performed at concentrations of 10, 100 and 1000 mg/l of the active ingredient.
Assuming a purity of 65%, nominal concentrations of 15.4, 154 and 1538 mg/l, respectively, were prepared. - Details on test conditions:
- TEST SYSTEM
- Test vessel: 400 ml beaker
- Material, size, headspace, fill volume: glass with 200 ml of test medium
GROWTH MEDIUM
- Standard medium used: yes
Test medium STEINBERG with the following composition:
Macroelements mg/l
KNO3 350
KH2PO4 90
K2HPO4*3H2O 16.5
MgSO4*7H2O 100
Ca(NO3)2*4H2O 295
Microelements μg/l
H3BO3 120.0
ZnSO4*7H2O 180.0
Na2MoO4*2H2O 44.0
MnCl2*4H2O 180.0
FeCl3*6H2O 760.0
C10H14N2Na2O8*2H2O 1500.0
ILLUMINATION: Continuos (3500 - 7500 lux) from Osram Fluora L18W77 (Osarm AG, Winterthur, Switzerland) - Reference substance (positive control):
- no
Results and discussion
Effect concentrations
- Duration:
- 7 d
- Dose descriptor:
- EC50
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
Any other information on results incl. tables
The number of fronds is counted on day 3, 5 and 7. On day 7 the dry weight is determined by incubating the duckweed at 60° C over night.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- The results showthat the tested item is not toxic to Lemna minor with EC50 > 1000 mg/L.
- Executive summary:
Effect on frond numbers:The inhibitory effect based on the average specific growth rate and the yield (duckweed biomass production) of the tested item to the duckweedLemna minorwas investigated over a period of 7 d.The test was performed at concentrations of 10, 100 and 1000 mg/l of the active ingredient. Assuming a purity of 70%, nominal concentrations of 15.4, 154 and 1538 mg/l, respectively, were prepared.With respect to duckweed growth rate and yield inhibition for the endpoint frond numbers, no significant effects were observed at all concentrations as compared to the untreated controlsas determined by Dunnett’s test.Based on these data the median effect concentration with respect to growth rate (ErC50) and yield (EyC50) for the endpoint frond numbers of the tested item toLemna minorwas estimated to be >1538 mg/l nominal concentration.The no-observed-effect concentration with respect to growth rate (NOErC) and yield (NOEyC) for the endpoint frond numbers was 1538 mg/l nominal concentration.
Effects on dry weight: With respect to duckweed growth rate inhibition for the endpoint dry weight no significant effects were observed at all concentrations as compared to the untreated controlsas determined by Dunnett’s test.Based on these data the median effect concentration with respect to growth rate (ErC50) for the endpoint dry weight of Direct Black 19 toLemna minorwas estimated to be >1538 mg/l nominal concentration.The no-observed-effect concentration with respect to growth rate (NOErC) for the endpoint dry weight was 1538 mg/l nominal concentration.With respect to duckweed yield inhibition for the endpoint dry weight the following effects as compared to the untreated controls were observed at the respective nominal concentrations: 1538 mg/l (27%) and154 mg/l (20%). No significant effects as determined by Dunnett’s test were observed at 15.4 mg/l.Based on these data the median effect concentration with respect to yield (EyC50) for the endpoint dry weight of the tested item toLemna minorwas estimated to be >1538 mg/l nominal concentration.The no-observed-effect concentration with respect to yield (NOEyC) for the endpoint dry weight was 15.4 mg/l nominal concentration.
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