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Reaction mass of 6-(2-ethyl-6-methylanilino)-5-(4-{4-[ethyl(3-sulfobenzyl) amino] phenylazo} phenylazo)-4-hydroxynaphthalene-2-sulfonic acid, sodium and/or disodium salt(s) and 6-(2-ethyl-6-methylanilino)-5-(4-{4-[ethyl(4-sulfobenzyl) amino] phenylazo} phenylazo)-4-hydroxynaphthalene-2-sulfonic acid, sodium and/or disodium salt(s)
EC number: 475-080-7 | 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
Adsorption / desorption
Administrative data
- Endpoint:
- adsorption / desorption
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 007
- Report date:
- 2007
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 121 (Estimation of the Adsorption Coefficient (Koc) on Soil and on Sewage Sludge using High Performance Liquid Chromatography (HPLC))
- Version / remarks:
- 2001
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- HPLC estimation method
- Media:
- soil/sewage sludge
Test material
- Reference substance name:
- Acid Navy RN-2682
- IUPAC Name:
- Acid Navy RN-2682
- Test material form:
- solid
Constituent 1
Study design
HPLC method
- Details on study design: HPLC method:
- HPLC with UV/vis detector
Reversed phase column and an aqueous mobile phase
Reference solutions
The reference items were chosen from the list given in the OECD guideline 121.
Stock solutions of the reference items were prepared as described:
11.95 mg of isoproturon, 10.58 mg of linuron, 10.59 mg of 2,4-DDT, 9.17 mg of pyrazophos, 9.69 mg of diclofop-methyl and 9.36 mg of acetanilide were each dissolved in 10 ml of methanol.
A combined reference solution was prepared by transferring 144 μl of the acetanilide stock solution, 115 μl of the isoproturon stock solution, 110 μl of the linuron stock solution, 1000 μl of the pyrazophos stock solution, 250 μl of the diclofop-methyl stock solution and 1000 μl of the 2,4-DDT stock solution into one volumetric flask and diluting to a volume of 10 ml with a solvent mixture of water and methanol (45:55; v/v). This reference solution was injected six
times.
Sodium nitrate (9.80 mg) was dissolved in 10 ml of methanol to obtain a stock solution. The stock solution (50 μl) was diluted to 1 ml with a solvent mixture of water and methanol (45:55; v/v). This sodium nitrate solution was injected twice for the determination of the dead time of the HPLC system.
HPLC-conditions
Column: LiChrospher CN, particle size 5 μm, 250 mm × 4 mm
Mobile phase: water / methanol (45:55; v/v); pH 6.55
Detection: test item: 254 nm
Reference items: 210 nm
Sodium nitrate: 254/ 210
Temperature: 25 °C
Injection volume: 10 μl
Flow: 1.0 ml/min
Run time: 15 minutes
Batch equilibrium or other method
- Analytical monitoring:
- yes
- Details on test conditions:
- The test item solution was injected three times and the reference solution was injected six times.
Results and discussion
Adsorption coefficient
- Type:
- log Koc
- Value:
- < 1.25 dimensionless
Results: HPLC method
- Details on results (HPLC method):
- Under the conditions of the test, the test item was found to elute as one peak at a retention time of about 1.06 minutes. Sodium nitrate, that was used for the dead time determination, was eluted at a retention time of about 1.18 minutes. The reference item with the lowest Koc was eluted at a retention time of about 2.83 minutes. Test item was not retained under the chromatographic conditions of the test and was eluted at the dead time. The Koc was therefore determined to be lower than that one of the lowest reference item used (acetanilide).
The chromatography of the test item resulted in one main peak with a well-defined and reproducible retention time. The HPLC method was therefore considered to be suitable for the purpose of the study. Based on the chromatographic data, test item was considered to be stable during the test procedure.
Applicant's summary and conclusion
- Conclusions:
- The log of the adsorption coefficient (Koc) of test item was found to be lower than that one of the lowest reference item acetanilide.
log Koc < 1.25 using the HPLC method.
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