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Reaction mass of copper complex of [(2,6-difluoroheterocycl-4-yl)amino]hydroxy{[2-hydroxy-3-sulfonato-5-(vinylsulfonyl)phenyl]diazenyl}naphthalene sulfonic acid, dialkali salt and copper complex of [(2,6-difluoroheterocycl-4-yl)amino]-hydroxy{[2-hydroxy-3-sulfonato-5-{[2-(sulfonatooxy)ethyl]sulfonyl}phenyl]diazenyl}naphthalene sulfonic acid, trialkali salt
EC number: 479-550-2 | 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
Endpoint summary
Administrative data
Description of key information
Additional information
Two hydrolysis studies with identical experimental setup were carried out to measure the rate of hydrolysis of the test substance. The results of both studies were similar. However, one study (study number AN-ASB 0260) was carried out using test substance with a purity of only 56.3 % and is therefore considered to be of supportive value only. The results presented below are based on study AN-ASB 0248 which is considered to be the key study.
The hydrolysis rate for the test substance was determined in accordance with EU method C.7, and in accordance with GLP. The test substance was assessed at a concentration of 1 g/L in all parts of the study. HPLC was used to analyse the test substance throughout. A preliminary test was carried out to assess the rate of hydrolysis at pH 4, 7 and 9 at 50 °C and as a result in accordance with the guidelines further testing was not carried out at pH 4.
The main test was carried out at pH 7 and 9 at 50 °C initially. A linear dependence on the time of degradation and the logarithm to base ten of the test item concentration was obtained which means that the hydrolysis reaction was a pseudo first order reaction. Therefore, further tests were carried out at pH 7 at 60 and 70 °C and pH 9 at 38 °C. From the measured results the rate constants and the half-lives of the test substance were calculated at:
pH 7, 50 °C: k = 0.0037 h-1, DT50 = 186 hours
pH 7, 60 °C: k = 0.136 h-1, DT50 = 51 hours
pH 7, 70 °C: k = 0.0431 h-1, DT50 = 16 hours
pH 9, 50 °C: k = 0.0872 4 h-1, DT50 = 8 hours
pH 9, 38 °C: k = 0.0186 h-1, DT50 = 37 hours.
The Arrhenius equation was used to calculate the rate constant at 25 °C. At pH 7 this was calculated at 1.114 ×10-4h-1, and at pH 9 at 3.018 × 10-3h-1. These rate constants were used to estimate the half-lives of 6222 hours and 230 hours at pH 7 and 9, respectively.
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