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EC number: 255-288-2 | CAS number: 41272-40-6
- 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
Phototransformation in water
Administrative data
Link to relevant study record(s)
Description of key information
Malachite Green degrade due to photolysis; during the photolytic degradation process a large number of transformation products are generated.
Key value for chemical safety assessment
- Half-life in water:
- 30 h
Additional information
Photolysis experiments (Perez et al, 2007) were performed by direct exposure of a solution of Malachite Green (MG) in water to natural sunlight. This resulted in a phototransformation half-life of 30 hours under natural sunlight conditions, with 8 hours of radiation/day. Due to the 8 hours radiation/day light cycle this photolytic half-life is an underestimation, and the result of a faster photolysis rate and a slower hydrolysis rate during non-radiation conditions, given that 45% hydrolysis was observed in the same study after 145 hours. Total degradation of MG in the closed batch system was observed after 210 hours at a temperature of 25°C. During this photolytic/hydrolytic degradation of MG, it has been shown that a large number of transformation products were generated. The kinetics of one of the, possible toxic, transformation products, 4-(dimethylamine)benzophenone (D20) indicated that photodegradation of D20 followed a similar photodegradation rate as MG (Pérez et al 2007).
The photodegradation of MG has been studied both under different pH values and varying amounts of TiO2 (Chen et al. 2006). Under the catalytic influence of TiO2, the photodegradation rate increased substantially, resulting in 99.9% degradation of the sample after 4 hours, indicating that the photodegradation of MG can be augmented substantially. Fischer et al, 2011 studied the influence of various wavelengths on the photodegradation of MG and MG carbinol, and concluded that MG carbinol is photodegraded more easily than MG. MG seemed to be rather resistant to photodegradation which is in contrast with the above mentioned study.
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