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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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
LC50 for freshwater = 0.0305 mg/L (based on results on Malachite Green Chloride)
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 0.03 mg/L
Additional information
Malachite Green (MG) was toxic to all species of fish exposed.
Most of studies done on MG were conducted in freshwater
In Bills study (1977) MG LC50 ranged from 0.0305 to 0.383 mg/L in 96 -h exposures in soft water at 12°C. Results showed that centrarchids were 1.5 to 3.5 times more sensitive to the chemical than the ictalurids and 3 to 7 times more sensitive than the salmonids; the bluegill was the most sensitive species (96-h LC50 0.0305 mg/Ll) and the coho salmon the most resistant (0.383 mg/L).
In some studies the influence that some physical-chemical parameters may have on the toxicity of MG has been reported. Some tests carried out at different pH, show a greater sensitivity to the substance at basic pH (pH=9.5) and this is probably due to conversion to cationic form (carbinol) (Bills et al. 1977).
The absence of positive charge may facilitate the absorption, which occurs almost exclusively through the gills (Plakas et al. 1995; see 6.5).
The variation of the toxicity of MG as a function of temperature is minimal. Small differences were found by testing bodies to unnatural temperatures and this probably induces a state of stress that can lead to greater sensitivity (Bills et al. 1993 and Van Heerden et al. 2000).
The toxicity of MG is not affected by variation in water hardness (Bills et al. 1993).
Some studies show that exposure to MG elicited iperactivity characterized by rapid pectoral and opercular movement, erratic swimming and gradual loss of equilibrium associated with breathing difficulties in the fish. The effects on the behaviour was similar to those observed in several teleostean species exposure to various pesticides (Srivastava et al. 1993).
From anatomical observation of the fish was seen that the MG poisoning leads to a greenish scales and an increased production of mucus from the skin. Some results show that MG does not interfere on the nervous system, but also causes damage to the liver and inhibits the process of conjugation (Srivastava et al. 1993). The activity of GPT had a significant increase. After treatment with MG were observed significant modifications also in the activity of LDH's (Lanari et al. 1996; see 6.4). Toxicants which affect the liver tissue also result in reduction of total serum protein in fish and the liver is found to be severely damaged. Hypercholesterolemia was observed too.
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