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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
Biological effects monitoring
Administrative data
- Endpoint:
- biological effects monitoring
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Read across from a similar substance which has the same main component and with a different counter ion that doesn't influence the characteristics related to the specific end-point
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- publication
- Title:
- Cytotoxic effects of sublethal concentrations of malachite green in isolated hepatocytes from rainbow trout
- Author:
- Zahn t. and Braunbeck T.
- Year:
- 1 995
- Bibliographic source:
- Toxicology in vitro, vol 9, No. 5, pp 729-741, 1995
Materials and methods
- Principles of method if other than guideline:
- Isolated hepatocytes of rainbow trout were used to evaluate cytotoxicity in a subcellular system and compare in vitro effects with those of in vivo experiments.
- Type of study / information:
- Cytotoxic effects of sublethal concentrations of Malachite Green (MG).
Test material
- Reference substance name:
- Malachite Green Oxalate
- IUPAC Name:
- Malachite Green Oxalate
- Details on test material:
- - Name of test material: malachite green
- IUPAC name: N-[4-[bis]4-(dimethylamino)-phenyl[phenyl]methylene] Cl 42000
- Source: Merck, Darmstadt, Germany
Constituent 1
Results and discussion
Any other information on results incl. tables
ACUTE TOXCITY OF MALACHITE GREEN
Viability of isolated hepatocytes as evidenced by trypan blue exclusion showed a senescence dependent decline from 90 or more to about 70% after 5 days (cf. Braunbeck and Storch, 1992) in culture for all experimental groups. Likewise. LDH release into the medium, which increased from 200 ± 35 mU ml at day 1 to approximately 240 mU/Uml at day 5 in controls. Did not show significant changes after exposure to malachite green. Thus, significant cytotoxic effects of malachite green on isolated hepatocytes could not be revealed at the concentrations tested.
ULTRASTRUCTURE OF CONTROL HEPATOCYTES
Nuclei showed heterochromatin randomly distributed in the nucleoplasm with small concentrations underneath the nuclear envelope. The organelle-rich portion of the cytoplasm comprised mitochondria. peroxisomes, tubules and cisternae of smooth endoplasmic reticulum (SER) and RER stacks with up to 12 non-fenestrated cisternae arranged in parallel array. Golgi fields consisting of 3- 5 cisternae and occasional lipid droplets. In control cells, only a modest increase of small myelinated bodies in the cytoplasm and the tendency of heterochromatin to condense in the nucleus of ageing cells could he observed from day 3 in culture.
ULTRASTUCTURE OF ISOLATED HEPATOCYTES EXPOSED TO 0.01 mg LITRE MALACHITE GREEN
After 24 h of exposure to malachite green, part of the hepatocytes showed an increasing tendency of the heterochromatin to condense in the nuclearperiphery and around the nucleolus. - Cytoplasmic effects after 3 days of exposure comprised a closer association of peroxisomes with single RER cisternae. a more intimate association o f RER cisternae with glycogen rosettes, a slight increase of lipid droplets and induction of glycogenosomes.
After 5 days of exposure, additional effects were a less regular compartmentation of hepatocytes, formation of mitochondria clusters and their more intimate association with RER cisternae and lipid droplets, an increased number of peroxisomes, RER fractionation, dilation, vesiculation and transformation into concentric membrane whorls, and elevated amounts of SER tubules. Rare observations were crystal-like inclusions in dilated RER cisternae.
ULTRASTUCTURE OF ISOLATED HEPATOCYTES EXPOSED TO 0.1 mg LITRE MALACHITE GREEN
Effects described for 0.01 mg litre malachite green were enhanced after exposure to 0.1 mg/litre. Most effects could be observed earlier. Thus, the reaction of isolated rainbow trout hepatocytes proved to be time and dose dependent. Additional effects at 0.1 mg litre comprised: - after day 1: increased amounts of lysosomes, vesiculation and decreased amounts of RER cisternae; - after day 5: increased heterogeneity of mitochondria size and morphology. Closer association of RER cisternae with mitochondria and formation of glycogen bodies.
ULTRASTUCTURE OF ISOLATED HEPATOCYTES EXPOSED TO 1 mg LITRE MALACHITE GREEN
At 1 mg litre malachite green effects were strongest. - After 1 day of exposure: the amount of RER was slightly decreased and numerous RER cisternae were transformed into concentric membrane whorls. Mitochondria were highly heterogeneous in shape and size, and the amount of peroxisomes and lysosomel elements (lysosomes, mvelinated bodies, vacuoles) was further increased. Glycogen fields were restricted to small areas and occasional glycogenosomes could be detected as early as day 1. - After prolonged exposure: increased amounts of lysosomes (day 3), myelinated bodies (day 5) and cytoplasmic vacuoles (day 5) were detected. Also, dilation and vesiculation of RER cistern were intensified after day 5
Applicant's summary and conclusion
- Conclusions:
- In vitro data provided evidence for nuclei and mitochondria as the major cellular targets of Malachite Green in both fish and mammals.
- Executive summary:
The fish therapeutic dye malachite green was tested or sublethal cytotoxic effects it concentrations of 0, 0.01, 0.1 and 1 mg/litre. Isolated hepatocytes of rainbow trout were used to evaluate its cytotoxicity in a subcellular system and compare in vitro effects with those of in vivo experiments. Whereas conventional ability tests [trypan blue exclusion, lactate dehydrogenase (LDH) release] failed to detect any acute toxic effect by Malachite Green exposure. Electron microscopy revealed time and dose dependent responses of isolated hepatocytes with first reactions after 1 -day exposure to 0.01 mg/litre. Whereas hepatocellular nuclei took a more irregular shape, cytoplasmic changes comprised an increase in heterogeneity of mitochondrial shape. Closer association of mitochondria with cisternae of the rough endoplasmic reticulum (RER), fractionation, dilation and vesiculation of RER. Formation of cytoplasmic membrane 0whorls glycogen bodies and induction of myelinated bodies and cytoplasmic vacuoles. In agreement with conclusions drawn from in vivo experiments, in vitro data provided evidence for nuclei and mitochondria as the major cellular targets of Malachite Green in both fish and mammals.
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