Inhibition of human glutathione S-transferases by basic triphenylmethane dyes

Effects of Malachite Green on the Microbiomes of Milkfish Culture Ponds

Intensive fish farming through aquaculture is vulnerable to infectious diseases that can increase fish mortality and damage the productivity of aquaculture farms. To prevent infectious diseases, malachite green (MG) has been applied as a veterinary drug for various microbial infections in aquaculture settings worldwide. However, little is known regarding the consequences of MG and MG-degrading bacteria (MGDB) on microbial communities in milkfish culture ponds (MCPs). In this study, small MCPs were used as a model system to determine the effects of MG on the microbial communities in MCPs. The addition of MG led to cyanobacterial blooms in the small MCP. The addition of MGDB could not completely reverse the effects of MG on microbial communities. Cyanobacterial blooms were not prevented. Microbial communities analyzed by next generation sequencing revealed that cyanobacterial blooms may be due to increase of nitrogen cycle (including nitrogen fixation, nitrate reduction and anammox) associated microbial communities, which raised the levels of ammonium in the water of the small MCP. The communities of anoxygenic phototrophic bacteria (beneficial for aquaculture and aquatic ecosystems) decreased after the addition of MG. The results of this investigation provide valuable insights into the effects of MG in aquaculture and the difficulties of bioremediation for aquatic environments polluted by MG.

Triphenylmethane dye activation of beta-arrestin

β-Arrestins regulate G protein-coupled receptor signaling as competitive inhibitors and protein adaptors. Low molecular weight biased ligands that bind receptors and discriminate between the G protein dependent arm and β-arrestin, clathrin-associated arm of receptor signaling are considered therapeutically valuable as a result of this distinctive pharmacological behavior. Other than receptor agonists, compounds that activate β-arrestins are not available. We show that within minutes of exposure to the cationic triphenylmethane dyes malachite green and brilliant green, tissue culture cells recruit β-arrestins to clathrin scaffolds in a receptor-activation independent manner. In the presence of these compounds, G protein signaling is inhibited, ERK and GSK3β signaling are preserved, and the recruitment of the beta2-adaptin, AP2 adaptor complex to clathrin as well as transferrin internalization is reduced. Moreover, malachite green binds β-arrestin2-GFP coated immunotrap beads relative to GFP only coated beads. Triphenylmethane dyes are FDA approved for topical use on newborns as components of triple-dye preparations and are not approved but used effectively as aqueous antibiotics in fish husbandry. As possible carcinogens, their chronic ingestion in food preparations, particularly through farmed fish, is discouraged in the U.S. and Europe. Our results indicate triphenylmethane dyes as a result of novel pharmacology may have additional roles as β-arrestin/clathrin pathway signaling modulators in both pharmacology research and clinical therapy.

Effects of malachite green (MG) and its major metabolite, leucomalachite green (LMG), in two human cell lines

Malachite green (MG) is still illegally used as a fungicide in aquaculture. In fish it is absorbed and metabolised to its major reduced metabolite, leucomalachite green (LMG). This latter represents the main residue found in fish tissues and may persist for several months. Since MG, suspected to act as a tumour promoter in vitro and in vivo, might be also present as a residue in fish, the present study was undertaken to ascertain the in vitro toxicity of both compounds in two human tumour cell lines (Caco-2 and HEp-2). After 24h incubation with MG, significant decreases of cell viability, measured by neutral red uptake (NRU) or total protein content (TPC) as well as proliferation capability (colony-forming ability, CFA) were noticed in HEp-2 cells; the mean IC(50) value was about 2 microM. As regards the differentiated Caco-2 cells, MG caused a dose-related significant cytotoxicity, measured either by MTT test, the LDH leakage or NRU, with a mean IC(50) value of about 15 microM. By contrast, LMG disclosed, in both cell lines, a lower cytotoxicity compared to MG. These results also show that HEp-2 cells are more sensitive than intestinal cells to the toxic action of both compounds.

Mutagenicity of malachite green and leucomalachite green in in vitro tests

The genotoxic potential of the fungicide malachite green (MG) and its reduced derivative leucomalachite green (LMG) was assessed in bacteria and mammalian cells using the standard Salmonella typhimurium/Ames and CHO/HGPRT tests. In vitro potential DNA damaging effects of MG and LMG were tested using the single-cell gel electrophoresis (Comet) assay on CHO cells. Malachite green was found to be extremely cytotoxic to bacteria and mammalian cells. It did not have any mutagenic activity, in any bacterial strains, in the presence or absence of metabolic activation for doses up to 10 microg per plate. In the CHO/HGPRT test, the mutagenic potential of MG could be evaluated only for very low concentrations ranging from 0.001 to 0.05 microg ml(-1) medium. When S9 fraction was added to the medium, the highest tested dose could be increased to 1 microg ml(-1). In these experimental conditions, MG did not increase the number of thioguanine-resistant mutants. Leucomalachite green was less toxic than MG to Salmonella typhimurium and did not have mutagenic activity in the Ames' test for doses up to 2000 microg per plate. It was also less cytotoxic than MG to CHO cells and was tested at doses ranging from 5 to 100 microg ml(-1). Overall results indicated that LMG was not mutagenic in the HGPRT test. In the Comet assay, MG induced DNA damage only at cytotoxic doses. Loss of cell viability was observed for doses of > or = 3 microg ml(-1), with parallel increase in DNA alterations as measured by the tail moment. After metabolic activation, however, DNA damage was observed at doses (15-20 microg ml(-1)) inducing only low cytotoxicity. In this case, the direct genotoxicity of MG metabolites could not be excluded. In the absence or presence of metabolic activation, LMG did not have any effect on cell viability or DNA damage for doses up to 500 microg ml(-1). This study indicates that LMG, which is the main residue found in fish tissues after treatment with MG, did not have any mutagenic or clastogenic effects in the experimental conditions used.