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Proteomic and phosphoproteomic analysis of cellular responses in medaka fish (Oryzias latipes) following oral gavage with microcystin-LRstar, open.

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Article
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Mezhoud, K. ; Bauchet, Anne-Laure ; Chateau-Joubert, S. ; Praseuth, D. ; Marie, A. ; Francois, J.C. ; Fontaine, J.J. ; Jaeg, J.P. ; Cravedi, J.P. ; Puiseux-Dao, S. ; Edery, M.

TOXICON

USM 505/EA 4105, Département de Régulations, Développement et Diversité Moléculaire, Ecosystèmes et Interactions Toxiques, Muséum National d'Histoire Naturelle, 12 Rue Buffon, F-75231 Paris Cedex 05, France. Département de Pathologie, Ecole Nationale Vétérinaire d' Alfort,next term 7 Avenue du Général de Gaulle, F-94704 Maisons-previous termAlfortnext term Cedex, France. CNRS, UMR 5153; INSERM, U565; USM 503, Département de Régulations, Développement et Diversité Moléculaire, Régulations et Dynamique des Génomes, Muséum National d'Histoire Naturelle, 57 Rue Cuvier, F-75231 Paris Cedex 05, France. Plateforme de Spectrométrie de Masse et de Protéomique, CNRS, UMR 5154, Département de Régulations, Développement et Diversité Moléculaire, Chimie et Biochimie des Substances Naturelles, Muséum National d'Histoire Naturelle, 63 Rue Buffon, F-75231 Paris Cedex 05, France. UMR 1089 Xénobiotiques, INRA Toulouse. 180 Chemin de Tournefeuille, BP3, F-31931 Toulouse Cedex 9, France

2008

Article

Chronic and subchronic toxicity resulting from exposure to microcystins (MCs) receives increasing attention due to the risk of bioaccumulation of these toxins by aquatic animals, including fish. The mechanisms of action of MCs that target the liver, involve modifications of protein phosphorylation resulting from phosphatases 1 and 2A inhibition. Therefore, studying phosphoprotein modifications by using a specific phosphoprotein stain Pro-Q Diamond in fish liver contaminated with MC-leucine-arginine (MC-LR), the most toxic MC, should help dissecting disturbed signaling and metabolic networks. We have recently used this technology to identify several proteins that are modulated either in expression or phosphorylation in the liver of medaka following short-term exposure to MC-LR by balneation. In the present study, we have decided to use an alternative way of introducing the toxin into fish; that is by gavage (force-feeding). This was first achieved using tritiated MC-LR and allowed us to quantify the quantity of toxin incorporated into fish and to demonstrate that the toxin is mainly accumulated in liver. Afterwards a proteomics study limited to liver cytosolic proteins of contaminated animals showed that several proteins were up or down regulated either in quantity or in phosphorylation or both. Some of them had been previously detected as modified in balneation experiments but new molecules were identified as involved in signal transduction pathways activated by the toxin. In addition, in the conditions used (5 ?g toxin/g body weight) anatomopathological studies supported a process of apoptonecrosis established after 24 h, which was suggested to proceed by the evolution of some of the proteins after 2 h contamination.
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