Chromatographic behaviour and determination of orellanine, a toxin from the mushroom Cortinarius orellanus.
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Biomedical subjects
Publications and source records attributed to D Cantin.
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Pure orellanine extracted from the mushroom Cortinarius orellanus is highly toxic in mice both when given intraperitoneally (LD50 = 12.5 mg/kg) or per os (LD50 = 90 mg/kg). The kidneys of mice injected i.p. with orellanine show similar tubular necrosis to that obtained with whole mushroom given per os. This demonstrates that orellanine is the true, principal toxin of C. orellanus. The similarity of the structures of the toxin and of bipyridinium herbicides such as methylviologen (paraquat) or the nephrotoxic diquat led other authors to presume a similar mechanism for orellanine toxicity. Our study of the electrochemical behaviour of orellanine shows that its mechanism of action has to be different from that of these poisons.
Orellanine, a toxic principle of Cortinarius orellanus Fr., efficiently inhibited the photosynthetic activity of duckweed, Lemna minor L., at a concentration of 0.4 mM. A lower concentration (0.06 mM) blocked the O2 production in isolated spinach class A chloroplasts. However, no effect was observed on thylakoids (class C chloroplasts), showing that orellanine does not interfere with the chloroplastic electron transfer chain and that orellanine does not act like methylviologen (paraquat) in green plants, as previously suggested. An electrochemical study of orellanine and related compounds showed that orellanine can neither be reduced by electrons derived from H2O nor from NADPH, as is methylviologen in plant and animal cells, respectively.
Amino-2 Benzimidazole, a residue of the decomposition of some fungicides (Benomyl, Carbendazine, Thiophanate, Methylthiophanate), is measured by polarography in aqueous medium, with a platinium rotating electrode, for the exploration in potentials from +0.5 v to 1.4 v. The best conditions for the quantitative determination are investigated, the study according to pH is performed and the standard curve is given for concentrations from 10(-5) to 10(-3) M/l. The interaction of elementts found in tap water and in aquarium water is also investigated.
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