Lusková V., M. Svoboda, J. Koláfiová: The Effect of Diazinon on Blood Plasma Biochemistry in Carp (Cyprinus carpio L.). Acta Vet. Brno 2002, 71: 117-123.The aim of this study was to evaluate the effect of diazinon [0,0-diethyl-0-(2-isopropyl-6-methylpyrimidin-4yl) phosphorothioate] on common carp (Cyprinus carpio L.). The effect was assessed by comparing the biochemical blood plasma profiles of a control group and a group exposed to the effect of the pesticide Basudin 600 EW (containing 600 g.l -1 diazinon as the toxic substance). The activities of selected enzymes, metabolite concentrations and electrolytes were measured in 15 specimens of controls, K 1-2, and in 16 specimens, K 1-2 , exposed for 96 h to the effects of Basudin 600 EW at a concentration of 32.5 mg.l -1 . Compared with the control group, a significant decrease of cholinesterase (p < 0.01) and lactate dehydrogenase (p < 0.05) was ascertained in the experimental group. The values of alanine and aspartate aminotransferases, creatine kinase, alkaline and acide phosphatases were comparable in the experimental and control groups. The total protein and lactate concentration were significantly lower (p < 0.05) in the experimental group, compared with the control group. On the contrary, glucose concentration in the plasma of the experimental group was significantly higher (p < 0.01) than in that of the control group. The experimental group showed a significantly higher (p < 0.05) concentration of plasmatic natrium and potassium, and a significantly lower (p < 0.05) concentration of plasmatic calcium and phosphorus, compared with those in the control group. The above results of examinations of the biochemical blood plasma profile indicate a marked neurotoxic effect of diazinon in fishes.

The first telemetry study analysing behaviour of the largest freshwater predator in European rivers, Silurus glanis, was performed bimonthly during the years 2002-2004. Movement of juveniles and adults occurred mostly in the same time intervals. The only statistical differences occurred for nocturnal activity in spring and autumn. In spring and winter, activity was low with the peaks during daylight, and in autumn, maximal movement was recorded during dusk. In summer, the European catfish were active across the whole 24 h even during high-flow conditions. During all other seasons, movement was inversely related to flow rate. Maximal home ranges occurred in summer, being larger for adults. Juveniles and adults were spatially segregated. With increasing flow, fish were displaced, and individuals from both groups got closer to each other. Only juveniles migrated downstream from the upstream isolated river stretch suggesting a negative impact of lateral obstructions on the fish population structure.

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