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<br />I <br />I <br />I <br />1< <br />I <br />I <br />I' <br />I' <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />15 <br /> <br />Fishes as a Monitoring Tool <br />The use of fishes as a long-term monitoring tool in riverine systems <br />has only briefly been described in literature. Using fishes as a monitoring <br />tool can be approached on one of two levels; (1) the individual level and <br />(2) the population level. The individual level of monitoring can examine <br />key species or "indicator" organisms in response to a perturbation. This <br />concept has limited application, particularly with fishes, which generally <br />possess wide tolerances to most impacts. It would have little utility in <br />assessing subtle effects. <br />Another approach to the individual level of monitoring involves the <br />physiological responses of individuals to a perturbation. Attempts to <br />examine perturbation impacts on individuals have been made using behavioral <br />locomotor responses (Kleerekoper 1975), respiration rates (Westlake and van <br />der Schalie 1975), and even a measure of acetylcholinesterase activity on <br />the central nervous system to detect sublethal effects of pesticides (Weber <br />1981). In all cases, fish were tested either in the laboratory or in cages <br />held in the field. This is necessary with fishes because their mobility in <br />riverine systems enables them to escape many lethal or sublethal effects. <br />This is expected to be the case in the White River. <br />The population level of monitoring has received more attention and <br />acceptance by fisheries biologists. Gaufin and Tarzwell (1956) showed that <br />little reliance can be placed on mere occurrence of a single species in a <br />given locality as an indicator of a perturbation. In evaluating the <br />reliability of aquatic organisms as indicators of pollution, one must <br />