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ce <br />8) <br />n- <br />~e <br />ie <br />~e <br />a- <br />i ). <br />ry <br />:n <br />b- <br />of <br />1- <br />~d <br />n <br />a, <br />r <br />•s <br />i- <br />Y <br />;t <br />.r <br />Direct Control of Fauna <br />hazard that comes with intentional use of <br />hatchery fish from inappropriate gene pools. In <br />Norwegian rivers, farmed Atlantic salmon (Salmo <br />salQr) are threatening native fish through cross- <br />breeding of wild with farmed fish, with the sub- <br />sequent risk of losing genetic material essential <br />for the survival of local populations (Gausen & <br />Moen 1991 ~. The river catchment manager must <br />always be awaze of this kind of threat. <br />The dangers inherent in introductions are <br />further enhanced by the blind faith put in recent <br />genetic 'breakthroughs' where managers were <br />made to believe large populations of desexed fish <br />established by stocking would never produce off- <br />spring. An excellent example of this fallacious <br />assumption was the release of reportedly sterile) <br />grass carp (Ctenopharyngodon idella) into the <br />Mississippi River and the subsequent colonization <br />of the system as naturally-reproduced popu- <br />lations established rapidly (Brown & Coon 1991), <br />all of this despite caution advised by scientists <br />well-placed to predict ecological disasters. <br />Effect of environmental contaminants <br />Residues of persistent, toxic substances that bio- <br />accumulate have been linked to the reproductive <br />failures of wildlife (e.g. bald eagle Haliaeetus <br />leucocephalus) and fish (e.g. lake trout Salvelinus <br />naymaycush). Obviously the body burden carried <br />by any hatchery fish and the potential to accumu- <br />late more in the environment into which it has <br />been introduced must be considered as factors <br />affecting the overall success of fish survival and <br />growth. It is possible that mega fish stocking pro- <br />grammes will fail to re-establish self-sustaining <br />fish populations in rivers because of uncontrolled <br />toxic effluents and high concentrations of con- <br />taminated sediment (Gilbertson 1992). <br />One pertinent criterion often ignored by man- <br />agers is whether or not the species chosen for a <br />river fish culture programme has the properisity <br />to accumulate persistent toxic substances that <br />may threaten human health. Notwithstanding <br />any effects that biomagnified toxic body burdens <br />may have on the general health of the carriers and <br />on the specific reproductability of mature fish, <br />there is the fundamental issue of effects from <br />toxic substances in fish on humans, especially <br />397 <br />women and children. Swain (1988) identified sig- <br />nificantly damaging effects on maternal health <br />and showed the risks associated with trans- <br />placental transmission to infants in utero and for <br />nursing infants. <br />20.4 ROLE OF REGULATIONS <br />Regulations are an important mechanism for <br />controlling risks to native fish communities <br />which may result from stocking-related activities. <br />Regulations can be used directly to control the <br />choice of species or strains used for stocking, <br />including the use of exotics, or to prevent the <br />introduction or spread of serious fish disease <br />agents. <br />Indirectly, regulations play a major role in con- <br />tributing to the success of a stocking programme. <br />Fishing seasons and access can be controlled to <br />protect stocked fish when they are most vulner- <br />able, such as at the stocking site, or in the case <br />where anadromous species aze stocked in a river <br />as pre-smolts, prior to their movement down- <br />stream to a lacustrine environment. More funda- <br />mental regulations controlling exploitation can <br />be used to eliminate the need for starting a stock- <br />ing programme. <br />Regulations are needed to provide protection at <br />continental, regional or local levels. Man-made <br />boundaries ~i.e. national, territorial or local govern- <br />ment) are the main mechanism used to develop, <br />implement and enforce regulations. The fact that <br />fish do not recognize man-made boundaries poses <br />a major challenge to the effectiveness of regula- <br />tions. For this reason, international commissions <br />such as the North Atlantic Salmon Conservation <br />Organization, EIFAC and the Great Lakes Fishery <br />Commission play an important role in developing <br />international agreements and co-ordinated <br />strategies which assist in managing large <br />watersheds. <br />National or territorial controls provide the ma- <br />jor framework for implementing legislation, re- <br />gulations and policy. These controls are often <br />easier to enforce, because they aze based on clearly <br />defined boundaries. Territorial legislation can be <br />used as the basis for regulations which control at <br />the local level, such as specifying the location of <br />fish sanctuaries. <br />