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Last modified
7/14/2009 5:01:47 PM
Creation date
5/22/2009 12:32:07 PM
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UCREFRP
UCREFRP Catalog Number
8210
Author
Dodge, D. P. and C. C. Mack.
Title
20
USFW Year
1994.
USFW - Doc Type
Direct Control of Fauna
Copyright Material
YES
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iy <br />KS <br />ie <br />es <br />ig <br />ys <br />3y <br />:k <br />al <br />e, <br />ut <br />c- <br />io <br />le <br />is <br />z. <br />~n <br />~e <br />it <br />s, <br />~o <br />~s <br />~r <br />-g <br />is <br />ae <br />es <br />;n <br />~s <br />le <br />c- <br />~s <br />es <br />~r- <br />es <br />c- <br />or <br />:n <br />es <br />is <br />D~~rect Control of Fauna <br />of fish species was to maintain or increase yields <br />and harvests. Some introductions met this pur- <br />posebut others may have compromised long-term <br />sustainable harvests, in part by altering the <br />aquatic environment and competing with native <br />species. The short-term benefits have .increased <br />the fish protein supply in these countries but <br />more reseazch and assessment aze necessary to <br />understand how introductions serve the reaching <br />of long-term objectives (Ogutu-Ohwayo 8t Hecky <br />1'991 ~. Holcik (1991 ] identified at least 134 fish <br />species that had been introduced or relocated <br />within 29 European countries, especially Central <br />and Eastern Europe. He noted that poor success <br />was recorded for most cases, as well as measurable <br />ill-effects on native fish and their habitat. <br />For further reading, especially for analyses <br />about the implications to fish genc;tics and <br />aquaculture from introductions, the publication <br />by Billington and Hebert (1991) is an excellent <br />reference. <br />It is imperative that fisheries managers use <br />some disciplined decision-making when con- <br />sidering introductions as a means to re-establish <br />a fishery. One approach applied by the. Province <br />of Ontario (Canada) as a procedure to evaluate <br />proposals to stock species beyond their current <br />range in Ontario waters is a sequential decision <br />model adapted from Kohler and Stanley (1984]. <br />Using this model, the decision process continues <br />until the fast `REJECT' decision is reached. <br />Successful completion of the decision model <br />would lead to a decision to approve the stocking <br />(see also Fig. 20.1]. <br />1 (aj Are reasons for introduction valid (includ- <br />ingdemonstrated need which cannot be met by <br />other management actions[? [No-REJECT] <br />(bj Would adequate precautions be taken to <br />safeguard against introduction of disease and <br />parasites? ]No-REJECT] <br />2 (aj Would the species be able to survive in the <br />range of habitats that would be available? [No <br />-REJECT] <br />3 (aj Would the species have adverse ecological <br />impacts? [Yes- REJECT] <br />(bj Would the species potentially be hazazdous <br />to humans? (Yes- REJECT] <br />(c) Is the species endangered, threatened or <br />rare in its native range? (Yes-- REJECT] <br />389 <br />Unless: <br />(i) purpose is to create a refuge, to prevent <br />species extinction, and/or <br />(iij source of fish is a hatchery stock or na- <br />turalized population(s) which is (are] not <br />threatened in any fashion. <br />(aj Was database adequate to develop a com- <br />plete species synopsis? [No-FURTHER <br />RESEARCH] <br />Based on all available information, do the ben- <br />efits of the fish introduction outweigh the risks? <br />(No-REJECT; Yes- APPROVE; Unclear <br />- FURTHER RESEARCH] <br />Hatchery-dependent fisheries <br />Stocking is also used to provide a fishery in water <br />bodies where natural reproduction cannot occur. <br />These hatchery-dependent fisheries often provide <br />important social and economic benefits, and the <br />lack of natural reproduction may actually be ben- <br />eficial since it may limit the damage caused by <br />bad stocking decisions. <br />However, hatchery-dependent fisheries have <br />often been used without adequate consideration <br />of biological, social or economic implications. <br />For example, the adaptability of introduced <br />species to reproduce naturally in water bodies <br />where they `couldn't' has tested the credibility of <br />many respected fisheries biologists. An example <br />of casual approaches to a potential disaster is the <br />treatment of the spread of the wide-ranging <br />cyprinid, the rudd (Scardinius erythrophthalmus), <br />throughout North America. Although the species <br />arrived in the USA in 1916 (Cahn 1927], Courtenay <br />et al [ 1986) considered the species as part of a <br />group of non-native fish whose populations were <br />in decline, as if there were unlikely now to be any <br />effects. However, the rudd was being cultured in <br />ponds in central USA and distributed extensively <br />to anglers, who preferred it as bait to catch bass. <br />Now Burkhead and Williams (1991) report that <br />the rudd has interbred with the native cyprinid <br />golden shiner (Notemigonus crysoleucas] to pro- <br />duce the first non-salmonid intergenic hybrid in <br />North America. The potential effects on any fish <br />community where golden shiner is the major <br />forage species may be horrific; the loss of the <br />genetic pool called golden shiner is immoral. <br />
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