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A systems approach such as outlined by Phenicie and Lyons (1973) should <br />be used to effectively establish priorities for the research and management <br />of threatened and endangered species. This type of systematic step-down <br />approach provides a mechanism for making the best use of the manpower and <br />budget constraints that face all conservation agencies. Earlier I stated <br />that the U.S. Fish and Wildlife Service has officially listed 172 species <br />as endangered and 11 species as threatened in the United States. In addition, <br />nearly 2,000 other species are being reviewed as candidates for listing. <br />Therefore, establishing realistic research and management priorites by spe- <br />cies will be imperative since the knowledge, time, politics, and available <br />funds required to save all threatened and endangered species will not be <br />adequate. It will also require effective cooperation and communication <br />among the recovery teams, state agencies, and federal agencies that are re- <br />sponsible for endangered species. <br />Pister (1976) summarized the future of wildlife management by rewriting <br />Leopold's prediction as follows: "Unless and until the common task of <br />teaching the public how to modify economic activities for conservation pur- <br />poses is accomplished, whatever else we might do in the management of fish <br />and wildlife resources is in the long run irrelevant." <br />Potential of Threatened and Endangered Species forFisher Management. <br />Behnke and Zarn 1976 pointed out that the idea of promoting angling for <br />a rare species may appear contradictory to the goal of increasing its <br />abundance. However, they also stated that certain subspecies of trout have <br />not become rare through overfishing and that, if they are re-established in <br />waters within their native range, and reproduce naturally, they may provide <br />unique, quality fisheries at almost no expense. Although some trout popu- <br />lations such as cutthroat trout (Salmo clarki) may not show any apparent <br />morphological differences, these populations (i.e., subspecies) may contain <br />the genetic diversity that controls physiological and behavioral character- <br />istics with a significant potential for management (Behnke, 1972). Depend- <br />ing on the species, some special regulations may be necessary to sustain <br />the populations. <br />Miller (1963) believed that the Colorado squawfish could become eagerly <br />sought by sportsmen, because the average size of the squawfish is larger <br />than most trout and, if the philosopy of fishing for fun rather than harvest <br />were encouraged, this native minnow could provide many hours of angling. He <br />cited an example of a university professor who found a greater challenge in <br />catching small darters and sculpins on artificial flies than in catching <br />trout. He further emphasized that the Europeans eagerly seek carp (Cyprinus <br />carpio) and other native species that are harvested for food or returned to <br />the water. Last fall, at a Resources for the Future Forum in Albuquerque, <br />New Mexico, Robert J. Behnke supported the contention of Miller (1963) when <br />he pointed out that one way to save a threatened or endangered species would <br />be to develop a sport fishery for it that generated economy. He also believ- <br />ed that anglers might seek the opportunity to catch and release Colorado <br />squawfish if this species were given proper publicity as a unique species <br />in the biological heritage of the United States. <br />In the future, agencies may have to manage all species that possess some <br />9