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<br /> <br />State and Federal agencies in the United States have legislative commitments under the Endangered Species Act; <br />ho~ever, political and environmental issues regarding restoration are often poorly defined, complex, and <br />controversial, especially if they threaten further land or water development. Administrative processes within <br />recovery programs are often plagued with inaction justified by uncertainty, inadequate resources and conflicting <br />management objectives, leading to slow or ineffective recovery programs (Rohlf 1991, Tear et al. 1993). The <br />ramifications are that short-lived species disappear and longer-lived species like the razorback sucker become <br />fleeting reminders of ecosystem dismantlement. <br /> <br />Deacon and Minckley (1991) pointed out that technology and resources are normally available to sustain or <br />replace endangered populations. The critical question is whether the affected agencies have the political <br />conviction to do so. We found that agencies and special interest groups support an active endangered species <br />program as long as the effort does not unreasonably conflict with their management objectives. Any major <br />conflict would demand formal coordination, consultation, and, most importantly, time necessary for resolution. <br />Quite often the restoration programs get tied up in litigation between government agencies and special interest <br />groups. Limited resources are diverted toward litigation and political positioning while environmental resources <br />continue to decline. <br /> <br />At Lake Mohave, we recognized that time and conflict were our greatest enemies. The old, relict population was <br />near extinction. We concluded our best chance to implement a restoration project was through an active stocking <br />and continued management program. We were confident that stocking 30-cm razorback suckers was feasible, <br />but we had to identify where, by whom, and how these fish were going to be raised. No one agency volunteered <br />the funds or facilities, so it became a cooperative effort. The program that evolved from the NFWG capitalized <br />on available resources and opportunities. Mitochondrial DNA studies have shown the reservoir population is <br />composed of direct descendants of a very large, diverse population that inhabited the river prior to impoundment <br />(Dowling et al. 1996). By collecting naturally-spawned sucker larvae, we are maintaining the genetic diversity <br />of this wild population. Rearing fish in local backwaters is an economical alternative to more costly hatchery <br />production. It also reduces transportation costs while acclimating fish to local conditions. This stocking approach <br />is working and is being adopted at other locations. <br /> <br />Engineering can create artificial streams and repair or duplicate some of the physical hydraulic processes required <br />in a healthy stream system. Biologists, on the other hand, can stock and manage specific fish populations. <br />However, we are less able to repair, let alone fully understand, the complex interactions associated with large river <br />ecosystems. While legislation may mandate recovery or restoration, attempts may, or may not, be feasible <br />depending upon economic, political, or technical constraints (Johnson 1977, Wydoski 1977). It therefore seems <br />logical that resource managers should first attempt to salvage and prevent the further loss of plant, animal, or fish <br />communities. Large-scale attempts to restore natural ecosystems have generally been unsuccessful. <br />Consideration must be given to more proactive, conservation management approaches and philosophies to <br />prevent the continued loss of these populations and ecosystem components (Miller 1982). Ten or fifteen-year <br />restoration programs in themselves are simply inadequate. Preservation, maintenance, or restoration of river <br />ecosystems will require a continued management commitment from society. <br /> <br />REFERENCES <br /> <br />Brooks, J.E. et. al.(1985) : Reintroduction and monitoring of razorback sucker In the lower Colorado River <br />basin. Pre. WDAFS 65, pp203. <br />Burdick, B.D.(l992) : A plan to evaluate stocking to augment or restore razorback sucker in the upper <br />Colorado River. USFWS, CRFP, Grand Junction, Colorado, USA. <br />