Laserfiche WebLink
In the proximate sense, populations of razorback suckers have declined because <br />recruitment has been insufficient to maintain population numbers. Some reduction in <br />recruitment is attributable to alterations to the physical habitat, or reduced access to <br />suitable habitat. But even with major modifications to physical conditions, razorback <br />suckers continue to spawn in riverine and lacustrine habitats. A number of investigators <br />have collected viable embryos and/or larvae in areas where razorback suckers have <br />been observed spawning (Bozek et al. 1984, Medel-Ulmer 1983, Marsh and Langhorst <br />1988, Tyus 1987, Mueller 1989), but few have collected larvae larger than 14 mm. <br />Many small larvae are collected in certain areas (e.g. Lake Mojave), but the small <br />number of larger larvae and juveniles suggests that recruitment is curtailed at this point. <br />The failure of adequate recruitment is largely attributable to predation by nonnative <br />fishes (Minckley et al. 1991, Johnson et al. 1993, Tyus and Saunders 1996). <br />Razorback suckers now exist in areas where the populations are geographically <br />isolated. With the possible exception of the population in Lake Mojave, all razorback <br />sucker populations are small. Small, isolated populations (isolates) are very <br />susceptible to "faunal collapse," a phenomenon that has been observed when such <br />isolates are invaded by nonnative species (Wilcox 1980, Frankel and Soule 1981). <br />Increasing fragmentation of the Colorado River system presents problems that are <br />presumably very similar to those observed in isolates elsewhere, where declining <br />habitat diversity and introduction of new predators are main reasons for declines of <br />native species (e.g., see Frankel and Soule 1981). Thus, the impact of nonnative <br />fishes is considered a significant detriment to isolates of a once larger Colorado River <br />native fish community (reviewed by Tyus and Saunders, 1996). <br />Conservation and Recovery <br />Recovery Planning <br />Recovery plans, written under the authority of Section 4 of the Endangered Species <br />Act, guide recovery activities. A recovery plan promotes conservation and provides the <br />steps required for delisting species. In addition, a recovery plan provides guidance for <br />implementing recovery actions and establishes priorities for those actions. <br />The Act incorporates several measures to promote conservation of listed species, <br />making the conservation of endangered species a high priority of Federal agencies <br />(Section 2). The act also aids recovery by identifying the status of a species by listing <br />and identification of critical habitat (Section 4), providing Federal grants to States <br />(Section 6), requiring Federal agencies to engage in conservation activities (Section 7), <br />prohibiting the unauthorized take of listed species (Section 9), requiring permits to <br />enhance survival of listed species (Section 10), and other means (e.g., research, land <br />acquisition, etc.). All of these measures are brought into action by recovery planning, <br />and the completion of recovery plans. <br />24 <br />