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' of the lack of the right sizes of food organisms at the right time and in <br />sufficient quantity (Wydoski and Wick 1994). <br />Flooded bottomland habitats occur in broad valleys along low gradient <br />stream reaches. Bottomlands are off- or out-of-channel habitats that include <br />' oxbow lakes, former side channels in broad valley floodplains, ponds, and wetland <br />depressions. During high flow events, some of these off-channel features were <br />temporarily connected to the river. Re-establishing connectivity to the mainstem <br />river may provide off-channel habitats for endangered fishes which are essential <br />' for effective management of the riverine ecosystem and recovery of endangered <br />fishes. Former natural riverine features could be integrated back into the <br />historic floodplain by removing portions of man-made dikes or natural <br />' obstructions (e.g., gravel/sand bars). <br />Protection, restoration, and enhancement of inundated bottomland habitat <br />t along mainstem riparian corridors are believed to be important for recovery of <br />razorback sucker. Riparian enhancement in the upper Colorado River basin can be <br />accomplished by providing sufficient flow to inundate bottomlands in a manner <br />that approximates the natural hydrograph. If sufficient flows cannot be obtained <br />' regularly, dikes and levees should be breached at intervals to allow inundation <br />of lowlands during the spring high flow period. To reconnect floodplain habitat <br />where existing dikes occur, "set-back" dikes may have to be constructed to <br />' protect private property in bottomlands near population centers and agricultural <br />areas. Local government entities may resist removal of structures that have been <br />built, maintained, and reinforced after major flood events to protect private as <br />well as public property. Therefore, institutional and social constraints may <br />' limit the amount of floodplain that can be reclaimed near population centers. <br />The river reach adjacent to the Escalante State Wildlife Area (SWA) is <br />t important historical habitat for the razorback sucker and Colorado squawfish. <br />The area has been identified as occupied habitat and recently was designated <br />critical habitat for both razorback sucker and Colorado squawfish by the U. S. <br />' Fish and Wildlife Service ([USFWS] effective 20 April 1994; Federal Register, <br />Vol. 59, No. 54, 21 March 1994) under authority of the Endangered Species Act <br />(USFWS 1973). This system formerly contained substantial numbers of razorback <br />suckers downstream from the Black Canyon of the Gunnison but now contains no or <br />' few razorback sucker. In 1889, Jordan (1891) reported that razorback sucker were <br />very abundant in the rivers of the upper Colorado system, including both the <br />Gunnison and Uncompahgre rivers near Delta, Colorado. Chamberlain (1946) noted <br />' razorback sucker were common in the lower Gunnison River between Delta and Grand <br />Junction. However, the number of razorback sucker began to decline in the <br />Gunnison River near Delta in the 1950's (Quartarone 1993). The capture of four <br />t adult razorback sucker in the Delta area in 1981 was the last documented report <br />in the Gunnison River (Holden et al. 1981). The razorback sucker now appears to <br />be extirpated from the Gunnison River upstream from the Redlands Diversion Dam. <br />1 Ob.iectives/PurDOse <br />' Habitat development and enhancement is identified as one of the five <br />principal elements of the Recovery Program (USFWS 1987). The general objectives <br />of this plan are, 1) to restore razorback sucker and other endangered fishes in <br /> <br />