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Abstract <br />Floodplain wetlands in the Colorado River system may serve as essential rearing and feeding areas <br />for some native species, including the endangered razorback sucker and Colorado squawfish. <br />Because channel and floodplain complexity have been reduced over the past 100 years by dam <br />construction, flood control and riparian vegetational changes, the Recovery Implementation <br />Program intends on restoring some floodplain function via levee removal. A concern with levee <br />removal is the response of nonnative fishes. Many of the nonnative fishes in the Colorado River <br />system are known to inhabit littoral or lentic habitats, consequently, levee removal may benefit <br />nonnnative fishes more than native fishes. The overall strategy for the levee removal program is <br />to remove levees (starting in the Green River system) from selected wetlands on a sequential <br />temporal and spatial scale so the response of native and nonnative fish populations can be <br />carefully evaluated. The design is based on selecting sites over a large spatial scale with the <br />following criteria: 1) Geographic location (above and below Desolation/Gray Canyons, Block 1 <br />and 2), 2) High versus low nonnative densities, 3) Depression versus terrace floodplain wetlands, <br />and 4) Natural (sites that naturally inundate during high water years) versus application sites (sites <br />where levees will be removed or breached). These criteria were used to develop a block design <br />selection process for analysis purposes. Levees will not be removed in 1996, however, the <br />methods for future levee removal activities, including sampling gear and sampling protocols, will <br />be determined by the 1996 activities. In 1996, 12 naturally inundated sites should be monitored <br />(6 in Block 1 and 6 in Block 2) for baseline data. The 1997 levee removal block design consists <br />of selection of 10 application sites and 10 natural sites, above versus below Desolation/Gray <br />Canyons. Two treatments will occur within each block. These are nonnative density and <br />floodplain wetland type. Each treatment has two levels: high versus low nonnative densities and <br />depression versus terrace habitats. Naturally flooded areas will be used to contrast responses in <br />levee removal sites. Besides measuring the response of the fish community, macroinvertebrates, <br />physical parameters and vegetation responses willbe documented in order to obtain a complete <br />understanding of Colorado River wetland ecology. Macroinvertebrate production will be higher <br />in floodplain wetlands than in the river channel, consequently, growth and possibly survivorship of <br />fishes in floodplain wetlands may increase. The riparian vegetation and macrophyte community <br />may change following levee removal. This shift could affect predator/prey interactions and food <br />production. All of these questions need to be answered to determine what benefits levee removal <br />will have for the endangered fishes. Following the initial year of levee removal evaluation, at least <br />two additional years (1998-1999) of evaluation should follow.