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<br />3.0 Scientific Basis And Underlying Principles <br /> <br />3-16 <br /> <br />April 2004 <br /> <br />3.7.5 Reconnection Of Floodplain To Main Channel <br /> <br />Reconnection of a floodplain to the main river channel is critical to completion of the <br />"reset theory" cycle of inundation and desiccation. Reconnection allows the 1 or 2-year old <br />razorback sucker to escape to the river where they can mature and reproduce. Observations of <br />hatchery razorback sucker indicate that age-l fish will not leave a floodplain during reconnection <br />(Personal Communication, Tim Modde, U.S. Fish and Wildlife Service; Kevin Christopherson, <br />Utah Division of Wildlife Resources). Similar observations have been made for fish 1 to 2 years <br />of age, although these conclusions are preliminary. These observations indicate that young <br />razorback sucker will remain in sheltered floodplains through their first 1-2 years of life, which <br />is consistent with the floodplain management strategy fundamental to this Plan. <br /> <br />Recent studies of hatchery razorback sucker released in floodplains also show that <br />survival in floodplains in the first month is low (<5%), but little or no survival is presumed in the <br />main river channel (Christopherson and Birchell2002; Birchell and Christopherson 2002). <br />Survival in floodplains after the first month is greatly increased, but it is believed that razorback <br />sucker must be over about 90 mm TL (about 6 months old at low growth rate) and preferably <br />over 230 mm TL (about 17 months old at low growth rate) to survive in the main channel. Fish <br />entrained in a floodplain depression that do not escape to the main channel during a flow <br />connection will become stranded until the following runoff cycle. Given that floodplain <br />connections during spring runoff are typically less than 1 week, the best survival strategy for <br />razorback sucker is believed to be a 24-month residence in a productive floodplain that allows <br />the fish to reach sufficient size for mainstem survival and to escape predators. Until self- <br />sustaining populations become established and multiple spawning sites and floodplains are used <br />by wild fish, it may be necessary to manually transfer fish from floodplains to the main channel <br />when river flows are insufficient to connect floodplains and fish are old enough for mainstem <br />survival. <br /> <br />Levee breaches at key floodplains will increase the frequency of connection with the <br />mainstem and inundation in all but dry and moderately dry years. The hydrologic cycle of the <br />Green River Subbasin typically consists of periods of 3-5 years of wet and moderately wet years <br />followed by periods of dry and moderately dry years (Muth et al. 2000). The "reset theory" is <br />based on this hydrologic cycle in which connection of most floodplains occurs annually in wet <br />years and desiccation (i.e., reset) occurs in intervening dry years. This cycle will also occur in <br />average years with fewer floodplain sites expected to be connected annually. This strategy also <br />recognizes that magnitude, duration, and possibly frequency of inundation will vary among <br />floodplain sites with river stage, and emphasizes the importance of all sites for overall recovery <br />of the endangered fish species. <br /> <br />3.7.6 Desiccation To Reset Floodplain <br /> <br />The key to the "reset theory" is periodic desiccation of the floodplain to reset or kill all <br />remaining fish and reset productivity. Ideally, floodplains should desiccate every fourth year to <br />