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<br />where levees are breached. Reconnection of breached areas on lowered <br />floodplains could be made without enhancing streamflows that may cause <br />economic losses or social issues. <br /> <br />I <br />I <br /> <br />Depression Ponds. Depression ponds in the floodplain provide habitat <br />where good to excellent growth of larval and juvenile razorback suckers <br />and juvenile Colorado squawfish have been demonstrated (Osmundson and <br />Kaeding 1989). In Humphrey's Pond along the Upper Colorado River, <br />razorback suckers grew from 55 to 307 mm TL (-2 to 12 inches) from June <br />until November, 1987 (Figure 3; Osmundson and Kaeding 1989). This growth <br />is similar to the growth in hatchery ponds. For example, razorback <br />suckers grew from 44 to 255 mm TL (- 2 to 10 inches) from April until <br />October, 1993 in Wahweap State Fish Hatchery (Lake Powell), Utah (Figure <br />3). Twenty-eight Age-O razorback suckers from Old Charley Wash along the <br />Middle Green River averaged 94 mm TL (- 4 inches) in September and <br />October, 1995 (Modde 1997). Forty-five Age-O razorbacks from Old Charley <br />Wash averaged 66 mm TL (- 2.5 inches) in August, 1996. In 1997, 95 <br />juvenile razorback suckers were collected from Old Charley Wash. The <br />razorback suckers collected from Old Charley Wash were survivors of wild <br />larvae that entered the wetland during high spring streamflows. Eleven <br />wild razorback suckers captured in a wetland (Leota Bottom wetland <br />complex along the middle Green River) in 1994 were between 250 and 370 mm <br />TL or -10 and -15 inches (Modde and Wick 1997). These fish were <br />yearlings based on scale analysis and probably entered the wetland in the <br />spring of the previous year when it was filled with Green River water. A <br />large number of mature razorback suckers were found in a gravel-pit pond <br />(Etter's Pond) along the Upper Colorado River in 1990 that apparently <br />gained access to the pond as larvae during the 100-year floods of 1983 <br />and 1984 (F. Pfeifer, 1994, Personal Communication). However, it is also <br />likely that these razorbacks were progeny from the spawning of only a few <br />adult razorback suckers that entered the pond during these floods, based <br />on mtDNA analysis (B. DeMarais and T. Dowling, 1994, personal <br />communication). Razorback suckers from the OUray National Fish Hatchery, <br />Utah, that were surplus to Recovery Program needs, were stocked into golf <br />course ponds at Page, Arizona where they grew from an average length of <br />115 mm TL (- 4 inches) to 383 mm (- 15 inches) between May, 1996 and <br />August, 1997 (Mueller and Wick 1998). Larval razorback suckers stocked <br />into depression ponds along Lake Mohave have exhibited good growth to <br />large sub-adults that are stocked into Lake Mohave (Minckley et al. 1991; <br />Mueller 1995; Mueller et al. 1993). <br /> <br />I <br /> <br />I <br />I <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />If frequency and duration of flooding discussed below cannot be restored, <br />then captive-rearing of razorback suckers in predator-free floodplain <br />depressions may be the only course of action left for maintenance of <br />razorback sucker stocks in the Upper Basin to prevent their extinction. <br /> <br />Reauired Freauency of Floodinq. The frequency of floodplain inundation <br />required for recovery of razorback suckers is unknown. Numerous <br />floodplains have been separated from the rivers for a long time so their <br />potential nutrient levels and productivity are unknown. The flood pulse <br />concept of nutrient cycling (Junk et al. 1989) provides the productivity <br />of present Upper Basin rivers because of fragmentation of river reaches <br />by dams. Therefore, reconnect ion of rivers may be required more often in <br />the future than when the Upper Basin ecosystem was unaltered. <br /> <br />I <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />The river elevation necessary to provide an adequate frequency of <br />inundation of floodplain habitats should initially be made on an annual <br />basis or as often as possible to assist razorback suckers through their <br />"critical period" that, in turn, should increase survival and <br />recruitment. <br /> <br />32 <br /> <br />I <br />J <br />I <br /> <br />I <br />