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Last modified
7/14/2009 5:02:36 PM
Creation date
5/17/2009 11:03:23 PM
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UCREFRP
UCREFRP Catalog Number
9508
Author
Valdez, R. A. and P. Nelson.
Title
Green River Subbasin Floodplain Management Plan.
USFW Year
2004.
USFW - Doc Type
Lakewood, Colorado.
Copyright Material
NO
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<br />4.0 Prioritization Of Reaches And Sites <br /> <br />4-3 <br /> <br />April 2004 <br /> <br />An inventory of existing and potential floodplains during 1993-94 identified 132 sites <br />with a potential of 18,430 acres on 393 miles ofthe mainstem Green River from Flaming Gorge <br />Dam to the confluence of the Upper Colorado River (Irving and Burdick 1995). Of this total, <br />7,720 acres were inundated during the May high flow period (18,200 cfs) and 2,438 acres were <br />inundated in the September low flow period (1,560 cfs). The maj ority of these sites were either <br />shallow depressions (i.e., sites that hold water for a few weeks but fail to hold water year-around) <br />or terraces (i.e., sites that flood and drain with river stage), and inundation may be from ground- <br />water intrusion and not necessarily through surface connection with the river. Based on this <br />inventory, the area of floodplains (and number of sites) in the Split Mountain to Desolation <br />Canyon reach was 11,409 acres (37) at full inundation potential; 6,164 acres (35) at 18,200 cfs; <br />and 1,660 acres (20) at 1,560 cfs (Table 4-1). Area of floodplain inundation in the Labyrinth and <br />Stillwater canyons reach was 2,905 acres (44) at full inundation potential; 121 acres (22) at <br />18,200 cfs; and 5 acres (1) at 1,560 cfs. Area of floodplain inundation in the Gray Canyon to <br />Labyrinth Canyon reach was 1,333 acres (21) at full inundation potential; 18 acres (5) at 18,200 <br />cfs; and 0 acres at 1,560 cfs. <br /> <br />Numbers of razorback sucker larvae potentially entrained in floodplains within each of <br />the three priority reaches were estimated with the Floodplain Model (Valdez 2004) and used as <br />indices of reach importance (Table 4-2, Figure 4-2). All model parameters were set equal and <br />actual floodplain site locations were used for each reach (Irving and Burdick 1995). It was <br />assumed that a spawning site was located 5 miles upstream from the upstream-most floodplain <br />site of each reach, as is the case with the Split Mountain to Desolation Canyon reach. The <br />location of each floodplain site relative to a spawning bar has a great influence on entrainment <br />and accounts for reach differences in numbers of larvae entrained. These model simulations <br />indicate that larval entrainment at full potential inundation was greatest in the Split Mountain to <br />Desolation Canyon reach (1,322,380), followed by Gray Canyon to Labyrinth Canyon (685,276), <br />and Labyrinth and Stillwater Canyons (379,460). Based on floodplain inundation at 18,200 cfs, <br />estimated larval entrainment was far greatest in the Split Mountain to Desolation Canyon reach <br />(1,322,371), and was similar to entrainment at full potential inundation because nearly all <br />floodplains are inundated (although not necessarily connected) at 18,200 cfs. Entrainment <br />estimates are not provided at 1,560 cfs because there is no surface connection between <br />floodplains and the river at that stage. Reliable inundated floodplains and the presence of a <br />known spawning bar in Split Mountain to Desolation Canyon highlight the importance ofthis <br />reach in species recovery. The majority of floodplain area identified for each of the three river <br />reaches is either shallow depressions or terraces that do not hold fish for long time periods for <br />maximum growth and survival. Hence, estimates of larval entrainment do not necessarily reflect <br />potential fish survival and recruitment from these floodplains. <br />
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