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Last modified
7/14/2009 5:02:36 PM
Creation date
5/17/2009 10:58:57 PM
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UCREFRP
UCREFRP Catalog Number
9560
Author
Valdez, R. A.
Title
A Generalized Interactive Model to Predict Floodplain Habitat Area Needed to Recover the Endangered Razorback Sucker in the Upper Colorado River Basin - Floodplain Model Version 5.1.
USFW Year
2004.
USFW - Doc Type
Logan, UT.
Copyright Material
NO
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<br />1 <br /> <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />:1 <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />1.0 INTRODUCTION <br /> <br />1.1 Background <br />The Upper Colorado River Endangered Fish Recovery Program (Recovery Program) has <br />invested considerable time and resources on identification, acquisition, and restoration of riverine <br />floodplains as nursery habitat for the endangered razorback sucker (Xyrauchen texanus; e.g., <br />FLO Engineering 1997; Nelson and Soker 2002). River floodplains are believed to be important <br />nursery and rearing habitats for the species (Tyus and Karp 1990; Modde 1996, 1997; Muth et al. <br />1998; Wydoski and Wick 1998). A major element of the Recovery Program is Habitat <br />Development, with the goal "to improve and maintain sufficient habitat to support the <br />endangered fish species; and to apply habitat development and enhancement techniques <br />experimentally to determine if the rare fishes will use developed habitat and if such techniques <br />contribute to recovery." As of November, 2002, a total of 1,087.2 acres have been acquired by <br />the Recovery Program for a total cost of$2,117,400. The Recovery Program is interested in <br />knowing if sufficient floodplain habitats are available to recover the endangered razorback sucker <br />and to support recovered populations. <br />The amount of floodplain habitat available on any given year is dependent on river stage. <br />A reconnaissance inventory ofbottomlands (Irving and Burdick 1995) identified 132 bottomland <br />habitat sites with a potential of 18,430 acres along 393 miles of the Green River in 1993. Of this <br />total, 7,720 acres (74 sites) were inundated during the May high-water flow period (18,200 cfs) <br />and 2,438 acres (28 sites) in the September low-water flow period (1,560 cfs). The largest <br />flooded bottomland areas were located in the Browns Park National Wildlife Refuge reach (RM <br />368-393; 1,371 acres inundated in May) and between Pariette Draw and Escalante Ranch (RM <br />238-310; 6,093 acres inun~ted in May). A follow-up effort by Irving and Day (1996) revealed <br />48,485 potential acres ofbottomlands in 111 inve~toried sites; only 6,113 acres were flooded in <br />May 1993, and 11,254 acres could be flooded with historic floods. Bell et al. (1998) analyzed <br />photographs and quantified surface area of inundation as a function of flow at the Jensen gage. <br />Inundated bottomland area between Split Mountain ,(RM 319) and Pariette Wash (RM 240) was <br />5,904 acres at 20,000 cfs; 9,550 acres at 22,000 cfs; and 13,927 acres at 25,000 cfs. Average <br />peak flow of the Green River near Jensen for 56 years of record through 2000, is 19,706 cfs. <br />
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