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Last modified
7/14/2009 5:02:37 PM
Creation date
5/22/2009 4:40:09 PM
Metadata
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UCREFRP
UCREFRP Catalog Number
9641
Author
Hedrick, T. N., K. R. Bestgen and K. D. Christopherson.
Title
Entrainment of Semi-Buoyant Beads and Razorback Sucker, Xyrauchen texanus, Larvae into Flood Plain Wetlands of the Middle Green River, Utah.
USFW Year
2009.
USFW - Doc Type
C-6/RZ-ENTR,
Copyright Material
NO
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<br />. <br /> <br />descending limb ofthe hydrograph) and at two different spawning bars (Razorback Bar, which is <br /> <br />on river right, and Escalante Bar on river left). Flow requests from Flaming Gorge Dam were <br /> <br />carefully coordinated with the U. S. Bureau of Reclamation and other agencies, including those <br /> <br />participating in the sampling, and were held at requested levels for two or more days to <br /> <br />accommodate sampling. During that time, flow releases were adjusted based on levels of the <br /> <br />tributary Yampa River to keep Green River flows stable and near requested targets, and flow <br /> <br />managers should be commended for their efforts. <br /> <br />The three releases occurred on 20,24, and 31 May, 2005 (Table 1). Orange beads were <br /> <br />released at Razorback Bar and yellow beads at Escalante Bar. Five drift net stations were <br /> <br />established over the entire distance of the study area for each release. Net stations were located <br /> <br />1.6 km downstream of Razorback Bar and at each of four different flood plain locations: <br /> <br />Thunder Ranch (multiple inflow breaches and an outflow), Stewart Lake (outlet gate was closed <br /> <br /> <br />in 2005 so had only one breach that acted as inflow and outflow depending on river stage), the <br /> <br /> <br />Stirrup (a single downstream breach that acted as inflow and outflow depending on river stage), <br /> <br /> <br />and L- 7 (a nonfunctional upstream inflow breach, and a downstream outflow breach that acted as <br /> <br />an inflow when river elevation overtopped the breach and when flows were increasing in 2005). <br /> <br />At sites 1.6 km downstream of release sites, nets were set at channel margins (one on the <br /> <br />far shoreline and two on the near shoreline) and in the midchannel (one net only) for a total of <br /> <br />four main channel nets. At flood plain sites, one drift net was set across the channel on the far <br /> <br />river bank (relative to the flood plain inlets), one or two at mid channel depending on the site, <br /> <br />and one in the river immediately downstream of the flood plain breaches. Two additional nets <br /> <br />were set in the breaches. Because beads were easily observed in the drift samples, their presence <br /> <br />was used to estimate drift rates and to determine when sampling at downstream sites should <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />23 <br /> <br />. <br />
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