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<br />result in a flow increase of 16,200 cfs and a stage change of 4, 7 feet, while an increase of 23,000
<br />cfs to 33,200 cfs will result in a flow increase of 10,200 cfs and a stage change of2,9 feet at the
<br />confluence of the LCR At an upramp rate of4,000 cfs per hour, this stage change of2,9-4,7 feet
<br />is expected to occur in a period of about 2,6-4,0 hours, The downramp rate of 1,500 cfs per hour
<br />will take about 6,8-10,8 hours for flows to return to present operating range,
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<br />This stage change of up to 4,7 feet over a period of4,O hours will produce dramatic and rapid
<br />changes in shoreline habitats used primarily by juvenile humpback chub, This habitat
<br />destabi1ization will be exacerbated by the downramp or return to present operations, The
<br />shoreline habitat changes include inundation and virtual elimination of all backwaters used as
<br />nurseries and rearing areas by young native fishes (Arizona Game and Fish Department 1996a,
<br />1996b), and changes in the composition of the shallow, sheltered shoreline zone (<1 m, <0,3 m1s)
<br />used by juvenile humpback chub, Increases in stage of this magnitude often result in this shallow
<br />shoreline zone moving upslope, Depending on shoreline type, suitable habitat may remain
<br />available with increasing stage, or habitat quality may change and force fish to find alternative
<br />habitats, For example, a continuous talus slope may continue to provide suitable habitat, but talus
<br />sloping from steep cliffs is likely to be unsuitable for cover and low velocity habitat, Conversely,
<br />a shoreline with sand beach-unsuitable habitat because of lack of cover-may become talus with
<br />increasing stage and hence suitable habitat,juxtapositioning of shoreline habitats leads to
<br />destabi1ization that can force the young fish to seek alternative locations at additional energy
<br />expenditure and increased exposure to predation by brown trout and rainbow trout,
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<br />The shallow shoreline habitats are used primarily by juvenile humpback chub (ages 0-2) up to
<br />about 175 mm TL, The most abundant age of chubs along the shorelines are the young This g-
<br />of-the-year (YOY; Le" age 0), which are usually 40-80 mm TL at 7 months of age (i,e., October),
<br />Swimming abilities of humpback chub up to 134 mm TL have been shown to be signifiClllltly
<br />reduced by cold water temperatures; releases from Glen Canyon Dam range from 8. C to 10. C,
<br />and warm to 10.C to 12.C at the confluence of the LCR. Although the high release of31,000
<br />cfs is not expected to signifiClllltly affect river temperature, the likelihood that the juvenile chubs
<br />would be forced to leave the protective cover of their shoreline habitats would result in
<br />downstream displacement of fish and increased exposure to predation by brown trout and
<br />rainbow, A large population of brown trout exits in Bright Angel Creek and in the Colorado
<br />River near the confluence of that tributary. These fish spawn in late faD, and are very active
<br />feeders during September-November, Large numbers of brown trout are usually seen near the
<br />confluence of the Lca in fiIll. The cold water temperatures, in the range of those in the
<br />Colorado River below Glen Canyon Dam, have been demonstrated to effect the swimming ability
<br />of humpback chub up to 100 mm TL, When cold temperatures are combined with displacement,
<br />vulnerability to predation may be increased even further,
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<br />Mid-channel habitats used by adults, such as large eddy complexes. are not expected to change
<br />dramatically enough to adversely modifY habitat of adult humpback chub, The release is not
<br />expected to affect spawning habitat of humpback chub,
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