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Last modified
8/11/2009 11:32:56 AM
Creation date
8/10/2009 4:00:27 PM
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UCREFRP
UCREFRP Catalog Number
7762
Author
Valdez, R. A. and B. R. Cowdell.
Title
Annual Summary Report-1994, Effects of Flow Regulation and Ice Formation on Overwinter Nursery Habitat of Age-0 Colorado Squawfish in the Green River Below Flaming Gorge Dam.
USFW Year
1994.
USFW - Doc Type
\
Copyright Material
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<br />10 <br /> <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />Frazil ice formed a second time during February 13 - 16. During this period small amounts of frazil ice <br />formed below Split Mountain Canyon, but melted by 1000 to 1100 hrs. No lily-pad ice was observed. <br /> <br />5.2.2 Surface Ice <br /> <br />Surface ice formed along shorelines and in all reaches of the study area. Shoreline ice began forming the week <br />of January 31 through February 4. Ice formation was minimal, typically extending less than a meter from <br />shore. After this initial formation, shoreline ice steadily decreased and was absent by late February. No <br />smooth surface ice extending the width of the channel was observed in the study area. Aerial reconnaissance <br />of the region on February 16 revealed sections of smooth surface ice near Sand Wash (approximately 30 river <br />miles below Ouray, UT) <br /> <br />5.2.3 .Jam Ice <br /> <br />Ice jams began forming in narrow portions of the Green River at Ouray approximately February 1. Ice jams <br />were created by dislodged surface ice and lily-pad ice transported from upstream. Jams formed in constricted <br />areas of the channel often damming water and diverting flow into dry, high water channels. Ice jams persisted <br />in the Ouray area throughout February breaking up February 28 - March 4. <br /> <br />6.0 RESULTS <br /> <br />The effects of flow regulation and ice formation on nursery habitat of age-O Colorado squawfish was addressed <br />by assessing changes in backwater habitat characteristics. Minimum physical and chemical habitat requirements <br />were designated and used to determine if a backwater could support fish through the winter. The following <br />section outlines the criteria used and provides a summary of winter conditions in each backwater sampled. <br /> <br />6.1 MINIMUM HABITAT REQUIREMENTS <br /> <br />Minimum habitat requirements were designated for the physical and chemical characteristics of a backwater <br />(Table 5). If the surface area of usable habitat (habitat above the minimum requirements) became less than <br />30 m2, then the backwater was determined unsuitable nursery habitaL A minimum of 30 m2 was designated <br />according to the minimum requirements for a suitable backwater used by the Interagency Standardized <br />Monitoring Program (McAda et a1. 1994). <br /> <br />6.1.1 PhYSical Habitat Criteria <br /> <br />Wintertime changes in the physical habitat of a backwater were principally related to: (1) reduction of free <br />water due to ice formation, (2) inundation or reduction in size of backwaters by fluctuations in river stage, and <br />(3) modifications to backwaters caused by changes in river channel morphology. <br /> <br />Ice formation within backwaters reduces the amount of free water within the water column and subsequently <br />the amount of usable habitat with in a backwater. For this study, 0.3 ft (9.0 em) of free water between the <br />substrate and bottom of the ice cover was determined minimal for usable habitaL The criterion of 0.3 it was <br />used to account for variations in undersurface of surface ice and unevenness of backwater substrate. Free <br />water depths less than 0.3 it may allow for local isolation and entrapment of fish. Free water between ice <br />layers and/or on top of the ice was not considered usable habitaL <br /> <br />River stage can change with river flows and/or ice formation. These fluctuations in stage can significantly alter <br />backwater habitats. Increases in river stage can flood high water channels, changing backwaters to flow- <br />through channels. Conversely, reductions in river stage can isolate or reduce the size of backwater habitats. <br />
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