Laserfiche WebLink
<br />. <br /> <br />. <br /> <br />Attachment to Proposal Aspinall-C: Aspinall Studies -- Evaluation of Gunnison <br />River flow manipulation upon availability and quality of nursery habitat for <br />Colorado squawfish in the Colorado River. <br /> <br />Lead Agency: <br /> <br />U. S. Fish and Wildlife Service (USFWS) <br /> <br />Submitted by: <br /> <br />Frank Pfiefer <br />U.S. Fish and Wildlife Service <br />529 25 1/2 Rd. <br />Suite B 110 <br />Grand Junction, CO 81505 <br /> <br />John Pitlick and Mark Van Steeter <br />Department of Geography, Box 260 <br />University of Colorado <br />Boulder, CO 80309-0260 <br /> <br />Date: <br /> <br />April 29, 1993 <br /> <br />I. Title of Proposal <br /> <br />Changes in channel morphology of the upper Colorado River <br /> <br />II. Relationship to Recovery program/Ranking Factors <br /> <br />The loss or alteration of backwater habitat appears to have contributed <br />significantly to the decline of native fishes in the upper Colorado <br />River basin. Results from our recent analysis of aerial photographs <br />taken between 1937 and 1986 indicate that there has been some reduction <br />in the overall width and complexity of the Colorado River within the <br />l5-mile and l8-mile reaches. Presumably these changes are associated <br />with reductions in peak flows due to water-resource development in the <br />upper basin, and with bank stabilizing activities (levees). Areas of <br />channel complexity and backwater habitat are, however, still found <br />within these reaches, and within the Ruby-Horsethief Canyon reaches, but <br />efforts to recover these fish will require more detailed information on <br />how backwater areas change in response to seasonally varying flow and <br />sediment transport patterns. <br /> <br />Recent recommendations for flows in the IS-mile reach of the Colorado <br />River are based on the assumption that higher flows are needed to <br />maintain backwater areas. It is not clear exactly how high these flows <br />need to be or how long they should last. Insight into this problem can <br />be gained by monitoring changes in channel morphology at specific sites <br />over the entire period of spring and summer runoff, and by <br />systematically measuring rates of sediment transport and deposition. It <br />is known from field surveys by FWS biologists that backwater sites <br />change from year to year, but it is not clear how these changes are <br />related to specific flow and sediment transport regimes. In spring <br />1993, we selected 4 field sites and set up a surveyed network of channel <br />cross sections to detect changes in side channels. We expect there will <br />be changes at these sites, particularly if runoff in 1993 is above <br />average. We propose to continue monitoring these sites through FY-94 to <br />determine how side channels develop over time. <br /> <br />In addition, we propose to expand the scope of work begun in FY-93 to <br /> <br />1 <br />