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<br />INTRODUCTION <br /> <br />The Animas/LaPlata is a water development project (Project) in southern Colorado and <br />northern New Mexico in the San Juan River Basin. The Project was authorized by the Colorado <br />River Basin Project Act of September 30, 1968, as a participating project under the Colorado <br />River Storage Act of April 11, 1956. Subsequent authorization for the construction, <br />maintenance, and operation of the Project was granted under the Colorado River Basin Act and <br />the Colorado Ute Indian Water Rights settlement of 1988. However, concern over the impact of <br />water depletions by the Project on endangered species resulted in a Jeopardy Opinion under the <br />ESA (Endangered Species Act) by the U.S. Fish and Wildlife Service (Service). Subsequently, a <br />Reasonable and Prudent Alternative was crafted which allowed the Project to proceed providing <br />that a multiyear research plan was developed and implemented, depletions were limited until <br />results of the research could be obtained, and Navajo Dam operated to produce test flows <br />mimicking a natural hydrograph. In addition, in July 1991 the U.S. Bureau of Reclamation <br />(Reclamation) requested consultation under the ESA on the operation of Navajo Dam and <br />agreed to release test flows during the 7-year research period so that flow effects on the <br />endangered fish and other native and non-native fishes below Navajo Dam could be determined. <br /> <br />This study is part of an interdisciplinary research effort addressing biological, hydrologic, and <br />sediment issues. This study, using videographic techniques, assesses flow levels in the San <br />Juan River versus habitat quantity (main channel and low velocity habitats such as backwaters <br />and side channels) needed for several life stages of the native fish. Studies conducted by the <br />Service concluded that backwaters in the Green River are preferred habitat for YOY <br />(young-of-the-year) Colorado squawfish (Holden and Stalnaker, 1975; Holden, 1977; Tyus and <br />McAda, 1984; Tyus et aI., 1987). Squawfish spawn during mid to late summer and their larvae <br />become distributed in shallow backwater habitat, reducing predation and protecting them from <br />adverse flow events (Tyus et al., 1987). This evidence suggests that maximizing backwater <br />habitat during summer will increase the survival rate of young Colorado squawfish and, <br />therefore, would be an important factor in the management and preservation of the species. <br />Studies conducted by Pucherelli et al., 1990a and 1990b, document backwaters per river mile in <br />the San Juan River to be three times less than backwaters in the Green River. This evidence <br />suggests that squawfish may be using the more available side channel habitat as well as <br />backwaters. <br /> <br />A technique was required to accurately map backwater habitat in response to various San Juan <br />River flows. The IFIM (instream flow incremental method) has not proven adequate to calculate <br />backwaters on large turbid and hydrologically complex rivers such as the Green River (Rose <br />and Hann, 1989). Rose and Hann's finding would apply to the San Juan because of similar <br />conditions. Therefore, alternative methods were employed. Pucherelli et al., 1990a, 1990b, and <br />1987, used aerial photographs and a GIS (Geographic Information System) to map backwater <br />habitat and changes in river morphology as a function ofriverflow. <br /> <br />This study examines the pretest flow operation relationship between flow and the number and <br />area of backwaters and side channels on the San Juan River in New Mexico and Utah. The <br />objective is to collect several years of habitat data from different flow scenarios and establish a <br />data base to assist in determining the optimal San Juan River flows needed to maximize low <br /> <br />1 <br />