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<br />. <br /> <br />. <br /> <br />.~'~_. <br />. ;l;~'l':.' <br />'''''~''' .".' <br /> <br />important because flow recommendations can be refined in response to the emerging understanding <br />of the mechanisms involved in recovery of the endangered species in the San Juan River. <br /> <br />This report is one of two reports that address the results of the 7-year research program_ This report <br />fucuses 011 the analysis and integTalion of biological, hydrologic. and geomorphoiogicai data to <br />determine flow needs of the endangered fish species_ A companion report. to be produced in 1999. <br />will compile and synthesize information on other aspects of recovery of the endangered fishes in the <br />San Juan River. The companion report will specifically address issues such as contaminants, <br />propagation, nonnative species control, and fish-passage needs. <br /> <br />RESULTS OF THE 7-YEAR RESEARCH PERIOD <br /> <br />The San Juan River is similar to other Upper Colorado River Basin (Upper Basin) streams, primarily <br />the Green and Colorado rivers, in that they are all large rivers with high spring flows and low base <br />flows, they are all fairly turbid most of the time, they typically have sand and cobble substrate, and <br />they are all subject to late summer and fall thunderstorm activity _ The San Juan River is also similar <br />to other portions of the Upper Basin in that it once supported populations of Colorado pikeminnow <br />and razorback sucker that have declined after the completion of major dams. However, the San Juan <br />River is different than the Green and Colorado rivers primarily because it has a steeper overall slope. <br />a higher overall sediment concentration, and more Jate summer and fall flood events. No wild <br />razorback sucker were found in the San Juan River during the research period, and the Colorado <br />pikeminnow population appears to be smaller than 100 individuals. Navajo Dam began affecting <br />flows in the San Juan River in 1962, and post-dam flows had lower spring flows and higher late <br />summer. fall, and winter flows than occurred during pre-dam periods. The advent of research flows <br />in 1992 to 1997 produced flows more typical of the pre-dam era. <br /> <br />Habitat needs of the two endangered fishes in the San Juan River involve a complex mix of low- <br />velocity habitats such as eddies, pools, and backwaters adjacent to swifter run and riffle habitats. <br />Habitat use changes with time of year and activity (e.g., spawning. feeding, nursery areas). A natural <br />hydrograph, in terms of peak spring flows and late summer base flows. is important to not only <br />provide the proper habitats at the correct time, but also to provide natural temperatures and <br />productivity cycles for those habitats. <br /> <br />Two key habitats important to Colorado pikeminnow and other native species that were used <br />extensively in the flow recommendation process were cobble bars and backwaters. Cobble bars are <br />spawning areas for Colorado pikeminnow, and the fish appear to have fidelity for a certain area of <br />the San Juan River called "the Mixer" for spawning. ln the Green River, similar fidelity to spawning <br />areas is seen for both Colorado pikeminnow and razorback sucker. An important feature of <br />Colorado pikeminnow spawning bars is that the cobbles are very clean with relatively little fine <br />sediments between individual cobbles. Clean cobble bars are more rare in the San Juan River, as <br />well as in other Upper Basin rivers. than just a typical cobble bar_ <br /> <br />SJAIP Biology Committee <br />May 1999 <br /> <br />5-2 <br /> <br />Executive Summary <br />Flow Report <br /> <br />00339 <br />