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Stream: San Miguel River Executive Summary
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Stream: San Miguel River Executive Summary
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Last modified
9/5/2012 2:16:12 PM
Creation date
9/5/2012 2:00:42 PM
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Water Supply Protection
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Stream: San Miguel River Executive Summary
State
CO
Water Division
4
Title
Stream: San Miguel River Executive Summary
Water Supply Pro - Doc Type
Report/Study
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boulders as cover (Sigler and Sigler 1996, Brouder et al., 2000). Roundtail chub begin spawning <br />when water temperatures reach about 65 °F (Vanicek and Kramer 1969, Joseph et al. 1977). In <br />most Colorado River tributaries, this increase in temperature coincides with a decrease in <br />discharge after peak runoff (Bezzerides and Bestgen 2002). <br />The flannelmouth sucker is a good indicator species for flow and habitat relationships (Stewart <br />and Anderson 2006 -CRI). The flannelmouth sucker is a large fish reaching up to almost 2 feet <br />in length. Historically, the flannelmouth sucker was commonly found in most, if not all, medium <br />to large, lower elevation rivers of the Upper Colorado River drainage (upstream of Glen Canyon <br />Dam). Within the State of Colorado, flannelmouth sucker are present in the Colorado River and <br />numerous tributaries including the Gunnison River up to the Aspinall Unit reservoirs (Bezzerides <br />and Bestgen 2002), the Uncompahgre River (Sigler and Miller 1963) and the Dolores River. <br />Flannelmouth suckers are typically found in slower, warmer rivers in plateau regions of the <br />Colorado River drainage (Deacon and Mize 1997). They usually inhabit the mainstem of <br />moderate to large rivers but are occasionally found in small streams. This species frequents <br />pools and deep runs but can also be found in the mouths of tributaries, riffles, and backwaters. <br />Flannelmouth sucker typically spawn in the Upper Colorado River basin between April and June <br />(McAda 1977, McAda and Wydoski 1980, Snyder and Muth 1990, Tyus and Karp 1990). <br />The bluehead sucker provides the most information for justifying instream flow needs to <br />maintain the native fish assemblage (Stewart and Anderson 2006 -CRI). The bluehead sucker is <br />a large fish reaching up to 17 inches in length. This species is found in a large variety of river <br />systems ranging from large rivers with discharges of several thousand cfs to small creeks with <br />less than a couple of cfs (Smith 1966). Adult bluehead suckers exhibit a strong preference for <br />specific habitat types (Holden and Stalnaker 1975). This species has been reported to typically <br />be found in runs or riffles with rock or gravel substrate (Vanicek 1967, Holden and Stalnaker <br />1975, Carlson et al. 1979, Sublette et al. 1990). The bluehead sucker is known to feed on <br />invertebrates, which have their highest densities in riffles. Although the species generally <br />inhabits streams with cool temperatures, bluehead suckers have been found inhabiting small <br />creeks with water temperatures as high as 82.4° F (Smith 1966). <br />Field Survey Data <br />The CDOW and BLM collected transect and flow data for 7 different cross - sections within an <br />815 foot reach of stream. The transect data was collected at a site approximately 1.5 miles <br />upstream from the confluence of the San Miguel River with Tabeguache Creek. These 7 <br />transects incorporated different mesohabitat types including riffles, runs, pools and glides. These <br />7 different cross - sections formed the basis for the PHABSIM/RHABSIM study conducted by the <br />CDOW and BLM. PHABSIM is widely used in North America to quantify instream flow <br />regimes and consists of two modeling components. The hydraulic component is a series of one - <br />dimensional cross - sections that are linked to produce a series of rectangular cells that form a <br />grid. Mean depth and velocity conditions are calculated for each cell for a given flow. The <br />biological component is a set of suitability index curves for depth and velocity criteria that are <br />used to rate micro - habitat suitability for each cell in the cross - sectional grid. Habitat availability <br />is measured by an index called weighted useable area (WUA), the summation of cell areas <br />weighted by its suitability index. When plotted versus discharge, WUA typically peaks at a <br />single flow that is considered the flow that maximizes habitat. <br />-4- <br />
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