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INTRODUCTION <br />Study Area <br />The Price River is a tributary to the Green River that drains approximately 1,892 square <br />miles of southeastern Utah (Figure 1). The upper portion of the drainage is located at 9,200 feet <br />above sea level, while the confluence of the Price River with the Green River is located at 4,200 <br />feet above sea level. Habitat in this drainage changes dramatically near Helper, Utah (Figure 2). <br />Upstream from this point, the Price River is ahigh-gradient stream supporting fish species that <br />prefer clear, cold water (e.g. mottled sculpin (Cottus bairdi), mountain sucker (Catostomus <br />platyrhynchus), bluehead sucker (Catostomus discobolus), and salmonids). Vegetation in this <br />portion of the drainage is dominated by montane species (e.g. conifers and aspen (Populus <br />tremuloides)) in upland areas, with willows (Salix spp.) and sedges (Carex spp.) in riparian <br />zones. Instream habitat is composed of pools, riffles and runs in the unaltered portions. <br />However, much of the stream has been channelized for highway and railroad construction. <br />Habitat in these sections is dominated by long riffles with large substrates. The upper portion of <br />the drainage also has a 2,815 surface acre impoundment, known as Scofield Reservoir. This <br />reservoir is used for irrigation and culinary water, and is located at an elevation of 7,618 feet <br />above sea level. This reservoir was originally built in 1926 (Judd 1992}, and enlarged to its <br />current size in 1946 (U.S. Bureau of Reclamation 1998a). A proposed dam and transbasin <br />diversion project (known as the Narrows Project) to be located above Scofield Reservoir would <br />deplete 5,709 acre-feet of water from the basin (U.S. Bureau of Reclamation 1998a). Depletions <br />would occur in the spring and summer in average and wet years and during the fall in dry years <br />(Table 1), and could have dramatic impacts on habitat-forming flows throughout the drainage. <br />Below Helper, upland vegetation is dominated by species that are better adapted to xeric <br />conditions (e.g. sagtbrush (Atriplex spp.), galleta grass (Hilaria jamesii), sagebrush (Artemisia <br />tridentata), greasewood (Sarcobatus vermiculatus), and Utah juniper (Juniperus osteosperma)). <br />Riparian plants include willows, tamarisk (Tamarix pentadra), canary reed grass (Palaris <br />arundinacea), and Fremont cottonwood (Populus fremontii). Instream habitat in the lower <br />portion of the Price River is dominated by long, uniform runs separated by riffles or rapids in the <br />higher gradient areas. The channel is characterized by steep banks and fairly uniform depths and <br />velocities. High amounts of sediment are carried through this part of the river during much of <br />the year, and summer water temperatures are much warmer than those found in the upper portion <br />of the basin. Farnham diversion, an irrigation structure located 88.5 miles upriver from the <br />confluence with the Green River (Figure 2), is a complete barrier to upstream movement of fish. <br />The river enters a deep, high-gradient canyon at river mile 19.5. Hereafter, the reach below river <br />mile 19.5 will be referred to as the Canyon section. The area from this point up to river mile <br />48.75 (the confluence with Grassy Trail Creek) will be referred to as the Woodside section. <br />Historical Accounts of Fish in the Price River <br />Relatively little is known about the fish community of the Price River downstream from <br />the town of Price, Utah. Originally, this area was probably inhabited by razorback sucker <br />(Xyrauchen texanus), Colorado pikeminnow (Ptychocheilus Lucius), roundtail chub (Gila <br />robusta), flannelmouth sucker (Catostomus latipinnis), bluehead sucker, speckled dace <br />1 <br />