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<br />,... " <br /> <br />~ <br /> <br />----.. <br /> <br />Pa2e 2 <br /> <br />. <br /> <br />increased rates of erosion directly below the dam. Because dams often serve to reduce the size of chaIUlel-defining <br />peak flows, the channel structure downstream of dams also may be affected by their construction. <br />In contrast to the unidirectional flows of the stream. reservoirs and lakes are dominated by vertical mixing driven <br />by the wind. This mixing can return small particles suspended in the water column to the surface a number of <br />times before they settle to the bottom. Consequently, reservoir dynamics are often dictated more by the wind- <br />driven cycling of these materials within the mixed layer than by the horizontal flux of materials through the lake, <br />If the reservoir is deep enough, it may become stratified with a warm, well-mixed upper layer overlying a cooler, <br />lower layer. Because the lower layer is relatively isolated for large periods of time, decomposition can strip <br />oxygen from the water, producing large regions that are unsuitable for fish, <br /> <br />The increased surface area and decreased shading of reservoirs often means that they are wanner than the stream <br />they replaced. This is particularly true if they are too shallow to stratify, Often, though not always, this means that <br />the reach is no longer suitable for coldwater fish species. Many of the aquatic insects that lived on the stream <br />bottom and relied on current to deliver their food are replaced by organisms, primarily zooplankton, that are better <br />suited to foraging in the water column or organisms, like worms, that can survive in the fine sediment. Depending <br />on the size of the impoundment, it may become better suited: to supporting non-native species like pike and bass, <br />which often prey upon or compete with native cutthroat trout. In short, the transfonnation from a stream to a lake <br />ecosystem is typically accompanied by dramatic changes in the species present. <br /> <br />Finally, dams can serve as a physical barrier for the movement offish. While the upstream migration of <br />anadromous fish, like salmon and steelhead trout, from the sea to headwater spawning sites is the most dramatic <br />example offish movement, many freshwater fish, including Colorado's native cutthroat trout species, move <br />significant distances during the course of their life cycle. Dams can block fish as they migrate upstream to <br />spawning habitats in small tributaries and downstream to over-wintering habitats in larger streams and rivers. By . <br />severing these migration pathways, dams can have significant, deleterious impacts on many fish populations and <br />downstream sport fisheries. <br /> <br />In summary, inundation transfonns free-flowing streams supporting cold-water species to lakes which potentially <br />support a different suite of organisms. Certainly, not all the effects outlined above will be realized in every case. <br />Nonetheless it is imperative that the very real damages resulting from inundation be recognized in order to ensure <br />full protection of the CWCB's ISF rights, At the very least, upderstanding the impacts produced by inundating a <br />stream reach will allow the CWCB to determine the appropriate mitigation and compensation strategy for <br />offsetting the damages to the ISF right. <br /> <br />Thank you for considering my comments, I will be at your May meeting to answer questions you may have. <br /> <br /> <br />Sincerely <br />/Z' ..' <br />~-' <br />. John Roach, Ph.D. <br />Aquatics Specialist <br /> <br />'. <br />