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ently disparate results requires a basic understanding of <br />forest hydrology, including infiltration, interception, soil <br />moisture storage, and evapotranspiration. Different types <br />of forest disturbance and forest regrowth can affect each <br />of these processes in different ways, depending on the <br />site conditions, how a given management action is car- <br />ried out, and the hydrologic event of concern (e.g., annu- <br />al water yields, summer low flows, spring snowmelt, or <br />extreme rain events). Generalizations and extrapolations <br />can be misleading unless there is a clear linkage to, and <br />understanding of, the underlying processes. <br />There is a close relationship between forest condition, <br />runoff processes, and the quality of the water emanat- <br />ing from a forest. In general, forests grow in more <br />mesic areas and generate relatively little overland flow <br />at the hillslope scale (Dunne and Leopold, 1978). As a <br />result, forested areas commonly provide large amounts <br />of high- quality water (Dissmeyer, 2000). Poor forest <br />management practices can degrade the quality of this <br />water, while careful forest management can alter the <br />amount of runoff with little or no detectable effect on <br />water quality. <br />These generalizations apply to Colorado, as most of the <br />state's runoff emanates from forested areas at higher el- <br />evations, and this water is generally of very high quality. <br />Rapid population growth is increasing the demand for <br />water in urban areas, and this increased demand is illus- <br />trated by the rapid increases in the price of water along <br />the Front Range. Increasing water demands are also <br />emanating from industry, recreational interests, and the <br />desire to restore natural flow regimes to improve aquatic <br />habitat and support endangered species. Municipal water <br />suppliers are required to assess the risks to their sources <br />of water, and in most cases this means an assessment of <br />how forest conditions affect water quality. Substantial <br />amounts of public and private funds are being spent to <br />improve water quality and aquatic habitat. Given these <br />demands and issues, there is an increasing need for a <br />more rigorous understanding of how current forest con- <br />ditions and possible management actions can affect the <br />amount, timing, and quality of runoff. <br />Current forest conditions, water yields, and water quality <br />also need to be evaluated in a broader historical context, <br />as past changes in land use and forest composition are <br />directly and indirectly affecting the amount of runoff <br />as well as the quality of that runoff. For example, fire <br />suppression and low levels of forest harvest are believed <br />to have increased the density of forest vegetation and <br />reduced annual water yields in the North Platte water- <br />shed (Leaf, 2000; Troendle and Nankervis, 2000). The <br />increase in forest density can indirectly affect water <br />quality, as denser forests tend to be at greater risk to <br />high- severity wildfires. Large, high - severity wildfires <br />are of particular concern because they can greatly in- <br />crease the size of peak flows, hillslope erosion rates, <br />and downstream sedimentation rates (Tiedemann et al., <br />1979; Robichaud et al., 2000). The effects of high- sever- <br />ity fires on runoff and water quality were dramatically il- <br />lustrated by the 1996 Buffalo Creek fire, where post -fire <br />flooding and erosion led to the loss of human life, severe <br />property damage, and greatly increased water treatment <br />costs (Agnew et al., 1997; Moody and Martin, 2001). <br />The large wildfires in 2002 focused public attention on <br />the changing wildfire risk due to prolonged drought and <br />high forest densities. <br />From a regulatory perspective, a detailed understanding <br />of the relationships between forests and water are needed <br />to meet the demands of several important pieces of en- <br />vironmental legislation. The National Environmental <br />Policy Act requires federal agencies to assess the likely <br />impact of proposed federal actions, including a larger - <br />scale assessment of potential cumulative impacts (CEQ, <br />1997). Regulations emanating from the Clean Water Act <br />and its amendments require a watershed approach to im- <br />prove water quality when water quality standards are not <br />being met despite the application of NPDES permits for <br />point sources and Best Management Practices (BMPs) <br />for nonpoint sources (EPA, 1991). The Endangered <br />Species Act (ESA) requires federal agencies to protect <br />endangered species and their habitat, and many of the <br />species of greatest concern are aquatic species that de- <br />pend on the water in, or emanating from, forested areas <br />(MacDonald, 2000). The net result is a renewed interest <br />and focusing of public attention on the interactions be- <br />tween forest management and the amount, timing, and <br />quality of runoff. <br />1.2. Objectives and Organization <br />The basic purpose of this report is to provide a state -of- <br />the -art summary on how forest management in Colorado <br />affects water quantity and quality, and to identify key <br />gaps in knowledge. This synthesis should help guide <br />public policy and decision - making, and help identify <br />future research priorities. <br />The preparation of this report was conducted under the <br />guidance of a panel of water managers and scientists. <br />This panel was first convened in April 2000, and the <br />specific objectives were defined as: <br />