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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 />
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