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<br />Figure 3. Stream valley cross-sections at various locations in a watershed illustrate basic
<br />principles about natural pathways of water moving downhill and human influences on
<br />hydrology. Runoff, which occurs when precipitation exceeds losses due to evaporation
<br />and plant transpiration, can be divided into four components (a): overland flow (1) occurs
<br />when precipitation exceeds the infiltration capacity of the soil; shallow subsurface
<br />stormflow (2) represents water that infiltrates the soil but is routed relatively quickly to
<br />the stream channel; saturated overland flow (3) occurs where the water table is close to
<br />the surface, such as adjacent to the stream channel, upstream of first-order tributaries,
<br />and in soils saturated by prior precipitation; and groundwater flow (4) represents
<br />relatively deep and slow pathways of water movement and provides water to the stream
<br />channel even during periods of little or no precipitation. Collectively, overland and
<br />shallow subsurface flow pathways create the peaks in the hydrograph that are a river's
<br />response to storm events, whereas deeper groundwater pathways are responsible for
<br />baseflow. Urbanized (b) and agricultural (c) land uses increase surface flow by increasing
<br />the extent of impermeable surfaces, reducing vegetation cover, and installing drainage
<br />systems. Relative to the unaltered state, channels often are scoured to greater depth by
<br />unnaturally high flood crests and water tables are lowered, causing baseflow to drop.
<br />Side-channels, wetlands, and episodically flooded lowlands comprise the diverse flood-
<br />plain habitats of unmodified river ecosystems (d). Levees or flood walls (e) constructed
<br />along the banks retain flood waters in the main channel and lead to a loss of floodplain
<br />habitat diversity and function. Dams impede the downstream movement of water and can
<br />greatly modify a river's flow regime, depending on whether they are operated for storage
<br />(e) or as "run-of-river," such as for navigation (f).
<br />rivers in accordance with both flow
<br />characteristics and the type and the
<br />availability of transportable materials.
<br />Within a river, different habitat
<br />features are created and maintained
<br />by a wide range of flows. For ex-
<br />ample, many channel and floodplain
<br />features, such as river bars and riffle-
<br />pool sequences, are formed and main-
<br />tained by dominant, or bankfull, dis-
<br />charges. These discharges are flows
<br />that can move significant quantities
<br />of bed or bank sediment and that
<br />occur frequently enough (e.g., every
<br />several years) to continually modify
<br />the channel (Wolman and Miller
<br />1960). In many streams and rivers
<br />with a small range of flood flows,
<br />bankfull flow can build and main-
<br />tain the active floodplain through
<br />stream migration (Leopold et al.
<br />1964). However, the concept of a
<br />dominant discharge may not be ap-
<br />plicable in all flow regimes (Wolman
<br />and Gerson 1978). Furthermore, in
<br />some flow regimes, the flows that
<br />build the channel may differ from
<br />those that build the floodplain. For
<br />example, in rivers with a wide range
<br />of flood flows, floodplains may ex-
<br />hibit major bar deposits, such as
<br />berms of boulders along the channel,
<br />or other features that are left by
<br />infrequent high-magnitude floods
<br />(e.g., Miller 1990). -
<br />Over periods of years to decades,
<br />a single river can consistently pro-
<br />vide ephemeral, seasonal, and per-
<br />sistent types of habitat that range
<br />from free-flowing, to standing, to no
<br />water. This predictable diversity of
<br />in-channel and floodplain habitat
<br />types has promoted the evolution of
<br />species that exploit the habitat mo-
<br />saic created and maintained by hy-
<br />drologic variability. For many river-
<br />ine species, completion of the life
<br />cycle requires an array of different
<br />habitat types, whose availability over
<br />time is regulated by the flow regime
<br />(e.g., Greenberg et al. 1996, Reeves
<br />et al. 1996, Sparks 1995). Indeed,
<br />adaptation to this environmental dy-
<br />namism allows aquatic and flood-
<br />plain species to persist in the face of
<br />seemingly harsh conditions, such as
<br />floods and droughts, that regularly
<br />destroy and re-create habitat elements.
<br />From an evolutionary perspective,
<br />the pattern of spatial and temporal
<br />habitat dynamics influences the rela-
<br />tive success of a species in a particu-
<br />lar environmental setting. This habi-
<br />tat template (Southwood 1977),
<br />which is dictated largely by flow
<br />regime, creates both subtle and pro-
<br />found differences in the natural his-
<br />tories of species in different segments
<br />of their ranges. It also influences
<br />species distribution and abundance,
<br />as well as ecosystem function (Poff
<br />and Allan 1995, Schlosser 1990,
<br />Sparks 1992, Stanford et al. 1996).
<br />Human alteration of flow regime
<br />changes the established pattern of
<br />natural hydrologic variation and dis-
<br />turbance, thereby altering habitat
<br />dynamics and creating new condi-
<br />tions to which the native biota may
<br />be poorly adapted.
<br />Human alteration of
<br />flow regimes
<br />Human modification of natural hy-
<br />drologic processes disrupts the dy-
<br />namic equilibrium between the move-
<br />ment of water and the movement of
<br />sediment that exists in free-flowing
<br />rivers (Dunne and Leopold 1978).
<br />This disruption alters both gross-
<br />and fine-scale geomorphic features
<br />that constitute habitat for aquatic
<br />and riparian species (Table 1). After
<br />772 BioScience Vol. 47 No. 11
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