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Last modified
5/14/2010 8:58:16 AM
Creation date
9/30/2006 10:00:00 PM
Metadata
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Template:
Publications
Year
1999
Title
Sustainability of Ground-Water Resources: U.S. Geological Survey Circular 1186
CWCB Section
Interstate & Federal
Author
William M. Alley, Thomas E. Reilly, O. Lehn Franke
Description
Illustration of the hydrologic, geologic, and ecological concepts to assure wise and sustainable use of ground-water resources
Publications - Doc Type
Historical
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<br />. <br /> <br />Velocities of ground-water flow generally are <br />low and are orders of magnitude less than <br />velocities of streamflow. The movement <br />of ground water normally occurs as slow <br />seepage through the pore spaces between <br />particles of unconsolidated earth materials <br />or through networks of fractures and solu- <br />tion openings in consolidated rocks. A <br />velocity of 1 foot per day or greater is a high <br />rate of movement for ground water, and <br />ground-water velocities can be as low as <br />1 foot per year or 1 foot per decade. In <br />contrast, velocities of streamflow generally <br />are measured in feet per second. A velocity <br />of 1 foot per second equals about 16 miles <br />per day. The low velocities of ground-water <br /> <br />~ <br />f <br />i <br /> <br />figure.5. A local scale ground-water-flow system. <br /> <br />In this loCal scale ground-water-flow system, <br />inflow of water from areal recharge occurs at the water <br />table. Outflow of water occurs as (1) discharge to the <br />atmosphere as ground-water evapotranspiration (tran- <br />spiration by vegetafion rooted at or near the water table <br />Or direct evaporation from the water table when it is at <br />or cIoseto the land surface) and (2) discharge of ground <br />water directly through the streambed, Short, shallow <br />flow paths originate at the water table near the stream. <br />As distance from the stream increases, flow paths to the <br />stream are longer and deeper. For lcmg-tenn average <br />conditions, inflow to this natural ground-water system <br />must equal outflow. <br /> <br />l <br /> <br />w <br /> <br />8 <br /> <br />flow can have important implications, <br /> <br />particularly in relation to the movement <br /> <br />of contaminants. <br /> <br />. <br /> <br />Under natural conditions, gro~d water <br />moves along flow paths from areas of <br />recharge to areas of discharge at springs <br />or along streams, lakes, and wetlands. <br />Discharge also occurs as seepage to bays <br />or the ocean in coastal areas, and as transpi- <br />ration by plants whose roots extend to near <br />the water table. The three-dimensional body <br />of earth material saturated with moving <br />ground water that extends from areas of <br />recharge to areas of discharge is referred to <br />as a ground-water-flow system (Figure 5). <br /> <br />Transpiration <br />by vegetation <br />In <br /> <br /> <br /> <br />Water table <br /> <br />Unconfined aquifer <br /> <br />~ <br /> <br />'- <br /> <br />~ <br />" <br /> <br />"Ii'lll <br />w ,@'lI II' <br />.~, '" 1$""" <br /> <br />EXPLANATION <br />o High hydraunc-conductivlty aquifer <br /> <br />~"",:~-~i Low hydraullc-conductivlty confining unit <br /> <br />Q Very low hydraulic--conductlvl1y ~rock <br /> <br />-+- Direction of ground-water flow <br /> <br />11 <br />I <br />II <br />-I <br />I <br />I <br />I <br /> <br />~ -~ <br />
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