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Last modified
5/14/2010 8:58:17 AM
Creation date
9/30/2006 10:12:13 PM
Metadata
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Template:
Publications
Year
1998
Title
Ground Water and Surface Water A Single Resource U.S. Geological Survey Circular 1139
CWCB Section
Interstate & Federal
Author
T.C. Winter, J.W. Harvey, O.L. Franke, W.M. Alley
Description
Overview of current understandimg of interaction of ground water and surface water in terms of quality and quantity
Publications - Doc Type
Historical
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<br /> <br />the surface drainage system, and to reappear at the <br />surface at another place. Seeps and springs of all <br />sizes are characteristic features of karst terrains. <br />Springs having sufficiently large ground-water <br />recharge areas commonly are the source of small- <br />to medium-sized streams and constitute a large <br /> <br /> <br />part of tributary flow to larger streams. In addi- <br />tion, the location where the streams emerge can <br />change, depending on the spatial distribution of <br />ground-water recharge in relation to individual <br />precipitation events. Large spring inflows to <br />streams in karst terrain contrast sharply with the <br />generally more diffuse ground-water inflow char- <br />acteristic of streams flowing across sand and <br />gravel aquifers. <br />Because of the complex patterns of surface- <br />water and ground-water flow in karst terrain, <br />many studies have shown that surface-water <br />drainage divides and ground-water drainage <br /> <br />divides do not coincide. An extreme example is a <br />stream that disappears in one surface-water basin <br />and reappears in another basin. This situation <br />complicates the identification of source areas <br />for water and associated dissolved constituents, <br />including contaminants, in karst terrain. <br />Water chemisfry is widely used for studying <br />the hydrology of karst aquifers. Extensive tracer <br />studies (see Box G) and field mapping to locate <br />points of recharge and discharge have been used <br />to estimate the recharge areas of springs, rates of <br />ground-water movement, and the water balance of <br />aquifers. Variations in parameters such as temper- <br />ature, hardness, calcium I magnesium ratios, and <br />other chemical characteristics have been used to <br />identify areas of ground-water recharge, differen- <br />tiate rapid- and slow-moving ground-water flow <br />paths, and compare springflow characteristics in <br />different regions. Rapid transport of contaminants <br />within karst aquifers and to springs has been <br />documented in many locations. Because of the <br />rapid movement of water in karst aquifers, water- <br />quality problems that might be localized in other <br />aquifer systems can become regional problems in <br />karst systems. <br />Some landscapes considered to be karst <br />terrain do not have carbonate rocks at the land <br />surface. For example, in some areas of the south- <br />eastern United States, surficial deposits overlie <br />carbonate rocks, resulting in a "mantled" karst <br />ferrain. Lakes and wetlands in mantled karst <br />terrain inferact with shallow ground water in a <br />manner similar to that in sandy glacial and dune <br />terrains. The difference between how lakes and <br />wetlands interact with ground water in sandy <br />glacial and dune terrain and how they interact <br />in the mantled karst is related to the buried <br />carbonate rocks. If dissolution of the buried <br />carbonate rocks causes slumpage of an overlying <br />confining bed, such that water can move freely <br />through the confining bed, the lakes and wetlands <br />also can be affected by changing hydraulic heads <br />in the aquifers underlying the confining bed (see <br />Box L). <br /> <br />51 <br />
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