Groundwater in the Great Lakes Basin
Groundwater in the Great Lakes Basin
Groundwater in the Great Lakes Basin
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INTRODUCTION<br />
<strong>Groundwater</strong>, a major natural resource <strong>in</strong> <strong>the</strong> <strong>Great</strong><br />
<strong>Lakes</strong> Bas<strong>in</strong>, supplies dr<strong>in</strong>k<strong>in</strong>g water for 8.2 million<br />
people <strong>in</strong> <strong>the</strong> bas<strong>in</strong>, and many manufactur<strong>in</strong>g processes<br />
and o<strong>the</strong>r <strong>in</strong>dustrial and agricultural applications use<br />
large amounts of groundwater. In addition to human<br />
uses, one of <strong>the</strong> most important functions of groundwater<br />
is to help ma<strong>in</strong>ta<strong>in</strong> flow <strong>in</strong> streams, lakes and wetlands<br />
by slowly and consistently discharg<strong>in</strong>g water dur<strong>in</strong>g<br />
periods of little or no ra<strong>in</strong>fall. Discharge to streams<br />
dur<strong>in</strong>g periods of no surface runoff is essential to support<br />
aquatic organisms, especially dur<strong>in</strong>g periods of drought.<br />
Although groundwater forms a large subsurface reservoir,<br />
<strong>the</strong> groundwater systems <strong>in</strong> <strong>the</strong> bas<strong>in</strong> are not a<br />
vast pool of contiguous water. Ra<strong>the</strong>r, groundwater is<br />
conta<strong>in</strong>ed <strong>in</strong> many different geologic units, each with<br />
its own dist<strong>in</strong>ct hydraulic properties. Some units are<br />
widely used aquifers that readily transmit water and<br />
yield large quantities of water to wells, while o<strong>the</strong>rs<br />
are not commonly used but do yield moderate amounts<br />
of water. In some limited parts of <strong>the</strong> bas<strong>in</strong>, little or<br />
no aquifer material exists. Issues generally <strong>in</strong>volve <strong>the</strong><br />
amount of groundwater available, <strong>the</strong> quality and/or<br />
<strong>the</strong> connection to an ecosystem (Grannemann, Hunt,<br />
Nicholas, Reilly and W<strong>in</strong>ter, 2000).<br />
The amount of groundwater available depends on many<br />
climatic and hydrogeologic factors. In conf<strong>in</strong>ed aquifers,<br />
<strong>the</strong> effects of pump<strong>in</strong>g are manifested rapidly. However,<br />
<strong>in</strong> unconf<strong>in</strong>ed or some semi-conf<strong>in</strong>ed aquifer systems,<br />
because of its relatively slow movement, <strong>the</strong> effects of<br />
pump<strong>in</strong>g groundwater <strong>in</strong> large quantities are manifested<br />
slowly. Years may pass before <strong>the</strong>re are measurable<br />
effects <strong>in</strong> ei<strong>the</strong>r <strong>the</strong> surface or groundwater systems.<br />
Threats to both groundwater quality and quantity can<br />
come from human activities on <strong>the</strong> land surface, <strong>the</strong><br />
effects of over-pump<strong>in</strong>g or natural conditions underground.<br />
The quality can be altered by ei<strong>the</strong>r po<strong>in</strong>t or<br />
non-po<strong>in</strong>t sources of contam<strong>in</strong>ation that enter from <strong>the</strong><br />
land surface and <strong>in</strong>filtrate to <strong>the</strong> groundwater system.<br />
Some of <strong>the</strong> more common contam<strong>in</strong>ants are hydrocarbons,<br />
solvents, pathogens, pesticides, herbicides and<br />
fertilizers. <strong>Groundwater</strong> quality also may be dim<strong>in</strong>ished<br />
by over-pump<strong>in</strong>g, which may <strong>in</strong>duce natural, but generally<br />
unwanted, chemical constituents <strong>in</strong>to <strong>the</strong> fresh<br />
groundwater system. These constituents may <strong>in</strong>clude<br />
br<strong>in</strong>e, arsenic and radium. Large-scale groundwater<br />
withdrawal also can redirect, or significantly reduce,<br />
<strong>the</strong> discharge of groundwater to streams, lakes and<br />
wetlands, thus depriv<strong>in</strong>g <strong>the</strong> surface water of a generally<br />
high-quality, constant temperature source of water. The<br />
result<strong>in</strong>g changes can alter <strong>the</strong> amount of surface water<br />
and also ecosystems that rely on groundwater discharge.<br />
The flow of many streams <strong>in</strong> <strong>the</strong> <strong>Great</strong> <strong>Lakes</strong> Bas<strong>in</strong>,<br />
especially those <strong>in</strong> watersheds with highly porous soils,<br />
consists largely of groundwater discharge to <strong>the</strong> streams.<br />
Hence, a high percentage of water flow<strong>in</strong>g to <strong>the</strong> <strong>Great</strong><br />
<strong>Lakes</strong> consists of water that <strong>in</strong>filtrates <strong>the</strong> land surface,<br />
enters <strong>the</strong> groundwater system, flows underground for<br />
vary<strong>in</strong>g distances, discharges to a stream or lake and<br />
<strong>the</strong>n cont<strong>in</strong>ues its path to <strong>the</strong> <strong>Great</strong> <strong>Lakes</strong> as streamflow.<br />
Therefore, to be comprehensive, management<br />
strategies for protect<strong>in</strong>g <strong>the</strong> quality of <strong>Great</strong> <strong>Lakes</strong> water<br />
must <strong>in</strong>corporate <strong>the</strong> groundwater flow component.<br />
In short, <strong>the</strong> <strong>Great</strong> <strong>Lakes</strong> cannot be protected without<br />
protect<strong>in</strong>g <strong>the</strong> groundwater resources <strong>in</strong> <strong>the</strong> bas<strong>in</strong>.<br />
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