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RBF_Cover (for eps) - National Water Research Institute

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FEET<br />

1,000<br />

900<br />

800<br />

700<br />

600<br />

VERTICAL SCALE GREATLY EXAGGERATED<br />

DATUM IS SEA LEVEL<br />

Modified from Gann and others, 1973<br />

0 1 2 MILES<br />

Figure 2. Glacial valley-fill aquifer overlain by fine grained sediments in the Great Miami River Valley, Ohio<br />

(from Miller and Appel, 1997).<br />

German researchers experimented with excavating a “window” by dredging accumulated<br />

sediment. While the measure increased <strong>RBF</strong> efficiency, it was considered temporary, lasting only<br />

weeks be<strong>for</strong>e silting over (Schubert, 2000). Rivers whose flow has been altered <strong>for</strong> flood control<br />

and navigation improvement, such as the Ohio River, are particularly prone to clogging. Steep<br />

gradients and floodwaters that may have scoured the riverbed in the past have been eliminated.<br />

Wells or specially designed tunnels used to extract groundwater and bank filtrate must also be<br />

properly located to maximize system efficiency. Rivers and streams that occur with the thumbprint<br />

of the most recent continental glacial period in the United States (e.g., Wisconsin ice age) have<br />

a similar terraced profile. The unaltered modern river channel carries normal stage flows within<br />

the primary terrace. This terrace corresponds to a 100-year flood plain. Where significantly altered<br />

<strong>for</strong> flood control or navigation, the river may now have inundated the primary terrace extending<br />

from bank to bank up to the secondary terrace. The secondary terrace extends outward to the<br />

500-year flood plain. This channel was cut into the bedrock by glacially fed rivers. The rivers were<br />

large braided streams laden with sand and gravel. As the glacial outwash diminished, the scour<br />

channels filled with sand and gravel to become aquifers. The tertiary terrace is the remnant of<br />

peak stage flooding and its resultant scouring into the bedrock. Relatively thin and finer grained<br />

sediments were deposited as the flood stage fell (see Figure 2). These sediments may have <strong>for</strong>med<br />

local, relatively less-productive aquifers that are not connected to the modern river channel. The<br />

secondary terrace is the most productive place to locate <strong>RBF</strong> wells (e.g., out of main navigation,<br />

interconnected to the river, relatively thicker aquifer, greater potential <strong>for</strong> effective filtration).<br />

Potential <strong>RBF</strong> Regions<br />

Grand River<br />

B<br />

0 1 2 KILOMETERS<br />

The greatest potential <strong>for</strong> <strong>RBF</strong> — and, in fact, where <strong>RBF</strong> has been implemented — in the United<br />

States is in the Midwestern states. Figure 3 shows the location of mid- to large-sized communities<br />

in the United States that are located along rivers and on alluvial aquifers. Due to site conditions,<br />

<strong>RBF</strong> is a viable water supply option <strong>for</strong> many, but not all, communities.<br />

Midwest stream-valley aquifers in Midwestern states west of the Mississippi River are important<br />

sources of water <strong>for</strong> communities and industries (Figure 4). These aquifers are unconsolidated sand<br />

and gravel deposits that are thicker, greater in extent, and more productive in the major river<br />

valleys of the region. The stream-valley aquifers are unconfined and in direct connection to adjacent<br />

streams and rivers. Average yields from wells range from 100 to 1,000 gallons per minute, with some<br />

wells yielding over 3,000 gallons per minute (Olcott, 1992). <strong>RBF</strong> opportunities may be available<br />

Buried Valley<br />

B<br />

EXPLANATION<br />

Clay, silt, and fine-grained sand<br />

Coarse-grained sand and gravel<br />

Sand, gravel, and boulders<br />

Till<br />

Bedrock<br />

169

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