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Ground-water development in East St. Louis area, Illinois. Urbana, IL ...

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charged <strong>in</strong>to the river as ground-<strong>water</strong> runoff or <strong>in</strong>to the<br />

atmosphere as evapotranspiration is diverted toward the<br />

pumped well. Water levels are ultimately lowered below<br />

all or part of the river bed <strong>in</strong> the immediate vic<strong>in</strong>ity<br />

of the well, and the aquifer is then recharged by the <strong>in</strong>fluent<br />

seepage of surface <strong>water</strong>. The cone of depression<br />

will cont<strong>in</strong>ue to grow until sufficient <strong>area</strong> of the river bed<br />

Table 10. Drillers Logs of Test Holes Used <strong>in</strong> Aquifer Test 3<br />

Figure 12. Time-drawdown data for observation well 2,<br />

aquifer test 2<br />

Figure 13. Location of wells used <strong>in</strong> aquifer test 3<br />

depth, respectively. The lower 6.4 feet of cas<strong>in</strong>g <strong>in</strong> each<br />

test hole was slotted. The logs of test holes are given <strong>in</strong><br />

table 10.<br />

A distance-drawdown field data graph (figure 14)<br />

prepared with <strong>water</strong>-level data collected <strong>in</strong> the observation<br />

wells after a pump<strong>in</strong>g period of 1335 m<strong>in</strong>utes was<br />

superposed on the nonequilibrium type curve. The Theis<br />

(1935) equations were used to determ<strong>in</strong>e coefficients of<br />

transmissibility and storage of the aquifer. The coefficient<br />

of transmissibility was computed to be 134,000<br />

gpd/ft. The coefficient of storage (0.155) is <strong>in</strong> the <strong>water</strong>table<br />

range.<br />

The cone of depression created by pump<strong>in</strong>g a well<br />

near a river that is hydraulically connected to the aquifer<br />

is distorted. The hydraulic gradients between the river<br />

and the pumped well will be steeper than the hydraulic<br />

gradients on the land side of the well. The flow towards<br />

the well will be greatest on the river side of the well, and<br />

under equilibrium conditions most of the pumped <strong>water</strong><br />

will be derived from the river.<br />

When the well is pumped, <strong>water</strong> is <strong>in</strong>itially withdrawn<br />

from storage with<strong>in</strong> the aquifer <strong>in</strong> the immediate vic<strong>in</strong>ity<br />

of the well. If pump<strong>in</strong>g is cont<strong>in</strong>ued long enough <strong>water</strong><br />

levels <strong>in</strong> the vic<strong>in</strong>ity of the river will be lowered and<br />

<strong>water</strong> that under natural conditions would have dis-<br />

Formation From To<br />

(ft)<br />

Test hole 3<br />

Brown clay 0 20<br />

Soft blue clay 20 46<br />

F<strong>in</strong>e sand 46 50<br />

Medium to coarse 50 82<br />

Sand, loose 82 104<br />

Gray clay 104 116<br />

F<strong>in</strong>e sand, loose 116 120<br />

Red clay 120<br />

Rock<br />

Test hole 4<br />

Brown clay 0 9<br />

F<strong>in</strong>e sand, clay streaks 9 25<br />

Medium sand, some clay 25 30<br />

F<strong>in</strong>e tight sand 30 52<br />

Coarse sand and gravel, loose 52 79<br />

Hard gray clay 79 83<br />

F<strong>in</strong>e sand, clay streaks 83 90<br />

Bedrock 90<br />

Test hole 5<br />

Brown clay 0 11<br />

F<strong>in</strong>e sand and clay 11 17<br />

F<strong>in</strong>e sand 17 55<br />

Coarse sand and gravel, loose 55 83<br />

Gray clay 83 100<br />

Test hole 6 (Pumped Well; )<br />

Brown clay 0 10<br />

F<strong>in</strong>e sand and clay 10 18<br />

F<strong>in</strong>e sand 18 48<br />

Coarse sand and gravel, boulders<br />

drilled like rock ledge at 57 feet 48 80<br />

Gray clay 80 84<br />

Figure 14. Distance-drawdown data for aquifer test 3<br />

16

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