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The impact of urban groundwater upon surface water - eTheses ...

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Analytical solution for the saturated thickness <strong>of</strong> the aquifer (m)<br />

70<br />

60<br />

50<br />

40<br />

30<br />

20<br />

10<br />

Sensitivity analyses <strong>of</strong> saturated thickness to different levels <strong>of</strong> seepage face (h1) and varying steepness <strong>of</strong><br />

gradient between the observation piezometer (h) and the river, and varying distant boundary conditions (h2).<br />

h mean 90.86, h2 mean 93.25<br />

h min 90.73, h2 mean 93.25<br />

h max 91.41, h2 mean 93.25<br />

h2 min 92.75, h mean 90.86<br />

h2 max 93.75, h mean 90.86<br />

2 2<br />

2 2<br />

h − h<br />

⎡h h b h h ⎤<br />

1<br />

2 − 1 ( 2 − 1)<br />

− b(<br />

h − h1)<br />

= ⎢ − ⎥x<br />

2<br />

⎣ 2l<br />

l ⎦<br />

River Level (90.3)<br />

Datum<br />

River<br />

h1 h h2<br />

x<br />

0<br />

90.2 90.25 90.3 90.35 90.4 90.45 90.5 90.55 90.6 90.65 90.7<br />

River/Seepage head, h1, (maod)<br />

b<br />

Aquifer<br />

Aquitard<br />

l<br />

90.67 is the maximum level<br />

<strong>of</strong> the seepage face if a<br />

linear extension <strong>of</strong> the<br />

regional gradient is used.<br />

Figure 6.10 Sensitivity <strong>of</strong> the analytical solution for saturated thickness to variations in boundary conditions

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