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3.3.3.10 Hydraulic Conductivity<br />

Several methods of measuring the hydraulic conductivity of soils have<br />

been developed (l)(ll). The most commonly used test is the percolation<br />

test. When run properly, the test can give an approximate measure of<br />

the soil's saturated hydraulic conductivity. However, the percolation<br />

of wastewater through soil below soil disposal systems usually occurs<br />

through unsaturated soils. Therefore, empirical factors must be used to<br />

estimate unsaturated conductivities. The unsaturated hydraulic conduc-<br />

tivities can vary dramatically from the saturated hydraulic conductivity<br />

with changes in soil characteristics <strong>and</strong> moisture content (see Appendix<br />

A).<br />

The percolation test is often criticized because of its variability <strong>and</strong><br />

failure to measure the hydraulic conductivity accurately. Percolation<br />

tests conducted in the same soils can vary by 90% or more (1)(11)(12)<br />

(13) (14) 0 Reasons for the large variability are attributed to the pro-<br />

cedure used, the soil moisture conditions at the time of the test, <strong>and</strong><br />

the individual performing the test. Despite these shortcomings, the<br />

percolation test can be useful if used together with the soil borings<br />

data. The test can be used to rank the relative hydraulic conductivity<br />

of the soil. Estimated percolation rates for various soil textures are<br />

given in Table 3-7.<br />

Soil Texture<br />

TABLE 3-7<br />

ESTIMATED HYDRAULIC CHARACTERISTICS OF SOIL (15)<br />

S<strong>and</strong> >6.0 (10<br />

S<strong>and</strong>y loams<br />

Porous silt loams<br />

Silty clay loams<br />

Clays, compact<br />

Silt loams<br />

Silty clay loams<br />

Percolation<br />

ml n/in.<br />

0.2-6.0 10-45<br />

39<br />

x0.2 >45

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