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concentrated flow which promoted erosion below <strong>the</strong> structure and resulted <strong>in</strong> short<br />

circuit<strong>in</strong>g <strong>in</strong> <strong>the</strong> ponded area.<br />

In contrast to <strong>the</strong> field monitor<strong>in</strong>g, high removal efficiencies were achieved with<br />

silt fences <strong>in</strong> <strong>the</strong> flume studies. The geometry of <strong>the</strong> flume created a large ponded area<br />

beh<strong>in</strong>d <strong>the</strong> controls result<strong>in</strong>g <strong>in</strong> long detention times and significant particle settl<strong>in</strong>g even<br />

with <strong>the</strong> f<strong>in</strong>e-gra<strong>in</strong>ed sediment used <strong>in</strong> <strong>the</strong> tests. Mean sediment removal efficiency <strong>in</strong> <strong>the</strong><br />

flume ranged from 68 to 90% and was highly correlated with <strong>the</strong> detention time of <strong>the</strong><br />

runoff. This <strong>in</strong>dicates that silt fences should be sited <strong>in</strong> <strong>the</strong> field so as to maximize <strong>the</strong><br />

ponded volume beh<strong>in</strong>d <strong>the</strong> fence.<br />

Sediment-laden runoff flow rates through <strong>the</strong> controls were two orders of<br />

magnitude less than those typically specified by transportation agencies. The flow rates<br />

of a sediment slurry through geotextile fences are a function of apparent open<strong>in</strong>g size as<br />

well as permittivity (or o<strong>the</strong>r measures of clean water flowrates). The fabric result<strong>in</strong>g <strong>in</strong><br />

<strong>the</strong> longest detention times <strong>in</strong> this series of flume tests had <strong>the</strong> highest reported<br />

permittivity, but it also had <strong>the</strong> smallest apparent open<strong>in</strong>g size, suggest<strong>in</strong>g that clogg<strong>in</strong>g<br />

of <strong>the</strong> fabric with sediment affected its hydraulic per<strong>for</strong>mance. Field per<strong>for</strong>mance can not<br />

be determ<strong>in</strong>ed from current parameters used to characterize <strong>the</strong> hydraulic properties of<br />

<strong>the</strong>se fabrics.<br />

In addition, tests of silt fence fabrics <strong>in</strong> a modified permeameter showed that<br />

flowrates through <strong>the</strong> fabric were not l<strong>in</strong>early related to head as is assumed <strong>in</strong> <strong>the</strong> ASTM<br />

def<strong>in</strong>ition. The discrepancy was due to <strong>the</strong> fact that flow at <strong>the</strong> heads fabrics are<br />

subjected to <strong>in</strong> silt fence applications is turbulent result<strong>in</strong>g <strong>in</strong> much lower flow rates.<br />

Permeameter tests of silt fence fabrics confirmed that entrapped air is not <strong>the</strong> cause of <strong>the</strong><br />

much lower flowrates.<br />

Flowrates through rock berms greatly exceeded <strong>the</strong> rates typically recommended<br />

<strong>in</strong> regulatory agency guidel<strong>in</strong>es. The short detention times and large pore size of <strong>the</strong><br />

berms resulted <strong>in</strong> only a slight reduction <strong>in</strong> <strong>the</strong> suspended solids load <strong>in</strong> <strong>the</strong> flume tests.<br />

Development of a new test or series of tests to characterize <strong>the</strong> expected<br />

per<strong>for</strong>mance of geotextile fabrics when used as silt fences is urgently needed. The use of<br />

current parameters results <strong>in</strong> an over-estimate of <strong>the</strong> area that can be treated without over-<br />

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