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Hydraulic performance of biofilter systems for stormwater management

Hydraulic performance of biofilter systems for stormwater management

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Figure 7 : K lab deep ini vs. Kf s shallow – white triangle, system with low initial hydraulic conductivity, black<br />

square, <strong>systems</strong> with high initial hydraulic conductivity<br />

This decrease can be explained by sediment deposition at the surface. However,<br />

final hydraulic conductivities are still relatively high (K fs shallow = 127 mm/h, n=17), and<br />

likely to be adequate to ensure good pollutant removal <strong>per<strong>for</strong>mance</strong>. This observation<br />

may be either because the <strong>systems</strong> are only partially clogged, or because creation <strong>of</strong><br />

macropores is having some effect in creating flow through the media, possibly even at<br />

the surface (<strong>for</strong> example, at the base <strong>of</strong> plant stems, where growing, senescence and<br />

even stem movement due to wind, may cause ‘breaking up’ <strong>of</strong> any clogging layer)<br />

(Figure 8).<br />

K lab deep ini = 241<br />

K fs shallow = 127 mm/h<br />

Figure 8 : Schematic representation <strong>of</strong> the evolution <strong>of</strong> the behaviour <strong>of</strong> bi<strong>of</strong>ilters with high initial K<br />

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