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Water Sensitive Urban Design

Book 2 | Planning and Management - WSUD

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<strong>Water</strong> <strong>Sensitive</strong> <strong>Urban</strong> <strong>Design</strong><br />

Figure 3b - Example of bioretention raingarden<br />

3.1.4 Sizing bioretention systems<br />

Figure 5 presents sizing curves for<br />

bioretention systems in Eastern and<br />

Western Sydney, showing typical<br />

performance for different catchment<br />

impervious fractions including 40, 60, 80<br />

and 100%. Different curves are provided<br />

for Eastern and Western Sydney to<br />

accommodate the influence of different<br />

rainfall patterns and volume on treatment<br />

performance. The sizing curves are<br />

presented in terms of the bioretention<br />

filter area as a percentage of the total<br />

catchment area.<br />

The curves assume that the bioretention<br />

system included 0.2m extended<br />

detention, 0.5m filter depth, and a<br />

sandy loam filter material, with<br />

a median particle size of 0.5mm<br />

and hydraulic conductivity of<br />

100mm/hr. It can be seen in Figure 5<br />

that in Western Sydney a bioretention<br />

system to treat a 40% impervious<br />

catchment can be sized at approximately<br />

1% of the catchment, whereas this<br />

increases to 1.5% in Eastern Sydney.<br />

For catchments with higher impervious<br />

fractions, a larger treatment area is<br />

required; at 100% impervious fraction,<br />

1.5% of the catchment is required in<br />

western Sydney and 2.1% in eastern<br />

Sydney.<br />

Other than the area, key aspects of<br />

bioretention system design that have a<br />

strong influence on pollutant removal<br />

performance include the extended<br />

detention depth, filter media depth<br />

and type of filter material. Bioretention<br />

performance improves with increasing<br />

depths of extended detention and the<br />

filter media, however deeper systems may<br />

not be feasible on all sites.<br />

16 Book 2 | planning and management

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