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smiths lake planning study volume 1: text - Great Lakes Council

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FLOODING AND DRAINAGE 32<br />

60<br />

50<br />

Natural<br />

Urbanised<br />

40<br />

30<br />

20<br />

10<br />

0<br />

0 0.2 0.4 0.6 0.8 Time 1 (hours) 1.2 1.4 1.6 1.8 2 2.2<br />

Figure 3-4 Impacts of Development on Tarbuck Creek 1% AEP Flows<br />

These higher flows and greater runoff <strong>volume</strong>s will also result in higher flood levels and<br />

increased velocities. This usually causes scour of the creek bed and under-cutting of creek<br />

banks. The subsequent bank slump into the creek can produce sedimentation of the creeks<br />

further downstream where slopes are flatter and velocities are lower. This sedimentation is in<br />

addition to the increased sediment load coming from the catchment through inappropriate<br />

construction practices.<br />

All of the impacts described above are able to be mitigated to varying degrees through the<br />

implementation of a workable Stormwater Management Plan. A plan would need to be created<br />

for each area of land to be developed taking into account the specifics of the site’s<br />

characteristics (eg. soil types, slopes, type of development). These issues are discussed in more<br />

detail in Section 4.<br />

3.3.2 Impacts of Filling for Residential Development in SLVA<br />

The primary impacts on the hydrological regime of filling for residential development include:<br />

• loss of flood storage causing increased flood levels in some circumstances; and<br />

• loss of floodway conveyance causing reduced flow capacity, increased velocities and flood<br />

levels.<br />

These two impacts are discussed below.<br />

Loss of Flood Storage<br />

In applying the first of these principles to the SLA, an important characteristic of the flood<br />

behaviour requires consideration. As described in Section 3.2.1, the peak flood levels around<br />

SMITHS_LAKE_PLANNING_STUDY.DOC<br />

O C E A N I C S<br />

A U S T R A L I A

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