Yanchep National Park Management Plan 1989-1999
Yanchep National Park Management Plan 1989-1999
Yanchep National Park Management Plan 1989-1999
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6.0 HYDROLOGY<br />
The hydrology of the <strong>Park</strong> involves a complex interconnecting system between a groundwater<br />
aquifer and the wetlands and caves. (For further information also refer to Sections 9.0 and 15.0.)<br />
Hydrological information was obtained predominantly from the Water Authority Gnangara Mound<br />
Ground Water Resource Environmental Review and <strong>Management</strong> Programme (ERMP) (1986) and<br />
the EPA's response to the ERMP in Bulletin 295 (August 1987), except where cited.<br />
The <strong>Park</strong> lies towards the western edge of the Gnangara Mound, an extensive, unconfined ground<br />
water aquifer that provides approximately 20 percent of the public water supply for Perth (Hopkins,<br />
pers. comm.). The Mound is recharged by the direct infiltration of rainfall, mostly between April and<br />
October. The water table generally reflects the topography, and wetlands occur where the water table<br />
is at or near the surface. Beneath the coastal strip the water table has a low gradient for three to four<br />
kms inland then rises very steeply immediately west of the lakes. This occurs close to the contact<br />
between limestone and sand and is believed to mark a ground water cascade where ground water<br />
locally moves through limestone caves.<br />
To cater for public water supplies the Water Authority has proposed a number of schemes, including<br />
the Pinjar and Yeal schemes near <strong>Yanchep</strong>. Their potential environmental impact is reviewed in the<br />
ERMP. The major constraint in managing ground water resources is the retention of wetlands and<br />
natural water depths in the caves.<br />
The Water Authority (1986) consider that the potential environmental impact on the <strong>Park</strong>'s wetlands<br />
is low because:<br />
,the water table contours rise steeply to the east of the lakes such that lake levels are less<br />
susceptible to reductions in ground water levels to the east" (where the proposed scheme is<br />
situated), "the high transmissivities of the limestone will tend to mitigate drawdowns as water<br />
will rapidly flow into the area, the lake's steep sides and depth means that falls in level affect a<br />
narrower fringe than would be the case of a shallower lake'.<br />
However, the ground water in the caves, which is essential to the maintenance of their environment,<br />
averages only 10 to 20 cms in depth. For the reasons above, abstraction of the ground water some<br />
distance away does not directly reflect a decrease of water depth in the caves. Nevertheless if there is<br />
any 'unnatural' change in depth it can be critical. It is crucial that the normal depth and variation in<br />
the caves is maintained.<br />
The EPA (1987) considered that the environmental impacts of the drawdown predicted in the ERMP<br />
are unacceptable for some wetlands, including Loch McNess and Yonderup Lake. The EPA<br />
recommended that for the Category 1 (Loch McNess) and Category 2 (Yonderup Lake) wetlands<br />
there should be no change in the existing regime of water quality and quantity, and normal climatic<br />
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