Dealing with salinity in Wheatbelt Valleys - Department of Water
Dealing with salinity in Wheatbelt Valleys - Department of Water
Dealing with salinity in Wheatbelt Valleys - Department of Water
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George and Coleman<br />
HIDDEN MENACE OR OPPORTUNITY – GROUNDWATER HYDROLOGY, PLAYAS AND<br />
COMMERCIAL OPTIONS FOR SALINITY IN WHEATBELT VALLEYS<br />
Richard George 1 and Mark Coleman 2<br />
ABSTRACT<br />
<strong>Wheatbelt</strong> valleys conta<strong>in</strong> evidence <strong>of</strong> a long history <strong>of</strong> hydrologic and climatic change. In particular they conta<strong>in</strong><br />
ancient palaeodra<strong>in</strong>age systems compris<strong>in</strong>g large volumes <strong>of</strong> sal<strong>in</strong>e groundwater. Prior to clear<strong>in</strong>g, these<br />
palaeodra<strong>in</strong>ages discharged small amounts <strong>of</strong> groundwater derived from episodic recharge on the hillslopes and <strong>in</strong><br />
situ <strong>with</strong><strong>in</strong> valleys. However, as a result <strong>of</strong> significant <strong>in</strong>creases <strong>in</strong> recharge follow<strong>in</strong>g clear<strong>in</strong>g, these palaeodra<strong>in</strong>ages<br />
are now becom<strong>in</strong>g saturated, and small natural discharge areas such as playas, which previously balanced recharge,<br />
are now too small to cope <strong>with</strong> <strong>in</strong>creased surface and groundwater flows. Discharge areas are expand<strong>in</strong>g and sal<strong>in</strong>e<br />
land is encroach<strong>in</strong>g on farmland, threaten<strong>in</strong>g other assets such as towns, roads and remnant vegetation.<br />
Today between 3 and 15% <strong>of</strong> the wheatbelt shires, and a higher percentage <strong>of</strong> valley floor farmland, is sal<strong>in</strong>e. A<br />
larger area <strong>of</strong> between 22 and 34% is likely to have shallow watertables <strong>with</strong> much <strong>of</strong> it be<strong>in</strong>g sal<strong>in</strong>e, if current<br />
trends <strong>in</strong> groundwater levels are ma<strong>in</strong>ta<strong>in</strong>ed. In addition, few management options are available to reduce recharge,<br />
the area required for effective management is large (> 50%) and there rema<strong>in</strong>s considerable uncerta<strong>in</strong>ty as to the<br />
effectiveness and economics <strong>of</strong> discharge based options. Despite this uncerta<strong>in</strong>ty, farmers threatened by <strong>sal<strong>in</strong>ity</strong><br />
have recognised that eng<strong>in</strong>eer<strong>in</strong>g options represent the most likely means <strong>of</strong> unilaterally manag<strong>in</strong>g <strong>sal<strong>in</strong>ity</strong>. Many<br />
also realise that discharge areas, sal<strong>in</strong>e or <strong>with</strong> a shallow watertable, are a complex mosaic <strong>of</strong> land <strong>with</strong> differ<strong>in</strong>g<br />
<strong>sal<strong>in</strong>ity</strong> levels and capabilities.<br />
Given current levels <strong>of</strong> effectiveness <strong>of</strong> management options, added economic <strong>in</strong>centives for the use <strong>of</strong> wheatbelt<br />
valleys is required. These may be needed to both partially refund recovery <strong>of</strong> land where eng<strong>in</strong>eer<strong>in</strong>g options have<br />
been used or as a means to develop a new resource and associated <strong>in</strong>dustry. We believe that this <strong>in</strong>centive, should<br />
it exist, may potentially come from the longer-term development <strong>of</strong> the large (1000 GL/yr) and sal<strong>in</strong>e<br />
(> 30,000 mg/L) groundwater resources which lie beneath wheatbelt valleys. While aquaculture, salt harvest<strong>in</strong>g,<br />
desal<strong>in</strong>isation and the production <strong>of</strong> solar energy are all possible, there rema<strong>in</strong>s a considerable economic gap to be<br />
filled before many <strong>of</strong> these new <strong>in</strong>dustries become reality and wheatbelt valleys change their current landuse and<br />
emphasis on reclamation for agriculture.<br />
INTRODUCTION<br />
Secondary sal<strong>in</strong>isation <strong>of</strong> dryland agricultural farms <strong>in</strong><br />
Western Australia has occurred as a result <strong>of</strong> the<br />
removal <strong>of</strong> perennial, deep-rooted native forests and<br />
woodlands over an area <strong>of</strong> some 200,000 km 2 and its<br />
replacement <strong>with</strong> predom<strong>in</strong>antly shallow-rooted,<br />
annual crops and pastures (George et al. 1997).<br />
Additional recharge causes watertables to rise,<br />
dissolv<strong>in</strong>g salts stored <strong>with</strong><strong>in</strong> the regolith and rootzone<br />
<strong>of</strong> poorly tolerant agricultural crops. By 1996,<br />
90% <strong>of</strong> the agricultural landscape had been cleared<br />
and shallow watertables and dryland <strong>sal<strong>in</strong>ity</strong> affected<br />
18,000 km 2 <strong>of</strong> previously productive agricultural land<br />
(Ferdowsian et al. 1996). National Land and <strong>Water</strong><br />
1 Senior Hydrologist, <strong>Department</strong> <strong>of</strong> Agriculture, PO Box 1231, Bunbury WA 6231<br />
2 ACTIS Environmental Services, 33 Anstey St, Mundijong WA 6123<br />
– 1 –<br />
Resources Audit research <strong>in</strong>dicated shallow<br />
watertables and <strong>sal<strong>in</strong>ity</strong> threatens at least two to<br />
three times this area unless appropriate management<br />
systems are developed and implemented quickly<br />
(Short & McConnell 2001).<br />
Changes to the water balance also impact on<br />
<strong>in</strong>frastructure: towns, roads, pipel<strong>in</strong>es, buried cables<br />
and rail networks. Already, 30 Shires <strong>in</strong> the region<br />
have begun to <strong>in</strong>vestigate <strong>sal<strong>in</strong>ity</strong> risk to rural towns<br />
and each are develop<strong>in</strong>g urban water management<br />
options (Pridham 2001). In addition, 50% <strong>of</strong> the<br />
region's divertible waters are sal<strong>in</strong>e and further losses<br />
are imm<strong>in</strong>ent. As a result <strong>of</strong> shallow watertables and<br />
expand<strong>in</strong>g near-permanently wet areas <strong>in</strong> valleys, a