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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Pannell<br />
ECONOMICS, SOCIETY AND<br />
ENVIRONMENT<br />
As noted above, economic development objectives<br />
provided much <strong>of</strong> the impetus for clear<strong>in</strong>g almost<br />
all <strong>of</strong> the WA <strong>Wheatbelt</strong>, start<strong>in</strong>g <strong>with</strong> the valley<br />
floors, over the course <strong>of</strong> the twentieth century.<br />
However, social objectives played a key role as<br />
well, particularly the objective <strong>of</strong> provid<strong>in</strong>g for<br />
returned servicemen follow<strong>in</strong>g each <strong>of</strong> the World<br />
Wars (Beresford et al. 2001). It is hard to<br />
dist<strong>in</strong>guish between economic and social<br />
objectives <strong>in</strong> that context. Environmental<br />
objectives did not appear to be high on the agenda<br />
until late <strong>in</strong> the Century, but this has changed<br />
radically. Indeed, an environmental issue<br />
(commercial harvest<strong>in</strong>g <strong>of</strong> logs from old-growth<br />
forests) is credited <strong>with</strong> contribut<strong>in</strong>g substantially<br />
to the change <strong>of</strong> State Government <strong>in</strong> Western<br />
Australia <strong>in</strong> 2001.<br />
The old-growth forest issue <strong>in</strong>volves difficult and<br />
sometimes messy trade<strong>of</strong>fs between<br />
environmental, social and economic outcomes.<br />
Increas<strong>in</strong>gly, <strong>sal<strong>in</strong>ity</strong> will do so as well. Here are<br />
three examples which illustrate the shape <strong>of</strong> th<strong>in</strong>gs<br />
to come.<br />
1. Disposal <strong>of</strong> sal<strong>in</strong>e water pumped from under<br />
towns.<br />
In towns located on valley floors, such as Merred<strong>in</strong><br />
and Katann<strong>in</strong>g, prevention <strong>of</strong> <strong>sal<strong>in</strong>ity</strong> damage will<br />
require eng<strong>in</strong>eer<strong>in</strong>g works, particularly pump<strong>in</strong>g.<br />
Disposal <strong>of</strong> the water poses problems. Use <strong>of</strong><br />
evaporation bas<strong>in</strong>s will be expensive enough <strong>in</strong><br />
some cases to tip the economic equation away<br />
from <strong>sal<strong>in</strong>ity</strong> prevention. Disposal <strong>of</strong> the water <strong>in</strong><br />
a creek or river may be the only way it can be<br />
made cheap enough to be worthwhile protect<strong>in</strong>g<br />
town <strong>in</strong>frastructure, but this clearly requires a<br />
judgement that the damage to the creek or river<br />
system is not excessive. Another proposal is to<br />
use the pumped water to irrigate salt-tolerant<br />
plants, but the feasibility <strong>of</strong> this would need further<br />
<strong>in</strong>vestigation.<br />
2. Social impacts from land use change<br />
Sal<strong>in</strong>ity prevention requires massive land use<br />
change. Few people have appreciated how far<br />
reach<strong>in</strong>g will be the consequences if we are<br />
successful <strong>in</strong> achiev<strong>in</strong>g change on the scale needed.<br />
The experience <strong>of</strong> blue gums on the south coast<br />
reveals that social impacts will be prom<strong>in</strong>ent<br />
among the concerns <strong>of</strong> local communities. There<br />
are grounds to hope that many <strong>of</strong> the social<br />
impacts from new perennials <strong>in</strong> the <strong>Wheatbelt</strong> will<br />
– 2 –<br />
be positive, but this may require government<br />
<strong>in</strong>tervention to curb some <strong>of</strong> the desired activities<br />
<strong>of</strong> bus<strong>in</strong>ess <strong>in</strong>terests. On the other hand, the<br />
<strong>in</strong>volvement <strong>of</strong> such bus<strong>in</strong>ess <strong>in</strong>terests seems<br />
essential to f<strong>in</strong>ance perennial establishment over a<br />
large scale.<br />
3. Budget limits and the need for prioritisation<br />
Protect<strong>in</strong>g assets from <strong>sal<strong>in</strong>ity</strong> is expensive. There<br />
are many assets at risk, and there will never be<br />
enough public money available to protect them all.<br />
Hard decisions will have to be made to prioritise<br />
the assets under threat. Is this wetland more or<br />
less important to protect than that town?<br />
The sort <strong>of</strong> trade-<strong>of</strong>fs <strong>in</strong>volved <strong>in</strong> these examples<br />
are the stuff <strong>of</strong> politics. They will <strong>in</strong>flame<br />
communities, especially those groups who feel<br />
they are losers, but they may also act as catalysts<br />
for community action and consensus.<br />
ECONOMIC COSTS AND BENEFITS OF<br />
SALINITY MANAGEMENT<br />
Until fairly recently, economists consider<strong>in</strong>g <strong>sal<strong>in</strong>ity</strong><br />
most commonly attempted to estimate “the cost<br />
<strong>of</strong> <strong>sal<strong>in</strong>ity</strong>”, usually <strong>in</strong> comparison to a mythical and<br />
unachievable scenario <strong>of</strong> zero <strong>sal<strong>in</strong>ity</strong>. “The cost<br />
<strong>of</strong> <strong>sal<strong>in</strong>ity</strong>” by itself is a concept <strong>of</strong> almost no<br />
practical value (Van Bueren & Pannell 1999;<br />
Bathgate & Pannell 2002). Indeed, the large<br />
estimated costs have probably done more to<br />
mislead th<strong>in</strong>k<strong>in</strong>g about <strong>sal<strong>in</strong>ity</strong> than to improve it.<br />
It is better <strong>in</strong>stead to focus on the costs and<br />
benefits <strong>of</strong> specific management strategies,<br />
allow<strong>in</strong>g for realistic levels <strong>of</strong> effectiveness. As<br />
much as possible, that will be the perspective<br />
taken here.<br />
Agriculture<br />
Sal<strong>in</strong>ity management practices for agriculture are<br />
considered here <strong>in</strong> three categories: prevention,<br />
liv<strong>in</strong>g <strong>with</strong> <strong>sal<strong>in</strong>ity</strong> (adaptation), and repair.<br />
Prevention <strong>of</strong> <strong>sal<strong>in</strong>ity</strong><br />
The term “prevention” is used here to mean<br />
avoidance (<strong>in</strong> part or <strong>in</strong> full) <strong>of</strong> a further worsen<strong>in</strong>g<br />
<strong>in</strong> <strong>sal<strong>in</strong>ity</strong>. It is not <strong>in</strong>tended to imply a reduction <strong>in</strong><br />
current levels <strong>of</strong> <strong>sal<strong>in</strong>ity</strong>. The scales <strong>of</strong> treatments<br />
recommended by hydrologists for prevent<strong>in</strong>g the<br />
various impacts <strong>of</strong> dryland <strong>sal<strong>in</strong>ity</strong> are daunt<strong>in</strong>g,<br />
particularly <strong>in</strong> large wheatbelt valleys. In recent<br />
years, we have lost earlier hopes that large-scale