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Underpinnings of fire management for biodiversity conservation in ...

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40<br />

The <strong>fire</strong>-<strong>management</strong> concept – with<strong>in</strong> the context <strong>of</strong> <strong>biodiversity</strong> <strong>conservation</strong> – is that track<br />

networks, <strong>fire</strong>-suppression capacity and potential <strong>fire</strong> behaviours need to be considered together,<br />

not alone, and <strong>in</strong> relation to the short- or long-term risk <strong>of</strong> ext<strong>in</strong>ction <strong>of</strong> plants and animals. Factors<br />

that limit track effectiveness need to be addressed <strong>in</strong> the short- and long-term – e.g. fund<strong>in</strong>g, terra<strong>in</strong>,<br />

environmental effects, equipment and knowledge.<br />

Conclusion<br />

Tracks and roads are seen as an <strong>in</strong>tegral part <strong>of</strong> any bush<strong>fire</strong>-fight<strong>in</strong>g <strong>in</strong>frastructure, but they have<br />

<strong>in</strong>direct and direct effects on the environment, <strong>in</strong>clud<strong>in</strong>g <strong>biodiversity</strong>. In short, these adverse effects<br />

may relate to: dra<strong>in</strong>age l<strong>in</strong>es, erosion and sedimentation; native animals and plants; weeds, diseases<br />

and feral animals; and unwanted ignitions. How can tracks be kept to a m<strong>in</strong>imum and negative<br />

impacts ameliorated? A first premise <strong>in</strong> exam<strong>in</strong><strong>in</strong>g this question is that suppression effectiveness<br />

is maximised by high accessibility. When a grid <strong>of</strong> po<strong>in</strong>ts is used to def<strong>in</strong>e a model area, the shape<br />

<strong>of</strong> the shortest (cheapest?) model track network to reach all these po<strong>in</strong>ts can be described. Hav<strong>in</strong>g<br />

done so, it becomes clear that factors other than access (e.g. <strong>fire</strong> fighter safety, ease <strong>of</strong> burn<strong>in</strong>g out<br />

blocks and cont<strong>in</strong>uous perimeter protection) need to be considered. To accommodate these matters,<br />

model networks can be revised to <strong>in</strong>clude perimeter tracks that def<strong>in</strong>e a series <strong>of</strong> areas <strong>of</strong> land suited<br />

to prescribed burn<strong>in</strong>g. Tracks vary <strong>in</strong> their characteristics, width be<strong>in</strong>g particularly important to the<br />

effectiveness <strong>of</strong> suppression <strong>in</strong> grass<strong>fire</strong>s and <strong>for</strong> traffic flow dur<strong>in</strong>g <strong>fire</strong>s.<br />

If aerial suppression is possible, are tracks needed at all? In <strong>for</strong>ests, aircraft can construct control<br />

l<strong>in</strong>es at about half the rate <strong>of</strong> bulldozers and cost someth<strong>in</strong>g like an order <strong>of</strong> magnitude more<br />

per kilometre. Bare-earth breaks <strong>of</strong> some sort almost <strong>in</strong>variably accompany wet l<strong>in</strong>es laid down<br />

by aircraft as they only provide a temporary hold<strong>in</strong>g function <strong>for</strong> <strong>fire</strong> spread. Bare-earth perimeter<br />

tracks around <strong>fire</strong>s are usually necessary to prevent rek<strong>in</strong>dl<strong>in</strong>g <strong>of</strong> the <strong>fire</strong> and further outbreaks.<br />

From a <strong>biodiversity</strong> po<strong>in</strong>t <strong>of</strong> view, it would be a mistake to th<strong>in</strong>k that aerial suppression can have no<br />

adverse effect, as effects <strong>of</strong> <strong>fire</strong> suppressants and <strong>in</strong>frastructure on the ground can be significant. All<br />

methods <strong>of</strong> suppression have limitations. No system is totally effective unless it is a complete bareearth<br />

system – an impractical, nonsensical extreme. For suppression alone, the concept is that track<br />

networks, suppression capacities and fuel modification need to be considered <strong>in</strong> concert with the <strong>fire</strong><br />

characteristics expected. For the best possible outcomes, suppression operations need to be addressed<br />

<strong>in</strong> relation to land <strong>management</strong> objectives.<br />

There is no s<strong>in</strong>gle simple answer to the question ‘What is the length <strong>of</strong> track is suited to <strong>fire</strong><br />

<strong>management</strong> <strong>of</strong> a reserve?’, partly because length is not the only criterion <strong>for</strong> the establishment <strong>of</strong><br />

a track network. Other criteria <strong>in</strong>clude: the activities that are to be serviced by tracks (e.g. access<br />

to beauty spots, access to <strong>fire</strong>s, egress from <strong>fire</strong>s, prescribed burn<strong>in</strong>g, <strong>fire</strong> suppression, servic<strong>in</strong>g <strong>of</strong><br />

boundary fenc<strong>in</strong>g and feral-animal control); the safety context <strong>of</strong> tracks (e.g. <strong>for</strong> <strong>fire</strong>fighters, general<br />

road users and park rangers); the establishment and servic<strong>in</strong>g cost-implications <strong>of</strong> the track network;<br />

and the limitations to local track networks imposed by the terra<strong>in</strong> (e.g. swamps, rivers, estuaries,<br />

gorges, ridges and sand drifts).<br />

Fire and adaptive <strong>management</strong> <strong>Underp<strong>in</strong>n<strong>in</strong>gs</strong> <strong>of</strong> <strong>fire</strong> <strong>management</strong> <strong>for</strong> <strong>biodiversity</strong> <strong>conservation</strong> <strong>in</strong> reserves

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