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Underpinnings of fire management for biodiversity conservation in ...

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30<br />

Sizes and shapes <strong>of</strong> areas delimited by track networks<br />

In the previous section a number <strong>of</strong> observations were made about track networks and the pr<strong>in</strong>ciples<br />

that may be applied to them. In this section the sizes, densities and shapes <strong>of</strong> areas def<strong>in</strong>ed by track<br />

networks are considered <strong>in</strong> relation to <strong>fire</strong> suppression. Here, areas are surrounded by tracks and are<br />

usually quite irregular <strong>in</strong> shape, compared with those <strong>in</strong> Figure 2.4.<br />

Consider the areas def<strong>in</strong>ed by perimeter tracks. They could be:<br />

1. Very small so that <strong>fire</strong>s never atta<strong>in</strong> properties that allow them to spread across the<br />

encircl<strong>in</strong>g tracks, even on a day <strong>of</strong> extreme <strong>fire</strong> weather – Fires start from a zero rate <strong>of</strong><br />

spread and accelerate to a quasi-steady state <strong>for</strong> rates <strong>of</strong> spread, flame lengths etc. The quasisteady<br />

state to stop them without active <strong>in</strong>tervention <strong>in</strong> the <strong>for</strong>m <strong>of</strong> burn<strong>in</strong>g out <strong>of</strong> fuels or the<br />

application <strong>of</strong> water and/or retardants may be well above that <strong>for</strong> perimeter tracks. Could <strong>fire</strong>s be<br />

conf<strong>in</strong>ed to areas <strong>in</strong> which <strong>in</strong>tensities were never uncontrollable? Us<strong>in</strong>g this criterion alone, areas<br />

would likely be very small, unless fuel loads were always light and weather never extreme.<br />

2. Small and grouped where there is a history <strong>of</strong> a high density <strong>of</strong> ignitions (by lightn<strong>in</strong>g<br />

or people), close proximity to economic assets or greater chance <strong>of</strong> effective suppression<br />

– Ignitions, proximity to economic assets and ease <strong>of</strong> suppression are not randomly located on<br />

landscapes. In areas where ignitions are more common, assets are denser, and ease <strong>of</strong> suppression<br />

is highest, a group <strong>of</strong> smaller areas might be contemplated. This group <strong>of</strong> areas could represent a<br />

zone <strong>in</strong> which <strong>management</strong> would be more <strong>in</strong>tensive with more track options if one failed. Some<br />

areas that receive high numbers <strong>of</strong> lightn<strong>in</strong>g ignitions, however, may be steep and unsuitable<br />

<strong>for</strong> high-density track networks. They may also be wild areas where tracks are to be avoided, if<br />

possible.<br />

3. Large enough to conta<strong>in</strong> <strong>fire</strong>s with<strong>in</strong> the first day – If areas surrounded by tracks are def<strong>in</strong>ed<br />

<strong>in</strong> such a way that the ma<strong>in</strong> run <strong>of</strong> a <strong>fire</strong> (dur<strong>in</strong>g a long summer afternoon on the day <strong>of</strong> ignition)<br />

is likely to run its course be<strong>for</strong>e reach<strong>in</strong>g a break where it can be conta<strong>in</strong>ed, then the m<strong>in</strong>imum<br />

length <strong>of</strong> track <strong>for</strong> the greatest effect might be obta<strong>in</strong>ed. There are a number <strong>of</strong> problems with this<br />

idea. Variables to consider <strong>in</strong>clude fuel type, ignition location and topography. It may be unknown<br />

just how large a <strong>fire</strong> can grow <strong>in</strong> a day. If a <strong>fire</strong> was travell<strong>in</strong>g at an average <strong>of</strong> 1m sec-1 (3.6 km hr- 1 ), <strong>for</strong> example, then <strong>in</strong> an eight hour run it would travel nearly 30 km (28.8 km). If the width was<br />

about one-third <strong>of</strong> the length, and the <strong>fire</strong> elliptical <strong>in</strong> shape, then the area burnt on this day would<br />

be about 22 000 ha or 220 km2 . Obviously, if the <strong>fire</strong> conveniently just fitted the area blocked out<br />

by tracks it would be nearly 30 km long by 10 km wide, aligned <strong>in</strong> the direction <strong>of</strong> the prevail<strong>in</strong>g<br />

w<strong>in</strong>d. A rectangular block just conta<strong>in</strong><strong>in</strong>g the <strong>fire</strong> would be nearly 30 000ha <strong>in</strong> area. If this was the<br />

size needed on a bad day, then what would happen on the more common days when <strong>fire</strong>s <strong>of</strong> this<br />

magnitude would be most unlikely? Either the <strong>fire</strong> would have to be put out with<strong>in</strong> the area, large<br />

areas <strong>of</strong> fuel would be deliberately burned out to avoid putt<strong>in</strong>g <strong>in</strong> tracks dur<strong>in</strong>g an event or smaller<br />

blocks would have to prevail.<br />

4. Of a size suited to a prescribed <strong>fire</strong> – Prescribed <strong>fire</strong>s may be very small if hand ignited near<br />

valuable assets, or quite large <strong>in</strong> <strong>in</strong>accessible terra<strong>in</strong>. In eucalypt <strong>for</strong>ests, 200 ha per day was<br />

considered reasonable <strong>for</strong> a ground party, but up to 15 000 ha per day when aerial ignition was<br />

carried out with ground support (Luke and McArthur 1978, pp. 144–145).<br />

5. Of a size where edge-based suppression measures reach the entire block – For example, if<br />

tankers that spray up to 30 m from the track are used, then blocks 60 m wide may be considered<br />

ideal. If hose relays are laid out to 1000 m (Gould 2004), then 2000 m is the significant metric <strong>of</strong><br />

block edges. Thus square blocks would be 400 ha <strong>in</strong> area.<br />

6. Of vary<strong>in</strong>g size created by encircl<strong>in</strong>g the <strong>fire</strong> with a new track (conta<strong>in</strong>ment l<strong>in</strong>e) <strong>for</strong><br />

every <strong>fire</strong> – If this is done then any adverse effects <strong>of</strong> tracks are multiplied, even if the effects<br />

are short lived; all the orig<strong>in</strong>al tracks are there yet more are created. Bulldozer tracks or grader<br />

tracks are likely to be visible <strong>for</strong> many years. Firefighters may deem such tracks necessary to halt<br />

the <strong>fire</strong> quickly, to lessen the chances <strong>of</strong> death <strong>of</strong> people or damage to property. In a major <strong>fire</strong>,<br />

suppression l<strong>in</strong>es may be created at successive stages if earlier ones fail. An alternative to the<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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