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Dryandra Woodland - Department of Environment and Conservation ...

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the south-west. This is despite <strong>Dry<strong>and</strong>ra</strong> experiencing more severe fire weather conditions than the<br />

main Jarrah forest belt. The primary reasons for the absence <strong>of</strong> large <strong>and</strong> devastating wildfires by<br />

comparison with the main forest belt to the west are:<br />

- the lower levels <strong>and</strong> discontinuous distribution <strong>of</strong> fuels;<br />

- lower spotting distances due to the lack <strong>of</strong> fibrous-barked trees;<br />

- the fragmented nature <strong>of</strong> <strong>Dry<strong>and</strong>ra</strong>;<br />

- the efficient fire detection <strong>and</strong> suppression system; <strong>and</strong><br />

- the reduced range <strong>of</strong> fire causes.<br />

Fire Ecology<br />

Burrows et al. (1987) considered the natural fire frequency at <strong>Dry<strong>and</strong>ra</strong> to be relatively infrequent<br />

based on the following factors:<br />

- the rate <strong>of</strong> litter accumulation is variable, depending on canopy density, but is generally slow. For<br />

most <strong>of</strong> <strong>Dry<strong>and</strong>ra</strong>, litter fuel accumulation rates in the order <strong>of</strong> 0.5 tonnes per year over the first<br />

ten years are typical. Rates slow even further as the canopy ages;<br />

- the high proportion <strong>of</strong> fire sensitive species, ie. those species that are killed outright by full<br />

foliage scorch;<br />

- lack <strong>of</strong> epicormic crown recovery following fire; <strong>and</strong><br />

- the slow post-fire response <strong>of</strong> rootstock species.<br />

Based on these factors, Burrows et al. (1987) considered that infrequent fires in the order <strong>of</strong> every<br />

20-60 years may be important in maintaining a diversity <strong>of</strong> successional stages, but that fires less<br />

than approximately 15 years apart could lead to a change in community floristics <strong>and</strong> structure, eg.<br />

fire sensitive species with a long juvenile period could be eliminated.<br />

While many fire management issues at <strong>Dry<strong>and</strong>ra</strong> are similar to those elsewhere, complicating features<br />

are:<br />

- the difficulty <strong>of</strong> predicting fire effects when regeneration is relatively slow;<br />

- the presence <strong>of</strong> many plant species 'vulnerable' to fire 6 ; <strong>and</strong><br />

- the highly fragmented nature <strong>of</strong> the <strong>Woodl<strong>and</strong></strong>.<br />

In addition, many <strong>of</strong> the native fauna species for which <strong>Dry<strong>and</strong>ra</strong> is noted have specific habitat<br />

requirements that may be maintained through the appropriate management <strong>of</strong> fire. Dense thickets <strong>of</strong><br />

Rock Sheoak, <strong>and</strong> poisonous plants such as Gastrolobium microcarpum, provide protection for the<br />

Woylie <strong>and</strong> Tammar, while hollow W<strong>and</strong>oo logs are <strong>of</strong> particular importance to Numbats.<br />

6 Plant species vulnerable to fire: vulnerability will depend on the stage <strong>of</strong> plant development <strong>and</strong> recent fire history. For<br />

example, it is unlikely that a single fire will be catastrophic, but it may well render the population vulnerable to disturbance<br />

for a period until reproductive capacity recovers.<br />

71

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