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Dryandra Woodland - Department of Environment and Conservation ...

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7. Monitor known fungal disease infections. Develop a comprehensive description <strong>of</strong> each<br />

infection, including information on species affected, vegetation association, infection area,<br />

rate <strong>of</strong> spread, soil pr<strong>of</strong>ile, topography <strong>and</strong> threat to ground <strong>and</strong> surface waters. Use this<br />

information to update predicted hazard ratings for vegetation associations in the <strong>Woodl<strong>and</strong></strong>.<br />

8. Investigate possible disease control <strong>and</strong> eradication procedures, while ensuring that they do<br />

not place other areas or values at risk.<br />

19. FIRE<br />

BACKGROUND<br />

Introduction<br />

The management <strong>of</strong> fire in <strong>Dry<strong>and</strong>ra</strong> will need to be flexible to achieve the multiple objectives <strong>of</strong><br />

management. During the term <strong>of</strong> this Plan there will be an on-going requirement for the protection<br />

<strong>of</strong> life, property, <strong>and</strong> the commercial Brown Mallet plantations, <strong>and</strong> an increasing emphasis upon the<br />

maintenance <strong>of</strong> habitat <strong>and</strong> species diversity.<br />

Fire History<br />

We do not have a complete underst<strong>and</strong>ing <strong>of</strong> the fire regimes <strong>of</strong> the wheatbelt area prior to European<br />

settlement. In other south-west areas, however, especially the coastal plain, it is well known that<br />

Aboriginal people used fire to modify their environment <strong>and</strong> increase the availability <strong>of</strong> food<br />

resources. This activity has commonly been termed fire stick farming. The object <strong>of</strong> fire stick<br />

fanning in wooded areas was probably to favour or attract game, <strong>and</strong> to improve access to food<br />

sources such as rivers <strong>and</strong> swamps (Hallam 1985). The present vegetation types have evolved under a<br />

fire regime that was influenced by Aboriginal burning <strong>and</strong> occasional lightning fires.<br />

Since records have been kept, there have been very few wildfires which have started in <strong>Dry<strong>and</strong>ra</strong>. Of<br />

the nine wildfires started in <strong>Dry<strong>and</strong>ra</strong> between 1938 <strong>and</strong> 1985, the largest burnt 260 ha <strong>of</strong> the<br />

<strong>Woodl<strong>and</strong></strong> <strong>and</strong> the average area burnt was 40 ha. Clearing for farml<strong>and</strong> has led to further<br />

fragmentation <strong>and</strong> a reduction in the area <strong>of</strong> native vegetation over this period (see Map 2). To date,<br />

no wildfire has burnt out <strong>of</strong> <strong>Dry<strong>and</strong>ra</strong> into private property. Over this same period, there were<br />

approximately 69 wildfires in surrounding farml<strong>and</strong> within a 20 km radius <strong>of</strong> <strong>Dry<strong>and</strong>ra</strong> fire tower.<br />

The period 1946-1970 was the worst in terms <strong>of</strong> numbers <strong>of</strong> wildfires <strong>and</strong> total area burnt by<br />

wildfire. This was due to the clearing <strong>of</strong> vegetation <strong>and</strong> associated burning which took place after the<br />

Second World War. There have been considerably fewer wildfires since the 1970s following the<br />

reduction in l<strong>and</strong> clearing.<br />

These records suggest that <strong>Dry<strong>and</strong>ra</strong> is under greater threat from wildfires burning into the<br />

<strong>Woodl<strong>and</strong></strong> than vice versa, <strong>and</strong> that the fire risk is lower than for the forests in higher rainfall areas <strong>of</strong><br />

70

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