CHAPTER 4. MARDO HABITAT PREFERENCES: IDENTIFYING KEY
5. GENERAL DISCUSSION
5.3. Developing and implementing strategies for the rehabilitation of affected and
Presently, Alcoa World Alumina and the Department of Environment and Conservation (DEC) are developing and implementing techniques to rehabilitate regions of the northern jarrah forest severely affected by P. cinnamomi. These rehabilitation techniques, known as Dieback Forest Rehabilitation (DFR) embrace some of the
findings and recommendations of the present study. For example, during the present study large fallen logs were identified as important habitat components to the mardo. Current DFR techniques now ensure that large logs are no longer piled and burnt, but instead they are retained and pushed into strategically located habitat piles. Preliminary trapping surveys show that female mardo are using the log piles for nesting (unpublished report to DEC 2005). Further research and long term monitoring is required. In addition, infested areas are being rehabilitated with P. cinnamomi resistant jarrah and marri as well as other species in an attempt to recreate the vegetation structure and complexity herein identified as important to the mardo. When, present in highly impacted areas, B. sessilis is also being retained. As shown during the present study, dense patches of B. sessilis appear to have a positive influence on mardo patch occupancy.
The conservation of nesting and refuge sites is critical to many small mammal species (van der Ree et al. 2006). Xanthorrhoea preissii is highly susceptible to P. cinnamomi and was identified as a major contributing factor to the presence of mardos. In addition, mardos have been found using X. preissii for nesting (Swinburn et al. 2007). Therefore, a major recommendation from the current study is that further research be conducted to (1) understand why some X. preissii individuals remain in long term degraded areas, (2) determine if there are variations in susceptibility to P. cinnamomi among X. preissii populations and (3) evaluate the feasibility of transplanting and maintaining mature X. preissii individuals to rehabilitate severely degraded sites. Any research conducted to evaluate the transplantation of X. preissii into highly disturbed locations should include phosphite applications or other fungicides to ensure that the plants are not killed by the
5.4. Concluding remarks and management implications
Phytophthora cinnamomi has devastated many native plant communities throughout southern Australia. In Western Australia, the magnitude of the impact has encouraged 40 years of funding, research and policy both at the university and Government level in an attempt to understand the pathogen. However, until the present study, the indirect impact of P. cinnamomi on habitat quality for native fauna has been largely ignored. The present study has been the first to provide definitive evidence that P. cinnamomi is a significant threatening process to a fauna species in Western Australia. As a consequence of this evidence, it is an urgent recommendation that research is continued to further our understanding about the threat P. cinnamomi presents to other Western Australian mammal fauna. Given inevitable funding restrictions, a way forward is to identify key fauna species from different guilds and model their responses to P. cinnamomi. Until such studies have been completed, P. cinnamomi should be considered by all environmental managers and planners as a significant threatening agent to the conservation of native mammal fauna in the south-west of Western Australia.
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