Post‐fire habitat use of the golden‐backed tree‐rat (Mesembriomys macrurus) in the northwest Kimberley, Western Australia

Fire regimes are changing throughout the world. Changed fire patterns across northern Australian savannas have been proposed as a factor contributing to recent declines of small‐ and medium‐sized mammals. Despite this, few studies have examined the mechanisms that underpin how species use habitat in...

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Published inAustral ecology Vol. 40; no. 8; pp. 941 - 952
Main Authors Hohnen, Rosemary, Tuft, Katherine D, Legge, Sarah, Radford, Ian J, Carver, Scott, Johnson, Christopher N
Format Journal Article
LanguageEnglish
Published Richmond Blackwell Science Asia 01.12.2015
Blackwell Publishing Ltd
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Summary:Fire regimes are changing throughout the world. Changed fire patterns across northern Australian savannas have been proposed as a factor contributing to recent declines of small‐ and medium‐sized mammals. Despite this, few studies have examined the mechanisms that underpin how species use habitat in fire‐affected landscapes. We determined the habitats and resources important to the declining golden‐backed tree‐rat (Mesembriomys macrurus) in landscapes partially burnt by recent intense fire. We aimed to (i) compare the relative use of rainforest and savanna habitats; (ii) examine the effect of fire history on use of savanna habitats; and (iii) identify key foraging and denning resources. Habitat selection was examined by comparing the availability of eight habitat types around real (used) and generated (available) location points. Individuals used a range of habitats, but consistently selected long unburnt rainforest in preference to recently burnt savanna (1–12 months post‐fire); however, recently burnt savanna was used in preference to long unburnt savanna. Tree‐rats foraged in Terminalia hadleyana, Planchonia rupestris, Celtis philippensis and Owenia vernicosa, tree species that are found in a variety of habitat types. Individuals used a range of den sites, including cliffs, trees, logs, scree and stags found throughout the study area. Although multiple factors may have led to the decline of Mes. macrurus across its range, these results are consistent with the idea that changes in the savanna structure as a consequence of contemporary fire patterns could also have a role. The continued persistence of Mes. macrurus in the northwest Kimberley may be supported by land management strategies that conserve fruiting and hollow‐bearing trees, and maintain the availability of fire‐sensitive vegetation types.
Bibliography:http://dx.doi.org/10.1111/aec.12278
istex:729D5F3BB322E6E41927487AC9139CBD36A26126
Australian Wildlife Conservancy
Appendix S1. Vegetation survey methods. Appendix S2. PERMANOVA analysis examining differences in vegetation types at the three sites. Appendix S3. Comparisons of habitat types at the three sites. Appendix S4. Dominant plant species available in eight habitat types at the three sites. Appendix S5. Variables recorded for den trees. Appendix S6. Correlations between number of fixes and estimates of home range area. Appendix S7. Home range estimates and tracking effort for each individual. Appendix S8. Proportion of home range overlap between adjacent individuals. Appendix S9. Den types used by males and females. Appendix S10. Selectivity indices of tree species available for use as dens. Appendix S11. Classification tree using the causal variables that predict if an individual tree was used or unused as a den site. Appendix S12. Tree species M. macrurus were sighted in. Appendix S13. Feeding observations of M. macrurus.
ArticleID:AEC12278
Australian Research Council Linkage Grant - No. LP100100033
ark:/67375/WNG-F3F73Z31-V
Department of Parks and Wildlife (Western Australia)
ObjectType-Article-1
SourceType-Scholarly Journals-1
ObjectType-Feature-2
content type line 23
ISSN:1442-9985
1442-9993
DOI:10.1111/aec.12278