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Ecology, management and conservation in natural and modified habitats
RESEARCH ARTICLE

Patch use by the greater glider (Petauroides volans) in a fragmented forest ecosystem. I. Home range size and movements

M. L. Pope A B , D. B. Lindenmayer A and R. B. Cunningham A
+ Author Affiliations
- Author Affiliations

A Centre for Resource and Environmental Studies, The Australian National University, Canberra, ACT 0200, Australia.

B Current address: State Forests of New South Wales, Tumut, NSW 2720, Australia.

Wildlife Research 31(6) 559-568 https://doi.org/10.1071/WR02110
Submitted: 29 November 2002  Accepted: 13 February 2004   Published: 23 December 2004

Abstract

This paper examines home-range attributes of 40 greater gliders (Petauroides volans) in five patches of remnant eucalypt forest surrounded by stands of radiata pine (Pinus radiata) near Tumut in south-eastern Australia. Fixed-kernel smoothing methods were used to estimate home-range size for P. volans. For males, home-range size varied from 1.38–4.10 ha (mean = 2.6 ± 0.8 ha, n = 12) and was significantly larger (P < 0.05) than for females (1.26–2.97 ha, mean = 2.0 ± 0.6 ha, n = 11). Home-range size increased significantly with increasing patch size and reduced patch population density. Thus, small patches had more animals per unit area with smaller home ranges and greater home-range overlap.

Our findings illustrate flexibility in the use of space by P. volans. Such results have not previously been reported for P. volans or any other species of arboreal marsupial. Considerable home-range overlap (at 95th percentile isopleth level) was observed between male and female P. volans. Pairs of females also exhibited home-range overlap. Males tended to maintain home ranges exclusive of other males, although some shared common areas. Contrary to the large variations observed in home-range area, core areas (50th isopleth) remained relatively constant, regardless of patch size, population density or sex. This may indicate that core areas are an essential requirement for individuals and resources they contain cannot be shared with congeners.


Acknowledgments

Alan Welsh and Christine Donnelly contributed many important ideas on the analysis of home-range data and assisted with many aspects of the data analysis. Henry Nix provided additional inspiration, insight and funding for this project. Many people assisted with fieldwork for this project but especially Ryan Incoll, Karen Viggers, Chris McGregor and Craig Tribolet. Karen Viggers assisted with the sedation of animals and expert veterinary advice. Ross Meggs from Faunatech Pty Ltd invested significant time and energy in tailoring and building radio-collars. Andrea Taylor kindly allowed access to preliminary genetic data. This project was supported by Land and Water Australia and a M.Sc. scholarship from the Centre for Resource and Environmental Studies at The Australian National University. MLP thanks Bill Foley, Ben Moore and Ivan Lawler, who kindly provided further background information on the use of trees and leaf chemistry. Comments by two anonymous reviewers improved an earlier version of this manuscript.


References

Barbour, M. S. , and Litviatis, J. A. (1993). Niche dimensions of New England cottontails in relation to habitat patch size. Oecologia 95, 321–327.
Digby P. G. N., and Kempton R. A. (Eds) (1987). ‘Multivariate Analysis of Ecological Communities.’ (Chapman and Hall: New York.)

Forman R. T. (1995). ‘Land Mosaics. The Ecology of Landscapes and Regions.’ (Cambridge University Press: New York.)

Gascon, C. , Lovejoy, T. , Bieeregaard, R. O. , Malcolm, J. R. , Stouffer, P. C. , Vasconcelos, H. L. , Laurance, W. F. , Zimmerman, B. , Tocher, M. , and Borges, S. (1999). Matrix habitat and species richness in tropical forest remnants. Biological Conservation 91, 223–229.
Crossref | GoogleScholarGoogle Scholar | Henry S. R. (1984). Social organisation of the greater glider (Petauroides volans) in Victoria. In ‘Possums and Gliders’. (Eds A. P. Smith and I. D. Hume.) pp. 221–228. (Surrey Beatty: Sydney.)

Henry S. (1985). The diet and socioecology of gliding possums in southern Victoria. Ph.D. Thesis, Monash University, Melbourne.

Hooge P. N., Solomon E., and Eichenlaub B. (1999). ‘Animal Movement Program.’ (Alaskan Biological Research Center: Anchorage.)

Ims, R. A. , Rolstad, J. , and Wegge, P. (1993). Predicting space use responses to habitat fragmentation: can voles Microtus oeconomus serve as an experimental model system (EMS) for capercaillie grouse Tetrao urogallus in boreal forest? Biological Conservation 63, 261–268.
Crossref | GoogleScholarGoogle Scholar | Kavanagh R. P. (1987). Floristic and phenological characteristics of a eucalypt forest in relation to its use by arboreal marsupials. M.Sc. Thesis, Australian National University, Canberra.

Kavanagh, R. P. (1988). The impact of predation by the powerful owl, Ninox strenua, on a population of the greater glider, Petauroides volans. Australian Journal of Ecology 13, 445–450.
Kehl J. A., and Borsboom A. (1984). Home ranges, den use and activity patterns in the greater glider Petauroides volans. In ‘Possums and Gliders’. (Eds A. P. Smith and I. D. Hume.) pp. 229–236. (Surrey Beatty: Sydney.)

Krebs, C. J. , Keller, B. L. , and Tamarin, R. H. (1969). Microtus population biology: demographic changes in fluctuating populations of M. ochrogaster and M. pennsylvanicus in southern Indiana. Ecology 50, 587–607.
Norton T. W. (1988). Ecology of greater gliders Petauroides volans Kerr 1792, in relation to variations in habitat quality in eucalypt forests in south-east New South Wales. Ph.D. Thesis, The Australian National University, Canberra.

Possingham H. P.Lindenmayer D. B. and McCarthy M. A. (2001). Population viability analysis. In ‘Encyclopedia of Biodiversity. Volume 4’. pp. 831–843.

Recher H. F., Shields J., Kavanagh R. P., and Webb G. (1987). Retaining remnant mature forest for nature conservation at Eden, New South Wales: a review of theory and practice. In ‘Nature Conservation: the Role of Remnants of Vegetation’. (Eds D. A. Saunders, G. W. Arnold, A. A. Burbidge and A. J. Hopkins.) pp. 177–194. (Surrey Beatty: Sydney.)

Rolstad, J. , and Wegge, P. (1987). Distribution and size of capercaillie leks in relation to old forest fragmentation. Oecologia 72, 389–394.
Saunders D. A., Arnold G. W., Burbridge A. A., and Hopkins A. J. (Eds) (1987). ‘Nature Conservation: The Role of Remnants of Native Vegetation.’ (Surrey Beatty: Sydney.)

Seaman, D. E. , and Powell, R. A. (1996). An evaluation of the accuracy of kernel density estimators for home range analysis. Ecology 77, 2075–2085.
White G. C., and Garrott R. A. (1990). ‘Analysis of Wildlife Radio Tracking Data.’ (Academic Press: San Diego.)

Wolff, J. O. , Schauber, E. M. , and Edge, W. D. (1997). Effects of habitat loss and fragmentation on the behavior and demography of gray-tailed voles. Conservation Biology 11, 945–956.
Crossref | GoogleScholarGoogle Scholar |

Worton, B. J. (1987). A review of models of home range for animal movement. Ecological Modelling 38, 277–298.
Crossref | GoogleScholarGoogle Scholar |

Worton, B. J. (1989). Kernel methods for estimating the utilisation distribution in home range studies. Ecology 70, 164–168.