Home range of the squirrel glider (Petaurus norfolcensis) in a network of remnant linear habitats

Linear strips of natural or semi-natural vegetation are a characteristic feature of rural landscapes throughout the world. Their value for the conservation of fauna in heavily modified landscapes depends on the response of species to the linear shape of the habitat, and the pressures this imposes on population processes and spatial organization. In south-eastern Australia, woodland habitats occupied by the squirrel glider Petaurus norfolcensis ,at hreatened species of arboreal marsupial, have been preferentially cleared for agriculture leaving only remnants within cleared farmland. In this study, the home range of P. norfolcensis was investigated by radio-tracking 40 gliders within a highly modified landscape where the majority (83%) of remaining wooded habitat occurs as a network of linear strips along roadsides and streams. Individuals were tracked for one to four seasons, resulting in the collection of 4213 independent locational ‘fixes’. All fixes of animals were from remnant woodland. Home ranges were elongated and linear, primarily determined by the shape and arrangement of woodland habitat. Seasonal home ranges were small (mean of 1.4–2.8 ha) and ranged between 320 and 840 m long. Small patches of trees in farmland adjacent to the linear habitats were also extensively used. Despite the highly modified landscape structure, home ranges of P. norfolcensis in the linear network were smaller than those estimated from other studies of this species in continuous habitat. The apparent high quality of the linear habitats is attributed to the density of large old trees, which provide foraging and breeding resources, and the productivity of the environment. Linear landscape elements may have a valuable conservation function where they provide resident habitat or enhance landscape connectivity, bu tt heir long-term viability is vulnerable to disturbance.

[1]  J. Wolff,et al.  Behavioral Model Systems , 1999 .

[2]  Age structure and density of red-capped robin populations vary with habitat size and shape , 1999 .

[3]  Lw Braithwaite,et al.  Studies on the Arboreal Marsupial Fauna of Eucalypt Forests Being Harvested for Wood Pulp at Eden, N.s.w. Iii. Relationships Between Faunal Densities, Eucalypt Occurrence and Foliage Nutrients, and Soil Parent Materials. , 1984 .

[4]  Steven W. Buskirk,et al.  HOME RANGE, TIME, AND BODY SIZE IN MAMMALS' , 1986 .

[5]  R. Forman Land Mosaics: The Ecology of Landscapes and Regions , 1995 .

[6]  Jacques Baudry,et al.  Hedgerow Network Patterns and Processes in France , 1990 .

[7]  R. V. D. Ree,et al.  Ecology of arboreal marsupials in a network of remnant linear habitats , 2000 .

[8]  John A. Wiens,et al.  Landscape mosaics and ecological theory , 1995 .

[9]  G. Merriam,et al.  Fencerow habitats for plants moving between farmland forests , 1993 .

[10]  A. Bennett Linkages in the Landscape: The Role Of Corridors And Connectivity In Wildlife Conservation , 1999 .

[11]  D. Quin Population ecology of the squirrel glider (Petaurus norfolcensis) and the sugar glider (P. breviceps) (Maruspialia:Petauridae) at Limeburners Creek, on the central north coast of New South Wales , 1995 .

[12]  G. W. Arnold,et al.  Factors determining the number and species of birds in road verges in the wheatbelt of western Australia , 1990 .

[13]  A. Bennett,et al.  Home-range use by the brush-tailed phascogale (Phascogale tapoatafa) (Marsupialia) in high-quality, spatially limited habitat , 2001 .

[14]  Robert E. Kenward,et al.  RANGES V: an analysis system for biological location data , 1996 .

[15]  S. Boutin Food supplementation experiments with terrestrial vertebrates: patterns, problems, and the future , 1990 .

[16]  H. Recher,et al.  Retaining remnant mature forest for nature conservation at Eden, New South Wales: a review of theory and practice , 1987 .

[17]  J. Majer,et al.  Eucalypts, arthropods and birds: on the relation between foliar nutrients and species richness , 1996 .

[18]  M. Elgar,et al.  The Use of Corridors by Mammals in Fragmented Australian Eucalypt Forests , 1997 .

[19]  T. Schoener Theory of Feeding Strategies , 1971 .

[20]  G. Suckling Population Ecology of the Sugar Glider, Petaurus breviceps, in a System of Fragmented Habitats , 1984 .

[21]  T. Sparks,et al.  Modelling the Relationship Between Bird Population Variables and Hedgerow and Other Field Margin Attributes. I. Species Richness of Winter, Summer and Breeding Birds , 1994 .

[22]  Robert E. Kenward,et al.  Wildlife radio tagging : equipment, field techniques and data analysis , 1987 .

[23]  A. Bennett,et al.  Woodland remnants along roadsides: a reflection of pre-European structure in temperate woodlands? , 2001 .

[24]  P. Menkhorst,et al.  Distribution, habitat and conservation status of the squirrel glider Petaurus norfolcensis (Petauridae: Marsupialia) in Victoria. , 1988 .

[25]  R. Ree The population ecology of the squirrel glider (Petaurus norfolcensis) within a network of remnant linear habitats , 2002 .

[26]  K. Handasyde,et al.  Seasonal-Variation in the Ranging Behavior of the Platypus (Ornithorhynchus-Anatinus) on the Goulburn River, Victoria , 1995 .

[27]  Rolf A. Ims,et al.  Movement patterns related to spatial structures , 1995 .

[28]  Ian D Clark,et al.  Box-Ironbark: Forests and Woodlands Investigation Resources and Issues Report , 1997 .

[29]  Sandra L. Haire,et al.  Wildlife species richness in shelterbelts: test of a habitat model , 1992 .

[30]  S. Petit,et al.  Hedgerows of the world : their ecological funtions in different landscapes : proceedings of the tenth annual IALE(UK) conference, held at Birmingham University, 5th-8th September 2001 , 2001 .

[31]  Per Wegge,et al.  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? , 1993 .

[32]  Andrew F. Bennett,et al.  ROADS, ROADSIDES AND WILDLIFE CONSERVATION: A REVIEW , 1991 .

[33]  R. Ims,et al.  Space-use responses to habitat fragmentation and connectivity in the root vole Microtus oeconomus , 1998 .

[34]  E. Debevec,et al.  LINEAR HOME RANGES: EFFECTS OF SMOOTHING, SAMPLE SIZE, AND AUTOCORRELATION ON KERNEL ESTIMATES , 2001 .

[35]  D. R. Voigt,et al.  Strategies for Analyzing Radio Tracking Data , 1980 .

[36]  D. Sharpe,et al.  Feeding behaviour of the squirrel glider at Bungawalbin Nature Reserve, north-eastern New South Wales , 1998 .