Home range and movements of male feral cats (Felis catus) in a semiarid woodland environment in central Australia

被引:70
作者
Edwards, GP [1 ]
de Preu, N [1 ]
Shakeshaft, BJ [1 ]
Crealy, IV [1 ]
Paltridge, RM [1 ]
机构
[1] Pk & Wildlife Commiss No Terr, Alice Springs, NT 0871, Australia
关键词
feral cat; fixed kernel; home range; minimum convex polygon; movement patterns;
D O I
10.1111/j.1442-9993.2001.01091.pp.x
中图分类号
Q14 [生态学(生物生态学)];
学科分类号
071012 ; 0713 ;
摘要
There is a paucity of data on the movement patterns of feral cats in Australia. Such data can be used to refine control strategies and improve track-based methods of monitoring populations of feral cats. In this study the home ranges and movements of male feral cats were examined over 3.5 years in a semiarid woodland environment in central Australia. Two home range estimators were used in the examination: (i) minimum convex polygon (MCP); and (ii) fixed kernel. The most widely used method of estimating home range in feral cats is MCP, while the fixed kernel method can be used to identify core areas within a home range. On the basis of the MCP method, the long-term home ranges of feral cats in central Australia were much larger than those recorded elsewhere (mean, 2210.5 ha). Twenty-four hour home ranges were much smaller (mean, 249.7 ha) and feral cats periodically shifted their 24 h ranges within the bounds of their long-term home ranges. Core area analysis indicated marked heterogeneity of space use by male feral cats. Several instances where feral cats moved large distances (up to 34 km) were recorded. These long distance movements may have been caused by nutritional stress. Using data from the literature, it is shown that prey availability is a primary determinant of long-term home range size in feral cats. The relevance of the results to the design of management strategies for feral cats in central Australia is also discussed.
引用
收藏
页码:93 / 101
页数:9
相关论文
共 58 条
[1]   Evaluation of three relative abundance indices for assessing dingo populations [J].
Allen, L ;
Engeman, R ;
Krupa, H .
WILDLIFE RESEARCH, 1996, 23 (02) :197-206
[2]   Movements and habitat use of feral house cats Felis catus, stoats Mustela erminea and ferrets Mustela furo, in grassland surrounding Yellow-eyed penguin Megadyptes antipodes breeding areas in spring [J].
Alterio, N ;
Moller, H ;
Ratz, H .
BIOLOGICAL CONSERVATION, 1998, 83 (02) :187-194
[3]   THE HOME RANGE - A NEW NONPARAMETRIC-ESTIMATION TECHNIQUE [J].
ANDERSON, DJ .
ECOLOGY, 1982, 63 (01) :103-112
[4]  
[Anonymous], 1999, THREAT ABATEMENT PLA
[5]  
Bayly C.P., 1976, South Aust Nat, V51, P22
[6]   PANTHER HABITAT USE IN SOUTHERN FLORIDA [J].
BELDEN, RC ;
FRANKENBERGER, WB ;
MCBRIDE, RT ;
SCHWIKERT, ST .
JOURNAL OF WILDLIFE MANAGEMENT, 1988, 52 (04) :660-663
[7]   A COMPARISON OF HOME-RANGE ESTIMATORS USING MONTE-CARLO SIMULATION [J].
BOULANGER, JG ;
WHITE, GC .
JOURNAL OF WILDLIFE MANAGEMENT, 1990, 54 (02) :310-315
[8]   WINTER HOME RANGES AND MOVEMENTS OF POLECATS MUSTELA-PUTORIUS IN BIALOWIEZA PRIMEVAL FOREST, POLAND [J].
BRZEZINSKI, M ;
JEDRZEJEWSKI, W ;
JEDRZEJEWSKA, B .
ACTA THERIOLOGICA, 1992, 37 (1-2) :181-191
[9]  
*BUR MET, 1991, CLIM AV MAY 1991
[10]   THRESHOLD MODEL OF FEEDING TERRITORIALITY AND TEST WITH A HAWAIIAN HONEYCREEPER [J].
CARPENTER, FL ;
MACMILLEN, RE .
SCIENCE, 1976, 194 (4265) :639-642