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Wildlife Research Wildlife Research Society
Ecology, management and conservation in natural and modified habitats
RESEARCH ARTICLE

Slow recruitment in a red-fox population following poison baiting: a non-invasive mark–recapture analysis

Oliver Berry A B E F , Jack Tatler A , Neil Hamilton B C , Steffi Hilmer C D , Yvette Hitchen A B and Dave Algar B C
+ Author Affiliations
- Author Affiliations

A School of Animal Biology (M092), The University of Western Australia, Crawley, WA 6009, Australia.

B Invasive Animals Co-operative Research Centre, Building 22, University of Canberra, University Drive South, Bruce, ACT 2617, Australia.

C Department of Parks and Wildlife, PO Box 51, Wanneroo, WA 6946, Australia.

D Johann Wolfgang Goethe-University, Frankfurt am Main 60323, Germany.

E Present address: CSIRO Marine and Atmospheric Research, PMB 5, Floreat, WA 6014, Australia.

F Corresponding author. Email: oliver.berry@csiro.au

Wildlife Research 40(7) 615-623 https://doi.org/10.1071/WR13073
Submitted: 16 April 2013  Accepted: 22 December 2013   Published: 30 January 2014

Abstract

Context: Optimal management of invasive species should determine the interval between lethal-control operations that will sustain a desired population suppression at minimum cost. This requires an understanding of the species’ rate of recruitment following control. These data are difficult to acquire for vertebrate carnivores such as the red fox (Vulpes vulpes), which are not readily trapped or observed.

Aims: To provide a long-term evaluation of the effects of 1080 poison baiting on the abundance and extent of movement of red foxes in a semiarid environment.

Methods: We used non‐invasive DNA sampling of fox hairs in semi-arid Western Australia where the population was subject to two episodes of aerially delivered sodium fluoroacetate (1080) poison baits within 12 months. Sampling took place at ~45-day intervals and individual foxes were identified by genotyping eight microsatellite DNA markers and a gender-specific marker. Open-population and spatially explicit mark–recapture models were used to estimate the density, apparent survival and movements of foxes before and following baiting.

Key results: Following a severe reduction in density after baiting, fox density during the ensuing 12 months increased slowly (0.01 foxes km–2 month–1), such that density had only reached 22% of pre-baiting levels ~10 months after the initial baiting. Moreover, recovery was non‐linear as population growth was negligible for 6 months, then exhibited a nine-fold increase 7–9 months after control, coincident with the dispersal of juveniles in autumn. Fox movements between recaptures were on average 470% greater after baiting than before, in line with expectations for low-density populations, suggesting that the probability of encountering baits during this period would be higher than before baiting.

Conclusions: Baiting with 1080 poison significantly reduced the density of foxes, and the low density was sustained for more than 6 months. Foxes moved significantly further between recaptures after baiting when at low densities.

Implications: Control programs in this region may be carried out at low frequency to suppress fox density to a fraction of unbaited levels. The intensity of follow-up baiting may also be adjusted downwards, to take account of an increased probability of bait encounter in more mobile foxes.


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