TY - JOUR
T1 - Reptile bycatch in a pest-exclusion fence established for wildlife reintroductions
AU - Roe, J
AU - GEORGES, Arthur
N1 - Funding Information:
We would like to thank the volunteers who helped spotting reptiles in the fence during the field work, also to the Mulligans Flat Nature Reserve park rangers (P. Mills, G. Woodbrigde, J. Lawler) for their support during this investigation, and to colleagues who shared their expertise in some topics in this study (S. Kazemi, G. Hirth, C. Gonzalez-Orozco, M. Boyle, A. Lopez-Aldana, D. Goodwin, M. Young, J. Blackburn, and J. Romero), and who provided references (J. Pickard, G. Kuchling, C.R. Dickman, and B.C. Chessman). Research was conducted under permit CEAE 11-09 from University of Canberra Committee for Ethics in Animal Experimentation, and permit LT2011502 from Environment ACT. The study was funded by the Institute for Applied Ecology , the ACT Herpetological Association and Turtles Australia Inc. BOF was sponsored by an Endeavor International Postgraduate Research Scholarship and a W.J. Weeden Scholarship and the Institute for Applied Ecology.
Publisher Copyright:
© 2014 Elsevier GmbH.
PY - 2014
Y1 - 2014
N2 - Conservation fences have been used as a tool to stop threatening processes from acting against endangered wildlife, yet little is known of the impacts of fences on non-target native species. In this study, we intensively monitored a pest-exclusion fence for 16 months to assess impacts on a reptile community in south-eastern Australia. We registered 1052 reptile records of six species along the fence. Encounters and mortality were greatest for eastern long-necked turtles (Chelodina longicollis), whereas impacts on lizards (Tiliqua rugosa, Tiliqua scincoides, Pogona barbata, Egernia cunninghami) and snakes (Pseudonajatextilis) were more moderate. We recorded several Chelodina longicollis recaptures at the fence and many of these were later found dead at the fence, indicating persistent attempts to navigate past the fence. We conservatively estimate that the fence resulted in the death of 3.3% and disrupted movements of 20.9% of the turtle population within the enclosure. Movement disruption and high mortality were also observed for turtles attempting to enter the nature reserve, effectively isolating the reserve population from others in the wider landscape. Of 98 turtle mortalities, the most common cause of death was overheating, followed by predation, vehicular collision, and entanglement. Turtle interactions were clustered in areas with more wetlands and less urban development, and temporally correlated with high rainfall and solar radiation, and low temperature. Thus, managers could focus at times and locations to mitigate impacts on turtles. We believe the impact of fences on non-target species is a widespread and unrecognized threat, and suggest that future and on-going conservation fencing projects consider risks to non-target native species, and where possible, apply mitigation strategies that maintain natural movement corridors and minimize mortality risk.
AB - Conservation fences have been used as a tool to stop threatening processes from acting against endangered wildlife, yet little is known of the impacts of fences on non-target native species. In this study, we intensively monitored a pest-exclusion fence for 16 months to assess impacts on a reptile community in south-eastern Australia. We registered 1052 reptile records of six species along the fence. Encounters and mortality were greatest for eastern long-necked turtles (Chelodina longicollis), whereas impacts on lizards (Tiliqua rugosa, Tiliqua scincoides, Pogona barbata, Egernia cunninghami) and snakes (Pseudonajatextilis) were more moderate. We recorded several Chelodina longicollis recaptures at the fence and many of these were later found dead at the fence, indicating persistent attempts to navigate past the fence. We conservatively estimate that the fence resulted in the death of 3.3% and disrupted movements of 20.9% of the turtle population within the enclosure. Movement disruption and high mortality were also observed for turtles attempting to enter the nature reserve, effectively isolating the reserve population from others in the wider landscape. Of 98 turtle mortalities, the most common cause of death was overheating, followed by predation, vehicular collision, and entanglement. Turtle interactions were clustered in areas with more wetlands and less urban development, and temporally correlated with high rainfall and solar radiation, and low temperature. Thus, managers could focus at times and locations to mitigate impacts on turtles. We believe the impact of fences on non-target species is a widespread and unrecognized threat, and suggest that future and on-going conservation fencing projects consider risks to non-target native species, and where possible, apply mitigation strategies that maintain natural movement corridors and minimize mortality risk.
KW - Dispersal
KW - Habitat fragmentation
KW - Hot moments
KW - Hotspots
KW - Mortality
KW - Predator-proof fence
UR - http://www.scopus.com/inward/record.url?scp=84930046805&partnerID=8YFLogxK
U2 - 10.1016/j.jnc.2014.08.014
DO - 10.1016/j.jnc.2014.08.014
M3 - Article
SN - 1617-1381
VL - 22
SP - 577
EP - 585
JO - Journal for Nature Conservation
JF - Journal for Nature Conservation
IS - 6
ER -