Abstract:
We deploy camera traps to monitor feral cat (Felis catus) populations at two pastoral sites in Hawke's Bay, North Island, New Zealand. At Site 1, cameras are deployed at pre-determined GPS points on a 500-m grid, and at Site 2, cameras are strategically deployed with a bias towards forest and forest margin habitat where possible. A portion of cameras are also deployed in open farmland habitat and mixed scrub. We then use the abundance-induced heterogeneity Royle-Nichols model to estimate mean animal abundance and detection probabilities for cameras in each habitat type. Model selection suggests that only cat abundance varies by habitat type. Mean cat abundance is highest at forest margin cameras for both deployment methods (3 cats [95% CI 1.9-4.5] Site 1, and 1.7 cats [95% CI 1.2-2.4] Site 2) but not substantially higher than in forest habitats (1.7 cats [95% CI 0.8-3.6] Site 1, and 1.5 cats [95% CI 1.1-2.0] Site 2). Model selection shows detection probabilities do not vary substantially by habitat (although they are also higher for cameras in forest margins and forest habitats) and are similar between sites (8.6% [95% CI 5.4-13.4] Site 1, and 8.3% [5.8-11.9] Site 2). Cat detections by camera traps are higher when placed in forests and forest margins; thus, strategic placement may be preferable when monitoring feral cats in a pastoral landscape.
