Abstract:
The use of camera ‐trap methods, though important, has pitfalls and inconsistencies such as factors and interactions that may influence species photo rates. Jaguar (Panthera onca)c a m e r a‐trap studies place cameras at sites where jaguar detections are likely greater (e.g., sites with previous evidence such tracks, feces, and other presence signs), but do not account for potential placement biases. Our study evaluated methodological implications of a paired camera ‐trap design at trail and off ‐trail locations, and climate seasonality, on photo rates of jaguars, their prey, and competitors. From June 2016 to June 2017, camera traps were deployed at 58 different sites in a hexagon grid array of 3 km 2 each in the Sector Santa Rosa (SSR) of Área de Conservación Guancaste in Costa Rica. Half of the cameras were located at a trail location that jaguars were likely to use, and the other half at an off ‐trail location closest to each hexagon centroid. We estimated a photographic relative abundance index (RAI; no. of independent photos/100 trap nights) and used Generalized Linear Models (GLMs) to assess statistical evidence of trail location and climate seasonality. With a total effort of 19,408 trap nights, we recorded 12,678 independent photo events of 64 species of amphibians, reptiles, birds, and mammals. For the 3 bird species and 14 mammal species we focused on, most Wildlife Society Bulletin 2023;e1428. wileyonlinelibrary.com/journal/wsb | 1o f1 4 https://