Abstract

Population monitoring is fundamental for informing management decisions aimed at reducing the rapid rate of global biodiversity decline. Herpetofauna are experiencing declines worldwide and include species that are challenging to monitor. Raw counts and associated metrics such as richness indices are common for monitoring populations of herpetofauna; however, these methods are susceptible to bias as they fail to account for varying detection probabilities. Our goal was to develop a program for efficiently monitoring herpetofauna in southern Texas. Our objectives were to (1) estimate detection probabilities in an occupancy modeling framework using trap arrays for a diverse group of herpetofauna and (2) to evaluate the relative effectiveness of funnel traps, pitfall traps, and cover boards. We collected data with 36 arrays at 2 study sites in 2015 and 2016, for 2105 array-days resulting in 4839 detections of 51 species. We modeled occupancy for 21 species and found support for the hypothesis that detection probability varied over our sampling duration for 10 species and with rainfall for 10 species. For herpetofauna in our study, we found 14 and 12 species were most efficiently captured with funnel traps and pitfall traps, respectively, and no species were most efficiently captured with cover boards. Our results show that using methods that do not account for variations in detection probability are highly subject to bias unless the likelihood of false absences is minimized with exceptionally long capture durations. For monitoring herpetofauna in southern Texas, we recommend using arrays with funnel and pitfall traps and an analytical method such as occupancy modeling that accounts for variation in detection.

Highlights

  • Global biodiversity is being lost at a rapid rate (Pimm et al, 2014)

  • Worldwide declines in herpetofauna, coupled with a paucity of information at the population level, prompts the need for more long-term monitoring of these communities

  • Monitoring herpetofauna is challenging and guidelines for establishing monitoring programs remain unclear, with some recommending targets of species richness or relative abundance based on indices that require numerous assumptions (Heyer et al, 1994; Smith & Petranka, 2000; JNCC, 2004)

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Summary

Introduction

Global biodiversity is being lost at a rapid rate (Pimm et al, 2014). Monitoring populations of wildlife is fundamental for conservation and is necessary for evaluating the effectiveness of past management strategies and to inform future management decisions. Due to the paucity of resources available for conservation efforts, identifying and employing efficient monitoring methods are often a primary objective. A monitoring program needs to be capable of detecting a change in population abundance early enough to allow for adjustments in management actions to reach conservation goals. The efficiency of a monitoring strategy must be balanced with the ability to meet specified objectives. Failure to design monitoring capable of meeting objectives will result in wasting limited resources (Legg & Nagy, 2006; Williams et al, 2002)

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