Abstract

AbstractThe estimation of population size remains one of the primary goals and challenges in ecology and provides a basis for debate and policy in wildlife management. Despite the development of efficient noninvasive sampling methods and robust statistical tools to estimate abundance, the maintenance of field sampling is still subject to economic and logistic constraints. These can result in intentional or unintentional interruptions in sampling and cause gaps in data time series, posing a challenge to abundance estimation, and ultimately conservation and management decisions. We applied an open population spatial capture–recapture (OPSCR) model to simulations and a real‐life case study to test the reliability of abundance inference to interruptions in data collection. Using individual detections occurring over consecutive sampling occasions, OPSCR models allow the estimation of abundance while accounting for lack of demographic and geographic closure between occasions. First, we simulated sampling data with interruptions in field sampling of different lengths and timing and checked the performance of an OPSCR model in deriving abundance for species with slow and intermediate life‐history strategies. Next, we introduced artificial sampling interruptions of various magnitudes and timing to a five‐year noninvasive monitoring data set of wolverines (Gulo gulo) in Norway and quantified the consequences for OPSCR model predictions. Inferences from OPSCR models were reliable even with temporal interruptions in monitoring. Interruption did not cause systematic bias, but increased uncertainty. Interruptions occurring at occasions near the beginning and the end of the sampling period caused higher uncertainty. The loss in precision was more severe for species with a faster life‐history strategy. OPSCR allows monitoring studies to provide contiguous abundance estimates to managers, stakeholders, and policy makers even when data are noncontiguous. OPSCR models do not only help cope with unintentional interruptions during sampling but also offer opportunities for using intentional sampling interruptions during the design of cost‐effective population surveys.

Highlights

  • Estimating population size remains one of the most fundamental goals and challenges in wildlife ecology

  • open population spatial capture–recapture (OPSCR) model We built a Bayesian OPSCR model that contained three main components: (1) an encounter model to estimate individual activity centers and account for imperfect detection of individuals (Royle et al 2014), (2) a multistate population dynamic model to estimate recruitment and survival (Seber 1965, Schwarz and Arnason 1996), and (3) a movement model to capture the movement of AC locations between years (Ergon and Gardner 2014)

  • The framework described here allows ecologists to assess the impact of sampling interruptions— whether intentional or unintentional—on parameter estimates from OPSCR models

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Summary

Introduction

Estimating population size remains one of the most fundamental goals and challenges in wildlife ecology. SCR models estimate the location of individual activity centers (ACs) using an observation model that describes the relationship between the spatial pattern of individual encounters and distance from the AC (i.e., detection probability). This allows SCR models to specify the spatial extent over which individuals occur and generate spatially explicit estimates of abundance. The maintenance of long-term data series, which is essential for establishing sound conservation and management plans (Lindenmayer and Likens 2009), can be subject to economic, logistic, and other constraints These can lead to intentional and unintentional interruption in sampling and thereby modify the temporal frequency of sampling (i.e., causing gaps in data time series)

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