4.7 Article

Substituting space for time: Empirical evaluation of spatial replication as a surrogate for temporal replication in occupancy modelling

Journal

JOURNAL OF APPLIED ECOLOGY
Volume 55, Issue 2, Pages 754-765

Publisher

WILEY
DOI: 10.1111/1365-2664.13005

Keywords

camera traps; detection probability; distribution; large carnivores; occupancy models; sign surveys; sloth bear; spatial replication; spatial variation; temporal replication

Funding

  1. Wildlife Conservation Society, New York
  2. Wildlife Conservation Society, India Program
  3. Centre for Wildlife Studies, Bengaluru
  4. Wildlife Conservation Society's Christensen Conservation Leaders Scholarship
  5. Wildlife Conservation Network's Sidney Byers Fellowship
  6. State Forest Department of Karnataka, Government of India
  7. Ministry of Environment, Forests and Climate Change, Government of India

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1. Occupancy models that account for detection probability are important analytical tools in conservation monitoring. Traditionally, occupancy models relied on detection/non-detection data generated from temporal replicates for estimating detectability. Due to logistical challenges and financial costs involved, many large-scale field studies instead use spatial replication as a surrogate. The efficacy of the two approaches and their statistical validity has generally sought support from simulation- based inferences rather than empirical data. 2. Using the sloth bear Melursus ursinus as an example, we compared estimates of occupancy and detection probabilities obtained from temporal and spatial sampling designs. We carried out temporally replicated camera trap surveys and spatially replicated sign surveys across a 754-km(2) area around Bhadra Tiger Reserve in the Western Ghats of India. 3. We sampled along forest/coffee plantation roads in 58 grid cells of 13 km(2) each, treating these cells as independent sites. We used the standard single-season model for the camera trap survey data, and the single-season correlated detections model (with Markovian dependence) for the sign survey data, and incorporated ecological covariates that likely influenced occupancy and detection probabilities. 4. Occupancy estimates from the two surveys and corresponding modelling approaches were similar [(psi) over cap (c)((SE) over cap) = 0.58 (0.03) for camera trap surveys; (psi) over cap (s) ((SE) over cap) = 0.56 (0.03) for sign surveys]. In both cases, the influence of covariates corroborated our a priori predictions. Site-level estimates of occupancy from the two methods were highly correlated (r =.78). We generated a combined estimate of sloth bear occupancy in the region as an inverse-variance weighted average of the two estimates [(psi) over cap((SE) over cap) = 0.57 (0.02)]. 5. Synthesis and applications. Studies that aim to evaluate occupancy models should account for spatial variation in occupancy/detection probabilities, particularly when making inferences on species-habitat relationships. We show that spatial replication can serve as a good surrogate for temporal replication in occupancy studies, which may be useful for distribution assessments of species when field resources are limited or logistical challenges preclude traditional survey approaches that yield temporally replicated data. Our results therefore provide a basis for efficient targeting of funds and field resources, particularly for practitioners involved in monitoring species at large landscape scales.

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