Abstract

Biotelemetry is increasingly used to study animal movement at high spatial and temporal resolution and guide conservation and resource management. Yet, limited sample sizes and variation in space and habitat use across regions and life stages may compromise robustness of behavioral analyses and subsequent conservation plans. Here, we assessed variation in (i) home range sizes, (ii) home range selection, and (iii) fine-scale resource selection of white storks across breeding status and regions and test model transferability. Three study areas were chosen within the Central German breeding grounds ranging from agricultural to fluvial and marshland. We monitored GPS-locations of 62 adult white storks equipped with solar-charged GPS/3D-acceleration (ACC) transmitters in 2013-2014. Home range sizes were estimated using minimum convex polygons. Generalized linear mixed models were used to assess home range selection and fine-scale resource selection by relating the home ranges and foraging sites to Corine habitat variables and normalized difference vegetation index in a presence/pseudo-absence design. We found strong variation in home range sizes across breeding stages with significantly larger home ranges in non-breeding compared to breeding white storks, but variation between regions. Home range selection models had high explanatory power and well predicted overall density of Central German white stork breeding pairs. Also, they showed good transferability across regions and breeding status although variable importance varied considerably. Fine-scale resource selection models showed low explanatory power. Resource preferences differed both across breeding status and across regions, and model transferability was poor. Our results indicate that habitat selection of wild animals may vary considerably within and between populations, and is highly scale dependent. Thereby, home range scale analyses show higher robustness whereas fine-scale resource selection is not easily predictable and not transferable across life stages and regions. Such variation may compromise management decisions when based on data of limited sample size or limited regional coverage. We thus recommend home range scale analyses and sampling designs that cover diverse regional landscapes and ensure robust estimates of habitat suitability to conserve wild animal populations.

Highlights

  • Land use change and increasing intensity of agriculture have decreased biodiversity worldwide (Sala et al, 2000; Green, 2005; Morán-Ordóñez et al, 2017), resulting in degraded habitats, displacement of species and population declines (Chamberlain and Fuller, 2000; Flynn et al, 2009; Ripple et al, 2014)

  • Home range selection in white storks was significantly different from random, and the presence of occupied home ranges was well explained by proportional land cover and Normalized Difference Vegetation Index (NDVI) with explained variances of 41–68% (Table 3)

  • Using the model-averaged generalized linear models (GLMs) calibrated on breeding home ranges from the entire study area, we predicted home range suitability across the study region and compared this against observed white stork breeding pair density per municipal district

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Summary

Introduction

Land use change and increasing intensity of agriculture have decreased biodiversity worldwide (Sala et al, 2000; Green, 2005; Morán-Ordóñez et al, 2017), resulting in degraded habitats, displacement of species and population declines (Chamberlain and Fuller, 2000; Flynn et al, 2009; Ripple et al, 2014). Habitat use by animals depends on intrinsic and extrinsic factors, and home ranges and resource selection are strongly driven by the quality and quantity of available resources (Börger et al, 2008; Buchmann et al, 2011). In cultural landscapes, these typically show patchy distributions (Kramer-Schadt et al, 2004; Niebuhr et al, 2015). Habitat or resource preferences may vary depending on these factors (Gadenne et al, 2014)

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