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Free food for everyone: artificial feeding of brown bears provides food for many non-target species

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Abstract

Artificial feeding of wildlife is a widely used tool for a range of conservation and management goals. While the effects of artificial feeding on target species have been studied rather extensively, little is known about its effects on non-target species. We used automatic video surveillance to monitor the vertebrate species using artificial feeding sites (n = 20) established primarily for brown bears (Ursus arctos) in Dinaric Mountains, Slovenia. We also studied how type of artificial food (only plant-based food vs. mixed food including carrion) affects the species diversity and assemblage at the feeding sites. In total, we analyzed 117,566 recordings and identified 23 vertebrate taxa, including the brown bear, using the feeding sites. Brown bear, European badger (Meles meles), and red fox (Vulpes vulpes) were the most frequently recorded species. Birds represented a substantial part (46%) of vertebrate community using the feeding sites, including species of a high conservation importance. Feeding sites were regularly used also by species for which intentional artificial feeding is forbidden in study area (e.g., roe deer Capreolus capreolus). Species diversity at the feeding sites was highest in spring while species composition varied both seasonally and according to the type of artificial food (with or without carrion). Our study indicates that artificial feeding affects numerous non-target species, which could have several ecological and management-relevant effects, including potentially undesired consequences. Artificial feeding of wildlife should be carefully planned and we provide recommendations on how to mitigate the side effects on non-target species.

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Acknowledgements

We would like to thank hunters from the Slovenia Forest Service and the Slovenian Hunting Association for their substantial help with the field work. Special thanks to M. Mohorović for her help in establishing the monitoring program and coordinating the activities of camera trapping. Many thanks to all the students that have helped process the photos from camera traps: R. Ule, M. Gagliardi, A. Jerina, L. Gal, F. Feurstein, G. Marolt, L. Stopar, L. Hočevar, and M. Predalič. We are grateful to A. Žagar for database maintenance, R. Luštrik for many useful tips on data organization, M. de Groot for his generous help with the data analysis, and E. Ferreira for useful comments on the early draft.

Funding

Funding for the study was provided by the European LIFE mechanism within the LIFE DINALP BEAR project (LIFE13 NAT/SI/000550). B.C. was supported by Unidade de Vida Selvagem. K.J. and M.K. were additionally supported by the Slovenian Research Agency (J4-7362, P4-0059).

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Appendix

Table 3 List of resident large and mid-sized mammals (> 1 kg in body mass) and nesting birds (> 30 cm in length) present in the Dinaric forest ecosystem in the study area, their relative abundance (abundant, common, uncommon, rare) and distribution (widespread, scattered, local), and number of bear feeding sites (n = 20) at which they were recorded in this study. Vagrant species are not included in the list, except for the one (red kite), which was recorded during the study. Number of visited feeding sites is presented separately for feeding sites without and with carrion. Data sources: Atlas ptic 2018; Kryštufek 1991, authors’ pers. obs
Table 4 Indicator species for site groups, i.e., feeding sites with or without carrion and different seasons (spring, summer, fall). “A” is the positive predicting value of the species abundance as indicator of the site group (specificity). “B” is the probability of finding the species in sites belonging to the site group (fidelity). Significant indicator values (alpha < 0.05) are italicized

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Fležar, U., Costa, B., Bordjan, D. et al. Free food for everyone: artificial feeding of brown bears provides food for many non-target species. Eur J Wildl Res 65, 1 (2019). https://doi.org/10.1007/s10344-018-1237-3

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