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A road risk map for the European polecat (Mustela putorius, Mammalia, Carnivora, Mustelidae) in Italy

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Abstract

The growing numbers of road infrastructure have a great impact on biodiversity, such as habitat loss, degradation, fragmentation and roads impacts. The European polecat (Mustela putorius) is a small-sized, elusive and poorly studied carnivore that is often fund along roads. We collected 223 records of polecat road casualties in Italy and analysed the relationships with land-cover categories to evaluate factors influencing the risk of road collisions. A buffer of 3 km radius, corresponding to the average home range size of the polecat, was created around each collision site. Within each buffer, we computed the area of each Corine Land Cover category (CLC, III level, 1:250.000). We generate 10000 random points with 3 km buffer along Italian roads to characterize the CLC coverage of the environment. Wilcoxon signed-rank tests were used to check for differences in extent of land-cover categories between road collisions sites and random points. Rice fields (2.1.3), Broad-leaved forests (3.1.1) and Water bodies were significantly overrepresented around collision sites than in background points. Several categories from agricultural areas (i.e. 2.2.3, 2.3.1, 2.4.1, and 2.4.2), forest and seminatural areas (i.e. 3.1.2, 3.1.3, 3.2.2, 3.3.2, and 3.3.4) and wetlands (i.e. 4.1.1) were significantly underrepresented around collision sites than in background points. We discuss the results in the light of known habitat preferences of the species, and dispersal routes.
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REFERENCES - Barrientos, R., & Bolonio, L. (2009). The presence of rabbits adjacent to roads increases polecat road mortality. Biodiversity and Conservation, 18(2), 405-418.;Bon M. (a cura di), 2017. Nuovo atlante dei Mammiferi del Veneto. WBA Monographs, 4, Verona;Grilo, C., Bissonette, J. A., & Santos-Reis,
M. (2009). Spatial–temporal patterns in Mediterranean carnivore road casualties: consequences for mitigation. Biological conservation, 142(2), 301-313.;iNaturalist. Available from http://www.inaturalist.org. Accessed 2017.Ornitho Available http://www.ornitho.it;Rondinini, C., Ercoli, V., & Boitani, L. (2006). Habitat use
and preference by polecats (Mustela putorius L.) in a Mediterranean agricultural landscape. Journal of Zoology, 269(2), 213-219.;THERIO Available http://www.therio.it:Virgós E, Cabezas-Díaz S, Lozano J (2007b) Mustela putorius, Linneaus, 1758. Ficha Libro Rojo. In: Palomo LJ, Gisbert J, Blanco JC (eds) Atlas y Libro
Rojo de los Mamíferos Terrestres de España. Dirección General de Conservación de la Naturaleza-SECEM-SECEMU, Madrid, pp 297–298;Zabala, J., Zuberogoitia, I., & Martínez-Climent, J. A. (2005). Site and landscape features ruling the habitat use and occupancy of the polecat (Mustela putorius) in a low density area:
a multiscale approach. European Journal of Wildlife Research, 51(3), 157-162
OUTCOMES'
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ACKNOWLEDGEMENTS''
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Habitat use and preference by polecats (Mustela putorius L.) in a Mediterranean agricultural landscape Mustela putorius, Linneaus, 1758. Ficha Libro Rojo Site and landscape features ruling the habitat use and occupancy of the polecat (Mustela putorius) in a low density area: a multiscale approach
  • M Rondinini
  • C Ercoli
  • V Boitani
  • L Cabezas-Díaz
  • S Lozano
M. (2009). Spatial-temporal patterns in Mediterranean carnivore road casualties: consequences for mitigation. Biological conservation, 142(2), 301-313.;iNaturalist. Available from http://www.inaturalist.org. Accessed 2017.Ornitho Available http://www.ornitho.it;Rondinini, C., Ercoli, V., & Boitani, L. (2006). Habitat use and preference by polecats (Mustela putorius L.) in a Mediterranean agricultural landscape. Journal of Zoology, 269(2), 213-219.;THERIO Available http://www.therio.it:Virgós E, Cabezas-Díaz S, Lozano J (2007b) Mustela putorius, Linneaus, 1758. Ficha Libro Rojo. In: Palomo LJ, Gisbert J, Blanco JC (eds) Atlas y Libro Rojo de los Mamíferos Terrestres de España. Dirección General de Conservación de la Naturaleza-SECEM-SECEMU, Madrid, pp 297-298;Zabala, J., Zuberogoitia, I., & Martínez-Climent, J. A. (2005). Site and landscape features ruling the habitat use and occupancy of the polecat (Mustela putorius) in a low density area: a multiscale approach. European Journal of Wildlife Research, 51(3), 157-162