4.7 Article

Invisible barriers: Differential sanitary regulations constrain vulture movements across country borders

Journal

BIOLOGICAL CONSERVATION
Volume 219, Issue -, Pages 46-52

Publisher

ELSEVIER SCI LTD
DOI: 10.1016/j.biocon.2017.12.039

Keywords

Aegypius monachus; Ecological barriers; EU sanitary policies; Extensive livestock; Gyps fulvus; Iberian Peninsula; Political boundaries; Portugal; Scavengers; Spain

Funding

  1. Consejeria de economia innovacion ciencia y empleo Junta de Andalucia (Proyecto de Excelencia) [2012 RNM-1925]
  2. Comunidad de Bardenas Reales de Navarra (Convenios EBD-CSIC)
  3. MInisterio de Economia, Industria y competitividad [CGL2015-66966-C2-1-2-R]
  4. La Caixa-Severo Ochoa International PhD Program
  5. Severo Ochoa Program for Centres of Excellence in R + D + I [SEV-2012-0262]
  6. MINECO [RYC-2015-19231]
  7. Juan de la Cierva Incorporacion of the Spanish Ministry of Economy and Competitiveness [IJCI-2014-20744]
  8. EDP Biodiversity Chair

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Political boundaries may represent ecological barriers due to differences in wildlife management policies. In the European Union, it might be expected that these differences should be highly diluted, because all countries have to comply with common directives issued by the European Commission. However, the subsidiarity principle may lead to the uneven uptake of European Union regulations, which can impact on biodiversity conservation due to unequal legislation in neighboring countries, particularly in the case of highly mobile organisms. Here we address this issue, by analyzing how EU regulations issued in response to the Bovine Spongiform Encephalopathy (BSE) crisis differentially affected vulture conservation in Portugal and Spain. Taking advantage of the intensive GPS-tracking of 60 griffon (Gyps fulvus) and 11 cinereous vultures (Aegypius monachus) from Spain, we found that the Spanish-Portuguese border acts as a quasi-impermeable barrier. In fact, there was an abrupt decline in the number of vulture locations across the Spanish-Portuguese border, with modelling showing that this was unlikely to be related to differences in land cover or topography. Instead, the pattern found was likely due to differences in trophic resource availability, namely carcasses from extensive livestock husbandry, resulting from the differential application of European sanitary legislation regarding the mandatory removal of dead livestock from the field. Overall, our results should be seen as a warning signal to policy makers and conservation managers, highlighting the need for a stronger integration of sanitary and environmental policies at the European level.

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