Journal
DIVERSITY AND DISTRIBUTIONS
Volume 21, Issue 3, Pages 357-367Publisher
WILEY
DOI: 10.1111/ddi.12291
Keywords
Buffer zones; conservation biogeography; countryside biogeography; ecological intensification; food security; land sparing; protected areas; sustainable intensification; systematic conservation planning; wildlife-friendly farming
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Funding
- Biotechnology and Biological Sciences Research Council (BBSRC)
- BBSRC [BB/J005851/1] Funding Source: UKRI
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AimConservation conflict takes place where food production imposes a cost on wildlife conservation and vice versa. Where does conservation impose the maximum cost on production, by opposing the intensification and expansion of farmland? Where does conservation confer the maximum benefit on wildlife, by buffering and connecting protected areas with a habitable and permeable matrix of crop and non-crop habitat? Our aim was to map the costs and benefits of conservation versus production and thus to propose a conceptual framework for systematic conservation planning in agricultural landscapes. LocationWorld-wide. MethodsTo quantify these costs and benefits, we used a geographic information system to sample the cropland of the world and map the proportion of non-crop habitat surrounding the cropland, the number of threatened vertebrates with potential to live in or move through the matrix and the yield gap of the cropland. We defined the potential for different types of conservation conflict in terms of interactions between habitat and yield (potential for expansion, intensification, both or neither). We used spatial scan statistics to find hotspots' of conservation conflict. ResultsAll of the hottest' hotspots of conservation conflict were in sub-Saharan Africa, which could have impacts on sustainable intensification in this region. Main conclusionsSystematic conservation planning could and should be used to identify hotspots of conservation conflict in agricultural landscapes, at multiple scales. The debate between land sharing' (extensive agriculture that is wildlife friendly) and land sparing' (intensive agriculture that is less wildlife friendly but also less extensive) could be resolved if sharing and sparing were used as different types of tool for resolving different types of conservation conflict (buffering and connecting protected areas by maintaining matrix quality, in different types of matrix). Therefore, both sharing and sparing should be prioritized in hotspots of conflict, in the context of countryside biogeography.
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