Spatially explicit species distribution models: A missed opportunity in conservation planning?
0106 biological sciences
spatial unit
15. Life on land
spatial autocorrelation
01 natural sciences
integer linear programming ; GUROBI ; spatial autocorrelation ; spatial unit ; Bayesian hierarchical modelling ; connectivity
6. Clean water
integer linear programming
13. Climate action
connectivity
Bayesian hierarchical modelling
14. Life underwater
Gurobi
DOI:
10.1111/ddi.12891
Publication Date:
2019-01-30T08:42:36Z
AUTHORS (7)
ABSTRACT
AbstractAimSystematic conservation planning is vital for allocating protected areas given the spatial distribution of conservation features, such as species. Due to incomplete species inventories, species distribution models (SDMs) are often used for predicting species’ habitat suitability and species’ probability of occurrence. Currently, SDMs mostly ignore spatial dependencies in species and predictor data. Here, we provide a comparative evaluation of how accounting for spatial dependencies, that is, autocorrelation, affects the delineation of optimized protected areas.LocationSoutheast Australia, Southeast U.S. Continental Shelf, Danube River Basin.MethodsWe employ Bayesian spatially explicit and non‐spatial SDMs for terrestrial, marine and freshwater species, using realm‐specific planning unit shapes (grid, hexagon and subcatchment, respectively). We then apply the softwaregurobito optimize conservation plans based on species targets derived from spatial and non‐spatial SDMs (10%–50% each to analyse sensitivity), and compare the delineation of the plans.ResultsAcross realms and irrespective of the planning unit shape, spatially explicit SDMs (a) produce on average more accurate predictions in terms of AUC, TSS, sensitivity and specificity, along with a higher species detection probability. All spatial optimizations meet the species conservation targets. Spatial conservation plans that use predictions from spatially explicit SDMs (b) are spatially substantially different compared to those that use non‐spatial SDM predictions, but (c) encompass a similar amount of planning units. The overlap in the selection of planning units is smallest for conservation plans based on the lowest targets and vice versa.Main conclusionsSpecies distribution models are core tools in conservation planning. Not surprisingly, accounting for the spatial characteristics in SDMs has drastic impacts on the delineation of optimized conservation plans. We therefore encourage practitioners to consider spatial dependencies in conservation features to improve the spatial representation of future protected areas.
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