
Evaluating predictive performance of statistical models explaining wild bee abundance in a mass‐flowering crop
Author(s) -
Blasi Maria,
Bartomeus Ignasi,
Bommarco Riccardo,
Gagic Vesna,
Garratt Michael,
Holzschuh Andrea,
Kleijn David,
Lindström Sandra A. M.,
Olsson Peter,
Polce Chiara,
Potts Simon G.,
Rundlöf Maj,
Scheper Jeroen,
Smith Henrik G.,
SteffanDewenter Ingolf,
Clough Yann
Publication year - 2021
Publication title -
ecography
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 2.973
H-Index - 128
eISSN - 1600-0587
pISSN - 0906-7590
DOI - 10.1111/ecog.05308
Subject(s) - pollinator , pollination , abundance (ecology) , habitat , threatened species , bumblebee , ecology , land cover , geography , land use , agricultural land , biology , pollen
Wild bee populations are threatened by current agricultural practices in many parts of the world, which may put pollination services and crop yields at risk. Loss of pollination services can potentially be predicted by models that link bee abundances with landscape‐scale land‐use, but there is little knowledge on the degree to which these statistical models are transferable across time and space. This study assesses the transferability of models for wild bee abundance in a mass‐flowering crop across space (from one region to another) and across time (from one year to another). The models used existing data on bumblebee and solitary bee abundance in winter oilseed rape fields, together with high‐resolution land‐use crop‐cover and semi‐natural habitats data, from studies conducted in five different regions located in four countries (Sweden, Germany, Netherlands and the UK), in three different years (2011, 2012, 2013). We developed a hierarchical model combining all studies and evaluated the transferability using cross‐validation. We found that both the landscape‐scale cover of mass‐flowering crops and permanent semi‐natural habitats, including grasslands and forests, are important drivers of wild bee abundance in all regions. However, while the negative effect of increasing mass‐flowering crops on the density of the pollinators is consistent between studies, the direction of the effect of semi‐natural habitat is variable between studies. The transferability of these statistical models is limited, especially across regions, but also across time. Our study demonstrates the limits of using statistical models in conjunction with widely available land‐use crop‐cover classes for extrapolating pollinator density across years and regions, likely in part because input variables such as cover of semi‐natural habitats poorly capture variability in pollinator resources between regions and years.