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Land-use history impacts functional diversity across multiple trophic groups
Le Provost et al., 2019
Land-use history impacts functional diversity across multiple trophic groups
Le Provost et al., 2019
Land-use change is a major driver of biodiversity loss worldwide.
Although biodiversity often shows a delayed response to land-use change,
previous studies have typically focused on a narrow range of current
landscape factors and have largely ignored the role of land-use history
in shaping plant and animal communities and their functional
characteristics. Here, we used a unique database of 220,000 land-use
records to investigate how 20-y of land-use changes have affected
functional diversity across multiple trophic groups (primary producers,
mutualists, herbivores, invertebrate predators, and vertebrate
predators) in 75 grassland fields with a broad range of land-use
histories. The effects of land-use history on multitrophic trait
diversity were as strong as other drivers known to impact biodiversity,
e.g., grassland management and current landscape composition. The
diversity of animal mobility and resource-acquisition traits was lower
in landscapes where much of the land had been historically converted
from grassland to crop. In contrast, functional biodiversity was higher
in landscapes containing old permanent grasslands, most likely because
they offer a stable and high-quality habitat refuge for species with low
mobility and specialized feeding niches. Our study shows that
grassland-to-crop conversion has long-lasting impacts on the functional
biodiversity of agricultural ecosystems. Accordingly, land-use legacy
effects must be considered in conservation programs aiming to protect
agricultural biodiversity. In particular, the retention of permanent
grassland sanctuaries within intensive landscapes may offset ecological
debts.
Importance of the drivers of multitrait diversity, mobility trait
diversity, resource-acquisition trait diversity, and body size trait
diversity. Relative effects (% R2), resulting from a model
averaging procedure, were calculated for each group of predictors (i.e.,
land-use history, current land use, and the species pool). All
predictors were scaled to interpret parameter estimates on a comparable
scale. Note that for mobility, resource-acquisition, and body size trait
diversity, we focused on animal traits and excluded plant traits from
the analyses. Results were consistent considering spatial scales ranging
from 500 to 1500 m radii surrounding the sampled grasslands.
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