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      Road verges support pollinators in agricultural landscapes, but are diminished by heavy traffic and summer cutting

      1 , 1 , 2 , 1
      Journal of Applied Ecology
      Wiley

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          Ecosystem services and dis-services to agriculture

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            Landscapes that work for biodiversity and people

            How can we manage farmlands, forests, and rangelands to respond to the triple challenge of the Anthropocene—biodiversity loss, climate change, and unsustainable land use? When managed by using biodiversity-based techniques such as agroforestry, silvopasture, diversified farming, and ecosystem-based forest management, these socioeconomic systems can help maintain biodiversity and provide habitat connectivity, thereby complementing protected areas and providing greater resilience to climate change. Simultaneously, the use of these management techniques can improve yields and profitability more sustainably, enhancing livelihoods and food security. This approach to “working lands conservation” can create landscapes that work for nature and people. However, many socioeconomic challenges impede the uptake of biodiversity-based land management practices. Although improving voluntary incentives, market instruments, environmental regulations, and governance is essential to support working lands conservation, it is community action, social movements, and broad coalitions among citizens, businesses, nonprofits, and government agencies that have the power to transform how we manage land and protect the environment.
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              Is Open Access

              Where is the UK's pollinator biodiversity? The importance of urban areas for flower-visiting insects

              Insect pollinators provide a crucial ecosystem service, but are under threat. Urban areas could be important for pollinators, though their value relative to other habitats is poorly known. We compared pollinator communities using quantified flower-visitation networks in 36 sites (each 1 km2) in three landscapes: urban, farmland and nature reserves. Overall, flower-visitor abundance and species richness did not differ significantly between the three landscape types. Bee abundance did not differ between landscapes, but bee species richness was higher in urban areas than farmland. Hoverfly abundance was higher in farmland and nature reserves than urban sites, but species richness did not differ significantly. While urban pollinator assemblages were more homogeneous across space than those in farmland or nature reserves, there was no significant difference in the numbers of rarer species between the three landscapes. Network-level specialization was higher in farmland than urban sites. Relative to other habitats, urban visitors foraged from a greater number of plant species (higher generality) but also visited a lower proportion of available plant species (higher specialization), both possibly driven by higher urban plant richness. Urban areas are growing, and improving their value for pollinators should be part of any national strategy to conserve and restore pollinators.
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                Author and article information

                Journal
                Journal of Applied Ecology
                J Appl Ecol
                Wiley
                0021-8901
                1365-2664
                August 05 2019
                August 05 2019
                Affiliations
                [1 ]Environment and Sustainability Institute University of Exeter Penryn UK
                [2 ]NERC Centre for Ecology and Hydrology Wallingford UK
                Article
                10.1111/1365-2664.13470
                e126f829-9360-4ae1-ad5b-68f71987feca
                © 2019

                http://doi.wiley.com/10.1002/tdm_license_1.1

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