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      The economic cost of losing native pollinator species for orchard production

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          Stability of pollination services decreases with isolation from natural areas despite honey bee visits.

          Sustainable agricultural landscapes by definition provide high magnitude and stability of ecosystem services, biodiversity and crop productivity. However, few studies have considered landscape effects on the stability of ecosystem services. We tested whether isolation from florally diverse natural and semi-natural areas reduces the spatial and temporal stability of flower-visitor richness and pollination services in crop fields. We synthesised data from 29 studies with contrasting biomes, crop species and pollinator communities. Stability of flower-visitor richness, visitation rate (all insects except honey bees) and fruit set all decreased with distance from natural areas. At 1 km from adjacent natural areas, spatial stability decreased by 25, 16 and 9% for richness, visitation and fruit set, respectively, while temporal stability decreased by 39% for richness and 13% for visitation. Mean richness, visitation and fruit set also decreased with isolation, by 34, 27 and 16% at 1 km respectively. In contrast, honey bee visitation did not change with isolation and represented > 25% of crop visits in 21 studies. Therefore, wild pollinators are relevant for crop productivity and stability even when honey bees are abundant. Policies to preserve and restore natural areas in agricultural landscapes should enhance levels and reliability of pollination services. © 2011 Blackwell Publishing Ltd/CNRS.
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            Non-bee insects are important contributors to global crop pollination

            Wild and managed bees are well documented as effective pollinators of global crops of economic importance. However, the contributions by pollinators other than bees have been little explored despite their potential to contribute to crop production and stability in the face of environmental change. Non-bee pollinators include flies, beetles, moths, butterflies, wasps, ants, birds, and bats, among others. Here we focus on non-bee insects and synthesize 39 field studies from five continents that directly measured the crop pollination services provided by non-bees, honey bees, and other bees to compare the relative contributions of these taxa. Non-bees performed 25-50% of the total number of flower visits. Although non-bees were less effective pollinators than bees per flower visit, they made more visits; thus these two factors compensated for each other, resulting in pollination services rendered by non-bees that were similar to those provided by bees. In the subset of studies that measured fruit set, fruit set increased with non-bee insect visits independently of bee visitation rates, indicating that non-bee insects provide a unique benefit that is not provided by bees. We also show that non-bee insects are not as reliant as bees on the presence of remnant natural or seminatural habitat in the surrounding landscape. These results strongly suggest that non-bee insect pollinators play a significant role in global crop production and respond differently than bees to landscape structure, probably making their crop pollination services more robust to changes in land use. Non-bee insects provide a valuable service and provide potential insurance against bee population declines.
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              How much does agriculture depend on pollinators? Lessons from long-term trends in crop production.

              Productivity of many crops benefits from the presence of pollinating insects, so a decline in pollinator abundance should compromise global agricultural production. Motivated by the lack of accurate estimates of the size of this threat, we quantified the effect of total loss of pollinators on global agricultural production and crop production diversity. The change in pollinator dependency over 46 years was also evaluated, considering the developed and developing world separately. Using the extensive FAO dataset, yearly data were compiled for 1961-2006 on production and cultivated area of 87 important crops, which we classified into five categories of pollinator dependency. Based on measures of the aggregate effect of differential pollinator dependence, the consequences of a complete loss of pollinators in terms of reductions in total agricultural production and diversity were calculated. An estimate was also made of the increase in total cultivated area that would be required to compensate for the decrease in production of every single crop in the absence of pollinators. The expected direct reduction in total agricultural production in the absence of animal pollination ranged from 3 to 8 %, with smaller impacts on agricultural production diversity. The percentage increase in cultivated area needed to compensate for these deficits was several times higher, particularly in the developing world, which comprises two-thirds of the land devoted to crop cultivation globally. Crops with lower yield growth tended to have undergone greater expansion in cultivated area. Agriculture has become more pollinator-dependent over time, and this trend is more pronounced in the developing than developed world. We propose that pollination shortage will intensify demand for agricultural land, a trend that will be more pronounced in the developing world. This increasing pressure on supply of agricultural land could significantly contribute to global environmental change.
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                Author and article information

                Journal
                Journal of Applied Ecology
                J Appl Ecol
                Wiley
                0021-8901
                1365-2664
                January 19 2020
                January 19 2020
                Affiliations
                [1 ]Instituto de Investigaciones en Recursos Naturales, Agroecología y Desarrollo Rural Universidad Nacional de Río Negro San Carlos de Bariloche Río Negro Argentina
                [2 ]IRTA Estació Experimental de l'Ebre Tarragona Spain
                [3 ]Centre for Environmental and Climate Research Lund University Lund Sweden
                [4 ]Evolution Génome Comportement et Ecologie CNRSIRDUniversité Paris‐SudUniversité Paris‐Saclay Paris France
                [5 ]Instituto Nacional de Pesquisas da Amazônia - INPA Amazonas Manaus Brazil
                [6 ]Grupo de Ecología de la Polinización INIBIOMAUniversidad Nacional del Comahue and Consejo Nacional de Investigaciones Científicas y Técnicas (CONICET) San Carlos de Bariloche Argentina
                [7 ]Centro Pyme Adeneu Agencia de desarrollo económico del Neuquén Neuquén Argentina
                [8 ]Estación Experimental Agropecuaria Famaillá – Programa Nacional de Apicultura (PROAPI) Instituto Nacional de Tecnología Agropecuaria (INTA) Tucumán Argentina
                [9 ]Instituto de Investigaciones en Recursos Naturales, Agroecología y Desarrollo Rural Consejo Nacional de Investigaciones Científicas y Técnicas San Carlos de Bariloche Río Negro Argentina
                Article
                10.1111/1365-2664.13561
                ce9bb911-de70-46d3-b880-8e218cf1bee2
                © 2020

                http://onlinelibrary.wiley.com/termsAndConditions#vor

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

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