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

Ecology Letters (2011) 14: 1062–1072 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 isol...

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Published inEcology letters Vol. 14; no. 10; pp. 1062 - 1072
Main Authors Garibaldi, Lucas A., Steffan-Dewenter, Ingolf, Kremen, Claire, Morales, Juan M., Bommarco, Riccardo, Cunningham, Saul A., Carvalheiro, Luísa G., Chacoff, Natacha P., Dudenhöffer, Jan H., Greenleaf, Sarah S., Holzschuh, Andrea, Isaacs, Rufus, Krewenka, Kristin, Mandelik, Yael, Mayfield, Margaret M., Morandin, Lora A., Potts, Simon G., Ricketts, Taylor H., Szentgyörgyi, Hajnalka, Viana, Blandina F., Westphal, Catrin, Winfree, Rachael, Klein, Alexandra M.
Format Journal Article
LanguageEnglish
Published Oxford, UK Blackwell Publishing Ltd 01.10.2011
Blackwell
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Abstract Ecology Letters (2011) 14: 1062–1072 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.
AbstractList 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.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.
Ecology Letters (2011) 14: 1062–1072 ABSTRACT: 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.
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 1km 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 1km 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.Original Abstract: Ecology Letters (2011) 14: 1062-1072
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.
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.
Ecology Letters (2011) 14: 1062–1072 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.
Ecology Letters (2011) 14: 1062-1072 Abstract 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 1km 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 1km 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. [PUBLICATION ABSTRACT]
Author Holzschuh, Andrea
Mandelik, Yael
Chacoff, Natacha P.
Klein, Alexandra M.
Bommarco, Riccardo
Krewenka, Kristin
Garibaldi, Lucas A.
Steffan-Dewenter, Ingolf
Kremen, Claire
Winfree, Rachael
Cunningham, Saul A.
Morales, Juan M.
Viana, Blandina F.
Westphal, Catrin
Mayfield, Margaret M.
Carvalheiro, Luísa G.
Isaacs, Rufus
Potts, Simon G.
Greenleaf, Sarah S.
Morandin, Lora A.
Ricketts, Taylor H.
Dudenhöffer, Jan H.
Szentgyörgyi, Hajnalka
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Issue 10
Keywords Visitor
Insecta
temporal stability
Apidae
Rural landscape
pollinator services
Environmental management
Bombus
Apis mellifera
Apoidea
Ecosystem services
Bombus spp
sustainable agricultural landscapes
Aculeata
Flower
richness
Rural environment
Stability
Social insect
Environmental design
Pollination
Pollinator
Arthropoda
landscape management
flower visitors
Hymenoptera
Invertebrata
spatial stability
Language English
License CC BY 4.0
2011 Blackwell Publishing Ltd/CNRS.
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Between Luísa Carvalheiro and Rachael Winfree, we choose an alphabetical order of authors, as they contributed equally to this synthesis.
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References Chacoff, N.P. & Aizen, M.A. (2006). Edge effects on flower-visiting insects in grapefruit plantations bordering premontane subtropical forest. J. Appl. Ecol., 43, 18-27.
Klein, A.M., Vaissière, B.E., Cane, J.H., Steffan-Dewenter, I., Cunningham, S.A., Kremen, C. et al. (2007). Importance of pollinators in changing landscapes for world crops. Proc. R. Soc. Lond. B Biol. Sci., 274, 303-313.
Blanche, R. & Cunningham, S.A. (2005). Rain forest provides pollinating beetles for atemoya crops. J. Econ. Entomol., 98, 1193-1201.
Lunn, D.J., Thomas, A., Best, N. & Spiegelhalter, D. (2000). WinBUGS - A Bayesian modelling framework: concepts, structure, and extensibility. Stat. Comput., 10, 325-337.
Bommarco, R., Biesmeijer, J.C., Meyer, B., Potts, S.G., Pöyry, J., Roberts, S.P.M. et al. (2010). Dispersal capacity and diet breadth modify the response of wild bees to habitat loss. Proc. R. Soc. Lond. B Biol. Sci., 277, 2075-2082.
Ricketts, T.H., Regetz, J., Steffan-Dewenter, I., Cunningham, S.A., Kremen, C., Bogdanski, A. et al. (2008). Landscape effects on crop pollination services: are there general patterns? Ecol. Lett., 11, 499-515.
Bogdanski, A. (2005). The Influence of Landscape Context on Flower Visitation and Pollination of Passiflora edulis Sims f. flavicarpa Degener in Central Bahia, Brazil. Department of Animal Ecology and Tropical Biology, University of Würzburg, Würzburg.
Ebeling, A., Klein, A.M., Schumacher, J., Weisser, W.W. & Tscharntke, T. (2008). How does plant richness affect pollinator richness and temporal stability of flower visits? Oikos, 117, 1808-1815.
Morandin, L.A. & Winston, M.L. (2005). Wild bee abundance and seed production in conventional, organic, and genetically modified canola. Ecol. Appl., 15, 871-881.
Winfree, R. & Kremen, C. (2009). Are ecosystem services stabilized by differences among species? A test using crop pollination. Proc. R. Soc. Lond. B Biol. Sci., 276, 229-237.
Haddad, N.M., Crutsinger, G.M., Gross, K., Haarstad, J. & Tilman, D. (2011). Plant diversity and the stability of foodwebs. Ecol. Lett., 14, 42-46.
Kremen, C. (2005). Managing ecosystem services: what do we need to know about their ecology? Ecol. Lett., 8, 468-479.
Meyer, B., Jauker, F. & Steffan-Dewenter, I. (2009). Contrasting resource-dependent responses of hoverfly richness and density to landscape structure. Basic Appl. Ecol., 10, 178-186.
Gathmann, A. & Tscharntke, T. (2002). Foraging ranges of solitary bees. J. Anim. Ecol., 71, 757-764.
Chacoff, N.P., Aizen, M.A. & Aschero, V. (2008). Proximity to forest edge does not affect crop production despite pollen limitation. Proc. R. Soc. Lond. B Biol. Sci., 275, 907-913.
Jauker, F., Diekötter, T., Schwarzbach, F. & Wolters, V. (2009). Pollinator dispersal in an agricultural matrix: opposing responses of wild bees and hoverflies to landscape structure and distance from main habitat. Landscape Ecol., 24, 547-555.
Kremen, C., Williams, N.M. & Thorp, R.W. (2002). Crop pollination from native bees at risk from agricultural intensification. Proc. Natl. Acad. Sci. USA, 99, 16812-16816.
Hoehn, P., Tscharntke, T., Tylianakis, J.M. & Steffan-Dewenter, I. (2008). Functional group diversity of bee pollinators increases crop yield. Proc. R. Soc. Lond. B Biol. Sci., 275, 2283-2291.
Isaacs, R. & Kirk, A.K. (2010). Pollination services provided to small and large highbush blueberry fields by wild and managed bees. J. Appl. Ecol., 47, 841-849.
Westphal, C., Steffan-Dewenter, I. & Tscharntke, T. (2006). Bumblebees experience landscapes at different spatial scales: possible implications for coexistence. Oecologia, 149, 289-300.
Lehman, C.L. & Tilman, D. (2000). Biodiversity, stability, and productivity in competitive communities. Am. Nat., 156, 534-552.
Blanche, K.R., Ludwig, J.A. & Cunningham, S.A. (2006). Proximity to rainforest enhances pollination and fruit set in orchards. J. Appl. Ecol., 43, 1182-1187.
Carré, G., Roche, P., Chifflet, R., Morison, N., Bommarco, R., Harrison-Cripps, J. et al. (2009). Landscape context and habitat type as drivers of bee diversity in European annual crops. Agricult. Ecosys. Environ., 133, 40-47.
Balvanera, P., Pfisterer, A.B., Buchmann, N., He, J.-S., Nakashizuka, T., Raffaelli, D. et al. (2006). Quantifying the evidence for biodiversity effects on ecosystem functioning and services. Ecol. Lett., 9, 1146-1156.
Mayfield, M.M. (2005). The importance of nearby forest to known and potential pollinators of oil palm (Elaeis guineënsis Jacq.; Areceaceae) in southern Costa Rica. Econ. Bot., 59, 190-196.
Chagnon, M., Gingras, J. & De Oliveira, D. (1993). Complementary aspects of strawberry pollination by honey and indigenous bees (Hymenoptera). J. Econ. Entomol., 86, 416-420.
Arthur, A.D., Li, J., Henry, S. & Cunningham, S.A. (2010). Influence of woody vegetation on pollinator densities in oilseed Brassica fields in an Australian temperate landscape. Basic Appl. Ecol., 11, 406-414.
Kremen, C., Williams, N.M., Bugg, R.L., Fay, J.P. & Thorp, R.W. (2004). The area requirements of an ecosystem service: crop pollination by native bee communities in California. Ecol. Lett., 7, 1109-1119.
Osborne, J.L., Martin, A.P., Shortall, C.R., Todd, A.D., Goulson, D., Knight, M.E. et al. (2008). Quantifying and comparing bumblebee nest densities in gardens and countryside habitats. J. Appl. Ecol., 45, 784-792.
Isbell, F.I., Polley, H.W. & Wilsey, B.J. (2009). Biodiversity, productivity and the temporal stability of productivity: patterns and processes. Ecol. Lett., 12, 443-451.
Ghazoul, J. (2006). Floral diversity and the facilitation of pollination. J. Ecol., 94, 295-304.
Cresswell, J.E., Osborne, J.L. & Goulson, D. (2000). An economic model of the limits to foraging range in central place foragers with numerical solutions for bumblebees. Ecol. Entomol., 25, 249-255.
Winfree, R., Williams, N.M., Dushoff, J. & Kremen, C. (2007). Native bees provide insurance against ongoing honey bee losses. Ecol. Lett., 10, 1105-1113.
Winfree, R., Aguilar, R., Vázquez, D.P., LeBuhn, G. & Aizen, M.A. (2009). A meta-analysis of bees' responses to anthropogenic disturbance. Ecology, 90, 2068-2076.
Gelman, A. & Hill, J. (2007). Data Analysis Using Regression and Multilevel/Hierarchical Models. Cambridge University Press, Cambridge, UK.
Doak, D.F., Bigger, D., Harding, E.K., Marvier, M.A., O'Malley, R.E. & Thomson, D. (1998). The statistical inevitability of stability-diversity relationships in community ecology. Am. Nat., 151, 264-276.
McCann, K.S. (2000). The diversity-stability debate. Nature, 405, 228-233.
Ricketts, T.H., Daily, G.C., Ehrlich, P.R. & Michener, C.D. (2004). Economic value of tropical forest to coffee production. Proc. Natl. Acad. Sci. USA, 101, 12579-12582.
Aguilar, R., Ashworth, L., Galetto, L. & Aizen, M.A. (2006). Plant reproductive susceptibility to habitat fragmentation: review and synthesis through a meta-analysis. Ecol. Lett., 9, 968-980.
Proulx, R., Wirth, C., Voigt, W., Weigelt, A., Roscher, C., Attinger, S. et al. (2010). Diversity promotes temporal stability across levels of ecosystem organization in experimental grasslands. PLoS ONE, 5, e13382.
Tscharntke, T., Klein, A.M., Kruess, A., Steffan-Dewenter, I. & Thies, C. (2005). Landscape perspectives on agricultural intensification and biodiversity - ecosystem service management. Ecol. Lett., 8, 857-874.
Klein, A.M., Steffan-Dewenter, I. & Tscharntke, T. (2003a). Fruit set of highland coffee increases with the diversity of pollinating bees. Proc. R. Soc. Lond. B Biol. Sci., 270, 955-961.
Tilman, D., Reich, P.B. & Knops, J.M.H. (2006). Biodiversity and ecosystem stability in a decade-long grassland experiment. Nature, 441, 629-632.
Ricketts, T.H. (2004). Tropical forest fragments enhance pollinator activity in nearby coffee crops. Conserv. Biol., 18, 1262-1271.
Greenleaf, S.S., Williams, N.M., Winfree, R. & Kremen, C. (2007). Bee foraging ranges and their relationship to body size. Oecologia, 153, 589-596.
Royal Society of London (2009). Reaping the Benefits: Science and the Sustainable Intensification of Global Agriculture. The Royal Society, London, UK.
Steffan-Dewenter, I. & Kuhn, A. (2003). Honeybee foraging in differentially structured landscapes. Proc. R. Soc. Lond. B Biol. Sci., 270, 569-575.
Steffan-Dewenter, I., Münzenberg, U., Bürger, C., Thies, C. & Tscharntke, T. (2002). Scale-dependent effects of landscape context on three pollinator guilds. Ecology, 83, 1421-1432.
Garibaldi, L.A., Aizen, M.A., Klein, A.M., Cunningham, S.A. & Harder, L.D. (2011). Global growth and stability in agricultural yield decrease with dependence on pollinator services. Proc. Natl. Acad. Sci. USA, 108, 5909-5914.
Westphal, C., Bommarco, R., Carré, G., Lamborin, E., Morison, N., Petanidou, T. et al. (2008). Measuring bee diversity in different European habitats and biogeographical regions. Ecol. Monogr., 78, 653-671.
Winfree, R., Williams, N.M., Gaines, H., Ascher, J.S. & Kremen, C. (2008). Wild bee pollinators provide the majority of crop visitation across land-use gradients in New Jersey and Pennsylvania, USA. J. Appl. Ecol., 45, 793-802.
Ellis, E.C., Klein Goldewijk, K., Siebert, S., Lightman, D. & Ramankutty, N. (2010). Anthropogenic transformation of the biomes, 1700 to 2000. Global Ecol. Biogeogr., 19, 589-606.
Greenleaf, S.S. & Kremen, C. (2006a). Wild bee species increase tomato production and respond differently to surrounding land use in Northern California. Biol. Conserv., 133, 81-87.
Klein, A.M. (2009). Nearby rainforest promotes coffee pollination by increasing spatio-temporal stability in bee species richness. Forest Ecol. Manag., 258, 1838-1845.
Kremen, C., Williams, N.M., Aizen, M.A., Gemmill-Herren, B., LeBuhn, G., Minckley, R. et al. (2007). Pollination and other ecosystem services produced by mobile organisms: a conceptual framework for the effects of land-use change. Ecol. Lett., 10, 299-314.
Klein, A.M., Cunningham, S.A., Bos, M. & Steffan-Dewenter, I. (2008). Advances in pollination ecology from tropical plantation crops. Ecology, 89, 935-943.
Williams, N.M., Crone, E.
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References_xml – reference: Westphal, C., Steffan-Dewenter, I. & Tscharntke, T. (2006). Bumblebees experience landscapes at different spatial scales: possible implications for coexistence. Oecologia, 149, 289-300.
– reference: Mayfield, M.M. (2005). The importance of nearby forest to known and potential pollinators of oil palm (Elaeis guineënsis Jacq.; Areceaceae) in southern Costa Rica. Econ. Bot., 59, 190-196.
– reference: Winfree, R. & Kremen, C. (2009). Are ecosystem services stabilized by differences among species? A test using crop pollination. Proc. R. Soc. Lond. B Biol. Sci., 276, 229-237.
– reference: Klein, A.M., Vaissière, B.E., Cane, J.H., Steffan-Dewenter, I., Cunningham, S.A., Kremen, C. et al. (2007). Importance of pollinators in changing landscapes for world crops. Proc. R. Soc. Lond. B Biol. Sci., 274, 303-313.
– reference: Kremen, C., Williams, N.M., Bugg, R.L., Fay, J.P. & Thorp, R.W. (2004). The area requirements of an ecosystem service: crop pollination by native bee communities in California. Ecol. Lett., 7, 1109-1119.
– reference: Kremen, C., Williams, N.M., Aizen, M.A., Gemmill-Herren, B., LeBuhn, G., Minckley, R. et al. (2007). Pollination and other ecosystem services produced by mobile organisms: a conceptual framework for the effects of land-use change. Ecol. Lett., 10, 299-314.
– reference: Isbell, F.I., Polley, H.W. & Wilsey, B.J. (2009). Biodiversity, productivity and the temporal stability of productivity: patterns and processes. Ecol. Lett., 12, 443-451.
– reference: Winfree, R., Aguilar, R., Vázquez, D.P., LeBuhn, G. & Aizen, M.A. (2009). A meta-analysis of bees' responses to anthropogenic disturbance. Ecology, 90, 2068-2076.
– reference: McCann, K.S. (2000). The diversity-stability debate. Nature, 405, 228-233.
– reference: Meyer, B., Jauker, F. & Steffan-Dewenter, I. (2009). Contrasting resource-dependent responses of hoverfly richness and density to landscape structure. Basic Appl. Ecol., 10, 178-186.
– reference: Osborne, J.L., Martin, A.P., Shortall, C.R., Todd, A.D., Goulson, D., Knight, M.E. et al. (2008). Quantifying and comparing bumblebee nest densities in gardens and countryside habitats. J. Appl. Ecol., 45, 784-792.
– reference: Pyke, G.H. (1984). Optimal foraging theory: a critical review. Annu. Rev. Ecol. Syst., 15, 523-575.
– reference: Kremen, C. (2005). Managing ecosystem services: what do we need to know about their ecology? Ecol. Lett., 8, 468-479.
– reference: Hoehn, P., Tscharntke, T., Tylianakis, J.M. & Steffan-Dewenter, I. (2008). Functional group diversity of bee pollinators increases crop yield. Proc. R. Soc. Lond. B Biol. Sci., 275, 2283-2291.
– reference: Jauker, F., Diekötter, T., Schwarzbach, F. & Wolters, V. (2009). Pollinator dispersal in an agricultural matrix: opposing responses of wild bees and hoverflies to landscape structure and distance from main habitat. Landscape Ecol., 24, 547-555.
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– reference: Ebeling, A., Klein, A.M., Schumacher, J., Weisser, W.W. & Tscharntke, T. (2008). How does plant richness affect pollinator richness and temporal stability of flower visits? Oikos, 117, 1808-1815.
– reference: Greenleaf, S.S., Williams, N.M., Winfree, R. & Kremen, C. (2007). Bee foraging ranges and their relationship to body size. Oecologia, 153, 589-596.
– reference: Ghazoul, J. (2006). Floral diversity and the facilitation of pollination. J. Ecol., 94, 295-304.
– reference: Greenleaf, S.S. & Kremen, C. (2006a). Wild bee species increase tomato production and respond differently to surrounding land use in Northern California. Biol. Conserv., 133, 81-87.
– reference: Tscharntke, T., Klein, A.M., Kruess, A., Steffan-Dewenter, I. & Thies, C. (2005). Landscape perspectives on agricultural intensification and biodiversity - ecosystem service management. Ecol. Lett., 8, 857-874.
– reference: Chagnon, M., Gingras, J. & De Oliveira, D. (1993). Complementary aspects of strawberry pollination by honey and indigenous bees (Hymenoptera). J. Econ. Entomol., 86, 416-420.
– reference: Klein, A.M. (2009). Nearby rainforest promotes coffee pollination by increasing spatio-temporal stability in bee species richness. Forest Ecol. Manag., 258, 1838-1845.
– reference: Haddad, N.M., Crutsinger, G.M., Gross, K., Haarstad, J. & Tilman, D. (2011). Plant diversity and the stability of foodwebs. Ecol. Lett., 14, 42-46.
– reference: Blüthgen, N. & Klein, A.M. (2011). Functional complementarity and specialisation: the role of biodiversity in plant-pollinator interactions. Basic Appl. Ecol., 12, 282-291.
– reference: Zhang, W., Ricketts, T., Kremen, C., Carney, K. & Swinton, S. (2007). Ecosystem services and dis-services to agriculture. Ecol. Econ., 64, 253-260.
– reference: Lunn, D.J., Thomas, A., Best, N. & Spiegelhalter, D. (2000). WinBUGS - A Bayesian modelling framework: concepts, structure, and extensibility. Stat. Comput., 10, 325-337.
– reference: Arthur, A.D., Li, J., Henry, S. & Cunningham, S.A. (2010). Influence of woody vegetation on pollinator densities in oilseed Brassica fields in an Australian temperate landscape. Basic Appl. Ecol., 11, 406-414.
– reference: Carré, G., Roche, P., Chifflet, R., Morison, N., Bommarco, R., Harrison-Cripps, J. et al. (2009). Landscape context and habitat type as drivers of bee diversity in European annual crops. Agricult. Ecosys. Environ., 133, 40-47.
– reference: Doak, D.F., Bigger, D., Harding, E.K., Marvier, M.A., O'Malley, R.E. & Thomson, D. (1998). The statistical inevitability of stability-diversity relationships in community ecology. Am. Nat., 151, 264-276.
– reference: Gathmann, A. & Tscharntke, T. (2002). Foraging ranges of solitary bees. J. Anim. Ecol., 71, 757-764.
– reference: Westphal, C., Bommarco, R., Carré, G., Lamborin, E., Morison, N., Petanidou, T. et al. (2008). Measuring bee diversity in different European habitats and biogeographical regions. Ecol. Monogr., 78, 653-671.
– reference: Carvalheiro, L.G., Seymour, C.L., Veldtman, R. & Nicolson, S.W. (2010). Pollination services decline with distance from natural habitat even in biodiversity-rich areas. J. Appl. Ecol., 47, 810-820.
– reference: Ricketts, T.H., Regetz, J., Steffan-Dewenter, I., Cunningham, S.A., Kremen, C., Bogdanski, A. et al. (2008). Landscape effects on crop pollination services: are there general patterns? Ecol. Lett., 11, 499-515.
– reference: Chacoff, N.P. & Aizen, M.A. (2006). Edge effects on flower-visiting insects in grapefruit plantations bordering premontane subtropical forest. J. Appl. Ecol., 43, 18-27.
– reference: Bommarco, R., Biesmeijer, J.C., Meyer, B., Potts, S.G., Pöyry, J., Roberts, S.P.M. et al. (2010). Dispersal capacity and diet breadth modify the response of wild bees to habitat loss. Proc. R. Soc. Lond. B Biol. Sci., 277, 2075-2082.
– reference: Winfree, R., Williams, N.M., Dushoff, J. & Kremen, C. (2007). Native bees provide insurance against ongoing honey bee losses. Ecol. Lett., 10, 1105-1113.
– reference: Gelman, A. & Hill, J. (2007). Data Analysis Using Regression and Multilevel/Hierarchical Models. Cambridge University Press, Cambridge, UK.
– reference: Proulx, R., Wirth, C., Voigt, W., Weigelt, A., Roscher, C., Attinger, S. et al. (2010). Diversity promotes temporal stability across levels of ecosystem organization in experimental grasslands. PLoS ONE, 5, e13382.
– reference: Klein, A.M., Steffan-Dewenter, T. & Tscharntke, T. (2003b). Pollination of Coffea canephora in relation to local and regional agroforestry management. J. Appl. Ecol., 90, 837-845.
– reference: Lehman, C.L. & Tilman, D. (2000). Biodiversity, stability, and productivity in competitive communities. Am. Nat., 156, 534-552.
– reference: Chacoff, N.P., Aizen, M.A. & Aschero, V. (2008). Proximity to forest edge does not affect crop production despite pollen limitation. Proc. R. Soc. Lond. B Biol. Sci., 275, 907-913.
– reference: Klein, A.M., Steffan-Dewenter, I. & Tscharntke, T. (2003a). Fruit set of highland coffee increases with the diversity of pollinating bees. Proc. R. Soc. Lond. B Biol. Sci., 270, 955-961.
– reference: Potts, S.G., Biesmeijer, J.C., Kremen, C., Neumann, P., Schweiger, O. & Kunin, W.E. (2010). Global pollinator declines: trends, impacts and drivers. Trends Ecol. Evol., 25, 345-353.
– reference: Blanche, R. & Cunningham, S.A. (2005). Rain forest provides pollinating beetles for atemoya crops. J. Econ. Entomol., 98, 1193-1201.
– reference: Steffan-Dewenter, I. & Kuhn, A. (2003). Honeybee foraging in differentially structured landscapes. Proc. R. Soc. Lond. B Biol. Sci., 270, 569-575.
– reference: Royal Society of London (2009). Reaping the Benefits: Science and the Sustainable Intensification of Global Agriculture. The Royal Society, London, UK.
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– reference: Tilman, D., Reich, P.B. & Knops, J.M.H. (2006). Biodiversity and ecosystem stability in a decade-long grassland experiment. Nature, 441, 629-632.
– reference: Aguilar, R., Ashworth, L., Galetto, L. & Aizen, M.A. (2006). Plant reproductive susceptibility to habitat fragmentation: review and synthesis through a meta-analysis. Ecol. Lett., 9, 968-980.
– reference: Ricketts, T.H., Daily, G.C., Ehrlich, P.R. & Michener, C.D. (2004). Economic value of tropical forest to coffee production. Proc. Natl. Acad. Sci. USA, 101, 12579-12582.
– reference: Bogdanski, A. (2005). The Influence of Landscape Context on Flower Visitation and Pollination of Passiflora edulis Sims f. flavicarpa Degener in Central Bahia, Brazil. Department of Animal Ecology and Tropical Biology, University of Würzburg, Würzburg.
– reference: Ricketts, T.H. (2004). Tropical forest fragments enhance pollinator activity in nearby coffee crops. Conserv. Biol., 18, 1262-1271.
– reference: Steffan-Dewenter, I., Münzenberg, U., Bürger, C., Thies, C. & Tscharntke, T. (2002). Scale-dependent effects of landscape context on three pollinator guilds. Ecology, 83, 1421-1432.
– reference: Blanche, K.R., Ludwig, J.A. & Cunningham, S.A. (2006). Proximity to rainforest enhances pollination and fruit set in orchards. J. Appl. Ecol., 43, 1182-1187.
– reference: Ellis, E.C., Klein Goldewijk, K., Siebert, S., Lightman, D. & Ramankutty, N. (2010). Anthropogenic transformation of the biomes, 1700 to 2000. Global Ecol. Biogeogr., 19, 589-606.
– reference: Isaacs, R. & Kirk, A.K. (2010). Pollination services provided to small and large highbush blueberry fields by wild and managed bees. J. Appl. Ecol., 47, 841-849.
– reference: Winfree, R., Williams, N.M., Gaines, H., Ascher, J.S. & Kremen, C. (2008). Wild bee pollinators provide the majority of crop visitation across land-use gradients in New Jersey and Pennsylvania, USA. J. Appl. Ecol., 45, 793-802.
– reference: Cresswell, J.E., Osborne, J.L. & Goulson, D. (2000). An economic model of the limits to foraging range in central place foragers with numerical solutions for bumblebees. Ecol. Entomol., 25, 249-255.
– reference: Klein, A.M., Cunningham, S.A., Bos, M. & Steffan-Dewenter, I. (2008). Advances in pollination ecology from tropical plantation crops. Ecology, 89, 935-943.
– reference: Aizen, M.A. & Harder, L.D. (2007). Expanding the limits of the pollen-limitation concept: effects of pollen quantity and quality. Ecology, 88, 271-281.
– reference: Kremen, C., Williams, N.M. & Thorp, R.W. (2002). Crop pollination from native bees at risk from agricultural intensification. Proc. Natl. Acad. Sci. USA, 99, 16812-16816.
– reference: Greenleaf, S.S. & Kremen, C. (2006b). Wild bees enhance honey bees' pollination of hybrid sunflower. Proc. Natl Acad. Sci. USA, 103, 13890-13895.
– reference: Williams, N.M., Crone, E.E., Roulston, T.H., Minckley, R.L., Packer, L. & Potts, S.G. (2010). Ecological and life-history traits predict bee species responses to environmental disturbances. Biol. Conserv., 143, 2280-2291.
– reference: Balvanera, P., Pfisterer, A.B., Buchmann, N., He, J.-S., Nakashizuka, T., Raffaelli, D. et al. (2006). Quantifying the evidence for biodiversity effects on ecosystem functioning and services. Ecol. Lett., 9, 1146-1156.
– reference: Morandin, L.A. & Winston, M.L. (2005). Wild bee abundance and seed production in conventional, organic, and genetically modified canola. Ecol. Appl., 15, 871-881.
– volume: 153
  start-page: 589
  year: 2007
  end-page: 596
  article-title: Bee foraging ranges and their relationship to body size
  publication-title: Oecologia
– volume: 258
  start-page: 1838
  year: 2009
  end-page: 1845
  article-title: Nearby rainforest promotes coffee pollination by increasing spatio‐temporal stability in bee species richness
  publication-title: Forest Ecol. Manag.
– volume: 7
  start-page: 1109
  year: 2004
  end-page: 1119
  article-title: The area requirements of an ecosystem service: crop pollination by native bee communities in California
  publication-title: Ecol. Lett.
– year: 2009
– volume: 71
  start-page: 757
  year: 2002
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Snippet Ecology Letters (2011) 14: 1062–1072 Sustainable agricultural landscapes by definition provide high magnitude and stability of ecosystem services, biodiversity...
Sustainable agricultural landscapes by definition provide high magnitude and stability of ecosystem services, biodiversity and crop productivity. However, few...
Ecology Letters (2011) 14: 1062-1072 Abstract Sustainable agricultural landscapes by definition provide high magnitude and stability of ecosystem services,...
Ecology Letters (2011) 14: 1062–1072 ABSTRACT: Sustainable agricultural landscapes by definition provide high magnitude and stability of ecosystem services,...
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SubjectTerms Agricultural land
Agricultural Science
Agriculture
Animal and plant ecology
Animal populations
Animal productions
Animal, plant and microbial ecology
Animals
Apiculture
Apis mellifera
Bees
Bees - physiology
Biodiversity
Biological and medical sciences
Bombus spp
Crop fields
Crop production
Ecosystem
Ecosystem services
ecosystems
Environmental Sciences related to Agriculture and Land-use
flower visitors
Flowers
fruit set
Fruits
Fundamental and applied biological sciences. Psychology
General aspects
Honey
honey bees
Insecta
Invertebrates
issues and policy
Jordbruksvetenskap
Land use
landscape management
landscapes
Miljö- och naturvårdsvetenskap
physiology
Plant reproduction
Pollination
Pollination - physiology
pollinator services
Pollinators
richness
spatial stability
sustainable agricultural landscapes
Sustainable agriculture
temporal stability
Terrestrial animal productions
Terrestrial ecosystems
Title Stability of pollination services decreases with isolation from natural areas despite honey bee visits
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https://onlinelibrary.wiley.com/doi/abs/10.1111%2Fj.1461-0248.2011.01669.x
https://www.ncbi.nlm.nih.gov/pubmed/21806746
https://www.proquest.com/docview/888882251
https://www.proquest.com/docview/1501362328
https://www.proquest.com/docview/900622699
https://www.proquest.com/docview/911153611
https://res.slu.se/id/publ/59351
Volume 14
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