Abstract
Context
As agricultural demands for land continues to expand, strategies are urgently needed to balance agricultural production with biodiversity conservation and ecosystem service provision in agricultural landscapes.
Objectives
We used a factorial landscape design to assess the relative contributions of forest proximity and local forest cover to bee diversity and the provision of coffee pollination services.
Methods
We quantified bee diversity and fruit set in 24 sun-grown coffee fields in Southeast Region of Brazil that were selected following a factorial sampling design to test the independent effects of local forest cover (in a radius of 400 m) and proximity to forest fragments. To assess the impact of landscape simplification, we also evaluated local coffee cover.
Results
Bee richness and abundance were higher in the proximity of forest fragments, but only bee abundance decreased when the coffee cover dominated the surrounding landscapes. Coffee fruit set was 16% higher overall with bee visitations compared with bee exclusion and increased to 20% when coffee bushes were near forest fragments, and the coffee cover was low. Surprisingly, local forest cover did not affect the bee community or coffee fruit set.
Conclusion
Our results provide clear evidence that the proximity of coffee crops to forest fragments can affect the abundance and richness of bees visiting the coffee flowers and thereby facilitate the provision of pollination services. The positive association between forest proximity and fruit set reinforces the importance of natural vegetation in enhancing bee diversity and, therefore, in the provision of pollination services. The negative effect of coffee cover on fruit set at the local scale suggests that the service demand can surpass the capacity of pollinators to provide it. These effects were independent of the local forest cover, although all studied landscapes had more than 20% remaining forest cover (within a 2 km radius), which is considered the extinction threshold for Atlantic Forest species. Interspersion of forest fragments and coffee plantations in regions with more than 20% of forest cover left could thus be a useful landscape management target for facilitating pollinator flows to coffee crops and thus for increasing coffee yields.
Similar content being viewed by others
References
Aizen MA, Garibaldi LA, Cunningham SA, Klein AM (2009) How much does agriculture depend on pollinators? Lessons from long-term trends in crop production. Ann Bot 103:1579–1588
Araújo ED, Costa M, Chaud-Netto J, Fowler HG (2004) Body size and flight distance in stingless bees (Hymenoptera: Meliponini): inference of flight range and possible ecological implications. Braz J Biol 64:563–568
Aristizábal N, Metzger JP (2019) Landscape structure regulates pest control provided by ants in sun coffee farms. J Appl Ecol 56:21–30
Banks-Leite C, Pardini R, Tambosi LR, Pearse WD, Bueno AA, Bruscagin RT, Condez TH, Dixo M, Igari AT, Martensen AC, Metzger JP (2014) Using ecological thresholds to evaluate the costs and benefits of set-asides in a biodiversity hotspot. Science 80(345):1041–1045
Barton K (2015) MuMIn: Multi-model inference. R package version 1.9.13. Version 1:18. 11961261
Batáry P, Báldi A, Kleijn D, Tscharntke T (2011) Landscape-moderated biodiversity effects of agri-environmental management: a meta-analysis. Proc Biol Sci 278:1894–1902
Bates D, Mächler M, Bolker BM, Walker SC (2015) Fitting linear mixed-effects models using lme4. J Stat Softw 67:1. https://doi.org/10.18637/jss.v067.i01
Batista MA, Ramalho M, Soares AEE (2003) Nesting sites and abundance of Meliponini (Hymenoptera: Apidae) in heterogeneous habitats of the Atlantic Rain Forest, Bahia, Brazil. Lundiana 4:19–23
Benjamin FE, Reilly JR, Winfree R (2014) Pollinator body size mediates the scale at which land use drives crop pollination services. J Appl Ecol 51:440–449
Benton TG, Vickery JA, Wilson JD (2003) Farmland biodiversity: is habitat heterogeneity the key? Trends Ecol Evol 18:182–188
Blitzer EJ, Dormann CF, Holzschuh A, Klein AM, Rand TA, Tscharntke T (2012) Spillover of functionally important organisms between managed and natural habitats. Agric Ecosyst Environ 146:34–43. https://doi.org/10.1016/J.AGEE.2011.09.005
Boesing AL, Nichols E, Metzger JP (2018) Biodiversity extinction thresholds are modulated by matrix type. Ecography 41(9):1520–1533
Brosi BJ, Daily GC, Shih TM, Oviedo F, Durán G (2008) The effects of forest fragmentation on bee communities in tropical countryside. J Appl Ecol 45:773–783
Burnham KP, Anderson DR (2002) Model selection and multimodel inference: a practical information-theoretic approach. Springer, New York
Burton RJF, Kuczera C, Schwarz G (2008) Exploring farmers’ cultural resistance to voluntary agri-environmental schemes. Sociol Ruralis 48:16–37
Connelly H, Poveda K, Loeb G (2015) Landscape simplification decreases wild bee pollination services to strawberry. Agric Ecosyst Environ 211:51–56
Dainese M, Martin EA, Aizen M , Albrecht M, Bartomeus I, Bommarco R, Ghazoul J (2019) A global synthesis reveals biodiversity-mediated benefits for crop production. Sci Adv 5:554170
DaMatta FM (2004) Ecophysiological constraints on the production of shaded and unshaded coffee: a review. F Crop Res 86:99–114
De Marco P, Coelho FM (2004) Services performed by the ecosystem: Forest remnants influence agricultural cultures’ pollination and production. Biodivers Conserv 13:1245–1255
Ekroos J, Olsson O, Rundlöf M, Wätzold F, Smith HG (2014) Optimizing agri-environment schemes for biodiversity, ecosystem services or both? Biol Conserv 172:65–71
Fahrig L (2003) Effects of habitat fragmentation on biodiversity. Annu Rev Ecol Syst 34:487–515
Fahrig L (2013) Rethinking patch size and isolation effects: the habitat amount hypothesis. J Biogeogr 40:1649–1663
Foley JA, Ramankutty N, Brauman KA, Cassidy ES, Gerber JS, Johnston M, Balzer C (2011) Solutions for a cultivated planet. Nature 478:337–342
Garibaldi LA, Carvalheiro LG, Vaissiere BE, Gemmill-Herren B, Hipólito J, Freitas BM, An J (2016) Mutually beneficial pollinator diversity and crop yield outcomes in small and large farms. Science 351:388–391
Garibaldi LA, Steffan-Dewenter I, Kremen C, Morales JM, Bommarco R, Cunningham SA, Holzschuh A (2011) Stability of pollination services decreases with isolation from natural areas despite honey bee visits. Ecol Lett 14:1062–1072
Garibaldi LA, Steffan-Dewenter I, Winfree R, Aizen MA, Bommarco R, Cunningham SA, Bartomeus I (2013) Wild pollinators enhance fruit set of crops regardless of honey bee abundance. Science 340:1608–1611
Giannini TC, Garibaldi LA, Acosta AL, Silva JS, Maia KP, Saraiva AM, Kleinert AM (2015) Native and non-native supergeneralist bee species have different effects on plant-bee networks. PLoS ONE 10:e0137198
Gibbs HK, Ruesch AS, Achard F, Clayton MK, Holmgren P, Ramankutty N, Foley JA (1990) Tropical forests were the primary sources of new agricultural land in the 1980s and 1990s. Proc Natl Acad Sci USA 107:16732–16737
Goulson D, Nicholls E, Botías C, Rotheray EL (2015) Bee declines driven by combined Stress from parasites, pesticides, and lack of flowers. Science 347:6229
Hartig F (2017) Package “DHARMa” Title Residual Diagnostics for Hierarchical (Multi-Level/Mixed) Regression Models
Hipólito J, Boscolo D, Viana BF (2018) Landscape and crop management strategies to conserve pollination services and increase yields in tropical coffee farms. Agric Ecosyst Environ 256:218–225
Holzschuh A, Dainese M, González-Varo JP, Mudri-Stojnić S, Riedinger V, Rundlöf M, Kleijn D (2016) Mass-flowering crops dilute pollinator abundance in agricultural landscapes across Europe. Ecol Lett 19:1228–1236
Holzschuh A, Dormann CF, Tscharntke T, Steffan-Dewenter I (2011) Expansion of mass-flowering crops leads to transient pollinator dilution and reduced wild plant pollination. Proc R Soc B Biol Sci 278:3444–3451
Jaffé R, Castilla A, Pope N, Imperatriz-Fonseca VL, Metzger JP, Arias MC, Jha S (2015) Landscape genetics of a tropical rescue pollinator. Conserv Genet. https://doi.org/10.1007/s10592-015-0779-0
Jha S, Vandermeer JH (2009) Contrasting bee foraging in response to resource scale and local habitat management. Oikos 118:1174–1180
Kennedy CM, Lonsdorf E, Neel MC, Williams NM, Ricketts TH, Winfree R, Carvalheiro LG (2013) A global quantitative synthesis of local and landscape effects on wild bee pollinators in agroecosystems. Ecol Lett 16:584–599
Klein AM (2009) Nearby rainforest promotes coffee pollination by increasing spatio-temporal stability in bee species richness. For Ecol Manag 258:1838–1845
Klein A-M, Steffan-Dewenter I, Tscharntke T (2003a) Fruit set of highland coffee increases with the diversity of pollinating bees. Proc R Soc B Biol Sci 270:955–961
Klein AM, Steffan-Dewenter I, Tscharntke T (2003b) Bee pollination and fruit set of Coffea arabica and C. canephora (Rubiaceae). Am J Bot 90:153–157
Krishnan S, Kushalappa CG, Shaanker RU, Ghazoul J (2012) Status of pollinators and their efficiency in coffee fruit set in a fragmented landscape mosaic in South India. Basic Appl Ecol 13:277–285
Librán-Embid F, De Coster G, Metzger JP (2017) Effects of bird and bat exclusion on coffee pest control at multiple spatial scales. Landsc Ecol 32:1907–1920
Lichtenberg EM, Mendenhall CD, Brosi B (2017) Foraging traits modulate stingless bee community disassembly under forest loss. J Anim Ecol 86:1404–1416
Losey JE, Vaughn M (2006) The economic value of ecological services provided by insects. Bioscience 56:311
Martin EA, Dainese M, Clough Y, Báldi A, Bommarco R, Gagic V, Marini L (2019) The interplay of landscape composition and configuration: new pathways to manage functional biodiversity and agroecosystem services across Europe. Ecol Lett 22:1083–1094
Metzger JP, Bustamante MMC, Ferreira J, Fernandes GW, Librán-Embid F, Pillar VD, Overbeck GE (2019) Why Brazil needs its Legal Reserves. Perspect Ecol Conserv. https://doi.org/10.1016/j.pecon.2019.07.002
Mitchell MGE, Suarez-Castro AF, Martinez-Harms M, Maron M, McAlpine C, Gaston KJ, Rhodes JR (2015) Reframing landscape fragmentation’s effects on ecosystem services. Trends Ecol Evol 30:190–198
Moreira EF, Boscolo D, Viana BF (2015) Spatial heterogeneity regulates plant-pollinator networks across multiple landscape scales. PLoS ONE 10:1–19
Moure JS, Melo GAR, Vivallo F (2012) Catalogue of Bees (Hymenoptera, Apoidea) in the Neotropical Region - online version. https://www.moure.cria.org.br/catalogue
Munyuli T (2011) Factors governing flower visitation patterns and quality of pollination services delivered by social and solitary bee species to coffee in central Uganda. Afr J Ecol 49:501–509
Ngo HT, Mojica AC, Packer L (2011) Coffee plant – pollinator interactions: a review. Can J Zool 89:647–660
Olschewski R, Tscharntke T, Benítez PC, Schwarze S, Klein AM (2006) Economic evaluation of pollination services comparing coffee landscapes in Ecuador and Indonesia. Ecol Soc 11:7
Perfecto I, Vandermeer J (2010) The agroecological matrix as alternative to the land-sparing/agriculture intensification model. Proc Natl Acad Sci USA 107:5786–5791
Potts SG, Biesmeijer JC, Kremen C, Neumann P, Schweiger O, Kunin WE (2010) Global pollinator declines: trends, impacts and drivers. Trends Ecol Evol 25:345–353. https://doi.org/10.1016/j.tree.2010.01.007
Quinn GP, Keough MJ (2002) Experimental design and data analysis for biologists. Cambridge University Press, Cambridge
R Develop Core Team (2018) R: a language and environment for statistical computing. Vienna, Austria: R Foundation for Statistical Computing. Retrieved from https://www.T-project.org/
Renner S (1983) The widespread occurrence of anther destruction by Trigona bees in Melastomataceae. Biotropica. https://doi.org/10.2307/2387649
Rezende CL, Scarano FR, Assad ED, Joly CA, Metzger JP, Strassburg BBN, Mittermeier RA (2018) From hotspot to hopespot: an opportunity for the Brazilian Atlantic Forest. Perspect Ecol Conserv 16:208–214
Ribeiro MC, Metzger JP, Martensen AC, Ponzoni FJ, Hirota MM (2009) The Brazilian Atlantic Forest: how much is left, and how is the remaining forest distributed? Implications for conservation. Biol Conserv 142:1141–1153
Ricketts TH (2004) Tropical forest fragments enhance pollinator activity in nearby coffee crops\rfragmentos de bosque tropical incrementan la actividad de polinizadores en cultivos de café cercanos. Conserv Biol 18:1262–1271
Ricketts T, Daily G, Ehrlich P, Michener C (2004) Economic value of tropical forest to coffee production. Proc Natl Acad Sci USA 101:12579–12661
Ricketts TH, Regetz J, Steffan-Dewenter I, Cunningham SA, Kremen C, Bogdanski A, Morandin LA (2008) Landscape effects on crop pollination services: are there general patterns? Ecol Lett 11:499–515
Roubik DW (2000) Pollination system stability in tropical America. Conserv Biol 14:1235–1236
Saturni FT, Jaffé R, Metzger JP (2016) Landscape structure influences bee community and coffee pollination at different spatial scales. Agric Ecosyst Environ 235:1–12
Saunders ME, Peisley RK, Rader R, Luck GW (2015) Pollinators, pests, and predators: recognizing ecological trade-offs in agroecosystems. Ambio 45:4–14
Sirami C, Gross N, Baillod AB, Bertrand C, Carrié R, Hass A, Girard J (2019) Increasing crop heterogeneity enhances multitrophic diversity across agricultural regions. Proc Natl Acad Sci USA 116:16442–16447
Taki H, Kevan PG, Ascher JS (2007) Landscape effects of forest loss in a pollination system. Landsc Ecol 22:1575–1587
Tscharntke T, Tylianakis JM, Rand TA, Didham RK, Fahrig L, Batáry P, Ewers RM (2012) Landscape moderation of biodiversity patterns and processes—eight hypotheses. Biol Rev 87:661–685
Vanbergen AJ (2013) Threats to an ecosystem service: pressures on pollinators. Front Ecol Environ 11:251–259
Veddeler D, Klein AM, Tscharntke T (2006) Contrasting responses of bee communities to coffee flowering at different spatial scales. Oikos 112:594–601
Vieira KM, Netto P, Dlas A, Mendes SS, Castro LC, Prezoto F (2016) Nesting stingless bees in urban areas: a reevaluation after eight years. Sociobiology 63:976–981
Villard MA, Metzger JP (2014) Beyond the fragmentation debate: a conceptual model to predict when habitat configuration really matters. J Appl Ecol 51:309–318
Westphal C, Steffan-Dewenter I, Tscharntke T (2003) Mass flowering crops enhance pollinator densities at a landscape scale. Ecol Lett 6:961–965
Zanette LRS, Martins RP, Ribeiro SP (2005) Effects of urbanization on Neotropical wasp and bee assemblages in a Brazilian metropolis. Landsc Urban Plan 71:105–121
Zuckerberg B, Desrochers A, Hochachka WM, Fink D, Koenig WD, Dickinson JL (2012) Overlapping landscapes: a persistent, but misdirected concern when collecting and analyzing ecological data. J Wildl Manag 76:1072–1080
Acknowledgements
We are profoundly thankful to the coffee farmers for granting us access to their properties. Especially to the Leite Marquezini family for the support during the fieldwork and throughout the research project. We would like to acknowledge Tereza Cristina Giannini, for her inputs on the experimental design and contributions throughout this project. Also, we thank Luisa G. Carvalheiro, Blandina F. Viana and Denise Araujo for valuable discussions over the first version of this manuscript. We thank Chris Davis for English revisions. We will also like to thank the teamwork which included all members of the Interface project, especially Natalia Aristizabal, Isabela Romitelli, Francisco d’Albertas, Felipe Libran, Larissa Boesing from the LEPaC laboratory, Liedson Carneiro, Sheina Koffler and William Sabino from the Bee Laboratory, USP.
Funding
The study was funded by a FAPESP grant (Interface Project, N. 2013/23457-6). RJ and JPM were supported by the Brazilian Science Council (CNPq; grants 301616/2017-5, 306121/2016-6, and 305484/2017-6). The Brazilian Ministry of Education supported A.G-Ch (CAPES–DS; 2014- 2016).
Author information
Authors and Affiliations
Contributions
Adrian González-Chaves (AGCh), Rodolfo Jaffé (RJ), Jean Paul Metzger (JPM), and Astrid de Matos Peixoto Kleinert (AMPK) together planned and design the project, as well as were involved in writing the manuscript. JPM obtained project funding was obtained by. AGCh collected the data, which was analyzed by AGCh and RJ.
Corresponding author
Additional information
Publisher's Note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Electronic supplementary material
Below is the link to the electronic supplementary material.
Rights and permissions
About this article
Cite this article
González-Chaves, A., Jaffé, R., Metzger, J.P. et al. Forest proximity rather than local forest cover affects bee diversity and coffee pollination services. Landscape Ecol 35, 1841–1855 (2020). https://doi.org/10.1007/s10980-020-01061-1
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s10980-020-01061-1