Abstract
Reductions in global bee populations are threatening the pollination benefits to both the planet and people. Whilst the contribution of bee pollination in promoting sustainable development goals through food security and biodiversity is widely acknowledged, a range of other benefits provided by bees has yet to be fully recognised. We explore the contributions of bees towards achieving the United Nation’s Sustainable Development Goals (SDGs). Our insights suggest that bees potentially contribute towards 15 of the 17 SDGs and a minimum of 30 SDG targets. We identify common themes in which bees play an essential role, and suggest that improved understanding of bee contributions to sustainable development is crucial for ensuring viable bee systems.
Similar content being viewed by others
Introduction
The United Nations’ 17 Sustainable Development Goals (SDGs) are designed to achieve synergy between human well-being and the maintenance of environmental resources by 2030, through the pursuit of 169 targets and more than 200 indicators (UN 2015). The biosphere is the foundation for all SDGs (Folke et al. 2016; Rockström and Sukhdev 2016; Leal Filho et al. 2018), and yet biodiversity conservation remains a persistent global challenge (Tittensor et al. 2014). An examination of how a particular suite of organisms within the global wealth of biodiversity can contribute to the attainment of the SDGs holds the potential to link sustainable development policy with conservation through the design of integrated solutions. We explore the interconnections between bees—a critical group of insects with diverse economic, social, cultural and ecological values—and people, in the context of the SDGs.
Bees, people and the planet
Bees comprise ~ 20 000 described species across seven recognised families (Ascher and Pickering 2014), with many more species yet to be described (Fig. 1). The evolutionary radiation of bees coincided with the evolutionary radiation of flowering plants (Cappellari et al. 2013), and bees occupy an important ecological role as pollinators of a range of flowering plant species. Although bees are not the most diverse group of pollinators (butterflies and moths comprise over 140 000 species), they are the most dominant taxonomic group amongst pollinators; only in the Arctic regions, is another group (flies) more dominant (Ollerton et al. 2017). The ability of bees to transport large numbers of pollen grains on their hairy bodies, reliance on floral resources, and the semi-social or eu-social nature of some species are amongst the characteristics that make bees important and effective pollinators (Ollerton et al. 2017; Klein et al. 2018). Fifty bee species are managed by people, of which around 12 are managed for crop pollination (Potts et al. 2016a).
A snapshot of the diversity of bees. Bees are taxonomically classified under the insect Order Hymenoptera, along with ants, wasps and sawflies, and are part of the superfamily Apoidea, and clade Anthophila, with seven recognised families. Although only 50 of the ~ 20 000 described bee species are actively managed by people, the entire clade is important for ecosystem functioning and human well-being. Bees and flowering plants have co-evolved, making bees effective pollinators of a large proportion of flowering plant species. There are perhaps a further ~ 5 000 bee species that are yet to be described. Data source: Ascher and Pickering (2014). Information for this figure was sourced from Michener 1979; Michener 2000; Michez and Patiny 2007; Litman et al. 2011; Cappellari et al. 2013; Peters et al. 2017; Meiners et al. 2019
The potential importance of bees for crop pollination has been highlighted as a particular reason to conserve wild bees and their habitat (Klein et al. 2007; Gill et al. 2016; Potts et al. 2016a; Klein et al. 2018). More than 90% of the world’s top 107 crops are visited by bees; however, wind- and self-pollinated grasses account for around 60% of global food production and do not require animal pollination (Klein et al. 2007). Wild bees contribute an average of USD$3 251 ha−1 to the production of insect-pollinated crops, similar to that provided by managed honey bees (Kleijn et al. 2015). A very small number of mostly common wild bee species provide the majority of bee-related crop pollination services (Kleijn et al. 2015), and other insects such as flies, wasps, beetles, and butterflies have an important, underemphasised role in crop pollination (Rader et al. 2016). Such research has highlighted the danger of exclusively highlighting the importance of bees for crop pollination, to the potential detriment of conserving diversity across the landscape (Kleijn et al. 2015; Senapathi et al. 2015). In our assessment of bees and the SDGs, we highlight that the diversity of wild and managed bees has crucial ecological, economic and social importance including and beyond crop pollination.
Long-standing associations exist across multiple bee species and human societies. Documented ancient bee–people interactions include honey hunting dating back to the Stone Age for the honey bee Apis mellifera in Europe (Roffet-Salque et al. 2015), more than 2 000 years of keeping the honey bee Apis cerana in Asia (Crane 1995), and beekeeping reaching back to at least pre-Columbian times for stingless bees (Melipona beechii) in Mayan Mexico (Quezada-Euán 2018). Bees also appear in many religious scriptures and are found within mythology, cosmology and iconography (Fijn 2014; Roffet-Salque et al. 2015; Potts et al. 2016a; Quezada-Euán 2018). Beeswax from culturally significant sugarbag bees (Tetragonula spp.) has been used in the production of rock art by Aboriginal peoples in northern Australia for at least 4 000 years (Watchman and Jones 2002). In Greek society, bees are closely linked with the cycle of birth and death, and considered an emblem of immortality (Cook 2013). “Telling the bees” was a popular tradition in 19th Century New England; it was customary for keepers to inform their bees of any major event such as a birth, death, marriage or long journey (Hagge 1957). These reciprocal bee–human relationships have historic legacy and are highly important for informing current practices around bee management.
Today, the long-standing mutualistic relationship between bees and people is jeopardised by recent reported declines in bee populations (Potts et al. 2016b). The loss of managed honey bee colonies (e.g. Potts et al. 2010) and declines in wild bee pollinators (e.g. Biesmeijer et al. 2006; Koh et al. 2016) have been observed, particularly in Europe and North America. However, much remains undocumented about the conservation status of most bee species (Goulson et al. 2015; Jamieson et al. 2019). The global conservation status of just 483 bee species has been assessed by the IUCN, most of which were ‘data deficient’ (IUCN 2019). The European Red List assessment of 1 965 species of European bees found that 9.2% were threatened, whilst insufficient data were available to assess the conservation status of nearly 57% of European species; many of these may also be threatened (Nieto et al. 2014). Goulson et al. (2015) reason that declines in wild bees definitively noted for Europe and North America are likely to have occurred elsewhere.
With a decline in bee populations, there has been a surge of research focusing on the drivers of bee decline and the impacts on provisioning ecosystem services (Goulson et al. 2015; Decourtye et al. 2019). Drivers such as habitat loss, pesticide use, the proliferation of parasites, availability and diversity of forage, change in land use and climate, and species competition have all contributed to the reduction in bee populations (Goulson et al. 2015; Sánchez-Bayo and Wyckhuys 2019; Wagner 2020). These drivers interact in complex ways; for example, market-driven agricultural intensification has limited bees’ access to forage resources and at the same time potentially increasing bees’ exposure to harmful agrichemicals (Durant 2019; Sánchez-Bayo and Goka 2014). People can act as a positive influence for ecosystem function through designing bee-friendly policies and contributing to bee conservation approaches (Potts et al. 2016a; Matias et al. 2017; Hill et al. 2019). Acknowledging the plethora of literature addressing the decline in bee populations and the consequences for agriculture, we contend that the ubiquitous importance of bees in connecting the planet and people remains relatively less explored, particularly with regard to broader goals in sustainable development.
Framing the broader importance of bees to sustainable development
Bees provide a range of ecosystem services that contribute to the wellbeing of people whilst maintaining the planet’s life support systems (Gill et al. 2016; Matias et al. 2017). Ecosystem services inherently contribute to achieving global sustainable development (Wood et al. 2018). Yet the extent to which bees contribute towards the achievement of the full suite of the SDGs has not been explored in detail. Existing research has highlighted the importance of insects in achieving multiple SDGs through the regulation of natural cycles, biological pest control, pollination, seed dispersal, and even as bio-inspiration (Gill et al. 2016; Sánchez-Bayo and Wyckhuys 2019; Dangles and Casas 2019). Bee pollination has been identified as directly contributing to food security (SDG2) and biodiversity (SDG15) (Dangles and Casas 2019). However, bees could also contribute to a broader range of SDGs.
We explicitly identify the realised and potential contributions of bees towards achieving the SDGs, presenting evidence to highlight the interconnectedness between bees, people and the planet from an integrated system perspective (Stafford-Smith et al. 2017). We review the SDGs alongside the potential contributions of bees in achieving individual SDG targets. As the SDGs explicitly build on the foundation of the biosphere (Folke et al. 2016; Leal Filho et al. 2018), the perspective presented here may help in designing implementation pathways to achieve SDG targets. We identify 30 targets to which bees may contribute (Table 1) through a range of direct and indirect connections between bees, people and the planet.
We incorporate contributions from all bee species, including wild and managed populations. The European honey bee (A. mellifera) and buff-tailed bumblebee (Bombus terrestris) could be considered as ‘massively introduced species’ having greatly expanded their geographic range through human management and escape (Geslin et al. 2017). We note the extensive and evolving literature on the interactions between native wild bees, introduced domesticated bees, and feral bees, noting evidence of competition for forage and nesting resources, disruption of native plant–pollinator networks, and potential for viral disease transmission between species (e.g. Geslin et al. 2017; Mallinger et al. 2017; Wojcik et al. 2018; Alger et al. 2019; Murray et al. 2019; Valido et al. 2019). We pursue a holistic perspective that encompasses native wild and managed introduced bees, following Kleijn et al.’s (2015, 2018) calls for an inclusive approach that safeguards all pollinators.
The identified critical role of bees in sustainable development
The importance of bee pollination for food crops has been widely acknowledged, with growing concern of a global crisis as demand for pollination services continues to outstrip supply, with an associated increase in less diverse, pollinator-dependant agriculture systems (Aizen and Harder 2009; Aizen et al. 2019). In addition to improving the yield of some crops (target 2.3) (Klein et al. 2007, 2018; Stein et al. 2017), bee pollination contributes to enhanced nutritional value (target 2.2) and improved quality and longer shelf life of many fruits and vegetables (Klatt et al. 2014), which could potentially help in reducing food waste (target 12.3) resulting from aesthetic imperfections (Gunders and Bloom 2017).
Less-explored aspects of bee pollination include the contribution to biofuels (SDG7). Despite being self-pollinated, oil seed crops show increased yield when pollinated by bees (target 7.2) (Halinski et al. 2018; Perrot et al. 2018). Research in Mexico on the performance of bees on Jatropha curcas found significant improvement in the seed set when the self-pollinated varieties were supported with bee pollination (Romero and Quezada-Euán 2013). Canola, another self-pollinating oilseed crop, also shows a positive association between higher yields and bee diversity (Halinski et al. 2018).
Beyond agricultural landscapes, research in urban bee ecology aids understanding of bee dynamics in our cities and informs urban bee conservation initiatives (Hernandez et al. 2009; Stange et al. 2017). Urban beekeeping strengthens residents’ connection to nature (Stange et al. 2018). Planting aesthetically pleasing, bee-attractive flowering species in landscape planning can provide forage for bees, and close proximity to such plantings may result in pollination rewards for trees and other species in public green spaces (target 11.7) (Lowenstein et al. 2015; Hausmann et al. 2016). European honey bees can be used as an indicator species for tracking contaminants and monitoring environmental health (target 13.3) in urban areas (Zhou et al. 2018). In addition, understanding bee forage preference, suitability of habitat and mobility between different habitat types is critical for designing sustainable urban (target 11.7) and rural landscapes (target 15.9) to optimize pollination benefits as well as support bee health (Stange et al. 2017; Langellotto et al. 2018). For example, the United Kingdom’s Protection of Pollinators Bill was proposed to develop a national network of wildflower corridors called B-lines to support bee populations and other pollinators (UK Parliament, House of Commons, 2017).
The contribution of wild and managed bees in pollinating wild plants in natural ecosystems and managed forests (target 15.1) is well-acknowledged (Senapathi et al. 2015; Klein et al. 2018). The biodiversity found within forests provides a critical range of ecosystem services including water cycle regulation (target 6.6) and carbon sequestration (Brockerhoff et al. 2017; Creed and van Noordwijk 2018). Bee-pollinated plants provide a source of food for wildlife and non-timber forest products for people (Bradbear, 2009; Senapathi et al. 2015). For example, Brazil nut trees (Bertholletia excelsa) require bee pollination to set their high-value fruit, with much greater productivity in the wild, likely due to low numbers of native bees in plantations (Cavalcante et al. 2012). Beekeeping within forest boundaries can support forest conservation (target 15.1) alongside rural livelihoods (Sande et al. 2009; Chanthayod et al. 2017; Mudzengi et al. 2019).
Keeping bees provides opportunities for income diversity (target 1.1) with low start-up costs, through diverse products and services including honey, pollen, beeswax, propolis, royal jelly, and pollination services (Bradbear 2009). Initiatives to promote beekeeping and pollination services in Kenya have resulted in livelihood improvements for smallholder farmers through increased farm productivity and an additional income stream (target 1.5) (Carroll and Kinsella 2013). However, in other regions of Africa, constraints to improve livelihoods through bee-related activities have been attributed to a lack of knowledge concerning bee husbandry processes, access to equipment, and training (Minja and Nkumilwa 2016). Vocational education in beekeeping (target 4.3) could promote economic opportunities for employment and entrepreneurial enterprise (targets 8.6 and 4.4) and diversification for Indigenous groups (targets 1.4 and 4.5), as well as help empower women (target 5.5) including those within traditionally patriarchal societies to promote gender equality (target 5.a) (Pocol and McDonough 2015; Mburu et al. 2017).
Beekeeping can be an important strategy for livelihood diversification (Bradbear 2009), which can directly contribute to an increase in per capita and household income (target 8.1) (Mazorodze 2015; Chanthayod et al. 2015) and also allow for enhanced fiscal opportunities (e.g. tourism) and sustained income growth for people in rural areas, irrespective of social and economic status (targets 10.1 and 10.2) (Pocol and McDonough 2015; Vinci et al. 2018). An initiative for sustainable tourism in Slovenia packages bee-related education and healing experiences with bee products, together with opportunities to create and purchase original crafts using bee products (Arih and Korošec 2015). In Fiji, The Earth Care Agency is working to promote organic honey production on remote islands to provide economic alternatives for indigenous Fijians (Matava Fiji Untouched 2019). These initiatives contribute to local economies and in the case of Slovenia (Arih and Korošec 2015), help in marketing the country’s natural attractions whilst providing additional livelihood opportunities through increased tourism activities (target 8.9).
In relation to health, honey, bee pollen, propolis, royal jelly, beeswax and bee venom have all been used in traditional and modern medicine (target 3.8) (Kocot et al. 2018; Easton-Calabria et al. 2019). Researchers have identified bioactive properties of honey, propolis and royal jelly which suggest the presence of compounds with antimicrobial, anti-inflammatory, antioxidant, antitumor, and anticancer activities (Pasupuleti et al. 2017; Kocot et al. 2018; Easton-Calabria et al. 2019). Honey is used in wound and ulcer care, to enhance oral health, fight gastric disorders, and liver and pancreatic diseases, as well as to promote cardiovascular health (Pasupuleti et al. 2017; Easton-Calabria et al. 2019). Propolis is used in gynaecological care, oral health, dermatology care, and oncology treatments, whilst royal jelly is used in reproductive care, neurodegenerative and aging diseases, and wound healing (target 3.4) (Pasupuleti et al. 2017).
Bees have contributed to industry, innovation and infrastructure by inspiring the design and development of a range of structures, devices and algorithms that can benefit sustainable development (target 9b). The honeycomb structure of beehives is often a mainstay in structural engineering (Zhang et al. 2015). Drawing inspiration from bee anatomy, the medical industry has benefited from innovations such as surgical needles adopted from the design of bee stingers (Sahlabadi and Hutapea 2018). Bee behaviour has inspired complex computer-based search and optimisation processes informing a new wave of genetic algorithms (Xing and Gao 2014).
Towards sustainable bee systems
The decline in global insect populations has attracted the attention of the scientific community, general public and policymakers (Potts et al. 2016a), with heightened public awareness of the importance of bees for pollination. Our research has highlighted the contribution bees can provide towards achieving a diverse range of SDG targets in addition to their crucial role in pollination. The increasingly positive attitude of the public towards bees, and insect pollinators more broadly, provides opportunities for efforts to conserve bee habitat and support pro-pollinator initiatives in land management, agricultural diversification and urban greening (Senapathi et al. 2015; Schönfelder and Bogner 2017).
A holistic view of ecosystems including wild and managed bees and humans is necessary to address sustainability challenges (Kleijn et al. 2018; Saunders et al. 2018). By employing a system approach, we can better understand the interconnections between elements within coupled human–environment systems. We strongly advocate the need for appropriate natural resource management approaches for maintaining sustainable systems as vital for allowing the continued success of bees in their natural role. We summarise our findings by suggesting eight key thematic priority areas whereby bees can play a crucial role in meeting the SDGs (Fig. 2).
Bees and the SDGs. Overarching themes whereby bees contribute to sustainable development targets
These themes provide a foundation for an emerging, yet urgently needed research agenda to explore the complex relationship between bees, people and the planet. A range of important questions should guide this research agenda including: (i) What social and ecological entities contribute to a bee–human system, what feedback and trade-offs exist amongst these entities, and how can understanding structural interconnectivities within this bee–human system contribute to sustainable decision making at various spatial scales? (ii) Are there critical thresholds of bee species diversity and/or bee population abundance beyond which there are significant impacts to meeting certain SDG targets, and do these thresholds vary by geographic regions? (iii) What ecosystem services can be optimized with existing bee diversity in a region, to what extent can they contribute to achieving SDG targets, and does the introduction of managed species enhance or suppress existing ecosystem services? In addition, the distinct roles of wild and managed bees provide a further research lens for identifying the critical role that bees can provide in achieving the SDGs. We must strive to restore balance and reverse bee decline trajectories if we are to encounter a future in which bees continue to contribute to the sustainable development of society.
References
Aizen, M.A., and L.D. Harder. 2009. The global stock of domesticated honey bees is growing slower than agricultural demand for pollination. Current Biology 19: 915–918.
Aizen, M.A., S. Aguiar, J.C. Biesmeijer, L.A. Garibaldi, D.W. Inouye, C. Jung, D.J. Martins, R. Medel, et al. 2019. Global agricultural productivity is threatened by increasing pollinator dependence without a parallel increase in crop diversification. Global Change Biology 25: 3516–3527.
Alger, S.A., P.A. Burnham, H.F. Boncristiani, and A.K. Brody. 2019. RNA virus spillover from managed honeybees (Apis mellifera) to wild bumblebees (Bombus spp.). PLoS ONE 14: e0217822.
Amjad Khan, W., H. Chun-Mei, N. Khan, A. Iqbal, S.-W. Lyu, and F. Shah. 2017. Bioengineered plants can be a useful source of omega-3 fatty acids. BioMed Research International 2017: 7348919–7348919.
Amulen, D.R., M. Dhaese, E. D’haene, J.O. Acai, J.G. Agea, G. Smagghe, and P. Cross. 2019. Estimating the potential of beekeeping to alleviate household poverty in rural Uganda. PLoS ONE 14: e0214113.
Arih, I.K., and T.A. Korošec. 2015. Api-tourism: Transforming Slovenia’s apicultural traditions into a unique travel experience. WIT Transactions on Ecology and the Environment 193: 963–974.
Ascher, J.S., and J. Pickering, 2014. Discover Life bee species guide and world checklist (Hymenoptera: Apoidea: Anthophila). Retrieved April 2019 from http://www.discoverlife.org/mp/20q?guide=Apoidea_species.
Biesmeijer, J.C., S.P. Roberts, M. Reemer, R. Ohlemüller, M. Edwards, T. Peeters, A. Schaffers, S.G. Potts, et al. 2006. Parallel declines in pollinators and insect-pollinated plants in Britain and the Netherlands. Science 313: 351–354.
Bradbear, N. 2009. Bees and their role in forest livelihoods. A guide to the services provided by bees and the sustainable harvesting, processing and marketing of their products. Rome: Food and Agriculture Organization of the United Nations (FAO).
Brockerhoff, E.G., L. Barbaro, B. Castagneyrol, D.I. Forrester, B. Gardiner, J.R. González-Olabarria, P.O.B. Lyver, N. Meurisse, et al. 2017. Forest biodiversity, ecosystem functioning and the provision of ecosystem services. Biodiversity and Conservation 26: 3005–3035.
Cappellari, S.C., H. Schaefer, and C.C. Davis. 2013. Evolution: Pollen or pollinators—which came first? Current Biology 23: R316–R318.
Carroll, T., and J. Kinsella. 2013. Livelihood improvement and smallholder beekeeping in Kenya: The unrealised potential. Development in Practice 23: 332–345.
Cavalcante, M.C., F.F. Oliveira, M.M. Maués, and B.M. Freitas. 2012. Pollination requirements and the foraging behavior of potential pollinators of cultivated Brazil Nut (Bertholletia excelsa Bonpl.) trees in central Amazon rainforest. Psyche 2012: 978019.
Chanthayod, S., W. Zhang, and J. Chen. 2017. People’s perceptions of the benefits of natural beekeeping and its positive outcomes for forest conservation: A case study in norther Lao PDR. Tropical Conservation Science 10: 194008291769726.
Cook, A.B. 2013. The bee in Greek mythology. The Journal of Hellenic Studies 15: 1–24.
Crane, E. 1995. History of beekeeping with Apis cerana in Asia. In The Asiatic hive bee Apciulture, biology, and role in sustainable development in tropical and substropical Asia, ed. P.G. Kewan, 3–18. Cambridge: Enviroquest Ltd.
Creed, I.F., and M. van Noordwijk (eds.). 2018. Forest and water on a changing planet: Vulnerability, adaptation and governance opportunities. A global assessment report. Vienna: International Union of Forestry Research Organizations.
Dangles, O., and J. Casas. 2019. Ecosystem services provided by insects for achieving sustainable development goals. Ecosystem Services 35: 109–115.
Decourtye, A., C. Alaux, Y. Le Conte, and M. Henry. 2019. Toward the protection of bees and pollination under global change: Present and future perspectives in a challenging applied science. Current Opinion in Insect Science 35: 123–131.
Durant, J.L. 2019. Where have all the flowers gone? Honey bee declines and exclusions from floral resources. Journal of Rural Studies 65: 161–171.
Easton-Calabria, A., K.C. Demary, and N.J. Oner. 2019. Beyond pollination: Honey Bees (Apis mellifera) as zootherapy keystone species. Frontiers in Ecology and Evolution 6: 161.
Ekele, G., T. Kwaghgba, and E. Essien. 2019. Vocational competencies required by youths in management of beekeeping for job creation in North East Zone of Benue State, Nigeria. Journal of Educational System 3: 42–49.
Fijn, N. 2014. Sugarbag dreaming: The significance of bees to Yolngu in Arnhem Land, Australia. HUMaNIMALIA 6: 1–21.
Folke, C., R. Biggs, A.V. Norstrom, B. Reyers, and J. Rockstrom. 2016. Social-ecological resilience and biosphere-based sustainability science. Ecology and Society 21: 41.
Geslin, B., B. Gauzens, M. Baude, I. Dajoz, C. Fontaine, M. Henry, L. Ropars, O. Rollin, et al. 2017. Massively introduced managed species and their consequences for plant–pollinator interactions. In Networks of invasion: Empirical evidence and case studies, vol. 57, ed. D.A. Bohan, A.J. Dumbrell, and F. Massol, 147–199., Advances in Ecological Research London: Academic Press.
Gill, R.J., K.C.R. Baldock, M.J.F. Brown, J.E. Cresswell, L.V. Dicks, M.T. Fountain, M.P.D. Garratt, L.A. Gough, et al. 2016. Protecting an ecosystem service: Approaches to understanding and mitigating threats to wild insect pollinators. In Ecosystem services: From biodiversity to society, Part 2, vol. 54, ed. G. Woodward and D.A. Bohan, 135–206., Academic Press London: Advances in Ecological Research.
Goulson, D., E. Nicholls, C. Botias, and E.L. Rotheray. 2015. Bee declines driven by combined stress from parasites, pesticides, and lack of flowers. Science 347: 1255957.
Gunders, D., and J. Bloom. 2017. Wasted: How America is losing up to 40 percent of its food from farm to fork to landfill. New York: Natural Resources Defense Council.
Hagge, C.W. 1957. Telling the Bees. Western Folklore 16: 58–59.
Halinski, R., C.F. Dos Santos, T.G. Kaehler, and B. Blochtein. 2018. Influence of wild bee diversity on canola crop yields. Sociobiology 65: 751–759.
Hausmann, S.L., J.S. Petermann, and J. Rolff. 2016. Wild bees as pollinators of city trees. Insect Conservation and Diversity 9: 97–107.
Hernandez, J.L., G.W. Frankie, and R.W. Thorp. 2009. Ecology of urban bees: a review of current knowledge and directions for future study. Cities and the Environment (CATE) 2: 3.
Hill, R., G. Nates-Parra, J.J.G. Quezada-Euán, D. Buchori, G. Lebuhn, M.M. Maués, P.L. Pert, P.K. Kwapong, et al. 2019. Biocultural approaches to pollinator conservation. Nature Sustainability 2: 214–222.
IUCN. 2019. The International Union of Conservation of Nature (IUCN) Red List of Threatened Species, Version 2019-3. Retrieved 17 January 2020, from http://www.iucnredlist.org.
Jamieson, M.A., A.L. Carper, C.J. Wilson, V.L. Scott, and J. Gibbs. 2019. Geographic biases in bee research limits understanding of species distribution and response to anthropogenic disturbance. Frontiers in Ecology and Evolution. 7: 194.
Klatt, B.K., A. Holzschuh, C. Westphal, Y. Clough, I. Smit, E. Pawelzik, and T. Tscharntke. 2014. Bee pollination improves crop quality, shelf life and commercial value. Proceedings of the Royal Society B 281: 20132440.
Kleijn, D., K. Biesmeijer, Y.L. Dupont, A. Nielsen, S.G. Potts, and J. Settele. 2018. Bee conservation: Inclusive solutions. Science 360: 389–390.
Kleijn, D., R. Winfree, I. Bartomeus, L.G. Carvalheiro, M. Henry, R. Isaacs, A.-M. Klein, C. Kremen, et al. 2015. Delivery of crop pollination services is an insufficient argument for wild pollinator conservation. Nature Communications 6: 7414.
Klein, A.M., B.E. Vaissière, J.H. Cane, I. Steffan-Dewenter, S.A. Cunningham, C. Kremen, and T. Tscharntke. 2007. Importance of pollinators in changing landscapes for world crops. Proceedings of the Royal Society B 274: 303–313.
Klein, A.M., V. Boreux, F. Fornoff, A.C. Mupepele, and G. Pufal. 2018. Relevance of wild and managed bees for human well-being. Current Opinion in Insect Science 26: 82–88.
Kocot, J., M. Kiełczykowska, D. Luchowska-Kocot, J. Kurzepa, and I. Musik. 2018. Antioxidant potential of propolis, bee pollen, and royal jelly: Possible medical application. Oxidative Medicine and Cellular Longevity 2018: 7074209.
Koh, I., E.V. Lonsdorf, N.M. Williams, C. Brittain, R. Isaacs, J. Gibbs, and T.H. Ricketts. 2016. Modeling the status, trends, and impacts of wild bee abundance in the United States. Proceedings of the National Academy of Sciences 113: 140–145.
Langellotto, G.A., A. Melathopoulos, I. Messer, A. Anderson, N. Mcclintock, and L. Costner. 2018. Garden pollinators and the potential for ecosystem service flow to urban and peri-urban agriculture. Sustainability 10: 2047.
Leal Filho, W., U. Azeiteiro, F. Alves, P. Pace, M. Mifsud, L. Brandli, S.S. Caeiro, and A. Disterheft. 2018. Reinvigorating the sustainable development research agenda: The role of the sustainable development goals (SDG). International Journal of Sustainable Development & World Ecology 25: 131–142.
Lemelin, R.H. 2019. Entomotourism and the stingless bees of Mexico. Journal of Ecotourism. https://doi.org/10.1080/14724049.2019.1615074.
Litman, J.R., B.N. Danforth, C.D. Eardley, and C.J. Praz. 2011. Why do leafcutter bees cut leaves? New insights into the early evolution of bees. Proceedings of the Royal Society B: Biological Sciences 278: 3593–3600.
Lowenstein, D.M., K.C. Matteson, and E.S. Minor. 2015. Diversity of wild bees supports pollination services in an urbanized landscape. Oecologia 179: 811–821.
Mallinger, R.E., H.R. Gaines-Day, and C. Gratton. 2017. Do managed bees have negative effects on wild bees?: A systematic review of the literature. PLoS ONE 12: e0189268.
Matava Fiji Untouched. 2019. Community Partnership Kadavu Organic Honey Program. Retrieved April, 2019, from http://matava.com/news/community-partnership-kadavu-organic-honey-program/.
Matias, D.M.S., J. Leventon, A.-L. Rau, C. Borgemeister, and H. Von Wehrden. 2017. A review of ecosystem service benefits from wild bees across social contexts. Ambio 46: 456–467. https://doi.org/10.1007/s13280-016-0844-z.
Mazorodze, B.T. 2015. The contribution of apiculture towards rural income in Honde Valley Zimbabwe. National Capacity Building Strategy for Sustainable Development and Poverty Alleviation Conference (NCBSSDPA-2015). Dubai: American University in the Emirates.
Mburu, P.D.M., H. Affognon, P. Irungu, J. Mburu, and S. Raina. 2017. Gender roles and constraints in beekeeping: A case from Kitui County, Kenya. Bee World 94: 54–59.
Meiners, J.M., T.L. Griswold, and O.M. Carril. 2019. Decades of native bee biodiversity surveys at Pinnacles National Park highlight the importance of monitoring natural areas over time. PLoS ONE 14: e0207566.
Michener, C.D. 1979. Biogeography of the bees. Annals of the Missouri Botanical Garden 66: 277–347.
Michener, C.D. 2000. The bees of the world. Baltimore: John Hopkins University Press.
Michez, D., and S. Patiny. 2007. Biogeography of bees (Hymenoptera, Apoidea) in Sahara and the Arabian deserts. Insect Systematics & Evolution 38: 19–34.
Minja, G.S., and T.J. Nkumilwa. 2016. The role of beekeeping on forest conservation and poverty alleviation in Moshi Rural District, Tanzania. European Scientific Journal, ESJ 12: 366.
Mudzengi, C., C.S. Kapembeza, E. Dahwa, L. Taderera, S. Moyana, and M. Zimondi. 2019. Ecological benefits of apiculture on savanna rangelands. Bee World 97: 1–10.
Murray, E.A., J. Burand, N. Trikoz, J. Schnabel, H. Grab, and B.N. Danforth. 2019. Viral transmission in honey bees and native bees, supported by a global black queen cell virus phylogeny. Environmental Microbiology 21: 972–983.
Nieto, A., S.P. Roberts, J. Kemp, P. Rasmont, M. Kuhlmann, M.G. Criado, J.C. Biesmeijer, P. Bogusch, et al. 2014. European red list of bees. Luxembourg: Publication Office of the European Union.
Ollerton, J., R. Winfree, and S. Tarrant. 2011. How many flowering plants are pollinated by animals? Oikos 120: 321–326.
Pasupuleti, V.R., L. Sammugam, N. Ramesh, and S.H. Gan. 2017. Honey, propolis, and royal jelly: A comprehensive review of their biological actions and health benefits. Oxidative Medicine and Cellular Longevity 2017: 1259510–1259510.
Perrot, T., S. Gaba, M. Roncoroni, J.-L. Gautier, and V. Bretagnolle. 2018. Bees increase oilseed rape yield under real field conditions. Agriculture, Ecosystems & Environment 266: 39–48.
Peters, R.S., L. Krogmann, C. Mayer, A. Donath, S. Gunkel, K. Meusemann, A. Kozlov, L. Podsiadlowski, et al. 2017. Evolutionary history of the Hymenoptera. Current Biology 27: 1013–1018.
Pocol, C.B., and M. McDonough. 2015. Women, apiculture and development: Evaluating the impact of a beekeeping project on rural women’s livelihoods. Bulletin of University of Agricultural Sciences and Veterinary Medicine Cluj-Napoca, Horticulture 72: 487–492.
Potts, S., V. Imperatriz-Fonseca, H. Ngo, J. Biesmeijer, T. Breeze, L. Dicks and B. Viana. 2016a. The assessment report on pollinators, pollination and food production. Summary for policymakers. Bonn: Intergovernmental Panel on Biodiversity and Ecosystem Services.
Potts, S.G., V. Imperatriz-Fonseca, H.T. Ngo, M.A. Aizen, J.C. Biesmeijer, T.D. Breeze, L.V. Dicks, L.A. Garibaldi, et al. 2016b. Safeguarding pollinators and their values to human well-being. Nature 540: 220–229.
Potts, S.G., S.P.M. Roberts, R. Dean, G. Marris, M.A. Brown, R. Jones, P. Neumann, and J. Settele. 2010. Declines of managed honey bees and beekeepers in Europe. Journal of Apicultural Research 49: 15–22.
Quezada-Euán, J.J.G. 2018. The past, present, and future of meliponiculture in Mexico. In Stingless Bees of Mexico, 243–269 pp. New York: Springer.
Rader, R., I. Bartomeus, L.A. Garibaldi, M.P.D. Garratt, B.G. Howlett, R. Winfree, S.A. Cunningham, M.M. Mayfield, et al. 2016. Non-bee insects are important contributors to global crop pollination. Proceedings of the National Academy of Sciences 113: 146–151.
Rockström, J. and P. Sukhdev. 2016. How food connects all the SDGs: A new way of viewing the Sustainable Development Goals and how they are all linked to food. Stockholm: Stockholm Resilience Centre. Retrieved 23 January, 2020, from https://www.stockholmresilience.org/research/research-news/2016-06-14-how-food-connects-all-the-sdgs.html.
Roffet-Salque, M., M. Regert, R.P. Evershed, A.K. Outram, L.J.E. Cramp, O. Decavallas, J. Dunne, P. Gerbault, et al. 2015. Widespread exploitation of the honeybee by early Neolithic farmers. Nature 527: 226–230.
Romero, M.J., and J.J.G. Quezada-Euán. 2013. Pollinators in biofuel agricultural systems: the diversity and performance of bees (Hymenoptera: Apoidea) on Jatropha curcas in Mexico. Apidologie 44: 419–429.
Sahlabadi, M., and P. Hutapea. 2018. Novel design of honeybee-inspired needles for percutaneous procedure. Bioinspiration & Biomimetics 13: 036013.
Sánchez-Bayo, F., and K.A.G. Wyckhuys. 2019. Worldwide decline of the entomofauna: A review of its drivers. Biological Conservation 232: 8–27.
Sánchez-Bayo, F., and K. Goka. 2014. Pesticide residues and bees—a risk assessment. PLoS ONE 9: e94482.
Sande, S.O., R.M. Crewe, S.K. Raina, S.W. Nicolson, and I. Gordon. 2009. Proximity to a forest leads to higher honey yield: another reason to conserve. Biological Conservation 142: 2703–2709.
Saunders, M.E., T.J. Smith, and R. Rader. 2018. Bee conservation: Key role of managed bees. Science 360: 389–389.
Schönfelder, M.L., and F.X. Bogner. 2017. Individual perception of bees: Between perceived danger and willingness to protect. PLoS ONE 12: e0180168.
Senapathi, D., J.C. Biesmeijer, T.D. Breeze, D. Kleijn, S.G. Potts, and L.G. Carvalheiro. 2015. Pollinator conservation—the difference between managing for pollination services and preserving pollinator diversity. Current Opinion in Insect Science 12: 93–101.
Sforcin, J.M., Bankova, V. and Kuropatnicki, A.K., 2017. Medical benefits of honeybee products. Evidence-Based Complementary and Alternative Medicine, 2017.
Smith, K.E., D. Weis, M. Amini, A.E. Shiel, V.W.M. Lai, and K. Gordon. 2019. Honey as a biomonitor for a changing world. Nature Sustainability 2: 223–232.
Stafford-Smith, M., D. Griggs, O. Gaffney, F. Ullah, B. Reyers, N. Kanie, B. Stigson, P. Shrivastava, et al. 2017. Integration: The key to implementing the Sustainable Development Goals. Sustainability Science 12: 911–919.
Stange, E., D.N. Barton, and G.M. Rusch. 2018. A closer look at Norway’s natural capital—how enhancing urban pollination promotes cultural ecosystem services in Oslo. In Reconnecting natural and cultural capital, ed. M.L. Paracchini, P.C. Zingari, and C. Blasi, 235–243. Brussels: European Commission.
Stange, E., G. Zulian, G. Rusch, D. Barton, and M. Nowell. 2017. Ecosystem services mapping for municipal policy: ESTIMAP and zoning for urban beekeeping. One Ecosystem 2: e14014.
Stein, K., D. Coulibaly, K. Stenchly, D. Goetze, S. Porembski, A. Lindner, S. Konaté, and E.K. Linsenmair. 2017. Bee pollination increases yield quantity and quality of cash crops in Burkina Faso, West Africa. Scientific Reports 7: 17691.
Tittensor, D.P., M. Walpole, S.L.L. Hill, D.G. Boyce, G.L. Britten, N.D. Burgess, S.H.M. Butchart, P.W. Leadley, et al. 2014. A mid-term analysis of progress toward international biodiversity targets. Science 346: 241–244.
Tomaselli, M.F., R. Kozak, R. Hajjar, J. Timko, A. Jarjusey, and K. Camara. 2014. Small forest-based enterprises in the Gambia: opportunities and challenges. In Forests under pressure—local responses to global issues, ed. P. Katila, G. Galoway, W. de Jong, and P. Pacheco, 315–328. Vienna: International Union of Forestry Research Organizations (IUFRO) Secretariat.
UK Parliament, House of Commons. 2017. Protection of Pollinators Bill 2017-2019. Bill 206 (withdrawn 24 October 2018), United Kingdom House of Commons.
UN. 2015. Transforming our world: The 2030 Agenda for Sustainable Development. New York: United Nations, Department of Economic and Social Affairs.
Valido, A., M.C. Rodríguez-Rodríguez, and P. Jordano. 2019. Honeybees disrupt the structure and functionality of plant–pollinator networks. Scientific Reports 9: 4711.
Van Der Steen, J.J., J. De Kraker, and J. Grotenhuis. 2015. Assessment of the potential of honeybees (Apis mellifera L.) in biomonitoring of air pollution by cadmium, lead and vanadium. Journal of Environmental Protection 6: 96–102.
Vinci, G., M. Rapa and F. Roscioli. 2018. Sustainable development in rural areas of Mexico through beekeeping. International Journal of Science and Engineering Invention 4:i08/01.
Wagner, D.L. 2020. Insect declines in the Anthropocene. Annual Review of Entomology 65: 457–480.
Watchman, A.L., and R. Jones. 2002. An independent confirmation of the 4 ka antiquity of a beeswax figure in Western Arnhem Land, Northern Australia. Archaeometry 44: 145–153.
Wojcik, V.A., L.A. Morandin, L. Davies Adams, and K.E. Rourke. 2018. Floral resource competition between honey bees and wild bees: Is there clear evidence and can we guide management and conservation? Environmental Entomology 47: 822–833.
Wood, S.L.R., S.K. Jones, J.A. Johnson, K.A. Brauman, R. Chaplin-Kramer, A. Fremier, E. Girvetz, L.J. Gordon, et al. 2018. Distilling the role of ecosystem services in the Sustainable Development Goals. Ecosystem Services 29: 70–82.
Xing, B., and W.J. Gao. 2014. Bee inspired algorithms. In Innovative computational intelligence: A rough guide to 134 clever algorithms, ed. B. Xing and W.-J. Gao. Cham: Springer.
Zhang, Q., X. Yang, P. Li, G. Huang, S. Feng, C. Shen, B. Han, X. Zhang, et al. 2015. Bioinspired engineering of honeycomb structure—Using nature to inspire human innovation. Progress in Materials Science 74: 332–400.
Zhou, X., M.P. Taylor, P.J. Davies, and S. Prasad. 2018. Identifying sources of environmental contamination in European honey bees (Apis mellifera) using trace elements and lead isotopic compositions. Environmental Science and Technology 52: 991–1001.
Acknowledgements
This research was undertaken with funding support from the Cooperative Research Centre for Honey Bee Products and the Faculty of Science, University of Western Australia. We thank the Associate Editor, Dr. Graciela Rusch, and two anonymous reviewers for providing the constructive, detailed and insightful comments to improve this paper.
Author information
Authors and Affiliations
Corresponding author
Additional information
Publisher's Note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Rights and permissions
Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/.
About this article
Cite this article
Patel, V., Pauli, N., Biggs, E. et al. Why bees are critical for achieving sustainable development. Ambio 50, 49–59 (2021). https://doi.org/10.1007/s13280-020-01333-9
Received:
Revised:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s13280-020-01333-9