Modeling the status, trends, and impacts of wild bee abundance in the United States

Significance In 2014, a presidential memorandum called for an assessment of the nation’s pollinators, in response to growing awareness of their economic importance and recent declines. We assess, for the first time to our knowledge, the status and trends of wild bee abundance and their potential impacts on pollination services across the United States. We develop national maps of wild bee abundance, report land-use–driven changes over time, and relate them to trends in agricultural demand for pollination. We estimate uncertainty in the findings, so future research can target the least-understood regions and topics. Our findings can also help focus conservation efforts where declines in bee abundance are most certain, especially where agricultural demand for pollination services is growing. Wild bees are highly valuable pollinators. Along with managed honey bees, they provide a critical ecosystem service by ensuring stable pollination to agriculture and wild plant communities. Increasing concern about the welfare of both wild and managed pollinators, however, has prompted recent calls for national evaluation and action. Here, for the first time to our knowledge, we assess the status and trends of wild bees and their potential impacts on pollination services across the coterminous United States. We use a spatial habitat model, national land-cover data, and carefully quantified expert knowledge to estimate wild bee abundance and associated uncertainty. Between 2008 and 2013, modeled bee abundance declined across 23% of US land area. This decline was generally associated with conversion of natural habitats to row crops. We identify 139 counties where low bee abundances correspond to large areas of pollinator-dependent crops. These areas of mismatch between supply (wild bee abundance) and demand (cultivated area) for pollination comprise 39% of the pollinator-dependent crop area in the United States. Further, we find that the crops most highly dependent on pollinators tend to experience more severe mismatches between declining supply and increasing demand. These trends, should they continue, may increase costs for US farmers and may even destabilize crop production over time. National assessments such as this can help focus both scientific and political efforts to understand and sustain wild bees. As new information becomes available, repeated assessments can update findings, revise priorities, and track progress toward sustainable management of our nation’s pollinators.

[1]  S. D. Hendrix,et al.  Bee communities (Hymenoptera: Apoidea) of small Iowa hill prairies are as diverse and rich as those of large prairie preserves , 2010, Biodiversity and Conservation.

[2]  V. Imperatriz-Fonseca,et al.  The Dependence of Crops for Pollinators and the Economic Value of Pollination in Brazil , 2015, Journal of economic entomology.

[3]  K. Goodell,et al.  The role of resources and risks in regulating wild bee populations. , 2011, Annual review of entomology.

[4]  Teja Tscharntke,et al.  Mass flowering crops enhance pollinator densities at a landscape scale , 2003 .

[5]  J. Dushoff,et al.  Native bees provide insurance against ongoing honey bee losses. , 2007, Ecology Letters.

[6]  H. Wiering The bees of the world , 2000 .

[7]  A. Klein,et al.  Biodiversity buffers pollination from changes in environmental conditions , 2013, Global change biology.

[8]  S. Droege,et al.  Detecting Insect Pollinator Declines on Regional and Global Scales , 2013, Conservation biology : the journal of the Society for Conservation Biology.

[9]  J. Regetz,et al.  Landscape-scale resources promote colony growth but not reproductive performance of bumble bees. , 2012, Ecology.

[10]  J. Losey,et al.  The Economic Value of Ecological Services Provided by Insects , 2006 .

[11]  Martin Kappas,et al.  Tradeoffs between income, biodiversity, and ecosystem functioning during tropical rainforest conversion and agroforestry intensification , 2007, Proceedings of the National Academy of Sciences.

[12]  Y. Assefa,et al.  Pollinator Decline: US Agro-Socio-Economic Impacts and Responses , 2013 .

[13]  J. Cane Soils of ground-nesting bees (Hymneoptera: Apoidea): Texture, moisture, cell depth and climate , 1991 .

[14]  Rufus Isaacs,et al.  Flower plantings increase wild bee abundance and the pollination services provided to a pollination-dependent crop , 2014 .

[15]  D. Wagner,et al.  Historical changes in northeastern US bee pollinators related to shared ecological traits , 2013, Proceedings of the National Academy of Sciences.

[16]  Hugh P. Possingham,et al.  How useful is expert opinion for predicting the distribution of a species within and beyond the region of expertise? A case study using brush-tailed rock-wallabies Petrogale penicillata , 2009 .

[17]  Claire Kremen,et al.  Modelling pollination services across agricultural landscapes. , 2009, Annals of botany.

[18]  T. Ricketts,et al.  Mapping the margin: comparing marginal values of tropical forest remnants for pollination services. , 2013, Ecological applications : a publication of the Ecological Society of America.

[19]  A. Klein,et al.  Importance of pollinators in changing landscapes for world crops , 2007, Proceedings of the Royal Society B: Biological Sciences.

[20]  H. V. D. Klis,et al.  Uncertainty analysis of a spatial habitat suitability model and implications for ecological management of water bodies , 2006, Landscape Ecology.

[21]  Jeffrey D. Lozier,et al.  Patterns of widespread decline in North American bumble bees , 2011, Proceedings of the National Academy of Sciences.

[22]  A F G Bourke,et al.  Bumble bee species' responses to a targeted conservation measure depend on landscape context and habitat quality. , 2011, Ecological applications : a publication of the Ecological Society of America.

[23]  Brendan A. Wintle,et al.  Quantifying variance components in ecological models based on expert opinion , 2011 .

[24]  R. Bommarco,et al.  Late-season mass-flowering red clover increases bumble bee queen and male densities , 2014 .

[25]  M. Wimberly,et al.  Recent land use change in the Western Corn Belt threatens grasslands and wetlands , 2013, Proceedings of the National Academy of Sciences.

[26]  J. Ollerton,et al.  How many flowering plants are pollinated by animals , 2011 .

[27]  S. Cameron,et al.  Decline of bumble bees (Bombus) in the North American Midwest , 2009 .

[28]  Claire Kremen,et al.  EDITOR'S CHOICE: Small‐scale restoration in intensive agricultural landscapes supports more specialized and less mobile pollinator species , 2015 .

[29]  H. Hines,et al.  Bumble Bee (Hymenoptera: Apidae) Diversity and Abundance in Tallgrass Prairie Patches: Effects of Local and Landscape Floral Resources , 2005 .

[30]  T. Roulston,et al.  Farming Practices Influence Wild Pollinator Populations on Squash and Pumpkin , 2005, Journal of economic entomology.

[31]  R. Morse,et al.  The value of honey bees as pollinators of U.S. Crops in 2000. , 2001 .

[32]  C. Kremen,et al.  Hedgerow restoration promotes pollinator populations and exports native bees to adjacent fields. , 2013, Ecological applications : a publication of the Ecological Society of America.

[33]  Neal M. Williams,et al.  Crop pollination from native bees at risk from agricultural intensification , 2002, Proceedings of the National Academy of Sciences of the United States of America.

[34]  C. Kremen,et al.  Evaluating nesting microhabitat for ground-nesting bees using emergence traps , 2014 .

[35]  J. Memmott,et al.  The forgotten flies: the importance of non-syrphid Diptera as pollinators , 2015, Proceedings of the Royal Society B: Biological Sciences.

[36]  Mike Hulme,et al.  Using expert knowledge to assess uncertainties in future polar bear populations under climate change , 2008 .

[37]  R Core Team,et al.  R: A language and environment for statistical computing. , 2014 .

[38]  James Regetz,et al.  Landscape effects on crop pollination services: are there general patterns? , 2008, Ecology letters.

[39]  Breno M. Freitas,et al.  Wild Pollinators Enhance Fruit Set of Crops Regardless of Honey Bee Abundance , 2013, Science.

[40]  Jennifer L. Hopwood The contribution of roadside grassland restorations to native bee conservation , 2008 .

[41]  N. Calderone,et al.  Insect Pollinated Crops, Insect Pollinators and US Agriculture: Trend Analysis of Aggregate Data for the Period 1992–2009 , 2012, PloS one.

[42]  Sarah S. Greenleaf,et al.  Bee foraging ranges and their relationship to body size , 2007, Oecologia.

[43]  J. Settele,et al.  Economic valuation of the vulnerability of world agriculture confronted with pollinator decline , 2009 .

[44]  Hannah R. Gaines,et al.  Wild bee pollinators provide the majority of crop visitation across land‐use gradients in New Jersey and Pennsylvania, USA , 2007 .

[45]  C. Kremen,et al.  Effect of Human Disturbance on Bee Communities in a Forested Ecosystem , 2007, Conservation biology : the journal of the Society for Conservation Biology.

[46]  R. Isaacs,et al.  Modeling Pollinator Community Response to Contrasting Bioenergy Scenarios , 2014, PloS one.

[47]  J. Biesmeijer,et al.  Global pollinator declines: trends, impacts and drivers. , 2010, Trends in ecology & evolution.

[48]  S. D. Hendrix,et al.  Prairie restorations and bees: The potential ability of seed mixes to foster native bee communities , 2015 .

[49]  I. Bartomeus,et al.  Native bees buffer the negative impact of climate warming on honey bee pollination of watermelon crops , 2013, Global change biology.

[50]  Alana L. Burley,et al.  A global quantitative synthesis of local and landscape effects on wild bee pollinators in agroecosystems. , 2013, Ecology letters.

[51]  Chris J. Johnson,et al.  Mapping uncertainty: sensitivity of wildlife habitat ratings to expert opinion , 2004 .

[52]  Neal M Williams,et al.  Complex responses within a desert bee guild (Hymenoptera: Apiformes) to urban habitat fragmentation. , 2006, Ecological applications : a publication of the Ecological Society of America.

[53]  D. Goulson,et al.  Bee declines driven by combined stress from parasites, pesticides, and lack of flowers , 2015, Science.

[54]  D. Bailey,et al.  How landscape structure, land-use intensity and habitat diversity affect components of total arthropod diversity in agricultural landscapes , 2007 .

[55]  C. Kremen Managing ecosystem services: what do we need to know about their ecology? , 2005, Ecology letters.

[56]  Gaines Day,et al.  Do bees matter to cranberry? The effect of bees, landscape, and local management on cranberry yield , 2013 .

[57]  James T. Wilkes,et al.  A national survey of managed honey bee 2011–12 winter colony losses in the United States: results from the Bee Informed Partnership , 2013 .

[58]  Giles M. Foody,et al.  Status of land cover classification accuracy assessment , 2002 .

[59]  Marcelo A. Aizen,et al.  The Global Stock of Domesticated Honey Bees Is Growing Slower Than Agricultural Demand for Pollination , 2009, Current Biology.

[60]  Barack Obama,et al.  Creating a Federal Strategy To Promote the Health of Honey Bees and Other Pollinators: Memorandum for Heads of Executive Departments and Agencies, June 20, 2014 , 2014 .

[61]  Françoise Burel,et al.  Intensification of agriculture, landscape composition and wild bee communities: a large scale study in four European countries. , 2010 .

[62]  C. Dormann,et al.  Spatial and Temporal Trends of Global Pollination Benefit , 2012, PloS one.