The Status of the Western Bumble Bee (Bombus Occidentalis
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To the University of Wyoming: The members of the Committee approve the thesis of Christine Bell presented on 8 May 2019. Dr. Michael E. Dillon, Chairperson Dr. Lusha Tronstad, Co-Chairperson Dr. Timothy Collier, External Department Member Zach Wallace APPROVED: Dr. Merav Ben-David, Department Chair, Zoology and Physiology Dr. Paula Lutz, Dean of the College of Arts and Sciences Bell, Christine, Sampling methods and distribution modeling of bees: the status of the western bumble bee (Bombus occidentalis) in Wyoming, M.S., Zoology and Physiology, August 2019. Native bees provide crucial pollination services in both agricultural and natural settings. Several native bee populations have experienced declines in the last few decades, particularly bumble bees (genus Bombus). The western bumble bee (B. occidentalis) has been petitioned for listing under the Endangered Species Act, and this bee has historically occurred in Wyoming. However, the western bumble bee has not been monitored or surveyed in Wyoming for the last decade. Monitoring declining species is essential to evaluate their conservation status and to inform future management practices as well as policy. Here, we first examine how sampling methods (both passive and active) affect the abundance and number of taxa of bees collected. We then fit species distribution models for B. occidentalis using both historical and new data. We found that sampling method does affect the number and species of bees we collected, and we recommend that surveyors tailor their protocols to the taxa of interest. Our models suggest a decline in predicted suitable habitat for the western bumble bee in Wyoming. 1 SAMPLING METHODS AND DISTRIBUTION MODELING OF BEES: THE STATUS OF THE WESTERN BUMBLE BEE (BOMBUS OCCIDENTALIS) IN WYOMING By Christine Bell A thesis submitted to the Department of Zoology and Physiology and the University of Wyoming in partial fulfillment of the requirements for the degree of MASTER OF SCIENCE in ZOOLOGY Laramie, WY August 2019 COPYRIGHT PAGE ©2019, Christine Bell ii ACKNOWLEGDEMENTS I would like to thank my advisors, Dr. Lusha Tronstad and Dr. Michael Dillon, as well as the members of my committee, Dr. Timothy Collier and Zach Wallace. I am very grateful to US National Parks Service, US National Forest Service, Wyoming State Parks, and private landowners for providing us access to sample sites. I would also like to thank technicians Madison Crawford, Charles Anderson, and Tighe Jones for their help in the field, Matthew Green for his help in the lab and the field, and Dr. Scott Hotaling and Mark Andersen for their assistance. This project was funded by the Wyoming Bureau of Land Management, US Forest Service, Wyoming Landscape Conservation Initiative, Wyoming NASA Space Grant Consortium, and the University of Wyoming Biodiversity Institute. (Permit numbers GRTE- 2017-SCI-0035, YELL-2017-SCI-8002, FOLA-2018-SCI-0005, DETO-2018-SCI-0007) iii TABLE OF CONTENTS Chapter One: Evaluating the best monitoring protocols for bees: vane traps, bee cups, and netting are not equal………………………………………………………………………………………. 1 Abstract……………………………………………………………………………………1 Introduction………………………………………………………………………………..2 Methods……………………………………………………………………………………4 Results……………………………………………………………………………………..6 Discussion…………………………………………………………………………………9 Chapter Two: Using species distribution models to assess the status of the declining western bumble bee (Hymenoptera: Apidae: Bombus occidentalis)………………………………………13 Abstract…………………………………………………………………………………..13 Introduction………………………………………………………………………………14 Methods…………………………………………………………………………………..17 Results……………………………………………………………………………………18 Discussion………………………………………………………………………………..20 References………………………………………………………………………………………..23 Tables…………………………………………………………………………………………….29 Figure Captions…………………………………………………………………………………..38 Figures……………………………………………………………………………………………41 iv CHAPTER 1 Evaluating the best monitoring protocols for bees: vane traps, bee cups, and netting are not equal Abstract Bees are prolific and vital pollinators in both agricultural and natural settings, but some populations are declining, including the western bumble bee (Bombus occidentalis). Monitoring declining species is crucial to understand their status and conservation needs; however, a lack of standardized sampling methods can make range-wide monitoring difficult. Monitoring bees is usually done by three common sampling methods: blue vane traps, bee cups, and aerial netting. Here we examine the difference in abundance and assemblages of bees sampled with these methods in Wyoming, USA, with a particular focus on bumble bees (genus Bombus). We sampled in Wyoming across 5 Level III Ecoregions. At each site we deployed the three most common methods as described above. We compared catch rate (insects/hour) and assemblage (total number of taxa represented) for all bee genera and for species of Bombus. We collected both a greater abundance and assemblage of bees in vane traps than bee cups, with the exception of smaller sweat bees. The abundance of Bombus species collected did not vary between the vane traps and aerial netting; however, the assemblages detected were different between these two sampling methods. Our analysis suggests that sampling methods can affect both the abundance and assemblage of bees, and that sampling protocols should be tailored to the taxa of interest. 1 Introduction Pollinators are vital to most terrestrial ecosystems for plant reproduction in both wild and agricultural settings. As many as 80% of native plant species depend on insect pollination to reproduce (Potts et al., 2010), including 35% of crops grown for human consumption. (Klein et al., 2007) Pollination by native bees often increases fruit set (Garibaldi et al., 2013). However, some native bee populations have been experiencing declines (Cameron et al., 2011; Jacobson et al., 2018; Meiners et al., 2019). Potential drivers of native bee declines include climate change, habitat loss and fragmentation, pathogens, invasive species, and pesticides (Potts et al., 2010). Declines in abundance of pollinators could negatively affect native plant populations (Potts et al., 2010), which could cause cascading effects for other herbivorous wildlife that feed on insect- pollinated plants like forbs and shrubs. Declining pollinators would likely have detrimental effects on crops requiring insect pollination, as many crops are sufficiently pollinated by native bees regardless of the presence of managed honey bees (Garibaldi et al., 2013; Mallinger and Gratton, 2014). Pollinator declines in the United States have been so precipitous that one species, the rusty-patched bumble bee (Bombus affinis), has been listed as Endangered in the United States under the Endangered Species Act (ESA; FR 50 CFR 17 3816 January 11, 2017), and three other species have been petitioned for ESA listing: the yellow-banded bumble bee (B. terricola), the western bumble bee (B. occidentalis), and Franklin’s bumble bee (B. franklini) (Defenders of Wildlife, 2015). Monitoring the decline of pollinator populations is crucial to understand their status and to identify potential causes for their declines (Joshi et al., 2015; Meiners et al., 2019; Rhoades et al., 2017). The lack of standardized sampling protocols in pollinator research makes comparison of studies and range-wide monitoring difficult (Lebuhn et al., 2013). Several methods are 2 commonly used to sample pollinators: colored pan traps/bee cups, vane traps, and aerial netting (Rhoades et al., 2017; Roulston et al., 2007; Wilson et al., 2008). Pan traps are colored bowls or cups usually filled with soapy water that sample bees passively, and are perhaps the most widely used method (Droege et al., 2010). Vane traps, a more novel passive sampling method, are plastic jars fitted with a lid with two intersecting vanes (Stephen and Rao, 2005). Netting involves active sampling either by sweep netting vegetation or visually targeting bees and capturing them in an aerial insect net. These three methods can vary in both the abundance and diversity of bees sampled (Grundel et al., 2011; Rhoades et al., 2017). For example, cups tend to catch a higher abundance of small bees while vanes primarily caught large bees (Joshi et al., 2015; McCravy et al., 2018). Sampling effort (e.g. netting duration and size of survey area, how long traps are deployed) will also change estimates of bee abundance and assemblage (Roulston et al., 2007; Wilson et al., 2008). Additionally, understanding what bees each sampling method collects is useful to better evaluate the status of the bee of interest, like bumble bees. Bumble bees are efficient generalist pollinators that provide invaluable ecosystem services to both forbs and insect-pollinated crops (Losey and Vaughan, 2006). In the last few decades, notable bumble bee declines have been observed in the United Kingdom (Goulson et al., 2008) and in the U.S. (e.g. Cameron et al., 2011; Colla and Packer, 2008; MacPhail et al., 2019). Monitoring is essential to help inform management practices and policy, which includes sampling methods. Different sampling methods – particularly vane traps and aerial netting – are known to be more effective for collecting bumble bees (Stephen and Rao, 2005; Strange and Tripodi, 2019); however, we are not aware of any studies that compare the abundance and assemblage of bumble bees collected using vane traps, bee cups, and netting. 3 Our objective was to investigate how different sampling methods altered the abundance and assemblage (total number