Insect pollinators are threatened by multiple environmental stressors, including pesticide exposure. Despite being important pollinators, solitary ground-nesting bees are inadequately represented by pesticide risk assessments reliant almost exclusively on honeybee ecotoxicology. Here we evaluate the effects of realistic exposure via squash crops treated with systemic insecticides (Admire-imidacloprid soil application, FarMore FI400-thiamethoxam seed-coating, or Coragen-chlorantraniliprole foliar spray) for a ground-nesting bee species (Hoary squash bee, Eucera pruinosa) in a 3-year semi-field experiment. Hoary squash bees provide essential pollination services to pumpkin and squash crops and commonly nest within cropping areas increasing their risk of pesticide exposure from soil, nectar, and pollen. When exposed to a crop treated at planting with soil-applied imidacloprid, these bees initiated 85% fewer nests, left 5.3 times more pollen unharvested, and produced 89% fewer offspring than untreated controls. No measurable impacts on bees from exposure to squash treated with thiamethoxam as a seed-coating or foliage sprayed with chlorantraniliprole were found. Our results demonstrate important sublethal effects of field-realistic exposure to a soil-applied neonicotinoid (imidacloprid) on bee behaviour and reproductive success. Soil must be considered a potential route of pesticide exposure in risk assessments, and restrictions on soil-applied insecticides may be justified, to mitigate impacts on ground-nesting solitary bee populations and the crop pollination services they provide.
Conserving pollinator biodiversity is becoming increasingly important with rising human demand for insect-pollinated crops1,2,3,4,5,6. Losses of pollination services will be particularly detrimental for crops like pumpkin, squash, and gourds (Cucurbita crops) that are entirely dependent upon pollination by bees to set fruit7,8. Among the most efficient and widely distributed wild pollinators of Cucurbita crops in North America is the hoary squash bee (Eucera (Peponapis) pruinosa (Say, 1837))8,9,10,11,12,13. This solitary bee species exhibits an unusually high degree of dietary specialization, depending entirely upon Cucurbita crops (Cucurbitaceae) for pollen across most of its range11,12,14,15. Each hoary squash bee female constructs its own nest in the ground16,17, commonly within cropping areas18,19 where systemic insecticides are often applied as soil drenches or seed treatments19.
Historically almost all information on impacts of pesticide exposure for bees has come from honeybees (Apis mellifera Linnaeus, 1758), the model species for insect pollinator pesticide risk assessments20,21,22,23,24. More recently, exposure to field-realistic levels of systemic neonicotinoid insecticides have been shown to have adverse effects on learning and memory25,26, foraging behaviour27,28,29,30,31,32, colony establishment33,34, reproductive success35,36,37,38, and the delivery of pollination services39,40 in bumblebees (Bombus spp.). Although non-social bees have received less attention, adverse effects from exposure to neonicotinoids on nest establishment37, homing ability41, reproductive output36,37,42, developmental delays43, and reduced adult size and longevity43 have been demonstrated for cavity-nesting solitary bees.
While all bees that forage on treated crops may be at risk of exposure to systemic pesticide residues in pollen and nectar22,23,24, there is an additional risk of exposure to residues in soil for ground-nesting bees19,20. This route of pesticide exposure is currently not considered in regulatory environmental risk assessments for pollinators because honeybees rarely come into direct contact with soil6,19,20. Although approximately 70% of solitary bee species nest in the ground20,44 where they spend most of their lives19,44, and many of these are associated with agriculture1,8,12,20,45,46, no studies have yet evaluated potential impacts of pesticide exposure on this highly significant group of insect pollinators.
We are the first to evaluate the potential effects of exposure to a crop treated with one of three different systemic insecticides on nest establishment, foraging behaviour and offspring production for a solitary, ground-nesting bee in a 3-year semi-field hoop house study that closely mimics normal agricultural practice. The insecticides applied were Admire (neonicotinoid, imidacloprid, applied as a soil drench at seeding), or FarMore FI400 (neonicotinoid, thiamethoxam, applied as a seed treatment), or Coragen (anthranilic diamide, chlorantraniliprole, applied as a foliar spray at the 5-leaf stage), following government pesticide application guidelines47. Imidacloprid and thiamethoxam are used in Ontario to control the striped cucumber beetle (Acalymma vittatum) which vectors bacterial wilt (Erwinia tracheiphila) to the crop47. Chlorantraniliprole is used to control cutworms that attack young plants47.
Results and discussion
To assess the impacts on wild squash bees of field realistic systemic insecticide exposure we grew squash plants (Cucurbita pepo) in twelve netted hoop houses. We applied Admire 240 Flowable Systemic Insecticide (imidacloprid, Methods) as a soil drench at seeding to three hoop houses; planted FarMore FI400 (thiamethoxam + 3 fungicides, Methods) treated seeds in three more hoop houses; applied Coragen (chlorantraniliprole, Methods) as a foliar spray to another three hoop houses, with the remaining three hoop houses left untreated as insecticide controls (Methods; Figure S1). The three different application methods (to soil, via a seed coating, and to foliage) reflect Ontario government recommendations for each product47.
We introduced mated female hoary squash bees into each hoop house at crop bloom (i.e., ~ 8-weeks later: Methods; Figure S1). After mating, hoary squash bee females begin their nesting phase involving three critical overlapping activities: (1) soil excavation and nest establishment; (2) foraging for pollen and nectar to provision nest cells; and (3) laying eggs in provisioned nest cells16,17.
To determine if exposure to squash crops treated with systemic insecticides interfered with nest establishment, we tracked the number of nests established by foundress (2017) and second generation (2018) females in each hoop house (Methods; Figure S1). Nest establishment was substantially affected by insecticide treatment (F3,14 = 7.33; p = 0.003; Table S1; Table S2), with significantly fewer nests established in the Admire-treated hoop houses than in other treatments (mean ± SE: Admire: 1.5 ± 1.3; Control: 9.8 ± 2.2; Coragen: 9.8 ± 1.0; FarMore FI400: 9.8 ± 2.20; Fig. 1; Table 1). Compared to the untreated control, nest establishment by hoary squash bees exposed to a squash crop treated with soil-applied Admire- was reduced by 76% in 2017 (mean ± SE: Admire: 0.3 ± 0.3; Control: 8.7 ± 2.6), 96% in 2018 (Admire: 2.7 ± 2.7; Control: 11.0 ± 4.0) with an 85% reduction across both years (Admire vs Control: t13 = − 3.83, p = 0.009; Fig. 1; Table 1; Table S3). We detected no significant differences in the numbers of nests established by females in the control, Coragen, and FarMore FI400 treatments (Table 1; Table S3). These results could reflect a lack of effect of exposure to chlorantraniliprole or thiamethoxam on squash bee behaviour or might be a result of the application method (foliar spray or seed coating) reducing the extent of exposure to the active ingredient in soil, nectar, and/or pollen. For Coragen, the lack of measurable effects could be because only a single application was made for cutworm control47 after which bees were not yet active during the period of residual activity (reported to be 21 days after application: https://ag.fmc.com/us/en/insecticides-miticides/coragen-insecticide). Exposure to a chlorantraniliprole-treated crop may have had greater impact if the chlorantraniliprole spray had been applied closer to the bee active period. It should be noted, however, that residues of imidacloprid, thiamethoxam (and its metabolite clothianidin), and chlorantraniliprole were detected in some of the soil samples taken during the bee active period in both 2017 and 2018 (Table S6).
The results for imidacloprid (Admire applied to the soil at seed planting) are consistent with studies indicating neonicotinoid-exposure can reduce nesting activity in stem-nesting solitary bees37,42 and delay or reduce the likelihood of nest establishment in bumblebees33,34,48,49. Our study is the first to report an impact of neonicotinoid-exposure on nesting in any solitary ground-nesting species, arguably the most ecologically important and biodiverse group of bees. The 85% reduction in nest establishment (over 2 years) by squash bee females exposed to a squash crop treated with soil-applied imidacloprid under real agricultural conditions incorporates both contact with soil and consumption of contaminated nectar and pollen as potential routes of exposure, whilst previous studies have focused solely on oral exposure32,33,34,37,42,48,49.
During their nesting phase, hoary squash bees also amass pollen to provision their nest cells. The reproductive success of female solitary bees is limited by the number of nest cells they can provision42,44, and the amount of pollen harvested affects the subsequent reproductive success of their offspring50,51,52. To determine if exposure to crops treated with systemic insecticides affected pollen harvesting by female hoary squash bees, we counted the pollen remaining on anthers of squash flowers at the end of the daily foraging period in each hoop house (Methods; Figure S1). Pollen collection was substantially affected by insecticide treatment (F3,114 = 37.82; p < 0.001; Table S1; Table S2) with 5.3 times more unharvested pollen remaining on anthers in the Admire-treatment than the control (Admire: 13,662.0 ± 1179.6; Control: 2168.0 ± 461.5; t114 = 9.38, p < 0.001; Fig. 2; Table S3). Although hoary squash bees in the Coragen treatment also collected significantly less pollen than bees in the control group (Coragen: 5422.0 ± 1075.4; Control: 2168.0 ± 461.5; t114 = − 2.7, p = 0.044; Table 1; Table S3), nest establishment and offspring production appeared unaffected (Table S2). Bees in the FarMore FI400 (2606.0 ± 457.0) and the control treatment collected comparable quantities of pollen (t114 = − 0.36, p = 0.984; Table 1; Table S3).
Our results show that female hoary squash bees exposed to Admire-treated crops constructed fewer nests and collected less pollen than unexposed bees, a combined negative effect that would likely reduce offspring production50,51,52. To determine if offspring production was affected by exposure to crops treated with systemic insecticides, we counted and sexed all hoary squash bees that emerged from all nests constructed in the hoop houses in 2017 and 2018 (Methods; Figure S1). Offspring production was significantly affected by insecticide treatment (F3,13 = 14.19, p < 0.001), year (F1,13 = 11.79, p = 0.004) and the abundance of flowers (F1,13 = 10.44, p = 0.007) as main model effects, and the interaction between insecticide treatment and year (F3,13 = 3.81, p = 0.037; Table S1; Table S2). In the Admire-treatment, 89% fewer offspring were produced than in the control (Admire = 3.3 ± 1.6, Control = 35.0 ± 8.3; t15 = − 5.98, p < 0.001; Table 1; Table S3).
Although fewer offspring were produced in the FarMore FI400 (thiamethoxam) seed treatment (FarMore FI400 = 22.2 ± 4.7; Table 1) compared to the control this difference was not statistically significant (t15 = 2.59, p = 0.091; Table S3). There was also no significant difference in offspring production between the Coragen treatment (32.3 ± 9.1; Table 1) and the untreated control (t15 = 0.80, p = 0.854; Table S3). The effect of exposure to squash crops treated with FarMore FI400, though not statistically significant at α = 0.05, may warrant more attention as clothianidin, a metabolite of thiamethoxam53,54 can have toxic effects on honeybees and can also affect stem-nesting solitary bees37,42,55.
Floral resources in the hoophouses affected the number of offspring produced (F3,13 = 10.44; p = 0.007; Table S2), but did not explain the variance in the number of offspring well (Y = 1.16 + 0.47X; r2 = 0.04). The effects of year, and the treatment*year interaction, are likely explained by expanding populations in the second generation (2018) in the Coragen and control hoop houses but not the Admire and FarMore FI400 treatments (Table S2; Table S4).
While cavity-nesting solitary bees can shift towards male-biased offspring sex ratios after exposure to sublethal doses of neonicotinoids42, we found no effect of exposure to systemic insecticide treatments (Admire, Coragen, FarMore FI400) on the sex ratio of hoary squash bees here (Model: Sex Ratio = Treatment + Year; Treatment: F3,14 = 0.08, p = 0.968; Year: F1,14 = 6.73, p = 0.021; Table S1; Table S2). Offspring sex ratios varied substantially between years within all treatments, becoming more male biased overall between 2017 and 2018 (2017: 0.7 ± 0.1; 2018: 3.5 ± 1.1; Table 1). It is unlikely that the shift towards more male biased sex ratios in 2018 was the result of weather conditions, such as flooding or severe cold, which should have impacted shallower (male-bearing) nest cells more than deeper (female-bearing) nest cells44,56. Alternatively, as hoop house populations expanded from 8 to ~ 16.5 bees from 2017 to 2018, increased competition among females for floral resources may have caused them to allocate limited pollen resources to the production of male offspring that require less pollen to develop57.
For all nesting phase effects (i.e. nest establishment, pollen collection, and offspring production), there was strong evidence of negative impacts of exposure to an Admire-treated crop under ecologically and agriculturally realistic field conditions in our study. There may also be less severe negative impacts on offspring production from exposure to FarMore FI400 which we were unable to detect statistically.
Potential routes of exposure to systemic insecticides here include topical exposure to soil residues (Table S6) during nest construction, and topical and oral exposure to all three systemic insecticides in the nectar and pollen of the squash crop19,58,59, although the hazard from these insecticides in squash pollen is low for hoary squash bees under Ontario growing conditions19. Topical exposure to chlorantraniliprole applied to crop leaves is unlikely as the bee active period occurred substantially (~ 5 weeks) after the 21-day residual activity period of this insecticide on foliage. Which exposure route(s) contributed most to the observed effects could not be discriminated, representing an important knowledge gap for future research. Imidacloprid (half-life: 28–1250 days), thiamethoxam (half-life: 7–353 days) and its metabolite clothianidin (half-life: 148–6931 days) are all soil persistent60 and have been found in soil in Ontario in the season after which they were applied19. Chlorantraniliprole residues have also been found in soil and pollen taken from pumpkin fields (Cucurbita pepo) in Ontario during the hoary squash bee active season (August)19 but are considered to be less soil persistent (half-life: 115–169 days)61. In this study, soil samples taken prior to treatment in 2017 contained residues of clothianidin in all hoop houses (mean ± SE: 3.58 ± 0.40; min = 1.1; max = 9.4 ppb; n = 24 samples), likely persisting from previous crops grown on the site before our research began. However, concentrations of clothianidin residues in soil samples taken before treatments were applied in 2018 were all below the method quantification limit of 1 ppb. Unfortunately, it was not possible to take nectar or pollen samples for pesticide residue analyses as this would not have left sufficient floral resources in hoop houses for the bees to forage and provision their nests.
For hoary squash bees exposed to an Admire-treated squash crop, the number of nests established was strongly reduced (Fig. 1), less pollen was collected (Fig. 2) and fewer offspring were produced (Fig. 3). These outcomes for Admire-exposed hoary squash bees are substantial and should be of concern to growers, pesticide regulators, and those engaged in pollinator conservation.
For squash crops, the pollination services of bees are especially important to growers because the pollen cannot be moved between flowers by wind7, and the size of the pollen load deposited on the stigmas of female flowers subsequently affects fruit quality62. We evaluated the effect of exposure to crops treated with systemic insecticides (Admire, Coragen, or FarMore FI400) on the hoary squash bee’s ability to deliver pollination services to the crop as measured by percentage of both fruit set and marketable fruit (> 500 g) (Methods). We found no measurable effect of treatment on either fruit set (F3,8 = 0.16, p = 0.919) or marketable fruit yield (F3,18 = 0.14, p = 0.936; Table 1; Table S1; Table S2).
Although hoary squash bees in Admire-treated hoop houses removed much less pollen from squash flowers, sufficient pollen was moved between flowers in all treatments to achieve the physiological fruit set limit of the squash crop (about 50%; Table 1)62. Thus, although hoary squash bees may not reproduce normally when exposed to an Admire-treated squash crop, they may still provide effective crop pollination services within a season.
However, those services could be severely reduced in subsequent seasons unless hoary squash bees disperse into the crop from other locations, a poor long-term strategy for achieving stable pollination services for squash crops. Clearly, the issue of pollinator population health and stability would not be detected by growers if they use yield within a single season as their measure. Although replacing wild pollinators with managed honeybees might be suggested in the short term, it is not a sustainable solution because global demand for managed hives to pollinate crops has already outstripped supply4,5,63. Furthermore, honeybees are often not the most effective crop pollinators on an individual basis for many insect dependent crops (including for pumpkin and squash9,10,64, and yield and quality of many crops are improved by exposure to the pollination services of many pollinator taxa1,2,3.
It is notable that exposure to Coragen-treated crops (chlorantraniliprole) seemed to have little impact on hoary squash bee reproduction in our study. This might be because chlorantraniliprole does not translocate effectively from one leaf to another when it is applied foliarly65. However, exposure to chlorantraniliprole has also been reported to be less of a concern to bees than neonicotinoids for laboratory trials with honey bees, bumble bees, or stingless bees66,67,68,69, semi-field trials with bumble bees70, and from our probabilistic risk assessment based on putative field exposure for hoary squash bees19. The low hazard to bees appears to be due to an insensitivity in non-Lepidopteran insects to the ryanodine target site for the insecticide65,66,71,72. As such, Coragen may offer a viable crop protection alternative for squash growers against insect pests that poses a lower risk to ground-nesting solitary bees than some other registered systemic insecticides.
The negative implications for hoary squash bees of exposure to Admire (imidacloprid) treated crops may be an indication of a wider negative impacts on other ground-nesting solitary bee species that forage on or nest around a wide variety of other neonicotinoid-treated crops1,45,46. As such, the importance of our findings should resonate with regulatory agencies seeking to ensure the environmental safety of pesticides, growers who depend on the pollination services of ground-nesting bees, and conservationists seeking to understand the mechanisms for pollinator decline.
To establish a captive hoary squash bee population and study the potential effects of exposure to systemic insecticide treatments under controlled conditions, twelve (12) hoop houses (Width 4.80 m × Length 6.10 m × Height 3.05 m) were set up on a farm in Peterborough County, Ontario, Canada in 2017 (Figure S1). All hoop houses were covered with 50% shade cloth to prevent introduced hoary squash bees from escaping and to exclude other bees from entering, while allowing exterior environmental conditions to prevail within the enclosures (Figure S2).
All doorways had both an outwards-opening door and a double plastic sheet across them inside to prevent bees from escaping when researchers entered or left the hoop house. Before hoary squash bees were introduced, all hoop houses were tested to ensure they were bee proof by introducing a hive of honeybees (Apis mellifera) and watching for escapees. Honeybees are similar in size to hoary squash bees and were unable to escape from the hoop houses, although they actively crawled over the netting. Colonies were removed from the site at night when all honeybees were back in the hive. Subsequent observations of hoary squash bees confirmed that they were not able or even trying to escape from hoop houses.
Growing squash plants and insecticide treatments
Inside each hoop house we established two growing areas for 28 plants (14 per growing area) at spacings recommended by the seed supplier (Rupp Seeds, Inc.) and a bare soil nesting area surrounded by a mulched path (Figure S2). Soil at the study site was Otonabee loam, providing an excellent substrate for growing cucurbits and for hoary squash bees to construct their nests below ground. The site had a soil texture gradient of increasing sand from north to south (Figure S1).
Acorn squash seeds (varieties were Table Star in 2017 and Celebration in 2018) were planted into the growing areas following the practices of commercial growers in the Peterborough area (May 23 in 2017 and June 8 in 2018). Seeds that did not germinate within five days were subsequently replanted. Untreated seeds were planted in nine hoop houses, and FarMore FI400 treated seeds (Neonicotinoid insecticide: Cruiser 5FS insecticide = 47.6% thiamethoxam, CAS No. 153719-23-4 + Fungicides: Apron XL = 33.3% mefenoxam, CAS Nos. 70630-17-0 and 69516-34-3; Maxim 480FS = 40.3% fludioxonil, CAS No. 131341-86-1; and Dynasty = 9.6% azoxystrobin, CAS No. 131860-33-8) were planted in the other three (2C, 3B, 4A; Figure S1). Admire 240 (neonicotinoid flowable insecticide: 21.4% imidacloprid, 240 g/L, CAS No. 138261–41-3) and Coragen (anthranilic diamide insecticide: 21.4% chlorantraniliprole, 200 g/L, CAS No. 500008-45-7) treatments used the highest labelled rate of pesticide application following the Ontario Ministry of Agriculture, Food and Rural Affairs (OMAFRA) Vegetable Crop Protection Guide47 and were applied by a licensed pesticide applicator with a 4-gallon backpack sprayer (Roundup 190367), calibrated before each application.
Following Ontario government guidelines47, Admire (imidacloprid) was applied in-furrow at time of seeding (18 mL/100 m row)47 to three of the hoop houses (1A, 3C, 4B; Figure S1). Coragen (chlorantraniliprole) was applied as a foliar spray at the 5-leaf stage of plant growth (250 mL/ha)47 in another three hoop houses (1C, 2B, 3A; Figure S1). In three more hoop houses (2C, 3B, 4A; Figure S1), seeds coated with FarMore FI400 technology (Insecticide: thiamethoxam + 3 Fungicides) were planted. The remaining three hoop houses (1B, 2A, 4C; Figure S1) were not treated with any pesticides as a control. Plants in all hoop houses were covered with row cover until the onset of flowering to provide a physical barrier against cucumber beetle (Acalymma vittatum) pests.
Insecticide treatments were assigned randomly with respect to hoop houses, with three blocks of four treatments and all treatments equally represented along the site soil gradient (Figure S1). All treatments were assigned to the same hoop houses in both 2017 and 2018. Observations were made blind with respect to treatment in 2017, but one observer (D.S.W.C.) was aware of the treatment assignments for logistical reasons in 2018. Squash plants were also planted in the hoop houses in 2019 to provide resting sites for emerging bees, making it easier to capture them. No pesticides were applied in 2019.
Squash plants began flowering during the third week of July in all years. At the start of bloom in 2017 we discovered that the nectary of staminate (male) flowers in the Table Star squash variety would be inaccessible to bees because these flowers lacked holes in the base of the stamen tissue covering the nectary. To overcome this issue, team members created three artificial holes in each staminate flower at the start of every day by inserting a dissection needle through the stamen tissue above the nectary (Figure S3). This effectively mimicked the holes that should have been present and allowed bees full access to the nectar supply throughout the experiment. We avoided this issue in 2018 by planting a different acorn squash variety (Celebration).
Hoary squash bee study population
To establish a population of hoary squash bees within the hoop houses, mated female hoary squash bees were captured from a wild population on a farm near Guelph, Ontario that has a large, well-established nesting aggregation with more than 3000 nests. To ensure that females to be introduced to the hoop houses were mated, only females entering a nest with a full pollen load were collected from the source population (Figure S4). In August 2017, we collected 96 female hoary squash bees so that we could introduce eight per hoop house. Each bee was placed in a separate aerated 2-mL microcentrifuge tube (Figure S5) kept upright in cool, dark conditions during transport. Upon arrival in Peterborough county, the bees were transferred to a refrigerator until the following morning when eight bees were haphazardly selected and released individually into each hoop house.
Releasing bees in the early morning coincided with the beginning of the daily bloom period of squash flowers ensuring that suitable food was immediately available. All bees (n = 96) introduced in 2017 survived the stress of capture, transport, and release into hoop houses and immediately flew out of the tubes on their own. Females began establishing nests as early as four days after introduction. To our knowledge this is the first time that mated adult hoary squash bees have been successfully introduced into and maintained under controlled semi-field conditions, offering the possibility of using hoary squash bees as a model species for other ground-nesting bees in insecticide risk assessments and research.
A second generation of hoary squash bees emerged in the hoop houses in summer 2018 from nests established by females introduced the previous summer (2017). This second generation of bees foraged, mated, and established nests in 2018. All 2018 observations were made on this second-generation and no new bees were introduced. We recorded the number and sex of all bees that emerged in the twelve hoop houses in 2018 and 2019 from nests established by the first- and second-generation females in the respective previous year.
Observations of nesting were made when female hoary squash bees were active, starting from 06:00 (dawn) until bee activity ceased around 11:00 each day, by four observers on ten and eight of the observation days in 2017 and 2018 respectively (Table S5). Each observer was responsible for surveying three hoop houses per day. At the beginning of every observation day, observers searched for active nests within the hoop house and uniquely identified them with a marker (Figure S6). Active nests were easy to locate as bees with bright yellow pollen entering the nest were conspicuous (Figure S4), and nests tended to be aggregated.
Female squash bees are able collect all the nutrients they require to both survive and provision their offspring from the nectar and pollen from Cucurbita crops12. Staminate (male) flowers provide both these resources, while pistillate (female) flowers produce only nectar7,73. To determine any potential variation in resource availability among treatments the total number of staminate and pistillate flowers in each hoop house was counted on six and eight of the observation days in 2017 and 2018 respectively (Table S5). Although it was not possible to directly examine pollen loads collected by individuals without unduly disturbing the bees, pollen harvesting behaviour by the female population within a hoop house was evaluated by quantifying the number of unharvested pollen grains remaining on anthers of staminate flowers at the end of the foraging period (data were collected on 17 and 23 August 2017: Table S5).
To do this, ten anthers were removed from staminate flowers in each hoop house and placed individually into 2-mL microcentrifuge tubes containing 0.5 mL of 70% ethanol. Pollen was dislodged from anther samples by centrifugation at 2500 rpm for three minutes and then the anther was removed. Subsequently, each microcentrifuge tube was topped up with 1.5 mL of 50% glycerine solution to bring the liquid volume to 2 mL and increase the solution viscosity73. The pollen samples were thoroughly agitated in the glycerine solution using a mini-vortex mixer and five 5-µL aliquots were removed from the solution, each of which was placed individually on each square of a gridded waterproof sheet. We counted the total number of pollen grains in each grid square under a microscope at 25× magnification. The number of pollen grains remaining on each anther was calculated by averaging the number of pollen grains counted per square across the five 5-µL aliquots and relating this back to the full 2-mL volume of the pollen-glycerine-alcohol suspension73.
Hoary squash bees are univoltine, producing a single generation of offspring each year17. During the 30 to 45-day period that adults are active, females provision nest cells and lay eggs that hatch and develop to the pre-pupal stage within several weeks17. The bees remain at the pre-pupal stage throughout the autumn, winter, and spring, pupating just before emerging as adults the following summer (July–August in Ontario)17. Because offspring emerge as adults the year after eggs were laid into nest cells, offspring counts did not include those individuals that did not develop to maturity or survive the winter.
To determine the number of bees that emerged from nests established in 2017, bees in each hoop house were collected from flowers at the end of the 2018 season. This approach was taken because the hoary squash bees emerged over an extended period. Because unmated female and male hoary squash bees normally rest in wilted Cucurbita flowers during the afternoon and night, all the wilted flowers in each hoop house were examined during two consecutive afternoons (August 23 and 24, 2018) and all bees found resting inside them were sexed, counted, and removed. Mated female bees entering nests or gathering pollen on flowers were collected in the same way at dawn on the mornings of August 24 and 25 (2018). As no bees were found in any hoop houses on the morning of August 25 or thereafter, we concluded that offspring emergence had finished. Although this method may underestimate offspring emergence if some individuals died before the final collection, it provides useful information about the relative numbers of male and female bees that could not otherwise be quantified. Bees emerging from nests established in 2018 were collected from wilted flowers from July 30-September 4, 2019, after which no more bees emerged. After this collection, each bee was sexed and released.
Squash fruit set and marketable yield
To evaluate fruit set individual pistillate flowers were marked within each hoop house with a flag and by scratching the date and hoop house number onto the skin of the undeveloped fruit (ovary). This process was repeated on ten days (August 4–24, 2017; Table S5) over the 3-week period during which hoary squash bees were active in the hoop houses, although pistillate flowers were not always in flower in each hoop house on any single day. At the end of the season, each ovary was evaluated as either aborted or having set fruit. Fruit set could not be evaluated in 2018 because the Celebration variety did not tolerate the marking technique and aborted all marked fruit. Marketable yield was evaluated by harvesting, counting, and weighing all fruit from each hoop house and calculating the percentage of marketable size (≥ 500 g).
To evaluate soil insecticide residues for each treatment during the period of female hoary squash bee activity, we took soil samples from the planted areas in each hoop house (on May 23, 2017 and June 8, 2018) just before applying the insecticide treatments and on three days during the bee active period (July and August; Figure S1). Samples were taken from the top 15 cm of soil because this is the depth at which hoary squash bees construct their nests17. For each planted area, four soil core samples were combined and subsampled to produce a single 3-g sample (i.e. 2 samples per hoop house). Potential for cross-contamination of samples was minimised by using disposable gloves, single-use containers and instruments, and thorough cleaning of the soil corer between hoop houses and a double rinse with clean water. Nectar and pollen samples were not taken within hoop houses because of concerns about depleting food resources for the study bees. This represents a knowledge gap, preventing this study from establishing the specific route of exposure (soil vs. pollen vs. nectar) that caused reported effects.
All samples were kept frozen at − 20 °C before submission for analysis to University of Guelph Agri-Food Laboratories (ISO/IEC 17025 accredited) which used liquid chromatography/electrospray ionization-tandem mass spectrometry (LC/ESI–MS/MS) and gas chromatography-tandem mass spectrometry (GC–MS/MS) (Modified Canadian Food Inspection Agency (CFIA) PMR-006-V1.0) to detect the presence and determine the concentrations of imidacloprid, clothianidin, thiamethoxam, and chlorantraniliprole in samples. Although clothianidin was not applied as a treatment, it is a common, persistent metabolite of thiamethoxam53,54 and was detected in our samples (Table S6).
Data were analysed using SAS Studio University Edition version 3.8 to generate summary statistics and carry out analyses using generalized linear mixed model (GLMM) procedures. Models were generated by including all measured fixed effects and their interactions and the random effect of block. Where the statistical output from SAS indicated that one or more of the variance components were estimated to be zero, the random effect of block was removed, and the model was re-analyzed74. Although measures were repeated over two years in the same hoop houses, the population within the hoop houses changed from eight foundresses in 2017 to the 2nd generation of offspring including males and females in 2018. As such, year was considered a categorical effect rather than a repeated measure. The model with the lowest Akaike Information Criterion (AIC) was chosen as the best fit and statistical analyses were executed using that model. We performed post hoc pairwise comparisons for all the significant categorical fixed effects using differences of least square means, and a Tukey–Kramer-adjusted p >|t| for multiple comparisons. The significance level used in all tests was α = 0.05.
Data are available in Supplementary Information.
Garibaldi, L. A. et al. Wild pollinators enhance fruit set of crops regardless of honey bee abundance. Science 339, 1608–1611. https://doi.org/10.1126/science.1230200 (2013).
Potts, S. G. et al. Safeguarding pollinators and their values to human well-being. Nature 540, 220–229. https://doi.org/10.1038/nature20588 (2016).
Rader, R. et al. Non-bee insects are important contributors to global crop pollination. Proc. Natl. Acad. Sci. U.S.A. 113, 146–151. https://doi.org/10.1073/pnas.1517092112 (2016).
Aizen, M. A., Garibaldi, L. A., Cunningham, S. A. & Klein, A. M. Long-term global trends in crop yield and production reveal no current pollination shortage but increasing pollinator dependency. Curr. Biol. 18, 1572–1575. https://doi.org/10.1016/j.cub.2008.08.066 (2008).
Aizen, M. A. & Harder, L. D. The global stock of domesticated honey bees is growing slower than the agricultural demand for pollination. Curr. Biol. 19, 915–918. https://doi.org/10.1016/j.cub.2009.03.071 (2009).
Vanbergen, A. J. & Initiative, I. P. Threats to an ecosystem service: Pressures on pollinators. Front. Ecol. Environ. 11, 251–259. https://doi.org/10.1890/120126 (2013).
Whitaker, T. & Davis, G. Cucurbits: Botany, Cultivation & Utilization (Biotech Books, Delhi, 2012).
Hurd, P. D. Jr., Linsley, E. G. & Whitaker, T. Squash and gourd bees (Peponapis, Xenoglossa) and the origin of the cultivated Cucurbita. Evolution 25, 218–234. https://doi.org/10.2307/2406514 (1971).
Artz, D. R. & Nault, B. A. Performance of Apis mellifera, Bombus impatiens, and Peponapis pruinosa (Hymenoptera: Apidae) as pollinators of pumpkin. J. Econ. Entomol. 104, 1153–1161. https://doi.org/10.1603/EC10431 (2011).
Cane, J. H., Sampson, B. J. & Miller, S. Pollination value of male bees: the specialist bee Peponapis pruinosa (Apidae) at summer squash (Cucurbita pepo). Environ. Entomol. 40, 614–620. https://doi.org/10.1603/EN10084 (2011).
Hurd, P. D. Jr. & Linsley, E. G. The squash and gourd bees-genera Peponapis Robertson and Xenoglossa Smith-inhabiting America north of Mexico (Hymenoptera: Apoidea). Hilgardia 35, 375–453. https://doi.org/10.3733/hilg.v35n15p375 (1964).
López-Uribe, M. M., Cane, J. H., Minckley, R. L. & Danforth, B. N. Crop domestication facilitated rapid geographical expansion of a specialist pollinator, the squash bee Peponapis pruinosa. Proc. R. Soc. B-Biol. Sci. 283, 20160443. https://doi.org/10.1098/rspb.2016.0443 (2016).
Tepedino, V. J. The pollination efficiency of the squash bee (Peponapis pruinosa) and the honey bee (Apis mellifera) on summer squash (Cucurbita pepo). J. Kansas Entomol. Soc. 54, 359–377. Retrieved from https://www.jstor.org/stable/25084168 (1981).
Patton, W. Generic arrangement of the bees allied to Melissodes and Anthophora. Bull. U. S. Geolog. Surv. 5, 471–479. Retrieved from https://books.google.ca/books?hl=en&lr=&id=R38uAAAAYAAJ&oi=fnd&pg=PA469&ots=LVcsvi2gE5&sig=xlz2XhDKuN5qMenv47JIRhYfy_8&redir_esc=y#v=onepage&q&f=false (1879).
Willis, D. S. & Kevan, P. G. Foraging dynamics of Peponapis pruinosa (Hymenoptera: Anthophoridae) on pumpkin (Cucurbita pepo) in Southern Ontario. Can. Entomol. 127, 167–175 (1995).
Hurd, P. D. Jr., Linsley, E. G. & Michelbacher, A. E. Ecology of the squash and gourd bee, Peponapis pruinosa, on cultivated cucurbits in California (Hymenoptera: Apoidea). Smiths. Contrib. Zool. 168, 1–17. Smithsonian Institution Press. Retrieved from https://repository.si.edu/bitstream/handle/10088/5347/SCtZ-0168-Lo_res.pdf?sequence=2 (1974).
Mathewson, J. A. Nest construction and life history of the eastern cucurbit bee, Peponapis pruinosa (Hymenoptera: Apoidea). J. Kansas Entomol. Soc. 41, 255–261. Retrieved from https://www.jstor.org/stable/25083703 (1968).
Julier, H. E. & Roulston, T. H. Wild bee abundance and pollination service in cultivated pumpkins: Farm management, nesting landscape effects. J. Econ. Entomol. 102, 563–573. https://doi.org/10.1603/029.102.0214 (2009).
Willis Chan, D. S., Prosser, R. S., Rodríguez-Gil, J. L. & Raine, N. E. Risks of exposure to systemic insecticides in agricultural soil in Ontario, Canada for the hoary squash bee (Peponapis pruinosa) and other ground-nesting bee species. Sci. Rep. 9, 11870. https://doi.org/10.1038/s41598-019-47805-1 (2019).
Sgolastra, F. et al. Pesticide exposure assessment paradign for solitary bees. Environ. Entomol. 48, 22–35. https://doi.org/10.1093/ee/nvy105 (2019).
Franklin, E. L. & Raine, N. E. Moving beyond honey bee-centric pesticide risk assessments to protect all pollinators. Nat. Ecol. Evol. 3, 1373–1375. https://doi.org/10.1038/s41559-019-0987-y (2019).
Blacquière, T., Smagghe, G., van Gestel, C. A. M. & Mommaerts, V. Neonicotinoids in bees: A review on concentrations, side-effects and risk assessment. Ecotoxicology 24, 73–92. https://doi.org/10.1007/s10646-012-0863-x (2012).
Godfray, H. C. J. et al. A restatement of the natural science evidence base concerning neonicotinoid insecticides and insect pollinators. Proc. R. Soc. B Biol. Sci. 281, 20140558. https://doi.org/10.1098/rspb.2014.0558 (2014).
Godfray, H. C. J. et al. A restatement of recent advances the natural science evidence base concerning neonicotinoid insecticides and insect pollinators. Proc. R. Soc. B Biol. Sci. 281, 20151821. https://doi.org/10.1098/rspb.2015.1821 (2015).
Samuelson, E. E. W., Chen-Wishart, Z. P., Gill, R. J. & Leadbeater, E. Effect of acute pesticide exposure on bee spatial working memory using an analogue of the radial-arm maze. Sci. Rep. 6, 38957. https://doi.org/10.1038/srep38957 (2016).
Stanley, D. A., Smith, K. E. & Raine, N. E. Bumblebee learning and memory is impaired by chronic exposure to a neonicotinoid pesticide. Sci. Rep. 5, 16508. https://doi.org/10.1038/srep16508 (2015).
Gill, R. J., Ramos-Rodríguez, O. & Raine, N. E. Combined pesticide exposure severely affects individual- and colony-level traits in bees. Nature 491, 105–108 https://doi.org/10.1038/nature11585 (2012).
Gill, R. J. & Raine, N. E. Chronic impairment of bumblebee natural foraging behaviour induced by sublethal pesticide exposure. Funct. Ecol. 28, 1459–1471. https://doi.org/10.1111/1365-2435.12292 (2014).
Feltham, H., Park, K. & Goulson, D. Field realistic doses of pesticide imidacloprid reduce bumblebee pollen foraging efficiency. Ecotoxicology 23, 317–323. https://doi.org/10.1007/s10646-014-1189-7 (2014).
Stanley, D. A. & Raine, N. E. Chronic exposure to a neonicotinoid pesticide alters the interactions between bumblebees and wild plants. Funct. Ecol. 30, 1132–1139. https://doi.org/10.1111/1365-2435.12644 (2016).
Stanley, D. A., Russell, A. L., Morrison, S. J., Rogers, C. & Raine, N. E. Investigating the impacts of field-realistic exposure to a neonicotinoid pesticide on bumblebee foraging, homing ability and colony growth. J. Appl. Ecol. 53, 1440–1449. https://doi.org/10.1111/1365-2664.12689 (2016).
Muth, F. & Leonard, A. S. A neonicotinoid pesticide impairs foraging, but not learning, in free-flying bumblebees. Sci. Rep. 9, 4764. https://doi.org/10.1038/s41598-019-39701-5 (2019).
Baron, G. L., Jansen, V. A. A., Brown, M. J. F. & Raine, N. E. Pesticide reduces bumblebee colony initiation and increases probability of population extinction. Nat. Ecol. Evol. 1, 1308–1316. https://doi.org/10.1038/s41559-017-0260-1 (2017).
Wu-Smart, J. & Spivak, M. Effects of neonicotinoid imidacloprid exposure on bumble bee (Hymenoptera: Apidae) queen survival and nest initiation. Environ. Entomol. 47, 55–62. https://doi.org/10.1093/ee/nvx175 (2018).
Whitehorn, P. R., O’Connor, S., Wackers, F. L. & Goulson, D. Neonicotinoid pesticide reduces bumble bee colony growth and queen production. Science 336, 351–352. https://doi.org/10.1126/science.1215025 (2012).
Woodcock, B. A. et al. Country-specific effects of neonicotinoid pesticides on honey bees and wild bees. Science 356, 1393–1395. https://doi.org/10.1126/science.aaa1190 (2017).
Rundlöf, M. et al. Seed coating with a neonicotinoid insecticide negatively affects wild bees. Nature 571, 77–80. https://doi.org/10.1038/nature14420 (2015).
Ellis, C., Park, K. J., Whitehorn, P., David, A. & Goulson, D. The neonicotinoid insecticide thiacloprid impacts upon bumblebee colony development under field conditions. Environ. Sci. Technol. 51, 1727–1732. https://doi.org/10.1021/acs.est.6b04791 (2017).
Switzer, C. M. & Combes, S. A. The neonicotinoid pesticide, imidacloprid, affects Bombus impatiens (bumblebee) sonication behavior when consumed at doses below the LD50. Ecotoxicology 25, 1150–1159. https://doi.org/10.1007/s10646-016-1669-z (2016).
Stanley, D. A. et al. Neonicotinoid pesticide exposure impairs crop pollination services provided by bumblebees. Nature 528, 548–550. https://doi.org/10.1038/nature16167 (2015).
Jin, N., Klein, S., Leimig, F., Bischoff, G. & Menzel, R. The neonicotinoid clothianidin interferes with navigation of the solitary bee Osmia cornuta in a laboratory test. J. Exp. Biol. 218, 2821–2825. https://doi.org/10.1242/jeb.123612 (2015).
Sandrock, C. et al. Sublethal neonicotinoid insecticide exposure reduces solitary bee reproductive success. Agric. For. Entomol. 16, 119–128. https://doi.org/10.1111/afe.12041 (2014).
Anderson, N. L. & Harmon-Threatt, A. N. Chronic contact with realistic soil concentrations of imidacloprid affects the mass, immature development speed, and adult longevity of solitary bees. Sci. Rep. 9, 3724. https://doi.org/10.1038/s41598-019-40031-9 (2019).
Danforth, B. N., Minckley, R. L. & Neff, J. L. The Solitary Bees: Biology, Evolution, Conservation (Princeton University Press, Princeton, 2019).
Wheelock, M. J., Rey, K. P. & O’Neal, M. E. Defining the insect pollinator community found in Iowa corn and soybean fields: Implications for pollinator conservation. Environ. Entomol. 4, 1099–1106. https://doi.org/10.1093/ee/nvw1087 (2016).
USDA. Attractiveness of agricultural crops to pollinating bees for the collection of nectar and/or pollen. Retrieved from https://www.ars.usda.gov/ARSUserFiles/OPMP/Attractiveness%20of%20Agriculture%20Crops%20to%20Pollinating%20Bees%20Report-FINAL_Web%20Version_Jan%203_2018.pdf (2017).
OMAFRA. Vegetable Crop Protection Guide, 82–83. Government of Ontario (2014).
Leza, M., Watrous, K. M., Bratu, J. & Woodard, S. H. Effects of neonicotinoid insecticide exposure and monofloral diet on nest-founding bumblebee queens. Proc. R. Soc. B Biol. Sci. 285, 20180761. https://doi.org/10.1098/rspb.2018.0761 (2018).
Baron, G. L., Raine, N. E. & Brown, M. J. F. General and species-specific impacts of a neonicotinoid insecticide on the ovary development and feeding of wild bumblebee queens. Proc. R. Soc. B Biol. Sci. 284, 20170123. https://doi.org/10.1098/rspb.2017.0123 (2017).
Roulston, T. H. & Cane, J. H. The effect of diet breadth and nesting ecology on body size variation in bees (Apiformes). J. Kansas Entomol. Soc. 73, 129–142. Retrieved from https://www.jstor.org/stable/25085957 (2000).
Klostermeyer, E., Mech, S. J. & Rasmussen, W. Sex and weight of Megachile rotundata (Hymenoptera: Megachilidae) progeny associated with provision weights. J. Kansas Entomol. Soc. 46, 536–548. Retrieved from https://www.jstor.org/stable/25082604 (1973).
Bosch, J. & Vicens, N. Relationship between body size, provisioning rate, longevity and reproductive success in females of the solitary bee Osmia cornuta. Behav. Ecol. Sociobiol. 60, 26–33. https://doi.org/10.1007/s00265-005-0134-4 (2006).
Bonmatin, J. M. et al. Environmental fate and exposure: Neonicotinoids and fipronil. Environ. Sci. Pollut. Res. 22, 35–67. https://doi.org/10.1007/s11356-014-3332-7 (2015).
Hilton, M., Jarvis, T. & Ricketts, D. The degradation rate of thiamethoxam in European field studies. Pest Manag. Sci. 72, 388–397. https://doi.org/10.1002/ps.4024 (2016).
Scott-Dupree, C. D., Conroy, L. & Harris, C. R. Impact of currently used or potentially useful insecticides for canola agroecosystems on Bombus impatiens (Hymenoptera: Apidae), Megachile rotundata (Hymenoptera: Megachildidae), and Osmia lignaria (Hymenoptera: Megachilidae). J. Econ. Entomol. 102, 177–182. https://doi.org/10.1603/029.102.0125 (2009).
Stephen, W. P., Bohart, G. E. & Torchio, P. F. The biology and external morphology of bees with a synopsis of the genera of northwestern America. Corvallis: Oregon State University. Retrieved from https://www.jstor.org/stable/25082339 (1969).
Seidelmann, K. & Ulbrich, K. M. Conditional sex allocation in the Red Mason bee Osmia rufa. Behav. Ecol. Sociobiol. 64, 337–347. https://doi.org/10.1007/s00265-009-0850-2 (2010).
Dively, G. P. & Kamel, A. Insecticide residues in pollen and nectar of a cucurbit crop and their potential exposure to pollinators. J. Agric. Food Chem. 60, 4449–4456. https://doi.org/10.1021/jf205393x (2012).
Stoner, K. A. & Eitzer, B. D. Movement of soil-applied imidacloprid and thiamethoxam into nectar and pollen of squash (Cucurbita pepo). PLoS ONE 7, e39114. https://doi.org/10.1371/journal.pone.0039114 (2012).
Goulson, D. An overview of the environmental risks posed by neonicotinoid insecticides. J. Appl. Ecol. 50, 977–987. https://doi.org/10.1111/1365-2664.12111 (2013).
Wang, T. T. et al. Suppression of chlorantraniliprole sorption on biochar in soil–biochar systems. Bull. Environ. Contam. Toxicol. 95, 401–406. https://doi.org/10.1007/s00128-015-1541-5 (2015).
Winsor, J. A., Davis, L. E. & Stephenson, A. G. The relationship between pollen load and fruit maturation and the effect of pollen load on offspring vigor in Cucurbita pepo. Am. Nat. 129, 643–656. https://doi.org/10.1086/284664 (1987).
Aizen, M. A., Garibaldi, L. A., Cunningham, S. A. & Klein, A. M. How much does agriculture depend on pollinators? Lessons from long-term trends in crop production. Ann. Bot. 103, 1579–1588. https://doi.org/10.1093/aob/mcp076 (2009).
McGrady, C. M., Troyer, R. & Fleischer, S. J. Wild bee visitation rates exceed pollination thresholds in commercial Cucurbita agroecosystems. J. Econ. Entomol. 113, 562–574. https://doi.org/10.1093/jee/toz295 (2020).
Pes, M. et al. Translocation of chlorantraniliprole and cyantraniliprole applied to corn as seed treatment and foliar spraying to control Spodoptera frugiperda (Lepidoptera: Noctuidae). PLoS ONE 15, e0229151–e0229151. https://doi.org/10.1371/journal.pone.0229151 (2020).
Dinter, A., Brugger, K. E., Frost, N.-M. & Woodward, M. D. Chlorantraniliprole (Rynaxypyr): A novel DuPont insecticide with low toxicity and low risk for honey bees (Apis mellifera) and bumble bees (Bombus terrestris) providing excellent tools for uses in integrated pest management. Julius-Kühn-Arch. 423, 84–96 (2009).
Gradish, A. E., Scott-Dupree, C. D., Shipp, L., Harris, C. R. & Ferguson, G. Effect of reduced risk pesticides for use in greenhouse vegetable production on Bombus impatiens (Hymenoptera: Apidae). Pest Manag. Sci. 66, 142–146. https://doi.org/10.1002/ps.1846 (2010).
Tomé, H. V. V. et al. Reduced-risk insecticides in neotropical stingless bee species: impact on survival and activity. Ann. Appl. Biol. 167, 186–196. https://doi.org/10.1111/aab.12217 (2015).
Williams, J. R., Swale, D. R. & Anderson, T. D. Comparative effects of technical-grade and formulated chlorantraniliprole to the survivorship and locomotor activity of the honey bee, Apis mellifera (L.). Pest Manag. Sci. 76, 2582–2588. https://doi.org/10.1002/ps.5832 (2020).
Larson, J. L., Redmond, C. T. & Potter, D. A. Assessing insecticide hazard to bumble bees foraging on flowering weeds in treated lawns. PLoS ONE 8, e66375. https://doi.org/10.1371/journal.pone.0066375 (2013).
Brugger, K. E. et al. Selectivity of chlorantraniliprole to parasitoid wasps. Pest Manag. Sci. 66, 1075–1081. https://doi.org/10.1002/ps.1977 (2010).
Wang, J. et al. Molecular characterization of a ryanodine receptor gene in the rice leaf folder, Cnaphalocrocis medinalis (Guenée). PLoS ONE 7, e36623. https://doi.org/10.1371/journal.pone.0036623 (2012).
Willis, D. S. The pollination system of Cucurbita pepo and Peponapis pruinosa in southern Ontario. MSc Thesis. University of Guelph, Guelph, Ontario, Canada (1991).
Kiernan, K. Insights into using the GLIMMIX procedure to model categorical outcomes with random effects. SAS Institute Inc. Retrieved from https://blogs.sas.com/con60tent/iml/2019/04/03/g-matrix-is-not-positive-definite.html (2018).
We would like to thank Katie Fisher, Dillon Muldoon, Loran Moran, Emma Jane Woods, Leonard Zettler, Matt Gibson, and especially Beatrice Chan for their excellent assistance in the field. This work was supported by Ontario Ministry of Agriculture, Food and Rural Affairs (OMAFRA) Grant UofG2015-2466 (awarded to N.E.R. and D.S.W.C.), the Ontario Ministry of Environment and Climate Change (MOECC) Best in Science grant BIS201617-06 (awarded to N.E.R.), Natural Sciences and Engineering Research Council (NSERC) Discovery Grants 2015-06783 (awarded to N.E.R.), the Fresh Vegetable Growers of Ontario (FVGO: awarded to N.E.R. and D.S.W.C.). D.S.W.C. was supported by the George and Lois Whetham Scholarship in Food Systems, an Ontario Graduate Fellowship, the Keith and June Laver Scholarship in Horticulture, the Fred W. Presant Scholarship, and a Latournelle Travel Scholarship. N.E.R. is supported as the Rebanks Family Chair in Pollinator Conservation by Weston Family Foundation.
The authors declare no competing interests.
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
About this article
Cite this article
Willis Chan, D., Raine, N.E. Population decline in a ground-nesting solitary squash bee (Eucera pruinosa) following exposure to a neonicotinoid insecticide treated crop (Cucurbita pepo). Sci Rep 11, 4241 (2021). https://doi.org/10.1038/s41598-021-83341-7
This article is cited by
Diversity and biological traits of bees visiting flowers of Cucurbita maxima var. zapallito differ between biodiversity-based and conventional management practices
Environmental Monitoring and Assessment (2024)
From metropolis to wilderness: Uncovering pollen collecting behavior in urban and wild sweat bees (Halictus ligatus)
Urban Ecosystems (2023)
Insectes Sociaux (2023)
Environmental Science and Pollution Research (2023)