The neonicotinoids thiacloprid,imidacloprid, and clothianidin affect the immunocompetence of honey bees (Apis mellifera L.)

A strong immune defense is vital for honey bee health and colony survival. This defense can be weakened by environmental factors that may render honey bees more vulnerable to parasites and pathogens. Honey bees are frequently exposed to neonicotinoid pesticides, which are being discussed as one of the stress factors that may lead to colony failure. We investigated the sublethal effects of the neonicotinoids thiacloprid, imidacloprid, and clothianidin on individual immunity, by studying three major aspects of immunocompetence in worker bees: total hemocyte number, encapsulation response, and antimicrobial activity of the hemolymph. In laboratory experiments, we found a strong impact of all three neonicotinoids. Thiacloprid (24 h oral exposure, 200 μg/l or 2000 μg/l) and imidacloprid (1 μg/l or 10 μg/l) reduced hemocyte density, encapsulation response, and antimicrobial activity even at field realistic concentrations. Clothianidin had an effect on these immune parameters only at higher than field realistic concentrations (50–200 μg/l). These results suggest that neonicotinoids affect the individual immunocompetence of honey bees, possibly leading to an impaired disease resistance capacity.     

Sperm viability and gene expression in honey bee queens (Apis mellifera) following exposure to the neonicotinoid insecticide imidacloprid and the organophosphate acaricide coumaphos

Honey bee population declines are of global concern. Numerous factors appear to cause these declines including parasites, pathogens, malnutrition and pesticides. Residues of the organophosphate acaricide coumaphos and the neonicotinoid insecticide imidacloprid, widely used to combat Varroa mites and for crop protection in agriculture, respectively, have been detected in wax, pollen and comb samples. Here, we assess the effects of these compounds at different doses on the viability of sperm stored in the honey bee queens’ spermatheca. Our results demonstrate that sub-lethal doses of imidacloprid (0.02 ppm) decreased sperm viability by 50%, 7 days after treatment. Sperm viability was a downward trend (about 33%) in queens treated with high doses of coumaphos (100 ppm), but there was not significant difference. The expression of genes that are involved in development, immune responses and detoxification in honey bee queens and workers exposed to chemicals was measured by qPCR analysis. The data showed that expression levels of specific genes were triggered 1 day after treatment. The expression levels of P450 subfamily genes, CYP306A1, CYP4G11 and CYP6AS14 were decreased in honey bee queens treated with low doses of coumaphos (5 ppm) and imidacloprid (0.02 ppm). Moreover, these two compounds suppressed the expression of genes related to antioxidation, immunity and development in queens at day 1. Up-regulation of antioxidants by these compounds in worker bees was observed at day 1. Coumaphos also caused a repression of CYP306A1 and CYP4G11 in workers. Antioxidants appear to prevent chemical damage to honey bees. We also found that DWV replication increased in workers treated with imidacloprid. This research clearly demonstrates that chemical exposure can affect sperm viability in queen honey bees.     

Differential sensitivity of honey bees and bumble bees to a dietary insecticide (imidacloprid)

Currently, there is concern about declining bee populations and the sustainability of pollination services. One potential threat to bees is the unintended impact of systemic insecticides, which are ingested by bees in the nectar and pollen from flowers of treated crops. To establish whether imidacloprid, a systemic neonicotinoid and insect neurotoxin, harms individual bees when ingested at environmentally realistic levels, we exposed adult worker bumble bees, Bombus terrestris L. (Hymenoptera: Apidae), and honey bees, Apis mellifera L. (Hymenoptera: Apidae), to dietary imidacloprid in feeder syrup at dosages between 0.08 and 125 μg l^?1. Honey bees showed no response to dietary imidacloprid on any variable that we measured (feeding, locomotion and longevity). In contrast, bumble bees progressively developed over time a dose-dependent reduction in feeding rate with declines of 10–30% in the environmentally relevant range of up to 10 μg l^?1, but neither their locomotory activity nor longevity varied with diet. To explain their differential sensitivity, we speculate that honey bees are better pre-adapted than bumble bees to feed on nectars containing synthetic alkaloids, such as imidacloprid, by virtue of their ancestral adaptation to tropical nectars in which natural alkaloids are prevalent. We emphasise that our study does not suggest that honey bee colonies are invulnerable to dietary imidacloprid under field conditions, but our findings do raise new concern about the impact of agricultural neonicotinoids on wild bumble bee populations.     

Effects of Imidacloprid and Varroa destructor on survival and health of European honey bees,Apis mellifera

There has been growing concern over declines in populations of honey bees and other pollinators which are a vital part to our food security. It is imperative to identify factors responsible for accelerated declines in bee populations and develop solutions for reversing bee losses. While exact causes of colony losses remain elusive, risk factors thought to play key roles are ectoparasitic mites Varroa destructor and neonicotinoid pesticides. The present study aims to investigate effects of a neonicotinoid pesticide Imidacloprid and Varroa mites individually on survivorship, growth, physiology, virus dynamics and immunity of honey bee workers. Our study provides clear evidence that the exposure to sublethal doses of Imidacloprid could exert a significantly negative effect on health and survival of honey bees. We observed a significant reduction in the titer of vitellogenin (Vg), an egg yolk precursor that regulates the honey bees development and behavior and often are linked to energy homeostasis, in bees exposed to Imidacloprid. This result indicates that sublethal exposure to neonicotinoid could lead to increased energy usage in honey bees as detoxification is a energy‐consuming metabolic process and suggests that Vg could be a useful biomarker for measuring levels of energy stress and sublethal effects of pesticides on honey bees. Measurement of the quantitative effects of different levels of Varroa mite infestation on the replication dynamic of Deformed wing virus (DWV), an RNA virus associated with Varroa infestation, and expression level of immune genes yields unique insights into how honey bees respond to stressors under laboratory conditions.     

Variations of chemical element composition of bee and beekeeping products in different taxons of the biosphere

Geographical variations in element composition of bee products are poorly investigated though a lot of attempts are made to utilize the data in ecological monitoring. So the comparison of chemical element composition of bee and beekeeping products in different taxons of the biosphere may become valuable to test the efficiency of such approach. For this purpose content of 25 elements in bee body, bee bread, propolis and honey from Ribnitsa district of Moldavia (unpolluted area, control), Henty province of Mongolia (selenium deficient area) and Voskresensk district of Moscow region (mineral fertilizers production) were determined by means of the ICP-MS. Among 3 investigated regions Mongolia was characterized by the lowest Se levels and the highest accumulation of Al, Ca, Cd, Cu, Co, K, Mn, Mg, Na, Ni, P, Zn and V in bee bodies. The highest levels of Pb, Cr, Fe, Si, Sr and B, Se, Li, Sn were typical for Voskresensk and Moldavia bees accordingly. The highest correlation coefficients were registered between element concentrations in bee body and bee bread (r = +0.97–0.99, P < 0.0001), less significant – in bee body and propolis (r = +0.5–0.7; P < 0.001) and no correlation was demonstrated between element composition of bee body and honey. Propolis was characterized by significantly higher capacity to accumulate Pb, Cr, Sn and Al than bee body. Compared to bee body honey accumulated the lowest level of Mn and the highest of Si in Se-deficient Mongolia but the opposite phenomenon was demonstrated in Moldavia with moderately increased Se content in the environment. The results suppose that the most promising object for ecological monitoring is bee body. Element composition of propolis seems to reflect prolonged accumulation of elements, especially Pb, Al, Sn and Cr, by plant resin rather than dynamic temporal elements loading. Accumulation levels of elements in bee bread may be used on a par with bee body mineral content only in cases with equal honey content in bee bread. Honey utilization in monitoring of geochemical elements loading should be used with caution due to peculiarities of pollen/nectar elements distribution.     

The effect of temperature on candidate gene expression in the brain of honey bee Apis mellifera (Hymenoptera: Apidae) workers exposed to neonicotinoid imidacloprid

Neonicotinoid insecticides are potent agonists of nicotinic acetylcholine receptors and are a major factor in the decline of pollinators worldwide. Several studies show that low doses of this neurotoxin influence honey bee physiology, however, little is known about how insecticides interact with other environmental variables. We studied the effects of two neonicotinoid Imidacloprid doses (IMD, 0, 2.5, and 10 ppb), and three temperatures (20, 28, and 36°C) on gene expression in the brains of worker honey bees (Apis mellifera). Using qRT-PCR we quantified the expression of eight key genes related to the nervous system, stress response, and motor and olfactory capacities. Gene expression tended to increase with the low IMD dose, which was further intensified in individuals maintained in the cold treatment (20°C). At 20°C the octopamine receptor gene (oa1) was underexpressed in bees that were not exposed to IMD, but overexpressed in individuals exposed to 2.5 ppb IMD. Also, heat shock proteins (hsp70 and hsp90) increased their expression at high temperatures (36°C), but not with IMD doses. These results suggest that despite the low insecticide concentrations used in this study (a field-realistic dose), changes in gene expression associated with honey bee physiological responses could be induced. This study contributes to the understanding of how neonicotinoid residual doses may alter honey bee physiology.     

Comparative study on the dynamics and performances of Apis mellifera jemenitica and imported hybrid honeybee colonies in southwestern Saudi Arabia

The aims of this study were to assess the seasonal population dynamics and evaluate the performance of Apis mellifera jemenitica (local bee) and introduced hybrid honeybee colonies in the lowlands and highlands of southwestern Saudi Arabia. Data regarding the performance and population dynamics parameters such as brood and adult bee population, amounts of stored pollen and nectar were gathered from the two races (25 colonies of each) for one year (April 2013 through March 2014), and statistically tested. The results indicated that at low lands, local bee colonies maintained relatively high brood and adult bee populations (P < 0.05) than introduced honeybee colonies and produced more (P < 0.05) honey. The local bee colonies were able to hoard three times more (P < 0.05) pollen and built more (P < 0.05) queen cells than introduced bees in both the low and highland areas. The annual survival rate of local bee colonies was almost double (P < 0.05) than that of introduced honeybee colonies. Moreover, local bees had greater (P < 0.05) adult bee and brood populations than imported, throughout the year. The relatively good performance of local colonies could be due to their long year’s adaptation to cope with resource scarcity and unpredictable environmental conditions of the regions. The possible reasons for the dwindling of the imported hybrid colonies could be due to continuing to exhibit adaptive characteristics of their original that might not fit well with the new environment.     

The fungicide Pristine® inhibits mitochondrial function in vitro but not flight metabolic rates in honey bees

Honey bees and other pollinators are exposed to fungicides that act by inhibiting fungal mitochondria. Here we test whether a common fungicide (Pristine®) inhibits the function of mitochondria of honeybees, and whether consumption of ecologically-realistic concentrations can cause negative effects on the mitochondria of flight muscles, or the capability for flight, as judged by CO₂ emission rates and thorax temperatures during flight. Direct exposure of mitochondria to Pristine® levels above 5 ppm strongly inhibited mitochondrial oxidation rates in vitro. However, bees that consumed pollen containing Pristine® at ecologically-realistic concentrations (≈1 ppm) had normal flight CO₂ emission rates and thorax temperatures. Mitochondria isolated from the flight muscles of the Pristine®-consuming bees had higher state 3 oxygen consumption rates than control bees, suggesting that possibly Pristine®-consumption caused compensatory changes in mitochondria. It is likely that the lack of a strong functional effect of Pristine®-consumption on flight performance and the in vitro function of flight muscle mitochondria results from maintenance of Pristine® levels in the flight muscles at much lower levels than occur in the food, probably due to metabolism and detoxification. As Pristine® has been shown to negatively affect feeding rates and protein digestion of honey bees, it is plausible that Pristine® consumption negatively affects gut wall function (where mitochondria may be exposed to higher concentrations of Pristine®).     

A Locomotor Deficit Induced by Sublethal Doses of Pyrethroid and Neonicotinoid Insecticides in the Honeybee Apis mellifera

The toxicity of pesticides used in agriculture towards non-targeted organisms and especially pollinators has recently drawn the attention from a broad scientific community. Increased honeybee mortality observed worldwide certainly contributes to this interest. The potential role of several neurotoxic insecticides in triggering or potentiating honeybee mortality was considered, in particular phenylpyrazoles and neonicotinoids, given that they are widely used and highly toxic for insects. Along with their ability to kill insects at lethal doses, they can compromise survival at sublethal doses by producing subtle deleterious effects. In this study, we compared the bee’s locomotor ability, which is crucial for many tasks within the hive (e.g. cleaning brood cells, feeding larvae…), before and after an acute sublethal exposure to one insecticide belonging to the two insecticide classes, fipronil and thiamethoxam. Additionally, we examined the locomotor ability after exposure to pyrethroids, an older chemical insecticide class still widely used and known to be highly toxic to bees as well. Our study focused on young bees (day 1 after emergence) since (i) few studies are available on locomotion at this stage and (ii) in recent years, pesticides have been reported to accumulate in different hive matrices, where young bees undergo their early development. At sublethal doses (SLD_48h, i.e. causing no mortality at 48h), three pyrethroids, namely cypermethrin (2.5 ng/bee), tetramethrin (70 ng/bee), tau-fluvalinate (33 ng/bee) and the neonicotinoid thiamethoxam (3.8 ng/bee) caused a locomotor deficit in honeybees. While the SLD_48h of fipronil (a phenylpyrazole, 0.5 ng/bee) had no measurable effect on locomotion, we observed high mortality several days after exposure, an effect that was not observed with the other insecticides. Although locomotor deficits observed in the sublethal range of pyrethroids and thiamethoxam would suggest deleterious effects in the field, the case of fipronil demonstrates that toxicity evaluation requires information on multiple endpoints (e.g. long term survival) to fully address pesticides risks for honeybees. Pyrethroid-induced locomotor deficits are discussed in light of recent advances regarding their mode of action on honeybee ion channels and current structure-function studies.     

Nectar secretion dynamics and honey production potentials of some major honey plants in Saudi Arabia

The contribution of a bee plant species to honey production depends on the plant’s nectar secretion quality and quantity, which is mainly governed by biotic and abiotic factors. The aim of the current study, was to investigate the nectar secretion dynamics and honey production potential of 14 major bee plant species of the target area. We examined the quantity and dynamics of nectar sugar per flower five times a day using a nectar sugar washing technique and direct measuring of nectar with calibrated capillary tubes. The average nectar sugar amount of the species varied from 0.41 mg/flower to 7.7 mg/flower (P < 0.0001). The honey sugar per flower was used to extrapolate the honey production potential per plant and per hectare of land. Accordingly the honey production potential of the species observed to vary from 14 kg/hectare in Otostegia fruticosa to 829 kg/hectare in Ziziphus spina-christi. The nectar secretion dynamics of the species generally showed an increasing trend early in the morning, peaking toward midday, followed by a decline but different species observed to have different peak nectar secretion times. Generally, the tree species secreted more nectar sugar/flower than the herbs. The nectar secretion amount of the species was positively correlated with the ambient temperature, indicating the adaptation of the species to hot climatic conditions. However, different species were observed to have a different optimum temperature for peak nectar secretion. Despite the limited rainfall and high temperature of the area, many plants were found to have good potential for honey production. The monetary value of honey per hectare of the studied honeybee plant species can be of equal or greater than the per-hectare monetary value of some cultivated crops that require numerous inputs. In addition, the information generated is believed to be useful in apiary site selection and to estimate the honey bee colony carrying capacity of an area.     

Imidacloprid Alters Foraging and Decreases Bee Avoidance of Predators

Concern is growing over the effects of neonicotinoid pesticides, which can impair honey bee cognition. We provide the first demonstration that sublethal concentrations of imidacloprid can harm honey bee decision-making about danger by significantly increasing the probability of a bee visiting a dangerous food source. Apis cerana is a native bee that is an important pollinator of agricultural crops and native plants in Asia. When foraging on nectar containing 40 µg/L (34 ppb) imidacloprid, honey bees (Apis cerana) showed no aversion to a feeder with a hornet predator, and 1.8 fold more bees chose the dangerous feeder as compared to control bees. Control bees exhibited significant predator avoidance. We also give the first evidence that foraging by A. cerana workers can be inhibited by sublethal concentrations of the pesticide, imidacloprid, which is widely used in Asia. Compared to bees collecting uncontaminated nectar, 23% fewer foragers returned to collect the nectar with 40 µg/L imidacloprid. Bees that did return respectively collected 46% and 63% less nectar containing 20 µg/L and 40 µg/L imidacloprid. These results suggest that the effects of neonicotinoids on honey bee decision-making and other advanced cognitive functions should be explored. Moreover, research should extend beyond the classic model, the European honey bee (A. mellifera), to other important bee species.     

Experimental infection of red dwarf honeybee,Apis florea,with Nosema ceranae

This research is the first record of the infection of Apis florea by Nosema ceranae, a newly identified pathogen of honeybee in Thailand which was initially isolated from A. florea workers. Each Nosema free-bee was fed 2 μl of 50% (w/v) sucrose solution containing 0, 10,000 20,000 or 40,000 Nosema spores/bee. The survival rates of treated bees were significantly lower compared to control bees. Infectivity was not statistically different among the three spore concentrations, whereas no infection was found in control bees. Protein content of control bee hypopharyngeal glands 14 days post inoculation (p.i) was significantly higher (21.47 ± 0.17 mg/bee) compared to all treatments. The infection ratio of bees treated with 40,000 spores/bee increased with time after inoculation. These results suggest that N. ceranae has a significant negative effect on honeybee hypopharyngeal gland protein production and contributes to their shortened life span.     

Using sensillum potential analysis to quantify pheromone sensing of the antennal sensilla of Apis florea Fabricius (1787), foragers and guards

Odor perception via the antennal sensilla in most honeybee species is poorly studied. We measured the antennal sensillum potential in response to Apis florea mandibular gland pheromone and showed that it is robust and reliable in forager and guard bees. Mandibular gland pheromone may be involved in signaling alarm or foraging resource depletion. Changes of antennal sensilla placodea potential of A. florea foragers and guards were measured after exposure to three concentrations of the synthetic pheromones, 2-heptanone and (Z)-11-eicosen-1-ol, using a potentiostat connected to an e-corder (ED401) with microelectrodes. The resting sensillum potential of A. florea foragers and guards were ?55.37 ± 3.44 and ?52.85 ± 5.34 mV, respectively. The sensillum potential of bees exposed to 1.0%, 5.0% and 10.0% (Z)-11-eicosen-1-ol were ?23.35 ± 0.98, ?16.78 ± 1.94 and ?24.24 ± 8.20 mV, respectively, in foragers, and ?21.95 ± 3.21, ?21.42 ± 4.73 and ?13.54 ± 4.16 mV, respectively, for guards. Exposure of bees to 1.0%, 5.0% and 10.0% 2-heptanone induced sensillum potentials of ?10.64 ± 2.44, ?44.88 ± 2.41 and ?48.84 ± 4.40 mV, respectively, in foragers and 15.85 ± 9.38, ?25.48 ± 1.43 and ?15.52 ± 6.61 mV, respectively, in guards. The highest sensillum potential was recorded in foragers exposed to 1.0% 2-heptanone. In general, except for the response to 1.0% 2-heptanone, the sensillum potentials of all bees to (Z)-11-eicosen-1-ol were higher than that of 2-heptanone. These results show that A. florea antennal sensilla in foragers and guard bees exhibit a stronger response to (Z)-11-eicosen-1-ol as compared to 2-heptanone. Our results also provide useful comparative data to explore olfactory perception in non-model honey bee species.     

Impact of Chronic Neonicotinoid Exposure on Honeybee Colony Performance and Queen Supersedure

Background

Honeybees provide economically and ecologically vital pollination services to crops and wild plants. During the last decade elevated colony losses have been documented in Europe and North America. Despite growing consensus on the involvement of multiple causal factors, the underlying interactions impacting on honeybee health and colony failure are not fully resolved. Parasites and pathogens are among the main candidates, but sublethal exposure to widespread agricultural pesticides may also affect bees.

Methodology/Principal Findings

To investigate effects of sublethal dietary neonicotinoid exposure on honeybee colony performance, a fully crossed experimental design was implemented using 24 colonies, including sister-queens from two different strains, and experimental in-hive pollen feeding with or without environmentally relevant concentrations of thiamethoxam and clothianidin. Honeybee colonies chronically exposed to both neonicotinoids over two brood cycles exhibited decreased performance in the short-term resulting in declining numbers of adult bees (−28%) and brood (−13%), as well as a reduction in honey production (−29%) and pollen collections (−19%), but colonies recovered in the medium-term and overwintered successfully. However, significantly decelerated growth of neonicotinoid-exposed colonies during the following spring was associated with queen failure, revealing previously undocumented long-term impacts of neonicotinoids: queen supersedure was observed for 60% of the neonicotinoid-exposed colonies within a one year period, but not for control colonies. Linked to this, neonicotinoid exposure was significantly associated with a reduced propensity to swarm during the next spring. Both short-term and long-term effects of neonicotinoids on colony performance were significantly influenced by the honeybees’ genetic background.

Conclusions/Significance

Sublethal neonicotinoid exposure did not provoke increased winter losses. Yet, significant detrimental short and long-term impacts on colony performance and queen fate suggest that neonicotinoids may contribute to colony weakening in a complex manner. Further, we highlight the importance of the genetic basis of neonicotinoid susceptibility in honeybees which can vary substantially.     

Effects of sequential exposures of sub-lethal doses of amitraz and thiacloprid on learning and memory of honey bee foragers,Apis mellifera

Pollinators, honey bees in particular, are continuously exposed to various mixtures of pesticides, which contribute to their population decline. Both amitraz and thiacloprid have been proven less toxic to honey bees and are frequently applied in- and out-hive, respectively. We examined the sub-lethal effects of amitraz, thiacloprid and their sequential exposure on learning, memory and sugar responsiveness in Apis mellifera using the Proboscis extension response (PER). Sub-lethal doses of amitraz (0.1, 0.2 and 0.4 µg/bee) and thiacloprid (0.05, 0.1 and 0.2 µg/bee) were tested. Sub-lethal effects were observed only at the highest doses of each pesticide treatment; amitraz (0.4 µg/bee) and thiacloprid (0.2 µg/bee) but not in lower doses. In sequential treatment of amitraz and thiacloprid, reduced acquisition and memory retention were significant across all tested doses. The same profile was also obtained on sugar responsiveness of foragers. Our results suggest that the sequential exposure would pose higher risk to honey bee compared to single pesticide exposure by reducing the bees’ appetitive olfactory learning, memory and sugar acuity more than individual pesticide exposures.     

Geometric morphometric analysis of giant honeybee (Apis dorsata Fabricius, 1793) populations in Thailand

Geometric morphometry was used to characterize 73 Apis dorsata colonies collected from 31 different localities in five major geographic regions of mainland Thailand. We measured 19 easily identified landmarks from the digitized images of the right forewing of 10 worker bees from each colony (730 bees in total); thus, avoiding the confounding variation from haploid or diploid males. After plotting the factor scores, A. dorsata from (mainland) Thailand were found to belong to a single group, which was further supported by a hierarchical cluster analysis-generated dendrogram. Multivariate analysis of variance (MANOVA, α = 0.05) demonstrated no significant differences among the five geographic groups of A. dorsata in Thailand, producing a low degree of accuracy (31.2%) in the identification of the geographic region from which any individual bee originated. Additionally, when the bee samples were classified into two groups, those north and south of the Isthmus of Kra were not significantly different (MANOVA, α = 0.05), and a low rate of correct classification in a cross-validation test (65% correct) was found. Therefore, this geometric morphometric based analysis of worker bee wing venation pattern suggests that A. dorsata populations in mainland Thailand are panmictic.     

Multiple routes of pesticide exposure for honey bees living near agricultural fields

Populations of honey bees and other pollinators have declined worldwide in recent years. A variety of stressors have been implicated as potential causes, including agricultural pesticides. Neonicotinoid insecticides, which are widely used and highly toxic to honey bees, have been found in previous analyses of honey bee pollen and comb material. However, the routes of exposure have remained largely undefined. We used LC/MS-MS to analyze samples of honey bees, pollen stored in the hive and several potential exposure routes associated with plantings of neonicotinoid treated maize. Our results demonstrate that bees are exposed to these compounds and several other agricultural pesticides in several ways throughout the foraging period. During spring, extremely high levels of clothianidin and thiamethoxam were found in planter exhaust material produced during the planting of treated maize seed. We also found neonicotinoids in the soil of each field we sampled, including unplanted fields. Plants visited by foraging bees (dandelions) growing near these fields were found to contain neonicotinoids as well. This indicates deposition of neonicotinoids on the flowers, uptake by the root system, or both. Dead bees collected near hive entrances during the spring sampling period were found to contain clothianidin as well, although whether exposure was oral (consuming pollen) or by contact (soil/planter dust) is unclear. We also detected the insecticide clothianidin in pollen collected by bees and stored in the hive. When maize plants in our field reached anthesis, maize pollen from treated seed was found to contain clothianidin and other pesticides; and honey bees in our study readily collected maize pollen. These findings clarify some of the mechanisms by which honey bees may be exposed to agricultural pesticides throughout the growing season. These results have implications for a wide range of large-scale annual cropping systems that utilize neonicotinoid seed treatments.