Abstract
The impact of neonicotinoid insecticides on insect pollinators is highly controversial. Sublethal concentrations alter the behaviour of social bees and reduce survival of entire colonies1-3. However, critics argue that the reported negative effects only arise from neonicotinoid concentrations that are greater than those found in the nectar and pollen of pesticide-treated plants4. Furthermore, it has been suggested that bees could choose to forage on other available flowers and hence avoid or dilute exposure4,5. Here, using a two-choice feeding assay, we show that the honeybee, Apis mellifera, and the buff-tailed bumblebee, Bombus terrestris, do not avoid nectar-relevant concentrations of three of the most commonly-used neonicotinoids, imidacloprid (IMD), thiamethoxam (TMX), and clothianidin (CLO) in food. Moreover, bees of both species prefer to eat more of sucrose solutions laced with IMD or TMX than sucrose alone. Stimulation with IMD, TMX, and CLO neither elicited spiking responses from gustatory neurons in the bees’ mouthparts nor inhibited the responses of sucrose-sensitive neurons. Our data indicate that bees cannot taste neonicotinoids and are not repelled by them. Instead, bees preferred solutions containing IMD or TMX even though the consumption of these pesticides caused them to eat less food overall. This work shows that bees cannot control their exposure to neonicotinoids in food and implies that treating flowering crops with IMD and TMX presents a significant hazard to foraging bees.
Determining the impacts of pesticides on pollinators is important to resolve for the future of world food security. Pollinating insects like bees increase the yields of human crops, but in doing so, are inadvertently exposed to pesticides in floral nectar and pollen6,7. Several studies have concluded that bees exposed to sublethal doses of neonicotinoid pesticides in food have difficulty learning floral traits, feeding, navigating, and foraging2,3,8-11 and have impaired motor function12. These changes in behaviour often lead to colony failure2,3. This body of work has galvanized public concern over bee welfare, and in 2013, led to a two-year ban on the use of the three most common neonicotinoids (IMD, TMX, CLO) on flowering crops by the European Union. The agricultural importance of these pesticides has motivated agrochemical producers and government scientists to challenge this ban. Critics of lab-based experiments contend that such studies use food laced with neonicotinoid concentrations that exceed the levels found in nectar and pollen13, or give bees no choice of food solutions4,5. They propose that free-living bees and other insect pollinators could choose to avoid the nectar and pollen of pesticide-treated crops4 if pollinators are repelled by neonicotinoids14,15 and if alternative sources were provided such as field margins in agricultural settings.
These arguments require that pollinators are able to detect neonicotinoids in food in order to avoid exposure. We tested whether bees avoid sucrose solutions (i.e. nectar) containing neonicotinoids using a two-choice test designed to identify the bumblebee’s gustatory detection thresholds for nectar toxins16. Individual foraging-age worker bumblebees or cohorts of 25 forager honeybees were housed in plastic boxes for 24 h and given access to two types of food tubes: one containing sucrose solution and one containing sucrose solution laced with a specific concentration of the IMD, TMX, or CLO. The concentrations used included values in the range reported from nectar and pollen (0.5-150 nM, Extended Data Table 1). Neither bumblebees nor honeybees avoided concentrations found within the naturally-occurring range (Figure 1a, b), even though high concentrations of TMX and CLO reduced their survival (Extended Data Fig 1). We also tested whether these pesticides inhibited the honeybee’s feeding reflex (proboscis extension) or caused honeybees to retract the proboscis once extended17. None of the sucrose solutions containing IMD, TMX, or CLO affected proboscis extension or retraction (Extended Data Fig 2).
Unexpectedly, we observed that both bumblebees and honeybees showed a preference for solutions containing IMD or TMX over sucrose alone (Fig 1, Extended Data Tables 2, 3). Concentrations of IMD and TMX proximate to those found in nectar (1-10nM, Extended Data Table 1) were most attractive to bumblebees (Fig 1a) whereas honeybees were preferred to consume IMD and TMX across a broader range of concentrations (Fig 1b). The ‘attractive’ effect of IMD also depended on bee age: newly-emerged adult worker bumblebees and honeybees largely avoided 1-10nM IMD (Extended Data Fig 3a). In addition, the presence of neonicotinoids influenced the total amount of food consumed from both tubes during 24 h (Fig1 c,d). Bumblebees fed with IMD or CLO consumed less total food on average than those fed TMX or the sucrose control (Fig 1c, Extended Data Table 2); this effect has also been observed by others11,15. In contrast, the total food consumption of forager honeybees was reduced only when bees fed from solutions containing 100 nM or 1μM TMX or CLO (Fig 2d, Extended Data Table 2). Thus, even in treatments where bees ate considerably less food in 24 h, they still preferred to consume solutions containing IMD over sucrose alone. Bumblebees also consumed 1.5-10 fold more of the neonicotinoid-laced food than honeybees and were, therefore, exposed to higher pesticide doses (Extended Data Table 4).
Insects detect nutrients and toxins in food via gustatory neurons in hair-like sensilla on the proboscis (mouthparts)18. Toxic, non-nutritious compounds elicit spikes in ‘bitter’-sensing neurons19,20 but can also be detected via suppression of the responses of sugar-sensing neurons21,22. Previous research has established that gustatory neurons located in sensilla on the honeybee’s mouthparts are more sensitive to toxins in food17 than its antennae21 or tarsi23. If bees have mechanisms for detecting neonicotinoids, sensilla on the mouthparts should respond to these substances in the same way they respond to other toxins17. To test this, we recorded from gustatory neurons in sensilla on the galea (part of the proboscis) of bumblebees and honeybees using the tip recording technique (Fig 2 a, b). Stimulation with IMD, TMX, or CLO in water did not elicit spikes from any of the neurons in the galeal sensilla of either bumblebees (Fig 2 c) or honeybees (Fig 2 d) whereas stimulation with nicotine hydrogen tartrate (NHT), KCl, and sucrose did (Fig 2 c-f). This effect was the same for all three neonicotinoids in both bee species (Extended Data Table 5). To test whether neonicotinoids are detected via suppression of the neurons’ responses to sugars, we applied sucrose solution laced with IMD, TMX, and CLO in an ascending series of concentrations from 1 nM-1 μM (Fig 2 g,h). None of the concentrations we tested altered the spiking activity of sucrose-sensitive gustatory neurons in the bumblebees’ or the honeybees’ sensilla (Fig 2 g, h, Extended Data Table 5). (Note: we confirmed that the mean spike rates reported in Fig 2 h were not a result of simultaneous excitation of bitter neurons and inhibition of sucrose-sensing neurons by manually spike sorting the records for IMD, Extended Data Fig 4). Furthermore, we found that both forager and newly-emerged honeybees lack taste neurons that respond to these compounds (Extended Data Fig 3b). Therefore, the behavioural data and electrophysiological recordings from mouthparts’ gustatory neurons lead us to conclude that bumblebees and honeybees cannot taste neonicotinoids in nectar.
The preference of the bees in our assays for solutions containing IMD or TMX probably arises from the pharmacological action of these compounds on nicotinic acetylcholine receptors (nAChRs) in the bees’ brains. It does not reflect a generalized enhancement of feeding because bees consuming these pesticides ate less food overall. Astonishingly, the preference occurred even when bees consuming these solutions were more likely to die. Our data may indicate, therefore, that IMD and TMX affect the neural mechanisms involved in learning about the location of rewarding food. Prior studies have demonstrated that free-flying honeybees prefer to collect sucrose solutions containing low concentrations of nicotine24. Nicotine also activates nAChRs25 expressed throughout the bee brain including the mushroom bodies required for learning, and memory26,27. It is notable that several studies have shown that chronic neonicotinoid administration impairs olfactory learning and memory in honeybees1,8,28,29. Our finding that bees acquire a preference for food laced with IMD or TMX could be explained by shorter neonicotinoid exposure in our experiments or by differential sensitivity of the nAChRs in the relevant brain regions necessary for each task26. It is also plausible that differential sensitivity of nAChRs accounts for our observed avoidance of newly-emerged bees towards solutions containing IMD.
Consumption of neonicotinoid-laced nectar by foraging bees could lead to higher attrition in this behavioural caste as well as reducing their foraging efficiency for pollen2,30. This would have a greater impact on wild bee colonies with relatively few foragers than on domesticated honeybees. If foragers prefer to collect nectar containing IMD and TMX, they will also bring more neonicotinoid-laced food back to the colony. For these reasons, whole colonies could be exposed to higher levels of these pesticides in the field than previously predicted. Mitigation strategies that rely on planting alternative sources of nectar and pollen, therefore, might not be enough to decrease the risk of poisoning pollinators with pesticides. Instead, long-term changes to policy that include reducing their use may be the only certain means of halting pollinator population decline.
Methods
Behavioural two-choice assays
Experiments were performed at Trinity College, Dublin with Bombus terrestris dalmatinus (Unichem Ltd, Co. Dublin, Irish distributor for Koppert). Colonies were maintained at 25-30 °C in 24 h darkness and fed commercial pollen and Biogluc (Agralan Ltd, Swindon) bee food ad libitum. Experiments were also performed at Newcastle University, Newcastle upon Tyne with Bombus terrestris audax (Biobest, Belgium) and Bombus terrestris terrestris (Koppert Biological Systems, NATURPOL, Netherlands). Bees from 3-5 different colonies were used for each neonicotinoid. Individual worker bumblebees were collected as they tried to exit the colony. For the experiments with newly-emerged bumblebees, colonies were monitored for newly emerged bees daily; newly-emerged adults were identified by their pale colour. These bees were extracted using forceps from within the colony. As previously described in Tiedeken et al. (2014)16, individual bumblebees were cold anesthetized, weighed and sex-determined, and transferred to individual 650 ml plastic containers (160×110×45mm). Containers were fitted with three 3 ml feeding tubes, inserted horizontally. Feeding tubes had four 2 mm holes so bees could alight on the tubes and feed from the openings. The feeding tubes contained one of three solutions: (1) deionized water; (1) 0.5M sucrose; or (3) 0.5M sucrose with a specific concentration of a neonicotinoid compound. Whether or not the bee was alive was noted 24 h after start of experiment. Bees that did not drink from either tube were excluded from the final analysis; the total number of these subjects was never greater than 3 per treatment (note: these subjects were always dead and likely to have died from stress or other causes).
Experiments with honeybees (Apis mellifera var Buckfast) were performed at Newcastle University during the summer months using 2 free-flying outdoor colonies originally obtained from the UK’s National Bee Unit (Sand Hutton, Yorkshire). Foraging adult worker honeybees were collected at the colony entrance as they returned from foraging; newly-emerged adult workers were collected from brood comb as they emerged in a purpose built box kept in an incubator at 34°C. Bees were cold anesthetized prior to placing in rearing boxes. Cohorts of 25 bees were placed in rearing boxes as previously described in Paoli et al. (2014)31. Four food tubes (as described above) were provided: (1) one with deionized water; (2) two with 1M sucrose; (3) two with 1M sucrose containing a specific concentration of a neonicotinoid. The number of bees alive in each cohort was counted at the time of measurement of the food consumption (24 h later).
All of the two-choice experiments were performed experimenter-blind (except IMD with bumblebees). Three neonicotinoid pesticides, imidacloprid (IMD), thiamethoxam (TMX) and clothianidin (CLO), were used in the experiments (Pestanal®, Sigma-Aldrich). The neonicotinoid concentrations used were 1nM, 10nM, 100nM, 1μM (see Extended Data Table 2 for conversions to ppb and ng/bee). Bees were kept in continuous darkness for 24 h at constant temperature and 60% RH (bumblebees: 28 °C; honeybees: 34 °C). Control boxes identical to the experimental boxes (without bees) for each neonicotinoid treatment were placed in the incubator simultaneously with the experiments to measure the rate of evaporation from the food solutions. Feeding tubes were weighed, placed in the experimental boxes with the bees for 24 h, and then removed and weighed a second time. The position of the treatment tubes was randomized across subjects. The amount of solution consumed was determined as the difference in the weight of each tube after 24 h; the average value for the evaporation control for each treatment was subtracted from this final value for each tube. For bumblebees, sample sizes were: IMD: 1nM = 57, 10nM = 66, 100nM = 65, 1μM = 66; TMX: 1nM = 38, 10nM = 39, 100nM = 36, 1μM = 40; CLO: 1nM = 57, 10nM = 59, 100nM = 48, 1μM = 62. For honeybees, N = 40 cohorts of 25 bees/treatment. Sample size was chosen as N ≥ 40 based on previous work16; sample size varied because some individuals died from unknown causes at the start of the experiments.
Honeybee antennal and mouthparts assays
Honeybees were collected at the entrance of an outdoor colony as they returned from foraging, cold anesthetized, and harnessed as described in Bitterman et al. (1983)32. Each was fed 1 M sucrose to satiety and left overnight in a humidified plastic box and assayed ~ 18 h later. Briefly, two assays were employed: one in which individual honeybees were lightly tapped on the antenna with a stimulating solution (e.g. sucrose) to elicit the feeding reflex (i.e. proboscis extension reflex, or PER) and a second assay in which a droplet of stimulating solution was placed at the end of the extended proboscis to test whether bees would consume it (further details described in Wright et al. 201017). Stimulating solutions were 1 M sucrose containing one of the following concentrations (1 nM, 10 nM, 100 nM, 1 μM, 10 μM) of one of three neonicotinoids (IMD, TMX, CLO).
Electrophysiology
Individual bumblebees (B. terrestris audax and B. terrestris terrestris) and honeybees were cold anesthetized on ice for 3-5 min, and then restrained in a metallic restraining harness as described in Bitterman et al. (1983)32. To avoid any movements of the mouthparts during recordings, muscles that trigger proboscis extension were cut by making an incision at the level of the proboscis fossa. Each galea was fixed with a curved metallic wire pinned into dental wax.
Electrophysiological recordings were made from taste neurons located in the first 11 sensilla chaetica33 located at the tip of the galea on the honeybee’s proboscis as in Wright et al. (2010)17 and in the first 6 sensilla in bumblebees. Bees were electrically grounded via a chlorinated silver wire inserted into the head. Sensilla were visualised under a microscope (M205C, Leica, Germany) at a magnification of 256×. To record from gustatory neurons, we used a method first described by Hodgson et al. (1955)34. Sensilla were stimulated with a recording borosilicate electrode (50 mm long, 20 μm diameter) containing the test compounds diluted in demineralized water. The recording electrode was connected via a chlorinated sliver wire to a high impedance “non-blocking” pre-amplifier (TastePROBE, Syntech, Germany)35 mounted on a motorized micromanipulator (MPC-200, Sutter Instrument, USA). The signal was further amplified and filtered with an AC amplifier (model 1800, gain: 100×, band-pass filter: 10-1000 Hz, A-M Systems, USA). Each stimulus trial was digitized (sampling rate 10 kHz, 16 bits; DT9803 Data Translation), stored on a computer with dbWave software (version 4.2014.3.22) and analysed with Matlab R2012b (version 8.0.0.783) utilising PeakFinder with fixed thresholds as the peak detection algorithm (PeakFinder.m., Mathworks file ID: 25500). Recordings were made for 2 s, but only data for the first second were included in the analysis. The first 100 ms were removed to avoid the contact artefact. For bumblebees, 2-6 sensilla were sampled per bee; for honeybees, 6-10 sensilla were sampled per bee.
Recording started when the open end of the electrode was placed over the tip of the sensillum. Individuals were repeatedly sampled in one of two protocols: (1) 50mM sucrose, 100mM KCl, water, 1μM neonicotinoid, 1mM neonicotinoid, 1mM NHT, 100mM KCl, 50mM sucrose; or (2) 50mM sucrose, 50mM sucrose + neonicotinoid in one of the following concentrations (1nM, 10nM, 1μM), 50 mM sucrose. The neonicotinoids IMD, TMX, or CLO were used in each protocol. Neonicotinoid (Pestanal®, Sigma-Aldrich) solutions were prepared as serial dilutions starting with 1mM concentration. Sucrose and nicotine tartrate were purchased from Sigma-Aldrich and KCl from Fisher Scientific at purity ≥ 98%. Demineralized water was used to prepare all solutions. Intervals between stimuli were 2-5 min.
Recordings with IMD diluted in sucrose (Extended Data Figure 4) were further analysed using dbWave (http://perso.numericable.fr/frederic.marion-poll/deterrents/tk/dbwave/index.htm). Predicted spiking neurons or ‘units’ were sorted from the digitally filtered signals according to their amplitude with the help of interactive software procedures. Electrophysiological recordings were then visually inspected to search for spike doublets, i.e. two spikes separated by an interspike interval shorter than the silent period36,37. Spike trains were analysed over 1 s following the first 100 ms removed to avoid the contact artefact.
Electron microscopy
Scanning electron microscopy was performed using a Cambridge Stereoscan 240 on samples that had been fixed with gluteraldehyde, washed in phosphate buffer then dehydrated through an ethanol gradient followed by a critical point dried. Specimens were then mounted on an aluminium stub with Acheson’s silver dag before gold coating with a Polaron SEM coating unit.
Statistics
All analyses were performed using IBM SPSS v 19. The mean total number of spikes in the electrophysiological recordings was analysed using repeated-measures analysis of variance (ANOVA) for each species with neonicotinoid as a main effect, sensillum number and bee as covariates, and stimulus as a repeated measure; a Levene’s test was employed to test for equality of variance. Post hoc comparisons were pairwise t-tests with a Bonferroni adjustment for experiment-wise error rate. A two-way generalized linear model (GLM) was used to compare the behaviour of bees fed each of the neonicotinoid treatments for each bee species with least squares post hoc comparisons (Note: the sucrose-sucrose choice data were not included because of the requirements of GLM for factorial design). The difference in the amount eaten between the 2 food tubes in the behavioural choice assays was also analysed using a one-sample t-test against zero for each treatment; critical values were Bonferroni-adjusted. The proportion of bees alive after 24 h was analysed using logistic regression (lreg). Each individual bee was entered in the analysis for the experiments with bumblebees and with honeybees. For the analysis with honeybees, ‘cohort’ was entered as a covariate.
Extended Data
Extended Data Table 1: Concentrations of neonicotinoids reported in floral nectar.
Source | Imidacloprid | Thiamethoxam | Clothianidin | ||||||
---|---|---|---|---|---|---|---|---|---|
ng/g | PPB | nM | ng/g | PPB | nM | ng/g | PPB | nM | |
Schmuck et al. 20017 | 1.9 | 1.9 | 7.43 | - | - | - | - | - | - |
Pohorecka et al. 201238 | 0.6 | 0.6 | 2.34 | 4.2 | 4.2 | 14 | 2.3 | 2.3 | 9.2 |
Dively and Kamel 20126 | 0.4-11 | 0.4-11 | 1.5-43 | 8.2-9.5 | 8.2-9.5 | 28-37 | - | - | - |
Stoner and Eitzer 201238 | 10 | 10 | 39 | 11 | 11 | 37 | - | - | - |
Byrne et al. 201339 | 2.9-39 | 2.9-39 | 11-154 | - | - | - | - | - | - |
Larson et al. 201340 | - | - | - | - | - | - | 171 | 171 | 684 |
Pilling et al. 201341 | - | - | - | 0.65-2.4 | 0.65-2.4 | 2.2-8.2 | - | - | - |
Defra 201342 | 0.13 | - | 0.5 | 1-3.9 | 1-3.9 | 3.4-13 | 0.18-4 | 0.18-4 | 0.7-16 |
Extended Data Table 2: Generalized linear models for the neonlcotlnold choice experiment and total food consumption in Figure 1.
B. terrestris | Choice test | Total food consumption | ||||
---|---|---|---|---|---|---|
Between-subjects contrasts | df | χ 2 | P-value | df | χ 2 | P-value |
Concentration | 3 | 27.9 | <0.001 | 3 | 263 | <0.001 |
Neonicotinoid | 2 | 12.1 | 0.002 | 2 | 150 | <0.001 |
Neonic × Conc | 6 | 7.97 | 0.240 | 6 | 47.7 | <0.001 |
A. mellifera | Choice test | Total food consumption | ||||
---|---|---|---|---|---|---|
Between-subjects contrasts | df | χ 2 | P-value | df | χ 2 | P-value |
Concentration | 3 | 4.93 | 0.176 | 3 | 37.1 | <0.001 |
Neonicotinoid | 2 | 11.1 | 0.004 | 2 | 10.5 | 0.005 |
Neonic × Conc | 6 | 5.89 | 0.435 | 6 | 11.4 | 0.076 |
Values in bold indicate interpreted model parameters. Note: sucrose-sucrose (control) data were not included.
Extended Data Table 3: One-sample t-tests against ‘0’ for each treatment of the 24 h behavioural assay in Figure 1.
B. terrestris | |||||||||
---|---|---|---|---|---|---|---|---|---|
IMD | TMX | CLO | |||||||
N | t(df) | P-value | N | t(df) | P-value | N | t(df) | P-value | |
Sucrose | 55 | −0.24(54) | 0.402 | ||||||
1nM | 57 | 5.13(56) | <0.001 * | 38 | 3.11(38) | 0.002 * | 57 | 0.22(56) | 0.246 |
10nM | 66 | 2.39(65) | 0.010 | 39 | 3.11(37) | 0.002 * | 59 | 0.26(58) | 0.183 |
100nM | 65 | 2.33(64) | 0.012 | 36 | 1.31(35) | 0.099 | 48 | 0.09(47) | 0.465 |
1μM | 66 | −2.6(65) | 0.005 | 40 | −1.15(39) | 0.128 | 62 | −2.36(61) | 0.021 |
A. mellifera | |||||||||
---|---|---|---|---|---|---|---|---|---|
IMD | TMX | CLO | |||||||
N | t(df) | P-value | N | t(df) | P-value | N | t(df) | P-value | |
Sucrose | 40 | −0.85(39) | 0.199 | ||||||
1nM | 40 | 1.93(39) | 0.031 | 40 | −0.32(39) | 0.376 | 40 | −0.288 | 0.387 |
10nM | 40 | 1.75(39) | 0.044 | 40 | 3.80(39) | <0.001 * | 40 | 0.882 | 0.191 |
100nM | 40 | 2.97(39) | 0.002 * | 40 | 3.23(39) | 0.001 * | 40 | −0.221 | 0.414 |
1μM | 40 | 2.00(39) | 0.026 | 40 | 3.25(39) | 0.001 * | 40 | 0.423 | 0.337 |
P-values are for 1-tailed tests. P-values in bold are below P = 0.05.
Application of a Bonferroni adjustment criterion alters the P-value threshold from P = 0.05 to P = 0.002.
Extended Data Table 4: Comparison of doses consumed by each bee species for each treatment in Figure 1.
B. terrestris | ||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
1nM | 10 nM | 100 nM | 1μM | |||||||||
ml/bee | PPB | ng/bee/24 h | ml/bee | PPB | ng/bee/24 h | ml/bee | PPB | ng/bee/24 h | ml/bee | PPB | ng/bee/24 h | |
IMD | 0.257 | 0.256 | 0.064(0.043) | 0.167 | 2.56 | 0.418(0.337) | 0.159 | 25.6 | 3.98(3.22) | 0.055 | 256 | 13.9(18.4) |
TMX | 0.360 | 0.292 | 0.105(0.077) | 0.357 | 2.92 | 1.05(0.862) | 0.354 | 29.2 | 10.3(8.74) | 0.115 | 292 | 33.6(33.9) |
CLO | 0.279 | 0.250 | 0.070(0.065) | 0.259 | 2.50 | 0.647(0.600) | 0.211 | 25.0 | 5.28(4.93) | 0.041 | 250 | 10.3(13.6) |
A. mellifera | ||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
1nM | 10 nM | 100 nM | 1μM | |||||||||
ml/bee | PPB | ng/bee/24 h | ml/bee | PPB | ng/bee/24 h | ml/bee | PPB | ng/bee/24 h | ml/bee | PPB | ng/bee/24 h | |
IMD | 0.046 | 0.256 | 0.012(0.010) | 0.046 | 2.56 | 0.118(0.103) | 0.045 | 25.6 | 1.16(0.974) | 0.045 | 256 | 11.7(9.95) |
TMX | 0.040 | 0.292 | 0.012(0.011) | 0.048 | 2.92 | 0.141(0.117) | 0.036 | 29.2 | 1.07(1.02) | 0.035 | 292 | 10.3(8.63) |
CLO | 0.043 | 0.250 | 0.011(0.010) | 0.044 | 2.50 | 0.112(0.101) | 0.043 | 25.0 | 1.08(0.868) | 0.034 | 250 | 8.51(7.86) |
Note: ng/bee values were calculated based on the mean values consumed from the neonicotinoid-containing food tubes for each treatment (ml/bee). This calculation is the product of the ng/μl of neonicotinoid in the food solution and the amount of solution eaten (μl) per bee in 24h. The values in parentheses in the ng/bee/24h column are the expected values if bees had eaten from both tubes equally. This value was calculated by dividing the total amount eaten for each treatment in Figure 1 c and d by 2 and using this quantity to estimate the dose.
Extended Data Table 5: Repeated-measures ANOVA for Figure 2.
B. terrestris | Water | Sucrose solution | ||||
---|---|---|---|---|---|---|
Within subjects contrasts | df | F | P-value | df | F | P-value |
Stimulus | 1 | 8.60 | 0.004 | 1 | 0.579 | 0.449 |
Stimulus × bee (cov) | 1 | 4.45 | 0.038 | 1 | 1.23 | 0.271 |
Stimulus × sensillum (cov) | 1 | 0.038 | 0.846 | 1 | 0.558 | 0.458 |
Stimulus × neonicotinoid | 2 | 0.935 | 0.397 | 2 | 0.287 | 0.752 |
Error(stim) | 77 | 86 |
Between subjects contrasts | df | F | P-value | df | F | P-value |
---|---|---|---|---|---|---|
Neonicotinoid | 2 | 10.2 | 0.937 | 2 | 0.004 | 0.996 |
Bee (cov) | 1 | 0.164 | 0.686 | 1 | 0.871 | 0.354 |
Sensillum (cov) | 1 | 5.63 | 0.020 | 1 | 3.35 | 0.071 |
Error | 77 | 86 |
A. mellifera | Water | Sucrose solution | ||||
---|---|---|---|---|---|---|
Within subjects contrasts | df | F | P-value | df | F | P-value |
Stimulus | 1 | 95.6 | <0.001 | 1 | 7.47 | 0.007 |
Stimulus × bee (cov) | 1 | 4.20 | 0.042 | 1 | 5.31 | 0.023 |
Stimulus × sensillum (cov) | 1 | 0.303 | 0.583 | 1 | 0.142 | 0.707 |
Stimulus × neonicotinoid | 2 | 2.38 | 0.096 | 2 | 3.00 | 0.053 |
Error(stim) | 144 | 127 |
Between subjects contrasts | df | F | P-value | df | F | P-value |
---|---|---|---|---|---|---|
Neonicotinoid | 2 | 1.23 | 0.295 | 2 | 6.70 | 0.002 |
Bee (cov) | 1 | 0.335 | 0.563 | 1 | 1.67 | 0.198 |
Sensillum (cov) | 1 | 1.37 | 0.244 | 1 | 12.6 | 0.001 |
Error | 144 | 127 |
For ‘Water’ model, the stimulus variable included: sucrose, KCl, nicotine, water, 1μM, and 1mM neonicotinoid. For the ‘sucrose solution’ model, the stimulus variable included: sucrose, 1nM, 100nM, and 1μM neonicotinoid. The significant stimulus × neonicotinoid’ term in the sucrose solution experiment for honeybees reflects a slight adaptive effect that occurred in the experiments with IMD, but not with TMX or CLO. Pairwise comparisons of each stimulus applied in the IMD experiment revealed that the 1 μM IMD and the final sucrose control stimulus produced fewer spikes than the first sucrose stimulus (P = 0.024 and P = 0.002). However, the 1μM IMD and the final sucrose stimulus were not significantly different (P = 0.546) indicating either that the neurons in these experiments exhibited a slight adaptation effect or that the 1μM IMD concentration had a toxic effect that influenced the integrity of their responses to sucrose.
Acknowledgments
We thank Malcolm Thompson for beekeeping, Amy Radcliffe for help with experiments, and Candy Rowe, Scott Waddell, Mary Palmer, and Neil Millar for comments. This work was funded jointly by a grant from the BBSRC, NERC, the Wellcome Trust, Defra, and the Scottish Government under the Insect Pollinators Initiative (BB/I000143/1) to GAW, a Leverhulme Trust research project grant (RPG-2012-708) to GAW, a Science Foundation Ireland grant (10/RFP/EOB2842) to JCS, a US National Science Foundation Graduate Research Fellowship awarded to EJT (Grant No. 2010097514), and an Irish Research Council’s EMBARK Postgraduate Scholarship Scheme grant (RS/2010/2147) to EJT.
Footnotes
The authors declare that they have no competing financial interests.
References
- 1.Decourtye A, Devillers J. Ecotoxicity of neonicotinoid insecticides to bees. Adv Exp Med Biol. 2010;683:85–95. doi: 10.1007/978-1-4419-6445-8_8. [DOI] [PubMed] [Google Scholar]
- 2.Gill RJ, Ramos-Rodriguez O, Raine NE. Combined pesticide exposure severely affects individual- and colony-level traits in bees. Nature. 2012;491:105–109. doi: 10.1038/nature11585. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 3.Whitehorn PR, O’Connor S, Wackers FL, Goulson D. Neonicotinoid pesticide reduces bumble bee colony growth and queen production. Science. 2012;336:351–352. doi: 10.1126/science.1215025. [DOI] [PubMed] [Google Scholar]
- 4.Defra . An assessment of key evidence about neonicotinoids and bees. 2013. [Google Scholar]
- 5.Godfray HC, et al. A restatement of the natural science evidence base concerning neonicotinoid insecticides and insect pollinators. Proc Roy Soc B. 2014;281 doi: 10.1098/rspb.2014.0558. doi:10.1098/rspb.2014.0558. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 6.Dively GP, Kamel A. Insecticide residues in pollen and nectar of a cucurbit crop and their potential exposure to pollinators. J Agr Food Chem. 2012;60:4449–4456. doi: 10.1021/jf205393x. [DOI] [PubMed] [Google Scholar]
- 7.Schmuck R, Schoning R, Stork A, Schramel O. Risk posed to honeybees (apis mellifera l, hymenoptera) by an imidacloprid seed dressing of sunflowers. Pest Manag Sci. 2001;57:225–238. doi: 10.1002/ps.270. doi:10.1002/ps.270. [DOI] [PubMed] [Google Scholar]
- 8.Decourtye A, Devillers J, Cluzeau S, Charreton M, Pham-Delegue MH. Effects of imidacloprid and deltamethrin on associative learning in honeybees under semi-field and laboratory conditions. Ecotox Environ Safe. 2004;57:410–419. doi: 10.1016/j.ecoenv.2003.08.001. [DOI] [PubMed] [Google Scholar]
- 9.Fischer J, et al. Neonicotinoids interfere with specific components of navigation in honeybees. PLoS ONE. 2014;9:e91364. doi: 10.1371/journal.pone.0091364. doi:10.1371/journal.pone.0091364. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 10.Henry M, et al. A common pesticide decreases foraging success and survival in honey bees. Science. 2012;336:348–350. doi: 10.1126/science.1215039. doi:10.1126/science.1215039. [DOI] [PubMed] [Google Scholar]
- 11.Laycock I, Lenthall KM, Barratt AT, Cresswell JE. Effects of imidacloprid, a neonicotinoid pesticide, on reproduction in worker bumble bees (bombus terrestris) Ecotoxicol. 2012;21:1937–1945. doi: 10.1007/s10646-012-0927-y. [DOI] [PubMed] [Google Scholar]
- 12.Williamson SM, Willis SJ, Wright GA. Exposure to neonicotinoids influences the motor function of adult worker honeybees. Ecotoxicol. 2014;23:1409–1418. doi: 10.1007/s10646-014-1283-x. doi:10.1007/s10646-014-1283-x. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 13.Carreck NL, Ratnieks FL. The dose makes the poison: Have “field realistic” rates of exposure of bees to neonicotinoid insecticides been overestimated in laboratory studies? J Apicult Res. 2014;53:607–614. [Google Scholar]
- 14.Easton AH, Goulson D. The neonicotinoid insecticide imidacloprid repels pollinating flies and beetles at field-realistic concentrations. PLoS ONE. 2013;8 doi: 10.1371/journal.pone.0054819. doi: 10.1371/journal.pone.0054819. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 15.Thompson HM, Wilkins S, Harkin S, Milnera S, Walters KFB. Neonicotinoids and bumblebees (bombus terrestris): Effects on nectar consumption in individual workers. Pest Manage Sci. 2014 doi: 10.1002/ps.3868. doi: 10.1002/ps.3868. [DOI] [PubMed] [Google Scholar]
- 16.Tiedeken EJ, Stout JC, Stevenson PC, Wright GA. Bumblebees are not deterred by ecologically relevant concentrations of nectar toxins. J Exp Biol. 2014;217:1620–1625. doi: 10.1242/jeb.097543. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 17.Wright GA, et al. Parallel reinforcement pathways for conditioned food aversions in the honeybee. Curr Biol. 2010;20:2234–2240. doi: 10.1016/j.cub.2010.11.040. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 18.Dethier VG. The hungry fly. Harvard University Press; 1976. [Google Scholar]
- 19.Chapman RF, Ascolichristensen A, White PR. Sensory coding for feeding deterrence in the grasshopper schistocerca-americana. J Exp Biol. 1991;158:241–259. [Google Scholar]
- 20.Weiss LA, Dahanukar A, Kwon JY, Banerjee D, Carlson JR. The molecular and cellular basis of bitter taste in drosophila. Neuron. 2011;69:258–272. doi: 10.1016/j.neuron.2011.01.001. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 21.de Brito Sanchez MG, Giurfa M, Mota TRD, Gauthier M. Electrophysiological and behavioural characterization of gustatory responses to antennal ‘bitter’ taste in honeybees. Eur J Neurosci. 2005;22:3161–3170. doi: 10.1111/j.1460-9568.2005.04516.x. [DOI] [PubMed] [Google Scholar]
- 22.Dethier VG, Bowdan E. The effect of alkaloids on sugar receptors and the feeding-behavior of the blowfly. Physiol Entomol. 1989;14:127–136. [Google Scholar]
- 23.Sanchez MGD, et al. The tarsal taste of honey bees: Behavioral and electrophysiological analyses. Front Behav Neurosci. 2014;8 doi: 10.3389/fnbeh.2014.00025. doi: 10.3389/fnbeh.2014.00025. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 24.Singaravelan N, Nee’man G, Inbar M, Izhaki I. Feeding responses of free-flying honeybees to secondary compounds mimicking floral nectars. J Chem Ecol. 2005;31:2791–2804. doi: 10.1007/s10886-005-8394-z. [DOI] [PubMed] [Google Scholar]
- 25.Brown LA, Ihara M, Buckingham SD, Matsuda K, Sattelle DB. Neonicotinoid insecticides display partial and super agonist actions on native insect nicotinic acetylcholine receptors. J Neurochem. 2006;99:608–615. doi: 10.1111/j.1471-4159.2006.04084.x. doi:10.1111/j.1471-4159.2006.04084.x. [DOI] [PubMed] [Google Scholar]
- 26.Dupuis JP, Gauthier M, Raymond-Delpech V. Expression patterns of nicotinic subunits alpha 2, alpha 7, alpha 8, and beta 1 affect the kinetics and pharmacology of ach-induced currents in adult bee olfactory neuropiles. J Neurophysiol. 2011;106:1604–1613. doi: 10.1152/jn.00126.2011. [DOI] [PubMed] [Google Scholar]
- 27.Palmer MJ, et al. Cholinergic pesticides cause mushroom body neuronal inactivation in honeybees. Nature Commun. 2013;4:1634. doi: 10.1038/ncomms2648. doi:10.1038/ncomms2648. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 28.Decourtye A, et al. Imidacloprid impairs memory and brain metabolism in the honeybee (apis mellifera l.) Pestic Biochem Phys. 2004;78:83–92. [Google Scholar]
- 29.Williamson SM, Wright GA. Exposure to multiple cholinergic pesticides impairs olfactory learning and memory in honeybees. J Exp Biol. 2013;216:1799–1807. doi: 10.1242/jeb.083931. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 30.Feltham H, Park K, Goulson D. Field realistic doses of pesticide imidacloprid reduce bumblebee pollen foraging efficiency. Ecotoxicol. 2014;23:317–323. doi: 10.1007/s10646-014-1189-7. [DOI] [PubMed] [Google Scholar]
- 31.Paoli PP, et al. Nutritional balance of essential amino acids and carbohydrates of the adult worker honeybee depends on age. Amino Acids. 2014;46:1449–1458. doi: 10.1007/s00726-014-1706-2. doi:DOI 10.1007/s00726-014-1706-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 32.Bitterman ME, Menzel R, Fietz A, Schafer S. Classical-conditioning of proboscis extension in honeybees (apis-mellifera) J Comp Psychol. 1983;97:107–119. doi:Doi 10.1037/0735-7036.97.2.107. [PubMed] [Google Scholar]
- 33.Whitehead AT, Larson JR. Ultrastructure of the contact chemoreceptors of apis mellifera l. (Hymenoptera: Apidae) Intl J Insect Morphol and Embryol. 1976;5:301–315. [Google Scholar]
- 34.Hodgson ES, Lettvin JY, Roeder KD. Physiology of a primary chemoreceptor unit. Science. 1955;122:417–418. doi: 10.1126/science.122.3166.417-a. [DOI] [PubMed] [Google Scholar]
- 35.MarionPoll F, vanderPers J. Un-filtered recordings from insect taste sensilla. Entomol Exp Appl. 1996;80:113–115. [Google Scholar]
- 36.Hiroi M, Meunier N, Marion-Poll F, Tanimura T. Two antagonistic gustatory receptor neurons responding to sweet-salty and bitter taste in drosophila. J Neurobiol. 2004;61:333–342. doi: 10.1002/neu.20063. [DOI] [PubMed] [Google Scholar]
- 37.Meunier N, Marion-Poll F, Rospars JP, Tanimura T. Peripheral coding of bitter taste in drosophila. J Neurobiol. 2003;56:139–152. doi: 10.1002/neu.10235. [DOI] [PubMed] [Google Scholar]
- 38.Pohorecka K, et al. Residues of neonicotinoid insecticides in bee collected plant materials from oilseed rape crops and their effect on bee colonies. J Apic Sci. 2012;56:115–134. [Google Scholar]
- 39.Stoner KA, Eitzer BD. Using a hazard quotient to evaluate pesticide residues detected in pollen trapped from honey bees (apis mellifera) in connecticut. PLoS ONE. 2013;8 doi: 10.1371/journal.pone.0077550. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 40.Byrne F, V PK, Leimkuehler B, Fischer DB, Grafton-Cardwell EE, Morse JG. Determination of exposure levels of honey bees foraging on flowers of mature citrus trees previously treated with imidacloprid. Pest Manag Sci. 2013;70:470–482. doi: 10.1002/ps.3596. [DOI] [PubMed] [Google Scholar]
- 41.Larson JL, Redmond CT, Potter DA. Assessing insecticide hazard to bumble bees foraging on flowering weeds in treated lawns. PLoS ONE. 2013;8 doi: 10.1371/journal.pone.0066375. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 42.Pilling E, Campbell P, Coulson M, Ruddle N, Tornier I. A four-year field program investigating long-term effects of repeated exposure of honey bee colonies to flowering crops treated with thiamethoxam. PLoS ONE. 2013;8 doi: 10.1371/journal.pone.0077193. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 43.Thompson H, H P, Wilkins S, Pietravalle S, Sweet D, Jones A. Effects of neonicotinoid seed treatments on bumble bee colonies under field conditions. Food and Enviroment Research Agency; Sand Hutton, York: 2013. [Google Scholar]