Neonicotinoids have become the most widely used class of insecticides world-wide. Although numerous studies have documented neonicotinoid toxicity in bees and other insects, the effects of exposure during early development in mammals remain largely unexplored. We assessed the effects of the neonicotinoid imidacloprid (IMI) in adult male and female mice after in utero and early postnatal exposure. Pregnant mice were infused with IMI (0.5 mg/kg/day) from gestational day 4 to the end of nursing at postnatal day 21. The young adult offspring were studied in a series of biochemical and behavioral tests. To assess reproducibility, the behavioral analyses were conducted in three separate studies using multiple exposed litters. Exposure to IMI reduced fecundity, and in adult offspring, decreased body weight in male but not female pups. Offspring from IMI-treated mothers displayed lower triglycerides, elevated motor activity, enhanced social dominance, reduced depressive-like behavior, and a diminution in social aggression compared to vehicle treated controls. Low levels of IMI were detected in the brains and livers of the treated mothers, while trace levels were detected in some offspring. Our results demonstrate that transient exposure to a neonicotinoid over the early developmental period induces long-lasting changes in behavior and brain function in mice.
Neonicotinoid pesticides are the most widely used and among the most effective insecticides on the planet1,2,3. Neonicotinoids were designed to be structurally similar to the potent toxin nicotine, and therefore act on central nervous system (CNS) nicotinic acetylcholine receptors (nAChRs; ref.4). While it has been widely assumed that neonicotinoids are selective for insect nAchRs with little or no activity toward mammalian receptors, the validity of this assumption has recently been challenged5,6,7. Thus, it becomes imperative to more rigorously investigate potential detrimental off-target effects of neonicotinoids on mammals including humans, livestock, and wildlife that may be exposed during pesticide application, or via contaminated food and water8,9,10,11,12.
Imidacloprid (IMI), a member of the chloronicotinyl nitroguanidine chemical family, was the first neonicotinoid to be commercialized and remains one of the most widely used insecticides10. It has been reported to act as a full agonist at house fly nAChRs12, or as a partial nAChR agonist in bees13,14, and chicken and Drosophila/chicken hybrid nAChRs expressed in Xenopus laevis oocytes15. In addition to structurally mimicking nicotine, IMI possesses the additional properties of being persistent in plants and soil and displaying high systemic toxicity against insects. An ideal insecticide is expected to quickly kill selected pests that harm crops while leaving other desirable species unaffected. However, several studies have reported off-target effects of IMI. For example, sublethal doses of IMI have been shown to cause neurotoxicity16, disrupt olfactory discrimination17, decrease sperm viability and fecundity, impair immunity, and alter responses to pheromones in bees and other insects18,19,20,21.
Studies conducted on adult mammals have shown that acute exposure to IMI at relatively high doses induces impaired immunity in both mice and rats22,23, genotoxicity in rabbits24, compromised reproductive function in rats (specifically, abnormal sperm morphology25), and oxidative stress and/or increased mortality in rats and increased mortality and reduced fat stores, body weight, and migratory orientation in birds26,27. In addition, IMI was reported to induce sensorimotor impairments in the offspring after single high toxic dose (337 mg/kg) in pregnant rats28. In separate groups of infant and adult rats, 2–8 mg/kg IMI given daily for 3 months impaired spatial learning and memory in the Morris water maze task29, a finding consistent with another study in rats using the neonicotinoid clothianidin30.
In light of the substantial body of knowledge detailing the detrimental effects of nicotine on the developing CNS following in utero and early postnatal exposure, and reports that neonicotinoids are present in fruits, vegetables, seeds, and honey9,31,32,33, it is essential to conduct more thorough testing to examine the developmental effects of neonicotinoids in mammals. The goal of the present study was to examine the effects of chronic in utero and early postnatal exposure of IMI in mice. After conception, pregnant mice were implanted with osmotic mini-pumps for slow infusion of IMI from gestational day 4 to the end of nursing at postnatal day 21. After reaching maturity the adult offspring of vehicle and IMI-exposed mothers were then subjected to a series of biochemical and behavioral tests to assess potential long-term alterations in motor and cognitive behaviors, and serum biochemical parameters. Our findings demonstrate the induction of abnormal behaviours in mice after in utero and early postnatal exposure to IMI.
The selection of behavioral tests employed was based on endophenotypes that have been shown to be affected by nicotine. This series of experiments was conducted serially over 18 months on three separate groups of mice; the three groups were designated Study A, B, and C. To assess reproducibility, several of the tests were repeated in two, or in all three studies (see Supplementary Table 1 for a summary of the tests conducted in each of the three studies). The data were analyzed initially via Two-way ANOVA with treatment group and sex constituting the two arms. When no significant sex differences were observed, male and female data were combined for assessment of the treatment effect. We note that ovariectomies were not performed and estrous cycles were not synchronized; this may have influenced the results of some tests in female mice. Additional groups of mice treated with either IMI or vehicle (DMSO) were generated for the collection of serum, and for IMI tissue quantitation.
Animals and Treatments
All animal experiments were carried out in accordance with the guidelines set by the Canadian Council on Animal Care and were approved by the University of Toronto Animal Care Committee. All mice were fed Teklad Global 18% protein rodent diet (#2918, Envigo). All mice were kept in standard mouse cages housed 2–4 mice per cage, given food and water ad libitum, and maintained at 22–23 °C on a 12-hour light/dark cycle. Adult (7–10 weeks old) female CD-1 mice (Charles River Inc.) were mated with male CD-1 mice. The status of the vaginal plug was assessed each day at 9 a.m. and 4 p.m.; the day the vaginal plug was present was designated as gestational day 0. For solubility testing, preliminary experimentation using a range of vehicle (dimethyl sulfoxide, DMSO) concentrations established that at DMSO concentrations of less than 15%, IMI precipitated out of solution; therefore, 25% DMSO was used to ensure IMI would remain in solution during chronic treatment.
Between gestational days 3–6, pregnant female mice were implanted with an osmotic mini-pump (Alzet Osmotic Pumps: Model 2006, 200 µL reservoir, 0.15 µL/hour flow rate, 42 days-duration) dispensing 0.5 mg/kg/day of IMI (PESTANAL 37894, Sigma-Aldrich) dissolved in 25% DMSO, or 25% DMSO alone for vehicle controls. For treatment via mini-pump, pregnant females were randomly allocated to either the vehicle or IMI exposure groups. In total, 10 pregnant females were implanted with mini-pumps containing the DMSO vehicle and 10 were implanted with IMI dissolved in DMSO. The offspring were housed with their mother until weaning on postnatal day (PND) 21. After weaning the offspring were sex-matched and housed with siblings in groups of 2–4 per cage. The mice were left undisturbed, with the exception of a biweekly cage cleaning until behavioural testing was initiated. All testing was performed blind and carried out between 9 a.m. and 5 p.m. beginning on PND 42. Each mouse was naïve to each test and was subjected to each test only once. Behavioural analyses were arranged such that all mice participated in a maximum of five tests; the less stressful tests were performed at the beginning (e.g. open field test) or earlier in testing series, while the more stressful tests (e.g. the forced swim test) were performed later in the testing regimen.
Open Field Test
The open field test measuring general motor activity was performed on PND 43–47 between 1 p.m. and 5 p.m. The basic procedures have been described previously34,35. Briefly, on the day of testing, mice were acclimated to the testing room which was dimly lit (~40 lux) by two 20 W light fixtures for 15 min. The open field test was performed using an automated open field monitoring system (Omnitech Electronics, Inc.). An automated monitoring system consisted of a 42 × 42 × 30 cm plexiglass box was placed inside a detection system, which emitted 16 × 16 × 16 laser beams, each separated by 2.5 cm. Movement was tracked by the animal disrupting the laser beams and the data were automatically quantitated by the system software. The test began with a mouse being placed in the center of the chamber, free to explore for one 20-min. trial. At the conclusion of the trial, the mouse was returned to its home cages and all materials and testing surfaces were cleaned. The time spent in the center zone and total distance travelled was recorded. The data obtained from the trial was analyzed in one 20-min. bin and in two 10-min. bins. A two-way ANOVA and a Bonferroni post-hoc test were used for statistical analysis. When statistically justified, males and females were combined, and DMSO and IMI treatment groups were compared using a two-tailed Student’s t-test with a 95% confidence interval.
Elevated plus maze
The elevated plus maze test measuring anxiety was conducted on PND 47–54 between 9 a.m. and 1 p.m. On the day of testing, the mice were acclimated to the testing room (with normal lighting) for 15 min. The apparatus consisted of two opposing open arms, two opposing closed arms, and a center zone; open arms are adjacent to closed arms, and all arms are at a 90° angle to each other. The mouse was placed in the center zone, facing an open arm and was left to explore the maze for one 5-min. trial. During the test, video recording software (Viewer2 BIOBSERVE GmbH) recorded the animal’s movements and position. The time spent in the open arms, closed arms, and center zone was recorded and analyzed. Two-way ANOVA with Bonferroni and Tukey post-hoc tests were used for data analysis.
Forced swim test
The forced swim test measuring depressive-like behavior was conducted on PND 61–67 between 9 a.m. and 1 p.m. The mice were acclimated to the testing room for 30 minutes (dimly lit ~40 lux). The testing session was video recorded and was initiated by placing a mouse, tail first, into a 2000 mL beaker filled with 1600 mL of tap water (22–24 °C). The mouse was free to swim in the beaker for one 6-min. trial. At the conclusion of the 6-min. trial, the mice were dried with a towel under a heat lamp, and returned back to their home caging. The water was replaced and the beaker was cleaned when it became visibly soiled. The final 4 min. of the 6-min. video recording were analyzed by measuring the time spent swimming and the time spent immobilized. Two-way ANOVA with Bonferroni post-hoc analysis was used for statistical computation. In cases where no significant sex effect was detected, males and females were combined and DMSO and IMI treatment groups were compared using a two-tailed Student’s t-test with a 95% confidence interval.
The tube test to assess social dominance took place on PND 54–64 between 1 p.m. and 5 p.m. On the day of testing, the mice were individually caged and acclimated to the testing. Before each trial, all materials and testing surfaces were cleaned with Virox followed by water. The tube test consisted of placing two sex-matched and age-matched mice, from two different treatment groups, at opposite ends of a transparent polyvinyl chloride tube (inner diameter: 2.5 cm, length: 30.5 cm). The mice were released simultaneously with both mice entering the tube. The test concluded when one mouse placed at least two hind paws outside the tube, with the mouse remaining inside the tube being declared the dominant winner; subsequently both mice were returned to their individual cage, and the tube was cleaned with Virox followed by water. This procedure was repeated a maximum number of times (5 matchups per mouse), such that the same matchup was never repeated. At the conclusion of the test, all mice were returned to their original home caging, and all materials and testing surfaces were thoroughly cleaned. The number of wins and winning percentage per treatment group were compared. The data were analyzed using Fisher’s Exact Test for statistical significance.
Resident intruder test
The resident intruder test was used to examine the effects of IMI on social aggression and dominance. The test was conducted on male mice on PND 66–72 between 1 p.m. and 5 p.m. Eleven to seventeen days prior to testing (PND 55–59), the mice were individually caged. On the day of testing, the mice were acclimated to the testing room (normally lit) for 20 min. A video camera recorded the activity of the mice during the test. The test began with the resident cage being placed in front of the video camera, and the age-matched and sex-matched wild type CD-1 intruder mouse being placed in the resident cage. The resident and intruder mice were free to interact for 10 min. At the conclusion of the test, the intruder mouse was returned to its home cage. The number of attacks (count), the duration of attacks (measured in seconds), and the total fight time (in seconds) were recorded for both the resident and the intruder. In addition, the latency to the first attack (measured in seconds) was also recorded, for the resident or the intruder (whichever initiated the first attack). Total fight time (in seconds) was calculated by adding the duration of attacks by resident to the duration of attacks by intruder. A two-tailed Student’s t-test with a 95% confidence interval was used as a test for statistical significance.
Serum was prepared from whole blood collected from young adult female offspring via cardiac puncture. Biochemical analysis of serum samples was conducted at the Toronto Centre for Mouse PhenoGenomics at the Hospital for Sick Children in Toronto using a Beckman Coulter AU480 analyzer.
Confirmation of dosing and tissue residues
Tissue samples from implanted mothers were collected 38–44 days after initial pump implantation, while tissue samples from the offspring were collected 60–70 days after initial pump implantation in the mother. Two LC/MS methods were used for quantitation of IMI in tissues from both the implanted mothers and offspring mice. In the first, samples of whole brain and liver were dissected from DMSO or IMI-treated young adult offspring and frozen at −80 °C. Samples were thawed, weighed, and extracted twice with acetonitrile at 4 °C using a Sonicator 3000 (Misonix Inc.) tissue disruptor for 2 min. followed by vigorous vortexing for 2 min. After centrifugation at 2000 × g for 15 min., the combined liquid extracts were evaporated to dryness under N2 at 25 °C. For quantitation of IMI, the samples were reconstituted in methanol and filtered through a 0.2 μm nylon filter syringe. Electrospray ionization LC/MS analysis was carried out using an LCMS-8050 triple quadrupole mass spectrometer (Shimadzu, Kyoto, Japan) with a LC-30A Nexera UHPLC system (Shimadzu, Kyoto, Japan). All analyses were conducted blind. The analysis was performed on an L-column2 ODS (2.1 mm × 150 mm, 3 mm; Chemicals Evaluation and Research Institute (CERI), Tokyo, Japan) at 40 °C. Gradient elution was used with solvents consisting of 0.05%(v/v) formic acid, 0.1%(v/v) acetic acid in ultra-pure water (solvent A) and methanol (solvent B). The elution gradient was 2% B to 95% B (2–10 min), 95% B (10–12 min), and 2% B (12–15 min) at a flow rate of 0.3 ml/min.
A triple quadrupole LCMS-8050 (Shimadzu) equipped with an ESI interface operating in the positive mode was used. Imidacloprid and Imidacloprid-D4 (deuterated IMI, added at the beginning of the extraction procedure) were detected by multiple reaction monitoring (MRM) in the positive ion mode, the ion transition m/z 256.1 → 175.2 and 209.15 for IMI and 260.1 → 213.1 and 179.15 for IMI-D4 were used. The following ESI inlet conditions were used. Nitrogen was used as a nebulizer gas with a flow rate of 3 l/min, the ESI probe temperature was 300 °C, the CDL temperature was 250 °C, and the detector voltage was 2.28 V. The peak-areas for all components were automatically integrated using Labsolutions Version 5.86 software (Shimadzu Chemical Laboratory Analysis System & Software, Kyoto, Japan).
For the second method used to assess IMI levels in DMSO and IMI-treated mothers, quantitation was performed as described in López-Antia et al.26 with some modifications. Samples (60–270 mg) were homogenized in 2 ml of acetonitrile in a homogenizer WISD WiseTis® after adding 20 µl of internal standard (thiacloprid) at a concentration of 1 ng/µl. Homogenate was centrifuged at 10,000 × g for 5 min. and filtered through a 2 µm de Nylon filter syringe. The analysis was performed with a HPLC system (Shimadzu LC30AD) coupled through an DuoSpray Ion Source (TurboIon Spay and APCI) to a quadrupole-time-of-flight (QTOF) mass spectrometer (TripleTOF 4600-1, AB Sciex Instruments). The temperature of TurboIon Spray was set at 500 °C. The injection volume was 4 µl. The chromatographic method was as described in López-Antia et al. 2013 (ref.26) but using acetonitrile instead of methanol as organic solvent. The chromatographic separation was performed on reverse-phase column (Poroshell 120 2.7 μm EC-C18, 150 mm × 2.1 mm i.d.). The mass spectrometer operated in the positive ionization mode, with an ion spray voltage floating of 5500 V, a flow rate of curtain gas (N2) of 9 L/min at 500 °C, and ion source gas GS (N2) flow of 30 L/min. Spectra were acquired in a mass range of mass/charge (m/z) of 100–2000. The m/z scale of the mass spectra was calibrated every 15 samples with a commercial calibration solution for APCI. MS/MS fragmentation used to identify IMI in samples was acquired from ions 256.06 m/z and 253.03 m/z as precursors of IMI and thiacloprid as internal standard respectively. The quantification was performed with the product ion 209.06 m/z for IMI and 198.93 m/z for thiacloprid. The compound parameters of mass were a collision energy 35 eV and declusting potential of 50 eV. Recorded data were processed with software Peak View 2.2 The LOD and LOQ calculated based on the SD of the response and the slope for 0.2 g of sample were 0.11 ng/g and 0.33 ng/g, respectively.
nAchRs were measured in control and IMI-treated brains from the offspring of the treated mothers using the nAChR ligand [3H]epibatidine (Perkin Elmer Corp. product #NET 1102; specific activity, 54 Ci/mmol) and a modified version of the protocol described by Whiteaker et al.,36 was conducted as follows. Sections (14 uM thickness) from unfixed frozen brains were cut on a cryostat, mounted on gelatin-coated slides, and dried. Sections were rehydrated in binding buffer (144 mM NaCl, 1.5 mM KCl, 2 mM CaCl2, 1 mM MgSO4, 20 mM HEPES, pH 7.5) at 22 °C for 15 min., followed by incubation with 1 nM [3H]epibatidine in binding buffer for 70 min. at 22 °C. (-) Nicotine (300 uM; ditartrate, Tocris) was used to define non-specific binding which was subtracted from total binding to obtain specific [3H]epibatidine binding. The slides were then washed once in binding buffer (at 4 °C) for 1 min. followed by drying under a stream of air for 48 h, after which they were apposed to Kodak Biomax MR film (Carestream Inc.) for 12 weeks at room temperature. The film was developed manually according to the manufacturer’s instructions. For quantitation, the positions of secondary motor cortex, superior colliculus superficial grey, thalamus and interpeduncular nucleus were determined using the Mouse Brain in Stereotaxic Coordinates (Academic Press). The intensity of the selected brain regions from 2 to 3 brain slices per mouse were quantified, and the average intensity of the blanks incubated with (-) nicotine were subtracted from each.
Fecundity, body weight, and serum biochemistry
Observation of all pregnant females after implantation revealed no mortality or obvious signs of toxicity or overt distress in either treatment group. Fecundity was defined as the number of offspring that were born and survived for more than one week. The number of mice born from IMI-treated CD-1 mouse mothers was lower than that from control DMSO-treated mothers (Fig. 1A). The number of males vs. the number of females born did not differ between the two treatment groups.
Body weights were recorded in Studies B and C between postnatal day (PND) 42–46 as a static measure of overall health. Analysis by two-way ANOVA indicated both a significant treatment effect in Study B (F = 29.46, p < 0.0001) and in Studies B and C combined (F = 18.28, p < 0.0001), and a significant sex effect in Study B (F = 221.9, p < 0.0001), Study C (F = 244.9, p < 0.0001) and in Studies B and C combined (F = 396.9, p < 0.0001); therefore, further statistical analyses were carried out separately on male and female body weights. In Study B, a significant decrease in body weight in the IMI treatment group compared to the DMSO control treatment group was observed in both males (p < 0.0001) and females (p < 0.01). In Study C the IMI treated male mice weighed less than control males but the difference was not significant for either sex. When the data from Study B and Study C were combined, a significant decrease in body weight in the IMI treatment group was observed in males (P < 0.001) but not females (p > 0.05; Fig. 1B).
Samples of serum were collected from young adult offspring of DMSO and IMI-treated mothers and analyzed for 18 biochemical parameters (Table 1). Although glucose and alkaline phosphatase were reduced, this did not reach statistical significance. However, triglycerides were highly and significantly reduced in IMI (114.5 mg/dL) mice compared to DMSO-treated mice (197.8 mg/dL; p < 0.005).
Open field test and elevated plus maze
The open field test was used to analyze motor activity (reflected in the total distance travelled) of the adult offspring in Studies A and B. Two-way ANOVA indicated a significant sex effect in Study B (F = 4.974, P = 0.0281) but not in Study A. Therefore, in Study B only, males and females were analyzed separately using two-way ANOVA, while in Study A and in Study A and B combined, the males and females were pooled for subsequent statistical analysis using the two-tailed Student’s t-test. In Study A, no significant difference in the total distance travelled by the DMSO and IMI treatment groups was observed (Suppl. Fig. 1A). In Study B, a non-significant trend of increased total distance travelled in the males of the IMI treatment group was observed, compared to the DMSO treatment group (P > 0.05; Suppl. Fig. 1B). Pooled data from both males and females from Study A and Study B together showed a significant increase in total distance travelled observed in the IMI-treated mice compared to the DMSO treatment group (P < 0.05; Fig. 2A).
The elevated plus maze, a well-established test used to assess anxiety and exploratory behavior35, was employed in Studies A and B. Reduced time spent in the open arms of the maze indicate increased anxiety. Two-way ANOVA analysis indicated no significant treatment effect in Study A (F = 1.658, p = 0.2018), in Study B (F = 1.909, p = 0.1703), or in Study A and Study B combined (F = 2.701, p = 0.1021), and no significant sex effect in Study A (F = 0.3279, p = 0.5686), Study B (F = 0.6828, p = 0.4107), or in Study A and Study B combined (F = 0.09784, p = 0.7548). Therefore, the results from males and females were combined and a two-tailed Student’s t-test was used to assess the differences between IMI and DMSO. Although there was a trend towards reduced time in the open arms in Study A (Suppl. Fig. 1C) and in Study B (Suppl. Fig. 1D), and in the combined data set (Fig. 2B), no significant differences in the time spent in the open arms were observed between the IMI and DMSO treatment groups.
Forced swim test
The forced swim test is a test of behavioural despair and is commonly used to assess depressive-like behavior. The results of a two-way ANOVA analysis indicated both a significant treatment effect in Study A (F = 10.91, p = 0.0015), Study B (F = 13.92, p = 0.0004), and in Studies A and B combined (F = 37.26, p < 0.0001), and a significant sex effect in Study A (F = 6.360, p = 0.0138), Study B (F = 13.73, p = 0.0004), and Studies A and B combined (F = 24.58, p < 0.0001). In addition, an interaction between treatment and sex was present when Studies A and B were combined (F = 6.003, p = 0.0155). Therefore, further statistical analyses were carried out on male and female data separately.
In Study A, a significant decrease in the time spent immobile in the IMI treatment group females (p < 0.01) compared to the DMSO treatment group was observed (Suppl. Fig. 2). In Study B, a significant decrease in the time spent immobile was again observed in the female IMI treatment group compared to the DMSO treatment group was observed (p < 0.0001; Suppl. Fig. 2B). When the results from Study A and Study B were combined a significant reduction in the time spent immobile was observed in the IMI treatment groups for both males (p < 0.05) and females (p < 0.0001) compared to the corresponding DMSO treatment groups (Fig. 3A). These results indicate a reduction in depressive-like behavior in the offspring of IMI-treated mothers.
The tube test is used to evaluate social dominance34,35. In Study A, IMI-treated offspring were tested against DMSO offspring in both males and females combined; no significant difference between the treatment groups was observed (Suppl. Fig. 3A). However, in males, a significant increase in winning in the IMI treatment group was observed (p < 0.05) compared to the DMSO treatment group (Suppl. Fig. 3A). In the females, a significant decrease in winning in the IMI treatment group was observed (p < 0.05), compared to the DMSO treatment group (Fig. 3A).
In Study B, when DMSO-treated mice were matched against IMI mice, a significant increase in winning in the IMI treatment group was observed in the males (p < 0.001), females (p < 0.001), and males and females combined (p < 0.001), compared the DMSO treatment group Suppl. Fig. 3B). In Study C, the females alone, and the females and males combined, showed a non-significant trend towards more wins in the IMI-treated mice (Suppl. Fig. 3C). When test results from Studies A, B and C were combined, the winning percentage in the IMI treatment group was significantly increased in the males alone (p < 0.001), in the females alone (p < 0.001), and in the males and females combined (p < 0.0001), compared to the DMSO treatment group (Fig. 3B). Thus, the results of the tube test indicated that IMI treatment induces increased social dominance behavior.
Resident intruder test
The resident intruder test was conducted on male mice in Studies B and C to further probe the effects of IMI on social aggression and dominance. In Study B, a significant decrease in the number of attacks by the IMI treatment group residents was observed (p < 0.05), compared to the DMSO treatment group (Suppl. Fig. 4A). In addition, the duration of the attacks by the resident mouse was significantly decreased in the IMI treatment group residents (p < 0.05) (Suppl. Fig. 4B), and a significant decrease in total fight time was also observed in the IMI treatment group compared to the DMSO treatment group (p < 0.05; Suppl. Fig. 4B). The numbers of attacks by the intruder, and the duration of the attacks by the intruder, were decreased in the IMI treatment group compared to the DMSO treatment group, but this parameter was not statistically significant (p > 0.05, Suppl. Fig. 4D,E).
In the Study C resident intruder test analysis, the attacks by resident, the duration of attacks by resident, and the total fight time, were decreased in the IMI treatment group residents, compared to the DMSO treatment group, but these parameters were not statistically significant (P > 0.05; Suppl. Fig. 4F–H). In addition, no significant differences in the number of attacks by intruder, or duration of attacks by intruder, were observed between treatment groups (P > 0.05; Suppl. Fig. 4I,J).
When the results from Studies B and C were combined, a significant decrease in the number of attacks by the IMI treatment group residents was observed (p < 0.01) compared to the DMSO treatment group (Fig. 4A), and the duration of the attacks by the resident was decreased in the IMI treatment group residents compared to the DMSO treatment group (p < 0.01; Fig. 4B). Additionally, a decrease in total fight time was also observed in the IMI treatment group (p < 0.01), compared to the DMSO treatment group (Fig. 4C). No significant differences in the number of attacks by intruder, or duration of attacks by intruder were observed between treatment groups (p > 0.05; Fig. 4D,E). These results demonstrate that interactive mouse-to-mouse aggression was highly reduced in offspring from IMI-treated mothers compared to offspring from vehicle-treated mothers.
Quantitation of IMI in tissues
To determine whether chronic exposure to IMI via an osmotic mini-pump implanted subcutaneously resulted in detectable levels of IMI in tissues, the livers and brains from treated mothers and their offspring were collected and analyzed using LC/MS (Fig. 5). Samples of liver and brain collected from mothers and offspring from mothers treated with the DMSO vehicle had levels of IMI that were either below the limit of detection, or in a few mice, slightly above the limit of detection, possibly as a result of low level contamination in the mouse chow. In the IMI-treated mothers, IMI was variably detected in tissues of some mice with higher levels observed in liver compared to brain (Fig. 5A and B). As expected, the levels in the treated mothers (Fig. 5A,B) were higher than those in the exposed offspring particularly in the livers of offspring mice which displayed highly variable levels of IMI (Fig. 5C and D).
To assess the status of nAChRs in the CNS after chronic IMI exposure (via osmotic mini-pump as described above), sections of brain from treated offspring mice were incubated with [3H]epibatidine (Fig. 6A) and receptor binding was quantified in selected brain regions (Fig. 6B–F). [3H]epibatidine was not different in IMI-treated vs. DMSO-treated mice in the thalamus, cerebral cortex, or superior colliculus; however, binding in the interpeduncular nucleus, a region known to contain a high density of nAChRs36,37,38, was significantly increased in IMI-treated mouse brains (Fig. 6F).
Unlike prenatal exposure to nicotine which has been examined in detail in both rodents and humans, the effects of prenatal and early postnatal exposure of mammals to neonicotinoids has remained relatively unexplored. We sought to begin to fill this gap by investigating the developmental effects of IMI, one of the most widely used neonicotinoids. We administered IMI to pregnant female mice during gestation and during the nursing period. Mice were exposed to 0.5 mg/kg/day of IMI from the first gestational week until approximately the time of weaning at PND 21. Based on the manufacturer’s specifications, the implanted mini-pumps were expected to be functional for 42 days, thereby theoretically covering the entire period from implantation up to weaning on PND 21. Behavioral testing commenced with an analysis of motor activity between PND 43–47, which was 22–26 days after weaning. We made the assumption that IMI exposure continued after birth via ingestion of the mother’s milk. Although no studies have investigated the presence of IMI in mother’s milk after subcutaneous or oral exposure, other neonicotinoids such as acetamiprid have been shown to cross the blood-brain barrier in mice after oral ingestion and enter and accumulate in the CNS39,40. Penetration into the CNS has also been demonstrated in bumblebees where exposure to 10 nM (2.1 ppb) IMI in the diet translated into accumulation of 4–10 nM IMI within the brain after 3 days of treatment41.
The 0.5 mg/kg/day dose of IMI used here is lower than that in almost all prior animal studies of this neonicotinoid. This dose, although likely to be higher than typical environmental exposure levels, represents a reasonable starting point for assessing the developmental effects of IMI in mammals. While the concentrations of neonicotinoids to which humans are exposed to has not been thoroughly established, studies quantitating neonicotinoids in human urine have reported a wide range of values42,43,44,45. In humans, IMI is metabolized in the liver to 6-chloronicotinic acid, 5-hydroxy-imidacloprid, 4,5-dihydroxy-imidacloprid and other metabolites43,44, while about 10–20% is excreted unchanged in the urine over several days subsequent to exposure45. However, it is difficult to compare human urine levels with our results in organ tissues. While the dose used in our mouse study was low relative to those used in animal studies published to date, it is likely higher than the levels of neonicotinoids that humans may be exposed to from ingesting contaminated food and water. Nevertheless, future animal studies should seek to determine the lowest dose of IMI and other neonicotinoids that induce biochemical and behavioral abnormalities, and concomitantly quantitate tissue levels (including urinary excretion). Another useful endeavor would be to assess neonicotinoid levels in human postmortem tissues which could then be compared with results from animal studies where the dose and length of exposure are known.
Results obtained from the LC/MS quantitation of IMI in mouse tissues illustrate the ability of peripherally administered IMI to accumulate in the livers and brains of the treated mothers. Moreover, the presence of trace levels of IMI detected in the brains and livers of some of the offspring 3–4 weeks after the end of exposure at weaning, indicate that IMI can be transferred from the mother to the pups; exposure of the mouse pups likely occurred through the fetal blood circulation and via mother’s milk. The inability to detect IMI in all treated animals could be explained by metabolism and elimination of the insecticide prior to sample collection, and in the case of the offspring, the long delay in samples collection (60–70 days after pump implantation in the mother), which corresponded to the time of completion of the behavioral testing.
As noted, most previous studies of neonicotinoid exposure in rodents used doses that were higher than the 0.5 mg/kg dose used in the present study, assessed acute effects of single doses, and/or did not administer the insecticide during both the prenatal and early postnatal period. In terms of experimental design, the study most similar to the present study was conducted by Kara et al.29. This group administered IMI to infant and adult rats at 2–8 mg/kg daily for 3 months via the oral route, and conducted a single behavioral test, the Morris water maze where the treated rats displayed impaired spatial learning and memory. We observed that transient exposure of CD-1 mice to IMI induced weight loss in male mice but not female mice, a mild elevation in motor hyperactivity, reduced depressive-like behavior, enhanced social dominance in the tube test, and decreased aggressiveness in the resident intruder test. Although the implanted mothers did not undergo behavioral testing, no overt abnormal or “sickness” behaviors were observed in any of the implanted females. Although unlikely, we cannot rule out the possibility that the mothers displayed subtle abnormal behaviors that influenced the behaviors of their pups.
Decreased body weight and elevated motor activity in IMI-treated male mice is consistent with the findings with nicotine46, and with the neonicotinoids dinotefuran and clothianidin where exposure during the prenatal and early postnatal periods also induced increased motor activity in adult mice47,48. Reduced body weight in the male IMI-treated mice is consistent with observations demonstrating that cholinergic neurons in the basal forebrain potently influence food intake and body weight. For example, impaired cholinergic signaling in mice increased food intake and induced severe obesity, whereas enhanced cholinergic signaling decreases food consumption and body weight49. In this context, our findings suggest elevated nAChR signaling after chronic neonatal IMI exposure.
The results of the forced swim test and the resident intruder test also revealed significant changes compared to vehicle-treated mice. The decrease in immobility in the forced swim test suggests reduced “depressive-like behavior”. This outcome is compatible with previous studies conducted on nicotine-treated rats50 and humans51 showing anti-depressant like behaviors after chronic nicotine exposure (see ref.52 for review). It is conceivable that decreased immobility in IMI-treated mice might have been due, at least in part, to the reduced body weight and/or mildly elevated motor activity whereby the slightly leaner IMI-treated mice may have had to keep moving continuously to keep their heads above the water line. However, arguing against body weight as a factor is the observation that the reduced body weight was only significant in the male mice, while in the forced swim test, both the consistency and magnitude of the decreased immobility was greater in the female mice.
The observations that IMI-treated mice showed increased social dominance in the tube test, while also demonstrating reduced mouse-to-mouse confrontation in the resident intruder test, at first glance seems contradictory. However, the two tests measure interactive behaviors under different conditions. In the tube test the two mice are positioned into the ends of a narrow tube and allowed to move forward into the tube to meet; typically, one of the nose-to-nose mice (“the winner”) pushes the other back out of the tube. The resident intruder test takes place in the home cage of the resident and the intruder is introduced. Both mice have access to the whole cage and therefore have the option of avoiding each other. We observed a robust decrease in attacks in IMI-treated resident mice compared to DMSO-treated resident mice, inferring a reduction in aggressive behavior. A similar reduction in attacks and reduced aggressive behaviors in the resident intruder test has been reported for nicotine in several mouse strains including the CD-1 strain used here52,53. An alternative interpretation of the data is that the IMI-treated mice displayed a strong propensity to engage in avoidance behavior and/or that the untreated mice engaged in avoidance behavior by reducing contact with the IMI-treated mice. This explanation is compatible with the finding that IMI-treated animals displayed highly significant reductions on several parameters including the number of attacks by the resident, the duration of the attacks, and the total fight time (Fig. 5 and Supplementary Fig. 4). It is conceivable that the reduced aggression and/or avoidance behavior observed may have been asserted through non-visible means, for example by olfactory and/or ultrasonic vocalization cues propagated by the IMI-treated mouse.
Previous work in mouse neuronal cultures has shown that chronic treatment with nicotine induced an up-regulation of [3H]epibatidine binding38. In the present study, results of the nicotinic receptor binding experiments showed that nicotinic radioligand [3H]epibatidine was not different in IMI-treated vs. DMSO-treated mice in the thalamus, cerebral cortex, or superior colliculus; however elevated [3H]epibatidine was observed in the interpeduncular nucleus. Increased [3H]epibatidine binding could have been caused by residual IMI remaining in this brain region several weeks after treatment, or by an increase in nAChRs induced earlier during peak IMI tissue concentrations, which then subsequently remained elevated in the absence of IMI.
The interpeduncular nucleus is a brain region expressing a very high density of nAChRs38,40. The interpeduncular nucleus is thought to have broad inhibitory effects on many other brain regions and is linked with decreased dopamine release and utilization from dopamine producing regions and appears to have a role in the regulation of rapid eye movement sleep. Activation of the GAD2 expressing sub-population of GABAergic inhibitory neurons in the interpeduncular nucleus produces the physical symptoms of nicotine withdrawal suggesting that neurons in this region may be involved in nicotine withdrawal38.
Taken together, our findings demonstrate that maternal IMI exposure in mice can be transferred to offspring over the prenatal and early postnatal period and induce perturbations in the behaviors of her adult offspring. Overall, the profile of altered behaviors observed with IMI coincides with those reported for nicotine. Our data suggest that transient exposure to a neonicotinoid insecticide during the critical early developmental period may have potentially long-term consequences that become apparent later in life. It is conceivable that the effects seen might be specific to CD-1 mice, and therefore the effects of IMI should be studied in another mouse strain, and ideally in another mammalian species. Future experimentation should also seek to establish the lowest brain concentration of IMI (and other neonicotinoids) that cause abnormal behaviors. Ultimately, the determination of the lowest tissue concentrations of neonicotinoids that are capable of inducing altered physiology and behavior in laboratory animals, will allow comparisons with the concentrations in food, drinking water, and human tissues. Documented evidence for neonicotinoid bioaccumulation in non-insect invertebrates54 and in humans43, and the identification of active metabolites of IMI and other neonicotinoids55,56,57,58,59,60 adds further incentive for conducting such studies.
The datasets are available from the corresponding author on reasonable request.
Jeschke, P., Nauen, R., Schindler, M. & Elbert, A. Overview of the Status and Global Strategy for Neonicotinoids. J. Agric. Food Chem. 59, 2897–908 (2011).
Tsvetkov, N. et al. Chronic exposure to neonicotinoids reduces honey bee health near corn crops. Science 356, 1395–1397 (2017).
Woodcock, B. A. et al. Country-specific effects of neonicotinoid pesticides on honey bees and wild bees. Science 356, 1393–1395 (2017).
Abreu-Villaca, Y. & Levin, E. D. Developmental neurotoxicity of succeeding generations of insecticides. Environ Int. 99, 55–77 (2017).
Kimura-Kuroda, J., Komuta, Y., Kuroda, Y., Hayashi & Kawano, M. H. Nicotine-Like Effects of the Neonicotinoid Insecticides Acetamiprid and Imidacloprid on Cerebellar Neurons from Neonatal Rats. Plos One 7, e32432 (2012).
Marfo, J. T. et al. Relationship between Urinary N-Desmethyl-Acetamiprid and Typical Symptoms including Neurological Findings: A Prevalence Case-Control Study. PLoS One 10, e0142172 (2015).
Cimino, A. M., Boyles, A. L., Thayer, K. A. & Perry, M. J. Effects of Neonicotinoid Pesticide Exposure on Human Health: A Systematic Review. Environ Health Perspect. 125, 155–162 (2016).
Bonmatin, J.-M. et al. Environmental fate and exposure; neonicotinoids and fipronil. Environ Sci Pollut Res Int. 22, 35–67 (2015).
Mitchell, E. A. D., Mulhauser, B. M., Mulot, M., Mutabazi, A. & Glauser, G. A worldwide survey of neonicotinoids in honey. Science 358, 109–111 (2017).
Simon-Delso, N. et al. Systemic insecticides (neonicotinoids and fipronil): trends, uses, mode of action and metabolites. Environ. Sci. Pollut. Res. 22, 5–34 (2015).
Hladik, M. L. et al. Year-round presence of neonicotinoid insecticides in tributaries to the Great Lakes. Environmental Pollution 235, 1022e1029 (2018).
Shao, X., Xia, S., Durkin, K. A. & Casida, J. E. Insect nicotinic receptor interactions in vivo with neonicotinoid, organophosphorus, and methyl-carbamate insecticides and a synergist. Proc. Natl. Acad. Sci. 110, 17273–17277 (2013).
Deglise, P., Grunewald, B. & Gauthier, M. The insecticide imidacloprid is a partial agonist of the nicotinic receptor of honeybee Kenyon cells. Neurosci. Lett. 321, 13–16 (2002).
Brown, L. A., Ihara, M., Buckingham, S. D., Matsuda, K. & Sattelle, D. B. Neonicotinoid insecticides display partial and super agonist actions on native insect nicotinic acetylcholine receptors. J. Neurochem. 99, 608–15 (2006).
Nishiwaki, H. et al. Correlations of the electrophysiological activity of neonicotinoids with their binding and insecticidal activities. Pest Manag. Sci. 59, 1023–1030 (2003).
Peng, Y. C. & Yeng, E. C. Sublethal Dosage of Imidacloprid Reduces the Microglomerular Density of Honey Bee Mushroom Bodies. Sci Rep. 6, 19298 (2016).
Decourtye, A., Devillers, J., Cluzeau, S., Charreton, M. & Pham-Delègue, M. H. Effects of imidacloprid and deltamethrin on associative learning in honeybees under semi-field and laboratory conditions. Ecotoxicol Environ Saf. 57, 410–419 (2014).
Laycock, I., Lenthall, K. M., Barratt, A. T. & Cresswell, J. E. Effects of imidacloprid, a neonicotinoid pesticide, on reproduction in worker bumble bees (Bombus terrestris). Ecotoxicology 21, 1937–45 (2012).
Rabhi, K. K. et al. Unexpected effects of low doses of a neonicotinoid insecticide on behavioral responses to sex pheromone in a pest insect. PLoS One. 9(12), e114411 (2014).
Brandt, A., Gorenflo, A., Siede, R., Meixner, M. & Büchler, R. The neonicotinoids thiacloprid, imidacloprid, and clothianidin affect the immunocompetence of honey bees (Apis mellifera L.). J. Insect Physiology 86, 40–47 (2016).
Chaimanee, V., Evans, J. D., Chen, Y., Jackson, C. & Pettis, J. S. Sperm viability and gene expression in honey bee queens (Apis mellifera) following exposure to the neonicotinoid insecticide imidacloprid and the organophosphate acaricide coumaphos. J. Insect Physiol. 89, 1–8 (2016).
Badgujar, P. C., Singh, A., Punia, J. S. & Chandratre, G. A. Immunotoxic effects of imidacloprid following 28 days of oral exposure in BALB/c mice. Environ. Toxicol. Pharmacol. 35, 408–418 (2013).
Gawade, L., Dadarkar, S. S., Husain, R. & Gatne, M. A detailed study of developmental immunotoxicity of imidacloprid in Wistar rats. Food Chem Toxicol. 51, 61–70 (2013).
Stivaktakis, P. D. et al. Long-term exposure of rabbits to imidacloprid as quantified in blood induces genotoxic effect. Chemosphere. 2016 Apr;149:108–13, https://doi.org/10.1016/j.chemosphere.2016.01.040 (2016).
Bal, R. et al. Insecticide imidacloprid induces morphological and DNA damage through oxidative toxicity on the reproductive organs of developing male rats. Cell Biochem. Funct. 30, 492–9 (2012).
Lopez-Antia, A., Ortiz-Santaliestra, M. E., Mougeot, F. & Mateo, R. Imidacloprid-treated seed ingestion has lethal effecton adult partridges and reduces both breeding investment and offspring immunity. Environ. Res. 136, 97–107 (2015).
Eng, M. L., Stutchbury, B. J. M. & Morrissey, C. A. Imidacloprid and chlorpyrifos insecticides impair migratory ability in a seed-eating songbird. Sci Rep. 7, 15176–15184 (2017).
Abou-Donia, M. B. et al. Imidacloprid Induces Neurobehavioral Deficits and Increases Expression of Glial Fibrillary Acidic Protein in the Motor Cortex and Hippocampus in Offspring Rats Following in Utero Exposure. J. Toxicol. Environ. Health, Part A 71, 119–130 (2008).
Kara, M. et al. Insecticide imidacloprid influences cognitive functions and alters learning performance and related gene expression in a rat model. Int J Exp Pathol. 96, 332–337 (2015).
Ozdemir, H. et al. Determination of the effects on learning and memory performance and related gene expressions of clothianidin in rat models. Cogn Neurodyn 8, 411–416 (2014).
Kapoor, U. U. et al. Analysis of imidacloprid residues in fruits, vegetables, cereals, fruit juices, and baby foods, and daily intake estimation in and around Lucknow, India. Environ. Toxicol. Chem. 32, 723–727 (2013).
Chen, M., Tao, L., McLean, J. & Lu, C. Quantitative analysis of neonicotinoid insecticide residues in foods: implication for dietary exposures. J. Agric. Food Chem. 62, 6082–90 (2014).
Sánchez-Hernández, L. et al. Residues of neonicotinoids and their metabolites in honey and pollen from sunflower and maize seed dressing crops. J. Chromatogr A. 1428, 220–7 (2016).
Gholizadeh, S. et al. Reduced Phenotypic Severity Following Adeno-Associated Virus Mediated Fmr1 Gene Delivery in Fragile X Knockout Mice. Neuropsychopharmacol. 39, 3100–11 (2014).
Arsenault, J. et al. FMRP Expression Levels in Mouse CNS Neurons Determine Behavioral Phenotype. Human Gene Therapy 27(12), 971–981 (2016).
Whiteaker, P., McIntosh, J. M., Luo, S., Collins, A. C. & Marks, M. J. 125I-Conotoxin MII Identifies a Novel Nicotinic Acetylcholine Receptor Population in Mouse Brain. Mol. Pharmacol. 57, 913–925 (2000).
Zambrano, C. A. et al. Density of a4b2 nAChR on the surface of neurons is modulated by chronic antagonist exposure. Pharma. Res. Per. 3(2), e00111, https://doi.org/10.1002/prp2.111 (2015).
Zhao-Shea, R., Liu, L., Pang, X., Gardner, P. D. & Tapper, A. R. Activation of GABAergic Neurons in the Interpeduncular Nucleus Triggers Physical Nicotine Withdrawal Symptoms. Current Biology 23(23), 2327–35 (2013).
Ford, K. A. & Casida, J. E. Chloropyridinyl neonicotinoid insecticides: Diverse molecular substituents contribute to facile metabolism in mice. Chem. Res. Toxicol. 19, 944–951 (2006).
Terayama, H. et al. Acetamiprid Accumulates in Different Amounts in Murine Brain Regions. Int. J. Environ. Res. Public Health 13, 937 (2016).
Moffat, C. et al. Chronic exposure to neonicotinoids increases neuronal vulnerability to mitochondrial dysfunction in the bumblebee (Bombus terrestris). FASEB J. 29, 2112–9 (2015).
Harris, S. A. et al. National Study of Exposure to Pesticides among Professional Applicators: An Investigation Based on Urinary Biomarkers. J. Agric. Food Chem. 58, 10253–10261, https://doi.org/10.1021/jf101209g (2010).
Taira, K., Fujioka, K. & Aoyama, Y. Qualitative Profiling and Quantification of Neonicotinoid Metabolites in Human Urine by Liquid Chromatography Coupled with Mass Spectrometry. Plos One 8, e80332 (2013).
Wang, L. & Liu, T. Fang Liu, Zhang, J., Wu, J., and Sun, H.. Occurrence and Profile Characteristics of the Pesticide Imidacloprid, Preservative Parabens, and Their Metabolites in Human Urine from Rural and Urban China. Environ. Sci. Technol. 49, 14633–14640, https://doi.org/10.1021/acs.est.5b04037 (2015).
Harada, K. H. et al. Biological Monitoring of Human Exposure to Neonicotinoids Using Urine Samples, and Neonicotinoid Excretion Kinetics. Plos One https://doi.org/10.1371/journal.pone.0146335 (2016).
Smith, D. et al. Adult Behavior in Male Mice Exposed to E-Cigarette Nicotine Vapors during Late Prenatal and Early Postnatal Life. Plos One. https://doi.org/10.1371/journal.pone.0137953 (2015).
Yoneda, N. et al. Peripubertal exposure to the neonicotinoid pesticide dinotefuran affects dopaminergic neurons and causes hyperactivity in male mice. J. Vet. Med. Sci. Apr 18;80P4R:6349637, https://doi.org/10.1292/jvms.1890014 (2018).
Tanaka, T. Effects of maternal clothianidin exposure on behavioral development in F1 generation mice. Toxicol. Ind. Health 28(8), 697–707 (2012).
Herman, A. H. et al. A cholinergic basal forebrain feeding circuit modulates appetite suppression. Nature 538, 253–256 (2016).
Jun’ichi Semba, C., Mataki, S., Yamada, S., M. Nankai, M. & Toru, M. Antidepressant-like Effects of Chronic Nicotine on Learned Helplessness Paradigm in Rats. Biol. Psychiatry. 43, 389–391 (1998).
McClernon, F. J., Berry Hiott, F., Westman, E. C., Rose, J. E. & Levin, E. D. Transdermal nicotine attenuates depression symptoms in nonsmokers: a double-blind, placebo-controlled trial. Psychopharmacol. 189, 125–133 (2006).
Picciotto, M. R., Lewis, A. S., Gerrit van Schalkwyk, I. & Mineur, Y. S. Mood and anxiety regulation by nicotinic acetylcholine receptors: A potential pathway to modulate aggression and related behavioral states. Neuropharmacol. 96, 235–243 (2015).
Lewis, A. S., Mineur, Y. S., Smith, P. H., Cahuzac, L. M. & Picciotto, M. R. Modulation of aggressive behavior in mice by nicotinic receptor subtypes. Biochem. Pharmacol. 97, 488–497 (2015).
Chevillot, F. et al. Selective bioaccumulation of neonicotinoids and sub-lethal effects in the earthworm Eisenia andrei exposed to environmental concentrations in an artificial soil. Chemosphere 186, 839–847 (2017).
Ueyama, J. et al. Temporal Levels of Urinary Neonicotinoid and Dialkylphosphate Concentrations in Japanese Women Between 1994 and 2011. Environ. Sci. Technol. 49, 14522–14528, https://doi.org/10.1021/acs.est.5b03062 (2015).
Chao, S. L. & Casida, J. E. Interaction of imidacloprid metabolites and analogs with the nicotinic acetylcholine receptor of mouse brain in relation to toxicity. Pestic. Biochem. Phys. 58, 77–88 (1997).
Tomizawa, M. & Casida, J. E. Neonicotinoid insecticide toxicology: Mechanisms of selective action. Annu. Rev. Pharmacol. Toxicol. 45, 247–268 (2005).
Tomizawa, M. & Casida, J. E. Unique Neonicotinoid Binding Conformations Conferring Selective Receptor Interactions. J Agric. Food Chem. 59, 2825–2828 (2011).
Swenson, T. L. & Casida, J. E. Aldehyde Oxidase Importance In Vivo in Xenobiotic Metabolism: Imidacloprid Nitroreduction in Mice. Toxicological Sci. 133, 22–28 (2013).
Vardavas, A. I. et al. The metabolism of imidacloprid by aldehyde oxidase contributes to its clastogenic effect in New Zealand rabbits. Mutat. Res. 829-830, 26–32, https://doi.org/10.1016/j.mrgentox.2018.03 (2018).
The authors thank Drs. P. Fletcher, P. Grootendorst, A. Ramsey, A. Salahpour, and P. G. Wells for helpful suggestions and comments. This study was supported by funds from the Leslie Dan Faculty of Pharmacy, University of Toronto, and the Natural Sciences and Engineering Research Council of Canada.
The authors declare no competing interests.
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Burke, A.P., Niibori, Y., Terayama, H. et al. Mammalian Susceptibility to a Neonicotinoid Insecticide after Fetal and Early Postnatal Exposure. Sci Rep 8, 16639 (2018). https://doi.org/10.1038/s41598-018-35129-5
- Early Postnatal Exposure
- Elevated Motor Activity
- Young Adult Offspring
- Imidacloprid (IMI)
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