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Impacts of neonicotinoid seed treatments on soil-dwelling pest populations and agronomic parameters in corn and soybean in Quebec (Canada)

  • Geneviève Labrie ,

    Roles Conceptualization, Data curation, Formal analysis, Funding acquisition, Investigation, Methodology, Project administration, Supervision, Validation, Writing – original draft

    Current address: Centre de recherche agroalimentaire de Mirabel (CRAM), Mirabel, Québec, Canada

    Affiliation Centre de recherche sur les grains Inc. (CÉROM), St-Mathieu-de-Beloeil, Québec, Canada

  • Annie-Ève Gagnon,

    Roles Conceptualization, Funding acquisition, Methodology, Validation, Writing – review & editing

    Current address: Agriculture and Agri-Food Canada, Saint-Jean-sur-Richelieu, Research and Development Centre, Saint-Jean-sur-Richelieu, Québec, Canada

    Affiliation Centre de recherche sur les grains Inc. (CÉROM), St-Mathieu-de-Beloeil, Québec, Canada

  • Anne Vanasse,

    Roles Conceptualization, Validation, Writing – review & editing

    Affiliation Département de phytologie, Université Laval, Québec, Québec, Canada

  • Alexis Latraverse,

    Roles Formal analysis, Methodology, Validation, Writing – review & editing

    Affiliation Centre de recherche sur les grains Inc. (CÉROM), St-Mathieu-de-Beloeil, Québec, Canada

  • Gilles Tremblay

    Roles Conceptualization, Methodology, Validation, Writing – review & editing

    Current address: Ministère de l’Agriculture, des Pêcheries et de l’Alimentation du Québec, Saint-Hyacinthe, Québec, Canada

    Affiliation Centre de recherche sur les grains Inc. (CÉROM), St-Mathieu-de-Beloeil, Québec, Canada

Impacts of neonicotinoid seed treatments on soil-dwelling pest populations and agronomic parameters in corn and soybean in Quebec (Canada)

  • Geneviève Labrie, 
  • Annie-Ève Gagnon, 
  • Anne Vanasse, 
  • Alexis Latraverse, 
  • Gilles Tremblay


Agricultural soil pests, including wireworms (Coleoptera: Elateridae), are managed primarily with pesticides applied directly to seeds before sowing. Seeds coated with neonicotinoids have been used widely in Quebec (Canada) for several years. To assess the agronomic and economic value of neonicotinoid seed treatments in soybeans and corn in Quebec, trials were conducted from 2012 to 2016 in 84 fields across seven regions in Quebec. We evaluated the effect of neonicotinoid seed treatments on soil pest densities, crop damage and yield. The results showed that 92.6% of corn fields and 69.0% of soybean fields had less than 1 wireworm per bait trap. However, no significant differences in plant stand or yield were observed between treated and untreated corn or soybeans during the study. This study shows that neonicotinoid seed treatments in field crops in Quebec are useful in less than 5% of cases, given the very low level of pest-associated pressure and damage, and that they should not be used prophylactically. Integrated pest management (IPM) strategies need to be developed for soil insect pests to offer effective alternative solutions to producers.


Since the middle of the 1990s, neonicotinoids (i.e. imidacloprid, clothianidin and thiamethoxam) have become the main class of insecticides routinely used to protect seeds and seedlings against injuries caused by soil insects [1, 2, 3]. Corn, canola, soybeans, wheat and cotton are the principal crops grown worldwide for which seed treatments are used on a large scale, with a rapid increase in the acreages treated [1, 4]. A vast body of scientific literature has demonstrated that the scale of use of those insecticides has resulted in widespread contamination of agricultural soils, freshwater resources, wetlands, and non-target vegetation, along with repeated and chronic exposure of the organisms inhabiting these habitats to potentially harmful concentrations of these pesticides [2, 5, 6, 7, 8, 9, 10, 11, 12, 13]. In Canada, widespread contamination of water [14, 15, 16, 17, 18, 19, 20, 21] and impacts on non-target organisms, such as pollinators [22, 23, 24, 25], have already been demonstrated.

In the province of Quebec, Canada, seeds coated with neonicotinoid insecticides are widely used as a prophylactic treatment on almost 100% of corn acreages and canola, and about 60% of soybean acreages, representing over 500,000 ha sown with treated seeds each year [26]. These seed treatments are mainly used to control soil pests, such as white grubs (Coleoptera: Scarabaeidae), seedcorn maggot (Diptera: Anthomyiidae) and wireworms (Coleoptera: Elateridae), and represent an attractive option as “insurance” against those pests because of their relatively low cost, ease of handling and low toxicity to mammals [1, 3, 27, 28]. The treatments are generally used in the absence of any documented increase in pest threats [1, 2, 29], partially driven by current market efficiencies [30], and few studies have examined their usefulness against soil-dwelling insect pests such as wireworms and seedcorn maggots.

Wireworms are considered major soil pests worldwide [31]. More than 1,000 species are found in North America [32] and 370 species in Canada [33, 34, 35], including 30 economically important species. A recent study reported that 9 genera of wireworms occur in Quebec, with the abbreviated wireworm, Hypnoidus abbreviatus Say, being the most abundant species, accounting for 72% of all wireworms collected in field crops [36]. Wireworms are early-season pests that can injure seeds and seedlings in spring, reducing the establishment and growth of young plants in the field [37, 38]. Seedcorn maggots (Delia platura Meigen, D. florilega [Zetterstedt, 1845]) are pests of numerous vegetable and field crops and can cause serious economic losses when larvae penetrate the germinating seeds or seedlings and mine cotyledons, small shoots and/or young roots before sprouting occurs [39, 40, 41, 42]. They are usually sporadic pests in field crops, mainly attracted by organic matter or cover crops incorporated into the soil before sowing [43, 44, 45]. In Quebec, the seedcorn maggot is observed sporadically in soybean or corn fields, but its impact has not been evaluated on a large scale.

The debate surrounding the prophylactic use of neonicotinoids has mainly focused on the potential yield increase in corn and soybeans. Recent studies have sought to analyze whether yield differences can be observed in soybean with or without neonicotinoid seed treatments targeting soybean aphids, Aphis glycines Matsumura [46, 47, 48, 49, 50, 51, 52, 53, 54, 55, 56]. A few studies demonstrated yield increases with the use of neonicotinoid treated seeds, mainly when more than one type of pest was present in the field [51, 52], while other studies presented no differences. However, those studies focused only on above-ground pests, and none evaluated the usefulness of neonicotinoids against soil-dwelling insect pests in soybean.

In corn, some studies have examined yield differences between treated and untreated seeds [30, 53, 57, 58, 59, 60, 61]; however, the results are inconsistent, with a recent meta-analysis covering 15 years of high dose of neonicotinoids applied to control western and northern corn rootworm in Indiana demonstrating no yield differences [30], while another study spanning 14 years and 91 trials in the southern part of the USA showed a 700 kg/ha higher yield in treated corn [59]. In the northeastern part of Canada, which has different climatic conditions and agronomic practices, no studies have been done to evaluate soil-borne insect pest pressure or the impact of using insecticide seed treatments in corn and soybean.

Our study was designed to evaluate agronomic parameters related to soybean and corn planted with neonicotinoid treated seed or untreated seed on a large scale over a five-year period in the province of Quebec, Canada. The main objectives of this project were to evaluate the impact of neonicotinoid seed treatments on 1) the incidence and abundance of wireworms and other soil-dwelling insect pests and 2) soybean and corn yield.

Materials and methods

Experimental sites

In 2012–13, an experiment was conducted at 12 and 13 corn growing sites in the Monteregie region (the main corn growing area), while in 2014–15, the study was conducted at 19 and 24 sites in seven corn producing regions across the province of Quebec, for a total of 68 sites. All sites were on commercial growers’ farms. No specific permissions have been requested to collect insects and agronomic parameters on grower’s farm for the 84 trials of the project. Each site was the property of a grower, and all of them give us the right to collect insects and soil samples. The study did not involve any endangered or protected species. In 2015–16, a study on soybean was conducted at 7 and 9 sites located in the Monteregie and Centre-du-Quebec areas. The locations were carefully chosen to represent sites with high risk factors (sandy soil, grassland as previous crop, no till, organic fertilization; high organic matter) or low risk factors (clay, soybean rotation, conventional tillage, mineral fertilization) to ensure that soil-dwelling pests would be present [31, 40], and to represent the variability observed in field crops in the province. The characteristics of each site are summarized in S1 Table (Appendix).

Each site was sown with two alternating strips of treated seed and untreated seed, repeated three times for a total of 6 plots (plots were 6 to 9 m wide × 200–300 m long). Seeds were sown at a depth of approximately 4.5 cm and with 76-cm spacing between rows. The approximate sowing rate was between 80,000 and 89,000 seeds per hectare (ha) for corn, and 400,000 and 500,000 seeds per ha for soybean. All sites were sown in the direction of the slope to prevent insecticide contamination of untreated plots caused by surface runoff. Fertilization differed according to the growers’ practices and consisted of mineral or organic manure (S1 Table, Appendix).

Seed treatments

For the corn study, different hybrids as well as different insecticide and fungicide seed treatments were used, depending on the year and the corn heat units (CHU) associated with the region. In 2012, the hybrid used was K293 RR (Horizon Seeds Canada Inc.) treated with Poncho® 600 (insecticide; clothianidin 0.25 mg/seed, Bayer CropScience Inc.) and Maxim® Quattro (fungicides; fludioxonil + metalaxyl-M and S-isomer + azoxystrobin + thiabendazole, Syngenta Canada Inc.). In 2013, the hybrid was HZ872BtGT (Horizon Seeds Canada Inc.) treated with Cruiser Maxx® (insecticide; thiamethoxam 0.25 mg/seed, Syngenta Canada Inc.) and Maxim® Quattro. Hybrids with 2850 CHU were used in both years. In 2014–15, hybrids with different CHU were used depending on the region (R E50G22: RR2, Genuity, 2400 CHU [14 sites]; E61P12 R: RR, Genuity VT Double Pro, 2700 CHU [17 sites] and R E65F12: RR Genuity VT Double Pro 2850 CHU [12 sites], all from Elite®). The seeds were treated with Poncho® 600 and Maxim® Quattro. The seeds used for the control plots in the corn assays between 2012 and 2015 were treated only with Maxim® Quattro (fungicides). Treated and control seeds came from the same seed lots in 2012, 2013 and 2015.

In both years of the soybean study, the plots were sown with the cultivar Montero RR (Prograin) treated with Cruiser Maxx® (Syngenta Canada Inc.), which includes an insecticide (thiamethoxam 0.25 mg/seed) and fungicides (difenoconaxole + metalaxyl-M + sedaxane). The seeds used for the control plots in the soybean assays were treated only with fungicides (difenoconaxole, metalaxyl-M and sedaxane). Treated and control seeds came from the same seed lots.

Insect sampling

Three 3 × 3 m sampling stations, each covering four rows of crop, were installed in each strip, for a total of 18 stations per site. Stations in the same strip were installed at least 50 m apart. Each site was visited five to eight times during the growing season to install and replace insect traps, collect data on seedling damage, and harvest plants.

Soil insects were sampled using two different methods: bait traps (2012–15 in corn and 2015–16 in soybean) and soil sampling (2014–15 in corn and 2015–16 in soybean). Bait traps were used to sample wireworms, while soil sampling was used to capture wireworms, white grubs and other soil-dwelling pests. One bait trap per station was installed (18 per field) just after sowing (in May). The traps consisted of a 15 × 15 × 15 cm hole in the ground filled with bait (one cup of an equal parts mixture of wheat flour, untreated wheat seeds and oatmeal), and covered with soil. The baits were dug out and destructively inspected in the field once a week. The wireworms in each trap were collected in vials (to be counted and identified in the laboratory), and a new trap was set up near the old one. Five soil samples (10 cm diameter × 15 cm depth) were taken weekly from each strip (i.e. one per sampling station and one between each station, for a total of 30 samples per site). Insects were extracted in the laboratory using Berlese funnels (kept for 24 h under 60W incandescent light bulb) and counted. Identification was done by morphological analysis using a species key [34, 62, 63, 64, 65]. Voucher specimens have been added to the Collection nationale des insectes du Québec (Québec, QC, Canada).

Plant and seedlings observations

Plant stand and seedling damage.

Corn and soybean populations were evaluated when the plants were between the 4- to 8-leaf stages. An assessment of plant stand was done by counting all the plants along the two central rows of each station over a length of 3 m.

Once a year, between 2013 and 2016, corn and soybean seedlings (2–6 leaves) were observed at each site to evaluate the main causes of damage. Three seedlings presenting symptoms (less vigorous, small or yellowing or stunted plants) or damage (holes, chewed parts) or dead seedlings were dug out at each station (i.e. 54 seedlings per site). Special care was taken when recovering the seeds to identify holes or galleries made by wireworms or other insects. Seedlings were taken to the laboratory to identify the damage. Any wireworms found were identified to species level.


To estimate crop yields under neonicotinoid treated and untreated seed treatments, soybean and corn were mechanically harvested in each strip. For the corn assays, a commercial harvester was used, and the grain car was weighed separately for each strip. For the soybean assays, the two middle rows of each strip were harvested with an experimental plot combine harvester (Wintersteiger AG, Ried im Innkreis, Austria). Subsamples of grain (corn and soybean) were collected to measure moisture in the laboratory and results were reported based on 15% moisture content for corn and 13% for soybean. In 2015, one soybean site (Roxton Pond) was not harvested because of water accumulation during summer.

Statistical analyses

The corn and soybean data were analyzed separately using a mixed model approach to account for the non-independent spatial associations (pseudoreplication) in the data and the unbalanced replication due to missing data at some of our sites [66, 67]. Plant stands and yields were analyzed using linear mixed models (LMM) assuming a Gaussian distribution of the error and the identity link function. Wireworm captures (bait traps and soil samples) were analyzed using generalized linear mixed models (GLMM) with a Poisson distribution of the error and a log link function. The Poisson distribution is recommended for the analysis of count data which are discrete and positive. Although plant stand is a count variable, it was normally distributed with a constant standard deviation. Proportions of damaged seedling were analyzed using GLMMs with a binomial distribution of the error and a logit link function. This distribution is recommended to analyze proportional data based on number of “success” over a known number of “trials”. The bait traps and soil samples analyses were conducted on the most abundant trapping survey. Because of the high number of zeros, wireworm captures were pooled per treatment per site prior to analysis and the number of traps or soil samples was used as an offset to account for the sampling effort. Only sites with more than five captures of wireworms were included in the models.

All response variables were modelled with seed treatments (treated or untreated) and year as fixed effects. The full model for the plant stands analysis included a random intercept and slope for Site and Block (nested within Site) as random effect, while the bait traps, soil samples and yield analyses, included a random slope for Site. The best random structure for each analysis was then determined using Akaike’s Information Criterion for smaller sample sizes (AICc) [68] using restricted maximum likelihood estimation (REML). Once determined the best random structures, the resulting models were refitted with maximum likelihood (ML) and the seed treatment effect was tested using likelihood ratio tests (LRT). The parameter estimates presented for the final models were evaluated based on restricted maximum likelihood.

Data exploration was carried out following the protocol described in Zuur et al. [69] and the assumptions of the models were checked visually. Analyses were performed using R language [70]. Linear mixed models and generalized linear mixed models were fit with the functions lmer and glmer, respectively, from the package lme4 [71]. The AICc values were calculated using function AICc from the package MuMIn [72] and the LRT test were performed using function drop1.


Effect of neonicotinoids on insect populations

Corn pests.

A total of 1,032 wireworms were captured in the bait traps over the four years of the project (2012 to 2015). The mean number of wireworms in each trap per visit varied between 1 and 21. Among the 68 sites sampled, only five exceeded 1 wireworm per trap (three in 2013 and two in 2014; Fig 1). The main species was H. abbreviatus, representing 56%, 82%, 48% and 76% of the assemblage in 2012, 2013, 2014 and 2015, respectively, followed by Agriotes mancus Say and Melanotus similis (Kirby, 1837), accounting for 2 to 17% of the assemblage depending on the year. Other wireworms captured belonged to the genera Limonius, Dalopius and Ampedus.

Fig 1. Mean abundance (±SE) of wireworms per bait trap in corn fields with or without neonicotinoid seed treatments (68 sites).

The average number of wireworms found at each site for the most abundant visit is presented for each year: (A) 2012, (B) 2013, (C) 2014, (D) 2015. Neonicotinoid seed treatment varies between years; complete information on treatments is described in the Materials and Methods section.

The number of wireworms per bait trap did not differ significantly across locations-years between neonicotinoid treated and untreated strips (LRT; χ(1) = 0.975; p = 0.32).

In 2014 and 2015, the number of wireworms captured in soil samples per sampling period varied between 0 and 94 larvae/m2 (Fig 2). The main species observed was H. abbreviatus, representing 47% and 87% of the assemblage in 2014 and 2015, respectively. For the bait traps, the number of wireworms did not differ significantly between neonicotinoid treated and untreated strips (χ2 = 0.728; df = 1; p = 0.393; Fig 2).

Fig 2.

Mean abundance (± SE) of wireworms per m2 in soil samples from corn fields with neonicotinoid treated strips and untreated strips in 2014 (A) and 2015 (B) (total of 43 sites).

Other soil insect pests have been observed in bait traps and soil samples, such as seedcorn maggot (Delia platura Meigen) pupae, white grubs (Phyllophaga anxia [Leconte]), Ateanius sp., Aphodius sp.), Noctuidae larvae (Lepidoptera), such as black cutworm (Agrotis ipsilon [Hufnagel]) and Tipulidae larvae (Diptera). Seedcorn maggots were omnipresent in all fields but did not affect seedlings in a systematic manner (see next section for a description of damage). Of the 239 larvae captured, only 16 were white grubs (P. anxia); all others belonged to the genera Ateanius and Aphodius. A total of 84 Tipulidae larvae were observed, of which 54 belonged to the species Tipula paludosa (Meigen). These low numbers precluded a comparison of neonicotinoid treated and untreated plots with respect to the abundance of other soil-dwelling insect pests.

Soybean pests.

A total of 271 wireworms were captured in bait traps over the two years during which this sampling method was used (48 in 2015 and 105 in 2016). The mean number of wireworms captured in bait traps per sampling period varied between 0 and 2.78 (Fig 3A and 3B). The main species observed was H. abbreviatus, with a total of 241 specimens captured, accounting for 84% and 86% of the assemblage in 2015 and 2016, respectively. The other wireworms collected belonged to the species A. mancus and the genera Hemicrepidius, Melanotus, Limonius and Oestodes. Among the 15 sites sampled, 5 sites (two in 2015 and three in 2016) exceeded a mean of 1 wireworm per trap (Fig 3A and 3B). Wireworm population density did not differ significantly between the neonicotinoid treatment and the control in 2015 (LRT; χ2 = 0.407; df = 1; p = 0.52) and 2016 (LRT; χ2 = 0.044; df = 1; p = 0.83).

Fig 3.

Mean abundance (±SE) of wireworms per bait trap (A, B) and soil sample (C, D) in 2015 and 2016 in soybean fields with or without neonicotinoid seed treatments. in 2015, only 6 of the 7 planted sites were harvested.

A total of 72 wireworms were captured in soil samples. The mean abundance varied between 0 and 59/m2 or 51 larvae/m2 in 2015 and 2016, respectively (Fig 3C and 3D). The main species observed was H. abbreviatus, with a total of 59 specimens captured, representing 81% of the species during both years of the study. The other wireworms collected belonged to the species A. mancus, M. similis and the genera Hemicrepidius and Oestodes. Only two larvae of P. anxia were captured on one site in 2015 and five larvae on two sites in 2016. A higher abundance of wireworms was observed in neonicotinoid treatment strips compared to control strips in 2015 (LRT; χ2 = 5.21; df = 1; p = 0.02) but not in 2016 (LRT; χ2 = 0; df = 1; p = 0.99).

Plant stand

Corn plant stands varied between 4 and 7 plants/m during the four-year study. Overall, for all sites and years, no significant differences in corn stand was observed between treated (5.80 ± 0.07 plants/m) and untreated plots (5.73 ± 0.07 plants/m) (LRT; F1, 67.1 = 3.20; p = 0.078).

In soybean, plant stands were very variables among sites (between 16 plants/m and 76 plants/m) during the two-year study. For all sites, no significant differences in the stand of soybean were observed between treated and untreated plots (LRT; F1, 12.14 = 2.76; p = 0.122).

Seedling damage

Visual inspection of three damaged plants in each plot showed that the damage associated with soil-dwelling insect pests in corn was characterized by a hole in the grain (caused by wireworms), or by smaller or less vigorous plants (caused indiscriminately by wireworms or seedcorn maggot larvae). Damage was observed in 8, 17 and 19 fields (62%, 89% and 79%) in 2013, 2014 and 2015, respectively. In all years, the percentage of corn seedlings damaged by soil-borne insect pests (wireworm, seedcorn maggot) was significantly higher at untreated stations (13.0%, 1.6% and 12.1% respectively) than in treated stations (7.0%, 0.6% and 7.4%) (LRT; χ2 = 8.11; df = 1; p = 0.004; Fig 4).

Fig 4. Seedling damage caused by soil-dwelling pests in 68 commercial corn fields in the province of Quebec, Canada, over a three-year period.

In soybean, very little damage to seedlings was observed, with only two sites presenting damage in 2015 (Nicolet: 1 plant/54 with a hole in the grain caused by wireworms; Roxton Pond: 3 plants/54 with stem damage caused by seedcorn maggot).

Effects of neonicotinoids on yields

In corn, yields were not significantly different between neonicotinoid treated and untreated strips regardless of the site, or the year (LRT; F1, 186.42 = 3.24; p = 0.073; Fig 5).

Fig 5. Mean yield (kg/ha) (±SE) in 68 commercial corn fields in the province of Quebec, Canada with neonicotinoid seed treatments or without (control strips).

In soybean, yield did not differ significantly between neonicotinoid treated (4413 ± 170 kg/ha) and untreated strips (4330 ± 170 kg/ha) during the two-year study (LRT; F1, 32.45 = 1.54; p = 0.223) (Fig 6).

Fig 6.

Mean yield (kg/ha) (±SE) in 15 commercial soybean fields in the province of Quebec, Canada with neonicotinoid seed treatments or without (control strips) in 2015 (A) and 2016 (B).


This study provides a strong demonstration that insecticide seed coatings on corn and soybean are not needed as a prophylactic control measure against soil-dwelling insect pests in field crops in Quebec, Canada. Overall, the abundance of such pests, including wireworms, was low in most fields monitored and no yield difference was observed between neonicotinoid seed treatments and control plots in corn or soybean.

Effects of neonicotinoids on insect populations and damage

The main group of soil insect pests found at our corn study sites that could be managed by neonicotinoid seed treatments were wireworms. The seedcorn maggot was observed on only a few seedlings but did not cause major damage during the four-year study. White grubs were largely absent from our 68 sites. Corn rootworms were also monitored in 2012 and 2013 but were present in very low numbers [73]. This could be explained by the main rotation scheme used in Quebec (corn/soybean), which is known to reduce the prevalence of this pest species [74, 75]. Insect pressure was low at almost 90% of our corn study sites (below a threshold of 1 wireworm/bait trap), which is representative of the extensive surveys that have been done in the province since 2011 [36]. Therefore, IPM strategies for soil insect pests in Quebec corn fields should focus on wireworms.

In our study, with neonicotinoid seed treatments, no decrease in wireworm abundance was found from one year to another [36]. Some studies [76, 77] have shown that neonicotinoid treatments induce a prolonged intoxication of wireworms, making them moribund for several weeks, but do not reduce their populations. Our results confirm that those insecticides did not affect wireworm population levels.

The study by Furlan [78] showed that the type and intensity of damage to corn differed between wireworm species. In this study, the three species of Agriotes (A. brevis, A. sordidus and A. ustulatus) differed in length and did not affect corn in the same manner. In our case, the main wireworm species observed was H. abbreviatus; very little information is available on this species’ biology and food preferences and the damage it causes in corn. This species was first observed in organic soil in raspberry fields in Quebec [79, 80, 81, 82], but no information was available on the type and intensity of damage it causes in corn or soybean. We observed higher proportions of damaged corn seedlings in untreated corn plots in 8, 17 and 19 fields in 2013, 2014, and 2015, respectively. In Europe, the presence of 5 to 10 larvae per m2 caused 30% mortality of maize seedlings [83]. Furlan [78] observed that a loss of 1 corn plant per m2 could cause significant yield losses. In our study, we observed more than 10 larvae per m2 in 11 (58%) and 10 (42%) fields in 2014 and 2015, respectively, but no differences in plant stand or grain yield were observed. The main damage that was observed in the seedlings was a hole in the grain, which can cause growth delay and sometimes no growth at all. However, the consequences were generally limited to irregular plant heights in different portions of the field. This kind of damage, less intense than that caused by larger wireworm species such as Agriotes spp. [84] or Melanotus spp. [85, 86], could explain the lack of differences in corn plant stand or grain yield between treated and untreated strips.

These results call into question the threshold of 1 wireworm per bait trap [83] commonly used for our main wireworm species, H. abbreviatus. This threshold was developed for Agriotes spp. found in northern France. Furlan [78] demonstrated that thresholds could differ with wireworm species and the type of damage they are causing. He identified thresholds varying between 1 and 5 wireworms per bait trap for species with a length between 40 mm and 12 mm. In our case, H. abbreviatus measured 12 mm at the last larval stage [36] and did not cause significant damage to corn plants. A study conducted in 2016 at 162 sites in Quebec showed that 5% seedling damage was observed when more than three wireworms/bait traps were found in the fields [87]. This suggests that the threshold for H. abbreviatus could be closer to three wireworms per bait trap, but this remains to be validated [87]. This low pest pressure, due in part to the prevalence of H. abbreviatus, a different wireworm species than the ones observed in other parts of Canada or the USA [88, 89, 90], could explain the lack of yield differences in our study.

In soybean, although high wireworm populations were observed in some fields, almost no damaged grains or plants were observed. Wireworms feed mainly on cereals [37, 84]; hence, soybean, a legume species, may not be an adequate food source for larvae. Although other soil insect pests could pose a threat to soybean, such as white grubs or seedcorn maggot, very small populations of those pests have been observed in monitored fields. However, they could become a problem in some years, sporadically, when harsh weather conditions are experienced [47, 48, 91, 92]. The wet springs that sometimes occur in Quebec can increase the damage caused by those pests, and insecticide seed treatments could be useful in such conditions. Soybean aphid, Aphis glycines (Matsumura), is one of the pest species targeted by neonicotinoid seed treatments. In one study [93], observations of soybean aphid populations showed that the threshold was not reached in all fields in either year. Aphids emerged too late in fields to be controlled by insecticide seed treatments, a finding also reported in other studies in the United States and Quebec [93, 94]. Overall, very low pressure associated with soil insect pests were observed in soybean in both years of the study.

Effects of neonicotinoids on corn and soybean yields

Overall, our study did not show any differences in grain yield between treated and untreated corn or soybean seed. Several factors may help explain these results, such as low pest pressure, compensatory growth, rapid decrease in neonicotinoid concentrations within the plants, or the absence of other non-abiotic stresses.

Some studies have reported an increase in yield associated with insecticide seed treatment when wireworms were present in high abundance [61] or when more than two pest species were present [51]. For example, Wilde et al. [61] evaluated the effect of seed treatments on wireworms in corn and found that this approach increased plant stands and grain yield almost 50% of the time, mainly when insects were present in high numbers. The same conclusion emerged from an overall analysis of soybean yield increases across the USA [51, 56], in which insecticide seed treatment was found to be useful only when three foliar-feeding pest species were present at the beginning of the summer. Cox and Cherney [48] showed, however, that there is high variability in soybean yield for the same varieties and seed densities at different locations in North America, and that the use of insecticide seed treatments did not provide benefits to all growers. In corn, a meta-analysis combining 15 years of U.S. data revealed that even at the highest dose used against corn rootworm, there was no significant benefit of using seed treated corn [30]. However, North et al. [59] found the opposite results in an analysis of 91 trials on 14 years in mid-south USA, with global yield gain of 700 kg/ha in corn treated with neonicotinoids. Such a high level of variability between studies could be explained by climatic conditions, which varied between sites and years, by the abundance of pest species and by the efficiency of the insecticides. Alford and Krupke [95] reported that less than 1.5% of clothianidin applied to the seeds translocate through the roots and shoots of corn plants under field conditions and that this treatment did not cover the entire window of activity of all soil insect pests. This temporally limited protection from insecticide within the plant could in part explain the variability in yield differences between treated and untreated plants in many field studies [57, 58, 61].

Overall, insect pest pressure was low in the five years of the study. Wireworm populations were below the threshold of 1 wireworm/bait trap in 69% of the soybean fields and in 92% of the corn fields. If we consider a threshold of 3 wireworms/bait traps, the threshold was reached in only 2 corn fields. White grub and seedcorn maggot numbers were also very low in all our fields. Even though some damage to seedlings was observed in corn fields and plant stands were greater in treated soybean plots, no overall differences in yield were observed.

A "stress shield" or growth facilitation effect has been observed with neonicotinoid treated seedlings in a few studies on corn, sorghum and wheat [96, 97, 98, 99]. Increased growth has been observed for neonicotinoid treated seeds compared to untreated seeds when exposed to different stresses [96, 97, 98, 99]. This "stress shield" may be observed mainly in response to drought stress or weed pressure. In our study, however, no such effect has been observed, which could be explained by compensatory growth. Compensatory growth is the increase that occurs in plant growth rate following a period of stress, such as drought, or increased plant population density [100, 101]. This compensatory growth is well documented in corn [30, 96, 100, 101, 102] and soybean [52, 103]. The stress caused by soil insect pests feeding on young seedlings could have triggered this phenomenon of compensatory growth, which would explain the lack of difference in yield.

Various IPM strategies have been developed in recent years for soil insect pests with the aim of reducing the use of insecticide seed treatment. Pest management of wireworms does not require the prophylactic use of neonicotinoids and in cases where pest densities are high, alternatives to insecticides exist. Some approaches are still being tested, such as mass trapping of adult wireworms with light traps [104], crop rotations with brown mustard or buckwheat [105], attraction to insecticide-treated wheat grown between untreated potato rows [106]; they represent alternative control measures that are under development in Canada. Other methods, such as trap crops using pea and lentil [107] or the use of entomopathogenic fungi such as Metarhizium anisopliae [108, 109, 110] could be tested on a large scale against wireworms. Furlan et al. [111] proposed a mutual funds approach covering the risk of implementing IPM programs for Italian producers, which increased farmer profits while reducing the use of pesticides. In Quebec, a decision support tool was developed based on a boosted regression analysis of all physical and landscape parameters that favour the presence of the main wireworm species in the province, H. abbreviatus. This tool is freely available online (VFF Qc, available at, and allows producers to predict the risk of encountering a high abundance of this wireworm species [87].

Our study clearly demonstrates that neonicotinoid seed treatments in corn and soybean are not justified in about 95% of the field crop acreage in the province of Quebec, which represents 500,000 ha of fields (corn, soybean and cereals). While the use of neonicotinoids is to be phased out completely in Canada by 2021 [112], other insecticide treatments are replacing them; they are based on the same marketing strategy of insurance against the risk of pest attack. With these new products, the same limited availability of untreated seed is observed as is the case for neonicotinoids. The widespread use of insecticides as seed treatments—even if the new products are potentially less harmful to the environment and human health—will not be sustainable over the long term, and will increase risk of the insects developing resistance [2, 30] along with contamination of the environment. An exponential increase has been observed in the levels of these new insecticides in rivers in Quebec since they were registered as seed treatments; they are already reaching the maximum allowable concentrations for aquatic life in some places [17]. IPM strategies based on pest densities and risk factors represent a more sustainable solution for protecting field crop from threats and for preserving the environment and human health.

Supporting information

S1 Table. Characteristics of the 84 experimental sites followed between 2012 and 2016 in corn and soybean in Quebec, Canada.

Fertilization: Organic fertilization involves the use of manure, but unspecified.



This paper is dedicated to Louis Robert, agronomist, in recognition of his integrity and his dedication to improving agriculture. The authors thank all the producers who provided access to their fields and collaborated with the research. Thanks are also extended to the members of the working team of the "Réseau d’Avertissements Phytosanitaires–Grandes Cultures" and the regional officials with the Ministère de l’Agriculture, des Pêcheries et de l’Alimentation du Québec (MAPAQ), specifically L. Bilodeau, J. Bonneville, J. Breault, B. Duval, I. Fréchette, D. Froment, J.-P. Légaré, S. Mathieu, C. Parent, E. Menkovic, A. Rondeau, Y. Faucher, and S. Goyette. The authors also thank the employees and agronomists of the advisory clubs involved in the project: Fertior, Club de Fertilisation de la Beauce, Yamasol, Dura-Sol, Cogenor, Profit-eau-sol, CAE Estrie, Gestrie-Sol, Pleine Terre, Club Conseil Les Patriotes, ConseilSol, Club Agroenvironnemental Nova-Terre, Agri-Conseil Maska, Club agroenvironnemental du Bassin Laguerre, Agrinove, Agri-Action de la Montérégie, Groupe conseil Montérégie sud, Club agri-durable, and Proconseil. Thanks are also due to the Laboratoire d’expertise et de diagnostic en Phytoprotection du MAPAQ for the initial identification of specimens in 2012 and 2013. The authors are grateful to Yves Dion for his revision of the manuscript and pertinent comments. They also thank the CEROM entomology team, namely J. de Almeida, A. Latraverse, C. Audette, and P. Hamelin, and all the summer students for all the work they did in the fields and laboratory to collect and identify insects.


  1. 1. Douglas MR, Tooker JR. Large-scale deployment of seed treatments has driven rapid increase in use of neonicotinoid insecticides and preemptive pest management in U.S. field crops. Environ Sci Technol. 2015;49:5088–5097. pmid:25793443
  2. 2. Hladik ML, Main AR, Goulson D. Environmental risks and challenges associated with neonicotinoid insecticides. Environ Sci Technol. 2018;52(6):3329–3335. pmid:29481746
  3. 3. Jeschke P, Nauen R, Schindler M, Elbert A. Overview of the status and global strategy for neonicotinoids. J Agric Food Chem. 2011;59:2897–2908. pmid:20565065
  4. 4. Simon-Delso N, Amaral-Rogers V, Belzunces LP, Bonmatin JM, Chagnon M, Downs C, et al. Systemic insecticides (neonicotinoids and fipronil): trends, uses, mode of action and metabolites. Environ Sci Pollut Res Int. 2015;22(1):5–34. pmid:25233913
  5. 5. Bonmatin JM, Giorio C, Girolami V, Goulson D, Kreutzweiser D, Krupke C, et al. Environmental fate and exposure; neonicotinoids and fipronil. Environ Sci Poll Res Int. 2015;22(1):35–67.
  6. 6. Chagnon M, Kreutzweiser D, Mitchell EAD, Morrissey CA, Noome DA, van der Sluijs JP. Risks of large-scale use of systemic insecticides to ecosystem functioning and services. Environ Sci Pollut Res Int. 2015;22(1):119–134. pmid:25035052
  7. 7. Douglas MR, Tooker JR. Meta-analysis reveals that seed-applied neonicotinoids and pyrethroids have similar negative effects on abundance of arthropod natural enemies. PeerJ. 2016;4:e2776. pmid:27957400
  8. 8. Gibbons DW, Morrissey CA Mineau P. A review of the direct and indirect effects of neonicotinoids and fipronil on vertebrate wildlife. Environ Sci Pollut Res Int. 2015;22(1):103–118. pmid:24938819
  9. 9. Goulson D. An overview of the environmental risks posed by neonicotinoid insecticides. J Appl Ecol. 2013;50:977–987.
  10. 10. Paquet-Walsh A, Bertolo A, Landry C, Deschamps L, Boily M. Interactive effects of neonicotinoids and natural ultraviolet radiation on yellow perch (Perca flavescens) larvae. Sci Total Environ. 2019;685:690–701. pmid:31203163
  11. 11. Pisa LW, Amaral-Rogers V, Belzunces LP, Bonmatin JM, Downs CA, Goulson D, et al. Effects of neonicotinoids and fipronil on non-target invertebrates. Environ Sci Poll Res. 2015;22(1):68–102.
  12. 12. van der Sluijs JP, Amaral-Rogers V, Belzunces LP, Bijleveld van Lexmond MFIJ, Bonmatin JM, Chagnon M, et al. Conclusions of the Worldwide Integrated Assessment on the risks of neonicotinoids and fipronil to biodiversity and ecosystem functioning. Environ Sci Poll Res. 2015;22(1):148–154.
  13. 13. Wood TJ, Goulson D. The environmental risks of neonicotinoid pesticides: a review of the evidence post 2013. Environ Sci Pollut Res Int. 2017; Jan;22(1):119–34.
  14. 14. Chrétien F, Giroux I, Thériault G, Gagnon P, Corriveau J. Surface runoff and subsurface tile drain losses of neonicotinoids and companion herbicides at edge-of-field. Environ Poll.2017;224:255–264.
  15. 15. Giroux I (Ministry of Agriculture of Quebec). Présence de pesticides dans l’eau au Québec: Portrait et tendances dans les zones de maïs et de soya– 2011 à 2014, Québec, Ministère du Développement durable, de l’Environnement et de la Lutte contre les changements climatiques, Direction du suivi de l’état de l’environnement, 47 p. 2015. French.
  16. 16. Giroux I (Ministry of Agriculture of Quebec). Portrait de la présence de pesticides dans l’eau souterraine près de secteurs maraîchers, vergers, vignes et petits fruits. Échantillonnage 2012 à 2014. Québec, ministère du Développement durable, de l’Environnement et de la Lutte contre les changements climatiques, Direction générale du suivi de l’état de l’environnement, 25 p. + 5 ann. 2016. French.
  17. 17. Giroux I (Ministry of Agriculture of Quebec). État de situation sur la présence de pesticides au lac Saint-Pierre. Québec, Ministère du Développement durable, de l’Environnement et de la Lutte contre les changements climatiques, Direction du suivi de l’état de l’environnement, 44 p. 2018. French.
  18. 18. Giroux, I (Ministry of Agriculture of Quebec). Présence de pesticides dans l’eau au Québec: Portrait et tendances dans les zones de maïs et de soya– 2015 à 2017, Québec, ministère de l’Environnement et de la Lutte contre les changements climatiques, Direction générale du suivi de l’état de l’environnement, 64 p. + 6 ann. 2019. French.
  19. 19. Main AR, Headley JV, Peru KM, Michel NL, Cessna AJ, Morrissey CA. Widespread use and frequent detection of neonicotinoid insecticides in wetlands of Canada’s prairie Pothole region. PLoS One.2014;9:e92821. pmid:24671127
  20. 20. Main AR, Michel NL, Cavallaro MC, Headley JV, Peru KM, Morrissey CA. Snowmelt transport of neonicotinoid insecticides to Canadian Prairie wetlands. Agri Ecosyst Environ. 2016;215:76–74.
  21. 21. Schaafsma A, Limay-Rios V, Baute T, Smith J, Xue Y. Neonicotinoid insecticide residues in surface water and soil associated with commercial maize (corn) fields in Southwestern Ontario. PLoS One.2015;10(2) e0118139. pmid:25710560
  22. 22. Samson-Robert O, Labrie G, Chagnon M, Fournier V. Neonicotinoid-contaminated puddles of water represent a risk of intoxication for honey bees. PLoS One.2014;9(12):e108443. pmid:25438051
  23. 23. Samson-Robert O, Labrie G, Mercier PL, Chagnon M, Derome N, Fournier V. Increased acetylcholinesterase expression in bumble bees during neonicotinoid-coated corn sowing. Sci Rep (Nature).2015;5(1):12636.
  24. 24. Samson-Robert O, Labrie G, Chagnon M, Fournier V. Planting of neonicotinoid-coated corn raises honey bee mortality and sets back colony development. PeerJ,2017;5:e3670 pmid:28828265
  25. 25. Tsvetkov N, Samson-Robert O, Sood K, Patel HS, Malena DA, Gajiwala PH, et al. Chronic exposure to neonicotinoids reduces honeybee health near corn crops. Science.2017;356(6345):1395–1397. pmid:28663503
  26. 26. Ministère du Développement durable, de l’Environnement et de la Lutte contre les changements climatiques (MDDELCC). Stratégie québécoise sur les pesticides 2015–2018. 2015.
  27. 27. Elbert A, Haas M, Springer B, Thielert W, Nauen R. Applied aspects of neonicotinoid uses in crop protection. Pest Manag Sci.2008;64:1099–105. pmid:18561166
  28. 28. Tomizawa M, Casida JE. Neonicotinoid insecticide toxicology: mechanisms of selective action. Ann Rev Pharm Toxicol. 2005;45:247–268. pmid:15822177
  29. 29. Krupke CH, Holland JD, Long EY, Eitzer BD. Planting of neonicotinoid-treated maize poses risks for honey bees and non-target organisms over a wide area without consistent crop yield benefit. J Appl Ecol. 2017;54(5):1449–1458.
  30. 30. Alford AM, Krupke CH. A meta-analysis and economic evaluation of neonicotinoid seed treatments and other prophylactic insecticides in Indiana maize from 2000–2015 with IPM recommendations. J Econ Entomol. 2018;111(2):689–699. pmid:29385499
  31. 31. Traugott M, Benefer CM, Blackshaw RP, Van Herk WG, Vernon RS. Biology, ecology, and control of Elateridae beetles in agricultural land. Ann Rev Entomol. 2015;60:313–34
  32. 32. Johnson PJ. Chapter 58. Family Elateridae, Leach 1815. In: Arnett RH Jr, Thomas MC, Skelley PE, Frank JH, editors. American Beetles, Vol. 2: Polyphaga: Scarabaeoidea through Curculionoidea. CRC Press LLC; 2002. p 160–173.
  33. 33. Bousquet Y, Bouchard P, Davies AE, Sikes DS. Checklist of beetles (Coleoptera) of Canada and Alaska. Second Edition. ZooKeys.2013;360:1–44.
  34. 34. Glen R, King KM, Arnason AP. The identification of wireworms of economic importance in Canada. Can J Res. 1943;21:358–88.
  35. 35. Van Herk WG, Vernon RS. Click beetles and wireworms (Coleoptera: Elateridae) of Alberta, Saskatchewan, and Manitoba. In: Giberson DJ, Carcamo HA, editors. Arthropods of Canadian Grasslands, Vol 4: Biodiversity and Systematics Part 2. Biological Survey of Canada, Ottawa, Canada; 2014. p. 87–117.
  36. 36. Saguez J, Latraverse A, de Almeida J, van Herk WG, Vernon RS, Légaré JP et al. Wireworm in Quebec field crops: specific community composition in North America. Environ Entomol. 2017;46(4):814–25. pmid:28881953
  37. 37. Barsics F, Haubruge E, Verheggen FJ. Wireworms’ management: An overview of the existing methods, with particular regards to Agriotes spp. (Coleoptera: Elateridae). Insects 2013;4:117–52. pmid:26466799
  38. 38. Parker WE, Howard JJ. The biology and management of wireworms (Agriotes spp.) on potato with particular reference to the U.K. Agric Forest Entomol.2001;3:85–98.
  39. 39. Fleischer SJ, Gesell S. Insect of the month: seedcorn maggot in vine and other vegetable crops. Veg Gaz. 1999;3:1–2.
  40. 40. Higley LG, Pedigo LP. Seedcorn maggot (Diptera: Anthomyiidae). Population, biology and aestivation in central Iowa. Environ Entomol.1984;13:1436–1442.
  41. 41. Valenciano JB, Casquero PA, Boto JA. Evaluation of the occurrence of bean plants (Phaseolus vulgaris L.) affected by bean seed fly, Delia platura (Meigen), grown under different sowing techniques and with different forms of pesticide application. Field Crop Res.2004;(85):103–109.
  42. 42. Whale J. Pest of the month: seedcorn maggots. Am Veg Grower., 2002;3:1–2.
  43. 43. Hammond RG. Effects of rye cover crop management on seedcorn maggot (Diptera: Anthomyiidae) populations in soybeans. Environ Entomol. 1984;5;13:1302–1305.
  44. 44. Hammond RG. Influence of cover crops and tillage on seedcorn maggot (Diptera: Anthomyiidae) populations in soybeans. Environ Entomol. 1990;19:510–4.
  45. 45. Hammond RG, Cooper RL. Interaction of planting times following the incorporation of a living, green cover crop and control measures on seedcorn maggot populations in soybean. Crop Protect. 1993;12:539–43.
  46. 46. Bohner H, Earl HK. Increasing profits through precision seeding and seed treatments. Crop Advances: Field Crop Reports 2009. 5 p.
  47. 47. Cox WJ, Shields E, Cherney JH. Planting dates and seed treatment effects on soybean in the Northeastern United States. Agron. J. 2008;100:1662–65.
  48. 48. Cox WJ, Cherney JH. Location, variety, and seeding rate interactions with soybean seed-applied insecticide/fungicides. Agron J. 2011;103(5):1366–71.
  49. 49. Magalhaes LC, Hunt TE, Siegfried BD. Efficacy of neonicotinoid seed treatments to reduce soybean aphid populations under field and controlled conditions in Nebraska. J Econ Entomol. 2009;102:187–95 pmid:19253636
  50. 50. McCarville MT, O’Neal ME. Soybean aphid (Aphididae: Hemiptera) population growth as affected by host plant resistance and an insecticidal seed treatment. J Econ Entomol. 2013;106(3):1302–09. pmid:23865195
  51. 51. Myers C, Hill E. Benefits of neonicotinoid seed treatments to soybean production. Memorandum to United States Environmental Protection Agency, 18 p. 2014.
  52. 52. North JH, Gore J, Catchot AL, Stewart SD, Lorenz GM, Musser FT, et al. Value of neonicotinoid insecticide seed treatments in Mid-South soybean (Glycine max) production systems. J Econ Entomol. 2016;109(3):1156–60. pmid:27091814
  53. 53. Penn HJ, Dale AM. Imidacloprid seed treatments affect individual ant behavior and community structure, but not egg predation, pest abundance or soybean yield. Pest Manag. 2017;73:1625–32.
  54. 54. Reisig DD, Herbert DA, Malone S. Impact of neonicotinoid seed treatments on thrips (Thysanoptera: Thripidae) and soybean yield in Virginia and North Carolina. J Econ Entomol. 2012;105:884–9. pmid:22812126
  55. 55. Seagraves MP, Lundgren JG. Effects of neonicotinoid seed treatments on soybean aphid and its natural enemies. J Pest Sci. 2012;85(1):125–32.
  56. 56. Mourtzinis S, Krupke CH, Esker PD, Varenhorst A, Arneson NJ, Bradley CA et al. Neonicotinoid seed treatments of soybean provide negligible benefits to US farmers. Sci Rep. 2019;9:11207 pmid:31501463
  57. 57. Cox WJ, Shields E, Cherney JH. The effect of clothianidin seed treatments on corn growth following soybean. Crop Sci. 2007;47:2482–5.
  58. 58. Jordan TA, Youngman RR, Laub CL, Tiwari S, Kuhar TP, Balderson TK, et al. Fall soil sampling method for predicting spring infestation of white grubs (Coleoptera: Scarabaeidae) in corn and the benefits of clothianidin seed treatment in Virginia. Crop Prot. 2012;39:57–2.
  59. 59. North JH, Gore J, Catchot AL, Stewart SD, Lorenz GM, Musser FR, et al. Value of neonicotinoid insecticide seed treatments in Mid-South corn (Zea mays) production systems. J Econ Entomol. 2018;111(1):187–2. pmid:29177425
  60. 60. Pons X, Albajes R. Control of maize pests with imidacloprid seed dressing treatment in Catalonia (NE Iberian Peninsula) under traditional crop conditions. Crop Prot. 2002;21:943–0.
  61. 61. Wilde G, Roozeboom K, Claassen M, Janssen K, Witt M. Seed treatment for control of early-season pests of corn and its effect on yield. Agric Urban Entomol. 2004;21(2):75–85
  62. 62. Glen R. Larvae of the elaterid beetles of the tribe Lepturoidini (Coleoptera: Elateridae). Smith Misc Coll. 1950;(111): 1–246.
  63. 63. Becker EC. Revision of the nearctic species of Agriotes (Coleoptera: Elateridae). Can Entomol. 1956;88(Suppl. 1): 5–101.
  64. 64. Becker EC. Elateridae (Elateroidae). In Stehr FW, editor, Immature Insects. Kendal/Hunt, Dubuque, IA. 1991. Pp 409–410.
  65. 65. Stehr F. Immature Insects. Vol. 2. Kendall-Hunt Publishing Company, Dubuque, FL. 1991.
  66. 66. Pinheiro JC, Bates DM. Linear Mixed-Effects Models: Basic Concepts and Examples. In: Mixed-Effects Models in S and S-PLUS. Statistics and Computing. Springer, New York, NY. 2000.
  67. 67. Bolker BM, Brooks ME, Clark CJ, Geange SW, Poulsen JR et al. Generalized linear mixed models: a practical guide for ecology and evolution. Trends Ecol. Evol. 2009;24(3):127–135. pmid:19185386
  68. 68. Zuur A, Ieno EN, Walker N, Saveliev AA, Smith GM. Mixed effects models and extensions in ecology with R. Springer, New York, NY. 2009.
  69. 69. Zuur A, Ieno EN, Elphick CS. A protocol for data exploration to avoid common statistical problems. Methods Ecol. Evol. 2010;1:3–14.
  70. 70. R Core Team. R: A language and environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria. URL 2018.
  71. 71. Bates D, Maechler M, Bolker B, Walker S. Fitting linear mixed-effects models using lme4. J. Stat. Soft. 2015;67(1):1–48.
  72. 72. Barton K. MuMIn: Multi-Model Inference. R package version 1.43.6. 2019.
  73. 73. Labrie G, Rondeau A, Faucher Y, Mathieu S, Perreault Y, Tremblay G. (Ministry of Agriculture of Quebec). Impact des traitements insecticides de semences sur les insectes ravageurs du sol et sur les paramètres agronomiques dans la culture du maïs grain. Rapport No CERO-1-LUT-11-1582, Prime-Vert Volet 11.1. 2014.
  74. 74. Barzman M, Bàrberi P, Nicholas A, Birch E, Boonekamp P, Dachbrodt-Saaydeh S, et al. Eight principles of integrated pest management. Agron Sustain Dev. 2015;35:1199–15.
  75. 75. Vasileiadis VP, Sattin M, Otto S, Veres A, Pálinkás Z, Ban R, et al. Crop protection in European maize-based cropping systems: current practices and recommendations for innovative integrated pest management. Agric Syst. 2011;104:533–0.
  76. 76. Vernon RS, Vernon RS, Vojtko RB, Snow S, Fortier J, Fortin C. Contact behaviour and mortality of wireworms exposed to six classes of insecticide applied to wheat seed. J Pest Sci. 2015;88: 717–39.
  77. 77. Vernon RS, Vernon RS, Clodius M, Harding C. Wireworm management I: Stand protection versus wireworm mortality with wheat seed treatments. J Econ Entomol. 2009;102(6):2126–36. pmid:20069841
  78. 78. Furlan L. IPM thresholds for Agriotes wireworm species in maize in Southern Europe. J Pest Sci. 2014;87(4):609–17.
  79. 79. Lafrance J. Emergence and flight of click beetles (Coleoptera: Elateridae) in organic soils of southwestern Quebec. Can Entomol. 1963;95:873–8.
  80. 80. Lafrance J. The seasonal movement of wireworms (Coleoptera: Elateridae) in relation to soil moisture and temperature in the organic soils of southwestern Quebec. Can Entomol. 1968;100:801–7.
  81. 81. Lafrance J, Cartier JJ. Distribution of wireworm population (Coleoptera: Elateridae) in unfrozen and frozen organic soils of southwestern Quebec. Phytoprotection 1964;45:83–7.
  82. 82. Levesque C, Levesque GY. Abundance and seasonal activity of Elateroidae (Coleoptera) in a raspberry plantation and adjacent sites in southern Quebec, Canada. Coleopts. Bull. 1993;47:269–7.
  83. 83. Chabert A, Blot T. Estimation des populations larvaires de taupins par un piège attractif. Phytoma. 1992;436:26–0.
  84. 84. Traugott M, Benefer CM, Blackshaw RP, van Herk WG, Vernon RS. Biology, ecology, and control of Elaterid beetles in agricultural land. Annu Rev Entomol. 2015;60:313–34. pmid:25341096
  85. 85. Hall DG, Cherry RH. Effect of temperature in flooding to control the wireworm Melanotus communis (Coleoptera: Elateridae). Florida Entomol. 1993;76:155–0.
  86. 86. Kuhar TP, Speese J, Whalen J, Alvarez JM, Alyokhin A, Ghidiu G. Current status of insecticidal control of wireworms in potatoes. Pest Outl. 2003;14(6):265–7.
  87. 87. Labrie G, Saguez J, Latraverse A (Ministry of Agriculture). Élaboration et validation d’un arbre décisionnel pour l’utilisation de semences traitées aux néonicotinoïdes contre les vers fil-de-fer dans le maïs. Projet Prime-Vert PV-3.2-2015-002. 2017a.
  88. 88. Lindroth E, Clark TL. Phylogenetic analysis of an economically important species complex of wireworms (Coleoptera: Elateridae) in the Midwest. J Econ Entomol. 2009; 102(2):743–9. pmid:19449656
  89. 89. Riley TJ, Keaster AJ. A pictorial field key to wireworms attacking corn in the Midwest. U.S. Dep Agric./ SEA Extension Integrated Pest Management Program. 1981.
  90. 90. Benefer CM, Van Herk WG, Ellis JS, Blackshaw RS, Vernon RS, Knight ME. The molecular identification and genetic diversity of economically important wireworm species (Coleoptera: Elateridae) in Canada. J Pest Sci. 2013;86:19–7.
  91. 91. Funderbunk J., Higley LG, Pedigo P. Seed corn maggot (Diptera: Anthomyiidae) phenology in central Iowa and examination of a thermal-unit system to predict development under field conditions. Environ Entomol. 1984;13:105–9.
  92. 92. Hesler LS, Allen KC, Luttrell RG, Sappington TW, Papiernik SK. Early-season pests of soybean in the United States and factors that affect their risk of infestation. J Pest Manag. 2018;9(1):1–15.
  93. 93. Krupke CH, Alford AM, Culleen EM, Hodgson EW, Knodel JJ, McCornack B, et al. Assessing the value and pest management window provided by neonicotinoid seed treatments, for management of soybean aphid (Aphis glycines Matsumura) in the Upper Midwestern United States. Pest Manag Sci. 2017b;7310:2184–93.
  94. 94. Maisonhaute J-É, Labrie G, Lucas E. Population dynamics of the soybean aphid (Hemiptera: Aphididae) in Quebec (Canada). J Econ Entomol. 2016;109(3):1465–8. pmid:27016599
  95. 95. Alford A, Krupke CH. Translocation of the neonicotinoid seed treatment clothianidin in maize. PLoS ONE. 2017;12:e0173836. pmid:28282441
  96. 96. Cataneo AC, Nunes JC, Ferreira LC, Corniani N, Carvalho JC, Sanine MS. Enhancement of soybean seed vigour as affected by thiamethoxam under stress conditions. In: Soybean Physiology and Biochemistry, El-Shemy H, editor, 1st ed., InTech, Croatia; 2011. p. 231–274.
  97. 97. Afifi M, Lee E, Lukens L, Swanton C. Thiamethoxam as a seed treatment alters the physiological response of maize (Zea mays) seedlings to neighbouring weeds. Pest Manag Sci. 2015;71(4):505–14. pmid:24700817
  98. 98. Ford KA, Casida JE, Chandran DAG, Gulevich RA, Okrent KA, Durkin R, et al. Neonicotinoid insecticides induce salicylate associated plant defense responses. PNAS 2010;107:17527–2. pmid:20876120
  99. 99. Macedo WR, Castro CPR. Thiamethoxam: Molecule moderator of growth, metabolism and production of spring wheat. Pest Biochem Physiol. 2011;100:299–4.
  100. 100. Wang XL, Wang JJ, Sun RH, Hou XH, Zhao W, Shi J, et al. Correlation of the corn compensatory growth mechanism after post-drought rewatering with cytokinin induced by root nitrate absorption. Agr Wat Manag. 2016;166:77–5.
  101. 101. Wang XL, Qin RR, Sun RH, Hou XG, Qi L, Shi J. Effects of plant population density and root-induced cytokinin on the corn compensatory growth during post-drought rewatering. PLoS ONE. 2018;13(6):e0198878. pmid:29953445
  102. 102. Kahler AL, Olness AE, Sutter GR, Dybing CD, Devine J. Root damage by western corn rootworm and nutrient content in maize. Agron J. 1985;77:769–4.
  103. 103. Murillo-Williams A, Pedersen P. Arbuscular mycorrhizal colonization response to three seed-
  104. 104. Isaacs J. New wireworm trap developed in PEI. Grains West, Fall 2016. 2016.
  105. 105. Noronha C. Procedure for using rotation crops as a wireworm management strategy. 2017
  106. 106. Vernon RS, van Herk WG, Clodius M, Tolman J. Companion planting attract-and-kill method for wireworm management in potatoes. J Pest Sci, 2015;89:375–389.
  107. 107. Sharma ARK, Sandhi S, Briar S, Miller JH, Reddy JVP. Assessing the performance of pea and lentil at different seeding densities as trap crops for the management of wireworms in spring wheat. J Appl Entomol. 2018;143(4):460–469.
  108. 108. Kabaluk T, Ericsson J. Seed treatment increases yield of field corn when applied for wireworm control. Agron J. 2007;99(5):1377–81.
  109. 109. Kabaluk T, Vernon RS, Goettel MS. Mortality and infection of wireworm, Agriotes obscurus (Coleoptera: Elateridae), with inundative field applications of Metarhizium anisopliae. Phytoprotection 2007;88(2):51–6.
  110. 110. Reddy GVP, Tangtrakulwan K, Wu S, Miller JH, Ophus VL, Prewett J. Evaluation of the effectiveness of entomopathogens for the management of wireworms (Coleoptera: Elateridae) on spring wheat. J Invert Patho. 2014;120:43–9.
  111. 111. Furlan L, Pozzebon A, Duso C, Simon-Delso N, Sanchez-Bayo F, Marchand PA. An update of the Worldwide Integrated Assessment (WIA) on systemic insecticides. Part 3: alternatives to systemic insecticides. Environ Sci Poll Res. 2018. pmid:29478160
  112. 112. Health Canada. 2018. Health Canada to consult on plan to phase out most uses of the neonicotinoids clothianidin and thiamethoxam.