15 research outputs found

    L'implication du mouvement syndical dans le développement économique communautaire

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    Mémoire numérisé par la Direction des bibliothèques de l'Université de Montréal

    Increased acetylcholinesterase expression in bumble bees during neonicotinoid-coated corn sowing

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    While honey bee exposure to systemic insecticides has received much attention, impacts on wild pollinators have not been as widely studied. Neonicotinoids have been shown to increase acetylcholinesterase (AChE) activity in honey bees at sublethal doses. High AChE levels may therefore act as a biomarker of exposure to neonicotinoids. This two-year study focused on establishing whether bumble bees living and foraging in agricultural areas using neonicotinoid crop protection show early biochemical signs of intoxication. Bumble bee colonies (Bombus impatiens) were placed in two different agricultural cropping areas: 1) control (≥3 km from fields planted with neonicotinoid-treated seeds) or 2) exposed (within 500 m of fields planted with neonicotinoid-treated seeds) and maintained for the duration of corn sowing. As determined by Real Time qPCR, AChE mRNA expression was initially significantly higher in bumble bees from exposed sites, then decreased throughout the planting season to reach a similar endpoint to that of bumble bees from control sites. These findings suggest that exposure to neonicotinoid seed coating particles during the planting season can alter bumble bee neuronal activity. To our knowledge, this is the first study to report in situ that bumble bees living in agricultural areas exhibit signs of neonicotinoid intoxication

    Une chambre d’écho : Tendre l’oreille

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    Planting of neonicotinoid-coated corn raises honey bee mortality and sets back colony development

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    Worldwide occurrences of honey bee colony losses have raised concerns about bee health and the sustainability of pollination-dependent crops. While multiple causal factors have been identified, seed coating with insecticides of the neonicotinoid family has been the focus of much discussion and research. Nonetheless, few studies have investigated the impacts of these insecticides under field conditions or in commercial beekeeping operations. Given that corn-seed coating constitutes the largest single use of neonicotinoid, our study compared honey bee mortality from commercial apiaries located in two different agricultural settings, i.e. corn-dominated areas and corn-free environments, during the corn planting season. Data was collected in 2012 and 2013 from 26 bee yards. Dead honey bees from five hives in each apiary were counted and collected, and samples were analyzed using a multi-residue LC-MS/MS method. Long-term effects on colony development were simulated based on a honey bee population dynamic model. Mortality survey showed that colonies located in a corn-dominated area had daily mortality counts 3.51 times those of colonies from corn crop-free sites. Chemical analyses revealed that honey bees were exposed to various agricultural pesticides during the corn planting season, but were primarily subjected to neonicotinoid compounds (54% of analysed samples contained clothianidin, and 31% contained both clothianidin and thiamethoxam). Performance development simulations performed on hive populations’ show that increased mortality during the corn planting season sets back colony development and bears contributions to collapse risk but most of all, reduces the effectiveness and value of colonies for pollination services. Our results also have implications for the numerous large-scale and worldwide-cultivated crops that currently rely on pre-emptive use of neonicotinoid seed treatments

    Neonicotinoid-Contaminated Puddles of Water Represent a Risk of Intoxication for Honey Bees

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    <div><p>In recent years, populations of honey bees and other pollinators have been reported to be in decline worldwide. A number of stressors have been identified as potential contributing factors, including the extensive prophylactic use of neonicotinoid insecticides, which are highly toxic to bees, in agriculture. While multiple routes of exposure to these systemic insecticides have been documented for honey bees, contamination from puddle water has not been investigated. In this study, we used a multi-residue method based on LC-MS/MS to analyze samples of puddle water taken in the field during the planting of treated corn and one month later. If honey bees were to collect and drink water from these puddles, our results showed that they would be exposed to various agricultural pesticides. All water samples collected from corn fields were contaminated with at least one neonicotinoid compound, although most contained more than one systemic insecticide. Concentrations of neonicotinoids were higher in early spring, indicating that emission and drifting of contaminated dust during sowing raises contamination levels of puddles. Although the overall average acute risk of drinking water from puddles was relatively low, concentrations of neonicotinoids ranged from 0.01 to 63 µg/L and were sufficient to potentially elicit a wide array of sublethal effects in individuals and colony alike. Our results also suggest that risk assessment of honey bee water resources underestimates the foragers' exposure and consequently miscalculates the risk. In fact, our data shows that honey bees and native pollinators are facing unprecedented cumulative exposure to these insecticides from combined residues in pollen, nectar and water. These findings not only document the impact of this route of exposure for honey bees, they also have implications for the cultivation of a wide variety of crops for which the extensive use of neonicotinoids is currently promoted.</p></div

    Le décrochage scolaire : approche clinique et psychopathologique

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    Comprend des références bibliographique

    Risk assessment of puddle water during corn planting and one month after completion (2012–2013).

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    <p>* Acute oral toxicity (AOT) values at 24 hours <a href="http://www.plosone.org/article/info:doi/10.1371/journal.pone.0108443#pone.0108443-Laurino1" target="_blank">[83]</a>.</p>†<p>Conversions are based on the drinking water intake rate of 0.047 ml (EFED & PMRA 2012).</p>‡<p>RQ  =  Risk Quotient.</p>§<p>Mean for detections> LOQ.</p><p>Risk assessment of puddle water during corn planting and one month after completion (2012–2013).</p

    Pesticide concentrations found in puddle water samples taken from a corn field in 2012 and 2013, when planting was in progress.

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    <p>* Class: FUNG  =  fungicide, HERB  =  herbicide, NEO  =  neonicotinoid, PS  =  partially systemic, S =  systemic.</p>†<p>LOQ  =  limit of quantification (µg/L).</p>‡<p>Mean and SEM for detections> LOQ.</p><p>Pesticide concentrations found in puddle water samples taken from a corn field in 2012 and 2013, when planting was in progress.</p
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