INRAE, UR 406 A&E, Laboratoire de Toxicologie Environnementale, F-84000, Avignon, France.
INRAE, UR 406 A&E, Laboratoire de Toxicologie Environnementale, CS 40509, 84914, Avignon Cedex 9, France.
Environ Sci Pollut Res Int. 2021 Aug;28(31):42807-42820. doi: 10.1007/s11356-021-13747-3. Epub 2021 Apr 6.
During all their life stages, bees are exposed to residual concentrations of pesticides, such as insecticides, herbicides, and fungicides, stored in beehive matrices. Fungicides are authorized for use during crop blooms because of their low acute toxicity to honey bees. Thus, a bee that might have been previously exposed to pesticides through contaminated food may be subjected to fungicide spraying when it initiates its first flight outside the hive. In this study, we assessed the effects of acute exposure to the fungicide in bees with different toxicological statuses. Three days after emergence, bees were subjected to chronic exposure to the insecticide imidacloprid and the herbicide glyphosate, either individually or in a binary mixture, at environmental concentrations of 0.01 and 0.1 μg/L in food (0.0083 and 0.083 μg/kg) for 30 days. Seven days after the beginning of chronic exposure to the pesticides (10 days after emergence), the bees were subjected to spraying with the fungicide difenoconazole at the registered field dosage. The results showed a delayed significant decrease in survival when honey bees were treated with the fungicide. Fungicide toxicity increased when honey bees were chronically exposed to glyphosate at the lowest concentration, decreased when they were exposed to imidacloprid, and did not significantly change when they were exposed to the binary mixture regardless of the concentration. Bees exposed to all of these pesticide combinations showed physiological disruptions, revealed by the modulation of several life history traits related mainly to metabolism, even when no effect of the other pesticides on fungicide toxicity was observed. These results show that the toxicity of active substances may be misestimated in the pesticide registration procedure, especially for fungicides.
在其所有生命阶段,蜜蜂都会接触到残留在蜂箱基质中的杀虫剂、除草剂和杀菌剂等农药,这些农药都有登记。由于对蜜蜂的急性毒性低,杀菌剂被批准在作物花期使用。因此,一只可能因食用受污染的食物而接触过杀虫剂的蜜蜂,在首次飞出蜂巢时可能会受到杀菌剂的喷洒。在这项研究中,我们评估了不同毒理学状态的蜜蜂急性接触杀菌剂的影响。出房后第 3 天,蜜蜂在食物中以环境浓度(0.0083 至 0.083μg/kg)接触 30 天的单独或二元混合物慢性接触杀虫剂吡虫啉和除草剂草甘膦,浓度分别为 0.01 和 0.1μg/L。在慢性接触农药 7 天后(出房后第 10 天),用登记田间剂量的杀菌剂苯醚甲环唑对蜜蜂进行喷雾处理。结果表明,当蜜蜂接触杀菌剂时,其生存能力显著延迟下降。当蜜蜂以最低浓度慢性接触草甘膦时,杀菌剂毒性增加,接触吡虫啉时毒性降低,接触二元混合物时毒性没有明显变化,而无论浓度如何。接触这些农药组合的蜜蜂表现出生理紊乱,这是通过调节与代谢有关的几个生命史特征来揭示的,即使没有观察到其他农药对杀菌剂毒性的影响。这些结果表明,在农药登记程序中,活性物质的毒性可能被错误估计,尤其是杀菌剂。