Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada.
Toxicology Centre, University of Saskatchewan, Saskatoon, Saskatchewan, Canada; School of Environment and Sustainability, University of Saskatchewan, Saskatoon, Saskatchewan, Canada; Institute of Loess Plateau, Shanxi University, Taiyuan, Shanxi, PR China.
Environ Pollut. 2018 Dec;243(Pt B):1727-1739. doi: 10.1016/j.envpol.2018.09.008. Epub 2018 Sep 5.
Neonicotinoid insecticide mixtures are frequently detected in aquatic environments in agricultural regions. Recent laboratory studies have indicated that neonicotinoid mixtures can elicit greater-than-additive toxicity in sensitive aquatic insects (e.g. Chironomus dilutus). However, this has yet to be validated under field conditions. In this study, we compared the chronic (28- and 56-day) toxicity of three neonicotinoids (imidacloprid, clothianidin, and thiamethoxam) and their mixtures to natural aquatic insect communities. Using experimental in-situ enclosures (limnocorrals), we exposed wetland insects to single-compounds and binary mixtures at equitoxic concentrations (1 toxic unit under the principle of Concentration Addition). We assessed the composition of all emerged insect taxa and the cumulative Chironomidae emergence and biomass over time. In treated limnocorrals, there were subtle shifts in community composition, with greater mean proportions of emergent Trichoptera and Odonata. Cumulative emergence and biomass increased over time and there was a significant interaction between time and treatment. At 28 days, cumulative Chironomidae emergence and biomass were not significantly different between neonicotinoid treatments and controls. However, cumulative emergence in the imidacloprid, clothianidin, and clothianidin-thiamethoxam treatments were 42%, 20%, and 44% lower than predicted from applied doses. At 56 days, effects on cumulative emergence and biomass were significant for imidacloprid, clothianidin, and the clothianidin-thiamethoxam mixture. Contrary to laboratory predictions, mixtures were not more toxic than single compounds under semi-controlled field settings. Furthermore, only clothianidin significantly shifted sex-ratios towards female-dominated populations. Results showed that the responses of natural Chironomidae populations to neonicotinoids and their mixtures cannot be adequately predicted from laboratory-derived single-species models, and although occasional overdosing may have influenced the magnitude of effects, reductions in Chironomidae emergence and biomass can occur at average neonicotinoid concentrations below some current water quality guidelines. Therefore, neonicotinoid guidelines should be revised to ensure that Chironomidae and other sensitive aquatic insects inhabiting agricultural wetlands are adequately protected.
新烟碱类杀虫剂混合物在农业区的水生环境中经常被检测到。最近的实验室研究表明,新烟碱类杀虫剂混合物对敏感水生昆虫(如摇蚊属幼虫)会产生大于相加的毒性。然而,这尚未在野外条件下得到验证。在这项研究中,我们比较了三种新烟碱类杀虫剂(吡虫啉、噻虫啉和噻虫嗪)及其混合物对自然水生昆虫群落的慢性(28 天和 56 天)毒性。使用实验原位围隔(limnocorrals),我们以等毒性浓度(浓度加和原则下的 1 个毒性单位)将湿地昆虫暴露于单一化合物和二元混合物中。我们评估了所有出现的昆虫分类群的组成以及随时间推移的累积摇蚊科昆虫的出现和生物量。在处理过的 limnocorrals 中,群落组成发生了微妙的变化,出现的毛翅目和蜻蜓目昆虫的比例更大。累积出现和生物量随时间增加,且时间和处理之间存在显著的相互作用。在 28 天时,新烟碱类处理与对照之间的累积摇蚊科昆虫的出现和生物量没有显著差异。然而,在吡虫啉、噻虫啉和噻虫啉-噻虫嗪处理中,累积出现的摇蚊科昆虫分别比预期应用剂量低 42%、20%和 44%。在 56 天时,吡虫啉、噻虫啉和噻虫啉-噻虫嗪混合物对累积出现和生物量的影响显著。与实验室预测相反,在半控制野外环境下,混合物并不比单一化合物更具毒性。此外,只有噻虫啉显著将性别比例向雌性主导种群倾斜。结果表明,自然摇蚊科种群对新烟碱类杀虫剂及其混合物的反应不能从实验室得出的单一物种模型中得到充分预测,尽管偶尔过量用药可能会影响影响的程度,但在低于某些当前水质标准的平均新烟碱类浓度下,摇蚊科昆虫的出现和生物量可能会减少。因此,新烟碱类杀虫剂指南应进行修订,以确保栖息在农业湿地中的摇蚊科和其他敏感水生昆虫得到充分保护。