吡虫啉和噻虫嗪的二元混合物似乎不会对黑头鲦鱼幼虫造成附加毒性。

IF 3.6 Q2 TOXICOLOGY
Frontiers in toxicology Pub Date : 2023-11-20 eCollection Date: 2023-01-01 DOI:10.3389/ftox.2023.1282817
Anya J Jeninga, Nicole Kooij, Elisabeth Harrahy, Tisha C King-Heiden
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引用次数: 0

摘要

简介:由于大量使用新烟碱类杀虫剂,全球地表水中都发现了这类杀虫剂,其中吡虫啉(IM)和噻虫嗪(TM)经常一起出现。新烟碱类杀虫剂是无脊椎动物烟碱乙酰胆碱受体(nAChR)的选择性激动剂,可导致麻痹和死亡。虽然对脊椎动物没有明显毒性,但越来越多的证据表明,长期接触单个新烟碱类会对鱼类健康造成不良影响。这项研究考察了长期接触吡虫啉(IM)和噻虫嗪(TM)的二元混合物是否会比单独接触其中一种杀虫剂对黑头呆鱼(Pimephales promelas)幼虫的毒性更大。材料和方法:将胚胎暴露于 1:1 的 IM 和 TM 混合物(每种杀虫剂的浓度分别为 0.2、2、20、200 或 2,000 μg/L)或 1:5、1:10 或 1:20 的 IM 和 TM 混合物(0.02 μg/L 的 IM 与 0.1、0.2 或 0.4 μg/L 的 TM)中,共持续 8 天。对存活率、发育毒性、胚胎运动活性和惊吓逃逸反应进行了量化。结果显示暴露于每种杀虫剂含量大于 2 μg/L 的 1:1 混合物后,存活率和生长率降低,孵化率降低,但暴露于含有环境相关浓度的混合物后,存活率和生长率降低,孵化率降低。急性接触 1:1 混合物不会改变胚胎的运动活动;然而,长期接触这些混合物会导致胚胎运动轻微但显著的下降。只有高浓度 IM 和 TM 的 1:1 混合物才会通过增加反应潜伏期来改变惊吓逃逸反应;然而,相当一部分暴露于 1:1 混合物的鱼类的潜伏期和爆发速度都发生了改变。综上所述,这些激活 nAChR 的行为指标表明,在混合物中,尽管新烟碱类物质对 nAChR 的亲和力较低,但仍可能干扰 nAChR 信号转导。结论我们的研究结果表明,IM 和 TM 的二元混合物的毒性主要由 IM 驱动,与我们之前单独评估每种新烟碱的研究相比,IM 和 TM 的混合物似乎不会产生明显的叠加毒性。鉴于新烟碱类杀虫剂混合物在鱼类中的毒理学数据有限,需要进一步研究,以更好地了解这些杀虫剂可能对水生生态系统造成的生态风险。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Binary mixtures of imidacloprid and thiamethoxam do not appear to cause additive toxicity in fathead minnow larvae (Pimephales promelas).

Introduction: Considerable use of neonicotinoid insecticides has resulted in their detection in surface waters globally, with imidacloprid (IM) and thiamethoxam (TM) frequently found together. Neonicotinoids are selective agonists for invertebrate nicotinic acetylcholine receptors (nAChR) leading to paralysis and death. While not overtly toxic to vertebrates, growing evidence suggests that chronic exposure to individual neonicotinoids can cause adverse health effects in fish. This work examined whether chronic exposure to binary mixtures of imidacloprid (IM) and thiamethoxam (TM) would be more toxic to fathead minnow (Pimephales promelas) larvae than either insecticide alone. Materials and Methods: Embryos were exposed to a 1:1 mixture of IM and TM (0.2, 2, 20, 200 or 2,000 μg/L of each pesticide) or a 1:5, 1:10, or 1:20 mixture of IM and TM (0.02 μg/L of IM with 0.1, 0.2, or 0.4 μg/L of TM) for a total of 8 days. Survival, developmental toxicity, embryonic motor activity, and startle escape responses were quantified. Results: Survival and growth were reduced, and hatching induced by exposure to a 1:1 mixture containing > 2 μg/L of each insecticide, but not following exposure to mixtures containing environmentally-relevant concentrations. Acute exposure to a 1:1 mixture did not alter embryonic motor activity; however, chronic exposure to these mixtures resulted in a slight but significant decrease in embryonic movements. Only 1:1 mixtures of high concentrations of IM and TM altered the startle escape response by increasing latency of response; however, a significant proportion of fish exposed to 1:1 mixtures had altered latency and burst speed. Taken together, these behavioral indicators of nAChR activation suggest that in mixtures, neonicotinoids could interfere with nAChR signaling despite their low affinity for the nAChR. Conclusion: Our findings suggest that toxicity of binary mixtures of IM and TM is primarily driven by IM, and that mixtures of IM with TM do not appear to cause significant additive toxicity when compared with our previous studies evaluating each neonicotinoid alone. Given the limited toxicological data available for mixtures of neonicotinoid insecticides in fish, further study is required to better understand the ecological risks these insecticides may pose to aquatic ecosystems.

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