PPG-SEA and NEEA/CRHEA/SHS, São Carlos Engineering School, University of São Paulo, Brazil; University of Campinas (UNICAMP), Institute of Chemistry, Campinas, São Paulo, Brazil.
Department of Physics, Mathematics, and Fluids, National Distance Education University (UNED), Madrid, Spain.
Pestic Biochem Physiol. 2024 Sep;204:106088. doi: 10.1016/j.pestbp.2024.106088. Epub 2024 Aug 18.
Herbicides are the main class of pesticides applied in crops and are capable of polluting the surrounding freshwater system; thus, understanding their impact on non-target species, whose mechanism of action is not described, helps to elucidate the real risks of these pollutants to the environment. 2,4-dichlorophenoxyacetic acid (2,4-D) is frequently detected in water and, due to its persistence, poses a risk to wildlife. In this way, the present work aimed to describe the implication of exposure to concentrations of 2,4-D already reported in aquatic environments in several physiological mechanisms of C. riparius at molecular and biochemical levels. To achieve this, bioassays were conducted with fourth instar larvae exposed to three concentrations of 2,4-D (0.1, 1.0, and 7.5 μg L). Larvae were collected after 24 and 96 h of exposure, and the expression of 42 genes, related to six subcellular mechanisms, was assessed by Real-Time PCR (RT-PCR). Besides, the activity of the enzymes catalase (CAT), glutathione S-transferase (GST), and acetylcholinesterase (AChE) was determined. The main metabolic route altered after exposure to 2,4-D was the endocrine system (mainly related to 20-hydroxyecdysone and juvenile hormone), confirming its endocrine disruptor potential. Four of the eleven stress response genes studied were down-regulated, and later exposure modulated DNA-repair genes suggesting genotoxic capacity. Moreover, only one gene from each detoxification phase was modulated at short exposure to 1.0 μg L. The molecular responses were not dose-dependent, and some early responses were not preserved after 96 h, indicating a transient response to the herbicide. Exposure to 2,4-D did not alter the activity of CAT, GST, and AChE enzymes. The responses described in this study reveal new mechanistic pathways of toxicity for 2,4-D in non-target organisms and highlight potential ecological consequences for chironomids in aquatic systems at the edges of agricultural fields.
除草剂是应用于农作物的主要农药类别,能够污染周围的淡水系统;因此,了解其对非靶标物种的影响,这些物种的作用机制尚未描述,有助于阐明这些污染物对环境的实际风险。2,4-二氯苯氧乙酸(2,4-D)经常在水中被检测到,由于其持久性,对野生动物构成威胁。因此,本工作旨在描述在分子和生化水平上,暴露于已在水生环境中报道的 2,4-D 浓度对 C. riparius 的几个生理机制的影响。为此,进行了生物测定,用第四龄幼虫暴露于三种浓度的 2,4-D(0.1、1.0 和 7.5μg/L)。幼虫在暴露 24 和 96 小时后收集,并通过实时荧光定量 PCR(RT-PCR)评估与六个亚细胞机制相关的 42 个基因的表达。此外,还测定了过氧化氢酶(CAT)、谷胱甘肽 S-转移酶(GST)和乙酰胆碱酯酶(AChE)的活性。暴露于 2,4-D 后改变的主要代谢途径是内分泌系统(主要与 20-羟基蜕皮酮和保幼激素有关),证实了其内分泌干扰潜力。在所研究的十一个应激反应基因中,有四个被下调,随后的暴露调节了 DNA 修复基因,表明其具有遗传毒性。在短时间暴露于 1.0μg/L 时,仅调节了每个解毒阶段的一个基因。分子反应不是剂量依赖性的,一些早期反应在 96 小时后没有保留,表明对除草剂的反应是短暂的。暴露于 2,4-D 不会改变 CAT、GST 和 AChE 酶的活性。本研究中描述的反应揭示了 2,4-D 对非靶标生物的新毒性机制途径,并强调了农业领域边缘水生系统中摇蚊的潜在生态后果。