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毒死蜱和氧乐果对大型溞的神经毒性。

Neurotoxicity of chlorpyrifos and chlorpyrifos-oxon to Daphnia magna.

机构信息

Oregon State University, Corvallis, OR, 97333, USA.

出版信息

Chemosphere. 2021 Aug;276:130120. doi: 10.1016/j.chemosphere.2021.130120. Epub 2021 Mar 1.

DOI:10.1016/j.chemosphere.2021.130120
PMID:33706179
Abstract

Chlorpyrifos (CPF) is a widely used broad-spectrum organophosphate insecticide. CPF elicits neurotoxic effects in exposed organisms by inhibiting the activity of acetylcholinesterase enzymes (AChE), which prolongs nerve transmission and results in neurotoxic symptoms and death at high doses. While CPF is capable of eliciting neurotoxic effects, chlorpyrifos-oxon (CPFO) is the primary neurotoxicant agent. Aquatic organisms bioactivate CPF to CPFO through the Cytochrome P450 phase I metabolic pathway following exposure to CPF. Additionally, in the environment, CPF transforms to CPFO, primarily through photo-oxidation. As both compounds can be transported in air and water to aquatic ecosystems, there is the potential for exposure to non-target organisms. The potential for adverse impacts on aquatic receptors depends on patterns of exposure and toxicity of individual compounds and the mixture. To study the neurotoxicity of these compounds, a 48 h acute and 21 d chronic Daphnia magna bioassay was conducted independently with CPF and CPFO. Acute bioassay results show a median lethal concentration (LC50) of 0.76 μg L-1 for CPF and 0.32 μg L-1 for CPFO, suggesting that CPFO is 2.4 times more acutely toxic to D. magna. Acute assay results were also used to derive Benchmark Dose Levels of 0.58 μg L-1 for CPF and 0.25 μg L-1 for CPFO. However, neither compound elicited an effect on reproduction or growth at relevant chronic exposures. As D. magna are a small and relatively sensitive species, and the AChE inhibition adverse outcome pathway is highly conserved, these results may be cautiously extrapolated in assessing adverse impacts on aquatic receptors..

摘要

毒死蜱(CPF)是一种广泛使用的广谱有机磷杀虫剂。CPF 通过抑制乙酰胆碱酯酶(AChE)的活性在暴露的生物体中产生神经毒性作用,这延长了神经传递,导致高剂量时出现神经毒性症状和死亡。虽然 CPF 能够产生神经毒性作用,但氯氧磷(CPFO)是主要的神经毒剂。水生生物通过接触 CPF 后细胞色素 P450 相 I 代谢途径将 CPF 生物转化为 CPFO。此外,在环境中,CPF 主要通过光氧化转化为 CPFO。由于这两种化合物都可以通过空气和水运输到水生生态系统中,因此存在暴露于非目标生物的可能性。对水生受体的潜在不利影响取决于单个化合物和混合物的暴露模式和毒性。为了研究这些化合物的神经毒性,我们独立地使用 CPF 和 CPFO 进行了 48 h 急性和 21 d 慢性大型溞生物测定。急性生物测定结果显示 CPF 的半致死浓度(LC50)为 0.76 μg L-1,CPFO 的为 0.32 μg L-1,表明 CPFO 对 D. magna 的急性毒性是 CPF 的 2.4 倍。急性测定结果还用于推导出 CPF 的基准剂量水平为 0.58 μg L-1 和 CPFO 的 0.25 μg L-1。然而,在相关慢性暴露下,这两种化合物均未对繁殖或生长产生影响。由于大型溞是一种小型且相对敏感的物种,并且 AChE 抑制不良结局途径高度保守,因此这些结果在评估对水生受体的不利影响时可以谨慎推断。

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