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液相色谱-串联质谱法测定土壤、沉积物和水中三种新型除草剂残留量

[Determination of three new herbicide residues in soil, sediment and water by liquid chromatography-tandem mass spectrometry].

作者信息

He Hong-Mei, Xu Ling-Ying, Zhang Chang-Peng, Fang Nan, Jiang Jin-Hua, Wang Xiang-Yun, Yu Jian-Zhong, Zhao Xue-Ping

机构信息

State Key Laboratory for Managing Biotic and Chemical Threats to the Quality and Safety of Agro-products, Key Laboratory for Pesticide Residue Detection of Ministry of Agriculture and Rural Affairs, Institute of Agro-product Safety and Nutrition, Zhejiang Academy of Agricultural Sciences, Hangzhou 310021, China.

出版信息

Se Pu. 2024 Mar 8;42(3):256-263. doi: 10.3724/SP.J.1123.2023.07006.

DOI:10.3724/SP.J.1123.2023.07006
PMID:38503702
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC10951813/
Abstract

Herbicides play an important role in preventing and controlling weeds and harmful plants and are increasingly used in agriculture, forestry, landscaping, and other fields. However, the effective utilization rate of herbicides is only 20%-30%, and most herbicides enter the atmosphere, soil, sediment, and water environments through drift, leaching, and runoff after field application. Herbicide residues in the environment pose potential risks to ecological safety and human health. Therefore, establishing analytical methods to determine herbicide residues in environmental samples is of great importance. In this study, an analytical method based on liquid chromatography-tandem mass spectrometry (LC-MS/MS) in positive electrospray ionization mode (ESI) was developed for the determination of isoxaflutole, metazachlor, and saflufenacil residues in soil, sediment, and water. The instrumental detection parameters, including electrospray ionization mode, mobile phase, and chromatographic column, were optimized. The mobile phases were methanol (A) and 0.1% formic acid aqueous solution (B). Gradient elution was performed as follows: 0-1.0 min, 60%A; 1.0-2.0 min, 60%A-90%A; 2.0-3.0 min, 90%A; 3.0-4.0 min, 90%A-60%A; 4.0-5.0 min, 60%A. The samples were salted after extraction with acetonitrile and cleaned using a C solid-phase extraction column. Different solid-phase extraction columns and leaching conditions were investigated during sample pretreatment. Working curves in the neat solvent and matrix were constructed by plotting the measured peak areas as a function of the concentrations of the analytes in the neat solvent and matrix. Good linearities were found for isoxaflutole, metazachlor, and saflufenacil in the solvent and matrix-matched standards in the range of 0.0005-0.02 mg/L, with ≥0.9961. The matrix effects of the three herbicides in soil, sediment, and water ranged from -10.1% to 16.5%. The limits of detection (LODs, =3) for isoxaflutole, metazachlor, and saflufenacil were 0.05, 0.01, and 0.02 μg/kg, respectively. The limits of quantification (LOQs, =10) for isoxaflutole, metazachlor, and saflufenacil were 0.2, 0.05, and 0.05 μg/kg, respectively. The herbicides were applied to soil, sediment, and water at spiked levels of 0.005, 0.1, and 2.0 mg/kg, respectively. The average recoveries for isoxaflutole, metazachlor, and saflufenacil in soil, sediment, and water were in the ranges of 77.2%-101.9%, 77.9%-105.1%, and 80.8%-107.1%, respectively. The RSDs for isoxaflutole, metazachlor, and saflufenacil were in the ranges of 1.4%-12.8%, 1.2%-7.7%, and 1.5%-11.5%, respectively. The established method was used to analyze actual samples collected from four different sites in Zhejiang Province (Xiaoshan, Taizhou, Dongyang, and Yuhang) and one site in Heilongjiang (Jiamusi). The proposed method is simple, rapid, accurate, stable, and highly practical. It can be used to detect isoxaflutole, metazachlor, and saflufenacil residues in soil, sediment, and water and provides a reference for monitoring the residual pollution and environmental behavior of herbicides.

摘要

除草剂在防治杂草和有害植物方面发挥着重要作用,并且越来越多地应用于农业、林业、园林绿化等领域。然而,除草剂的有效利用率仅为20%-30%,大多数除草剂在田间施用后通过漂移、淋溶和径流进入大气、土壤、沉积物和水环境。环境中的除草剂残留对生态安全和人类健康构成潜在风险。因此,建立测定环境样品中除草剂残留的分析方法至关重要。本研究建立了一种基于液相色谱-串联质谱(LC-MS/MS)的正电喷雾电离模式(ESI)分析方法,用于测定土壤、沉积物和水中的异恶唑草酮、异丙甲草胺和乙羧氟草醚残留。对仪器检测参数进行了优化,包括电喷雾电离模式、流动相和色谱柱。流动相为甲醇(A)和0.1%甲酸水溶液(B)。梯度洗脱条件如下:0-1.0分钟,60%A;1.0-2.0分钟,60%A-90%A;2.0-3.0分钟,90%A;3.0-4.0分钟,90%A-60%A;4.0-5.0分钟,60%A。样品用乙腈萃取后进行盐析,并用C固相萃取柱净化。在样品预处理过程中研究了不同的固相萃取柱和淋洗条件。通过绘制纯溶剂和基质中分析物浓度与测得峰面积的函数关系,构建了纯溶剂和基质中的工作曲线。异恶唑草酮、异丙甲草胺和乙羧氟草醚在溶剂和基质匹配标准中的线性良好,范围为0.0005-0.02 mg/L,相关系数≥0.9961。三种除草剂在土壤、沉积物和水中的基质效应范围为-10.1%至16.5%。异恶唑草酮、异丙甲草胺和乙羧氟草醚的检测限(LODs,n=3)分别为0.05、0.01和0.02 μg/kg。异恶唑草酮、异丙甲草胺和乙羧氟草醚的定量限(LOQs,n=10)分别为0.2、0.05和0.05 μg/kg。除草剂分别以0.005、0.1和2.0 mg/kg的加标水平添加到土壤、沉积物和水中。异恶唑草酮、异丙甲草胺和乙羧氟草醚在土壤、沉积物和水中的平均回收率分别为77.2%-101.9%、77.9%-105.1%和80.8%-107.1%。异恶唑草酮、异丙甲草胺和乙羧氟草醚的相对标准偏差分别为1.4%-12.8%、1.2%-7.7%和1.5%-11.5%。所建立的方法用于分析从浙江省四个不同地点(萧山、台州、东阳和余杭)和黑龙江省一个地点(佳木斯)采集的实际样品。该方法简便、快速、准确、稳定且实用性强。可用于检测土壤、沉积物和水中的异恶唑草酮、异丙甲草胺和乙羧氟草醚残留,为监测除草剂的残留污染和环境行为提供参考。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/8ac2/10951813/dd3399a318f0/cjc-42-3-256-img_3.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/8ac2/10951813/388d9b5fb1da/cjc-42-3-256-img_1.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/8ac2/10951813/7a5282ac9c26/cjc-42-3-256-img_2.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/8ac2/10951813/dd3399a318f0/cjc-42-3-256-img_3.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/8ac2/10951813/388d9b5fb1da/cjc-42-3-256-img_1.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/8ac2/10951813/7a5282ac9c26/cjc-42-3-256-img_2.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/8ac2/10951813/dd3399a318f0/cjc-42-3-256-img_3.jpg

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