安全检测

磁性固相萃取-超高效液相色谱-串联质谱法检测污水中14个芬太尼类毒品*

  • 董洛豪 ,
  • 刘猛 ,
  • 周婧 ,
  • 王海星 ,
  • 周凯 ,
  • 柯星 ,
  • 范一雷
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  • 1.浙江省毒品防控技术研究重点实验室 浙江警察学院, 杭州 310053;
    2.国家毒品实验室浙江分中心, 杭州 310053
第一作者 Tel:13396807121;E-mail:408451847@qq.com
**柯星 Tel:(0571)87787031;E-mail:kexing@zjjcxy.cn;范一雷 Tel:(0571)87787028;E-mail:fanyilei@zjjcxy.cn

收稿日期: 2024-09-19

  网络出版日期: 2025-11-13

基金资助

*国家重点研发计划项目(2023YFC3303903-3); 浙江省自然科学基金资助项目(LTGC24B050007,LTGC23H230001); 国家级大学生创新创业训练计划项目(国家级大学生创新创业训练计划项目(202411483025)**柯 星 Tel:(0571)87787031; E-mail:kexing@zjjcxy.cn; 范一雷 Tel:(0571)87787028; E-mail:fanyilei@zjjcxy.cn

Determination of 14 fentanyl analogs in wastewater by magnetic solid phase extraction combined with ultra performance liquid chromatography-tandem mass spectrometry*

  • DONG Luo-hao ,
  • LIU Meng ,
  • ZHOU Jing ,
  • WANG Hai-xing ,
  • ZHOU Kai ,
  • KE Xing ,
  • FAN Yi-lei
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  • 1. Key Laboratory of Drug Prevention and Control Technology of Zhejiang Province, Zhejiang Police College, Hangzhou 310053, China;
    2. National Anti-Drug Laboratory Zhejiang Regional Center, Hangzhou 310053, China

Received date: 2024-09-19

  Online published: 2025-11-13

摘要

目的: 建立一种磁性固相萃取-超高效液相色谱-串联质谱(MSPE-UHPLC-MS/MS)快速检测污水中14个芬太尼类毒品的方法。方法: 污水样品经新型混合模式弱阳离子交换磁性固相萃取材料Fe3O4@poly(ST/DVB/MA-COOH)净化和浓缩后,采用Waters Acquity UPLC HSS T3(150 mm×2.1 mm,1.8 μm)色谱柱进行分离,以0.1%甲酸-水溶液(A)和0.1%甲酸-乙腈溶液(B)为流动相,梯度洗脱,柱温40 ℃,流速0.3 mL · min-1,进样量2.5 µL,随后进入质谱电喷雾离子源,在多反应检测模式下进行检测。结果: 14个芬太尼类毒品质量浓度在0.04~4 ng · L-1范围内线性关系良好(r≥0.998 4),检出限(LOD)为0.013 ng · L-1,定量限(LOQ)为0.04 ng · L-1。14个分析物在低、中、高3种加标浓度下方法的回收率为85.4%~114.7%,日内精密度(n=6)为2.0%~6.4%,日间精密度(n=3)为0.4%~2.4%。在5份实际污水样品中检测出芬太尼,浓度范围为0.21~0.46 ng · L-1。结论: 本方法具有前处理时间短,操作简单,溶剂用量少,灵敏度高和重现性好等优点,适用于污水样品中芬太尼类毒品的高通量筛查和定量分析。

本文引用格式

董洛豪 , 刘猛 , 周婧 , 王海星 , 周凯 , 柯星 , 范一雷 . 磁性固相萃取-超高效液相色谱-串联质谱法检测污水中14个芬太尼类毒品*[J]. 药物分析杂志, 2025 , 45(7) : 1221 -1232 . DOI: 10.16155/j.0254-1793.2024-1139

Abstract

Objective: To establish a magnetic solid-phase extraction-ultra performance liquid chromatography-tandem mass spectrometry (MSPE-UHPLC-MS/MS) method for rapidly detecting 14 fentanyl analogs in wastewater. Methods: Wastewater samples were purified and concentrated using a novel mixed-mode weak cation exchange magnetic solid phase extraction adsorbent, Fe3O4@poly (ST/DVB/MA-COOH), followed by analysis with UHPLC-MS/MS method. Separation was performed on a Waters Acquity UPLC HSS T3 column (150 mm×2.1 mm, 1.8 μm)at 40 ℃. The mobile phase consisted of 0.1% formic acid-aqueous solution(A) and 0.1% formic acid-acetonitrile solution(B) with gradient elution. The flow rate was 0.3 mL · min-1, and an injection volume was 2.5 µL. Detection was carried out using electrospray ionization in multiple reaction monitoring mode. Results: The calibration curves for the 14 fentanyl analogs showed good linearity over the range of 0.04-4 ng · L-1 (r≥0.998 4). The limit of detection (LOD) was 0.013 ng · L-1 and the limit of quantitation (LOQ) was 0.04 ng · L-1. The recovery rates at low, medium and high spiked levels ranged from 85.4% to 114.7%. The intra-day precision(n=6) was between 2.0% and 6.4%, and the inter-day precision(n=3) was between 0.4% and 2.4%. Fentanyl was detected in five actual wastewater samples, with concentrations ranging from 0.21 to 0.46 ng · L-1. Conclusion: This method has the advantages of short pretreatment time, simple operation, low solvent consumption, high sensitivity, and good reproducibility. It is suitable for high-throughput screening and quantitative analysis of fentanyl analogs in wastewater samples.

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