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采用直接进样/SPE 与 UPLC-MS/MS 联用测定淡水蓝藻水华中的柱孢藻毒素、anatoxin-a 和 homoanatoxin-a。

Quantification of cylindrospermopsin, anatoxin-a and homoanatoxin-a in cyanobacterial bloom freshwater using direct injection/SPE coupled with UPLC-MS/MS.

机构信息

Institute of Research and Development, Duy Tan University, Da Nang 550000, Viet Nam; NUS Environmental Research Institute, National University of Singapore, 1 Create Way, Create Tower, #15-02, Singapore 138602, Singapore.

Department of Environmental Science and Engineering, Sichuan University, China.

出版信息

Sci Total Environ. 2020 Aug 20;731:139014. doi: 10.1016/j.scitotenv.2020.139014. Epub 2020 Apr 30.

DOI:10.1016/j.scitotenv.2020.139014
PMID:32428751
Abstract

Analytical methods based on direct injection (DI) and solid phase extraction (SPE) coupled with ultrahigh performance liquid chromatography-tandem mass spectrometry (UPLC- MS/MS) were developed for the determination of anatoxin-a (ATX-a), cylindrospermopsin (CYN), and homoanatoxin-a (HATX-a) in freshwater samples impacted with cyanobacterial blooms. The presence of CYN in freshwater samples was detected and quantified based on direct injection method, while ATX-a and HATX-a could be determined by both DI and SPE-based methods. Matrix effects (ME) on the signal intensity of the cyanotoxins were systematically evaluated for both direct injection and SPE extract samples. CYN, ATX-a, and HATX-a suffered a significant suppression during UPLC-MS/MS. The selection of internal standards (ISs) for compensating/correcting the losses of target cyanotoxins during sample preparation and matrix effects in UPLC-MS/MS analyses were systematically evaluated. Acetaminophen-d (an isotopically labelled acetaminophen) is a suitable internal standard for correcting the ME on the signal intensity of ATX-a and HATX-a, while the use of L-phenylalanine-d or caffeine-d as IS for correcting ME of these toxins was not efficient, as expected. The method detection limit (MDL) for the target cyanotoxins ranged from 0.6 to 15 ng/L, which is sensitive enough to detect the presence of these toxins in cyanobacterial bloom freshwater. The developed methods were successfully applied for routine monitoring of the occurrence of these cyanotoxins in a local water body. Monitoring results depicted that ATX-a, CYN and HATX-a were ubiquitously detected in water samples, at concentrations ranging from 70 to 24,600 ng/L.

摘要

建立了基于直接进样(DI)和固相萃取(SPE)与超高效液相色谱-串联质谱(UPLC-MS/MS)联用的分析方法,用于测定受水华影响的淡水样品中的anatoxin-a(ATX-a)、cylindrospermopsin(CYN)和 homoanatoxin-a(HATX-a)。基于直接进样法检测到淡水样品中 CYN 的存在并进行定量,而 ATX-a 和 HATX-a 可以通过 DI 和 SPE 两种方法进行测定。系统评价了基质效应对两种直接进样和 SPE 提取样品中神经毒素信号强度的影响。在 UPLC-MS/MS 中,CYN、ATX-a 和 HATX-a 受到显著抑制。系统评价了用于补偿/校正目标神经毒素在样品制备过程中的损失和 UPLC-MS/MS 分析中基质效应的内标(IS)的选择。乙酰氨基酚-d(一种同位素标记的乙酰氨基酚)是校正 ATX-a 和 HATX-a 信号强度基质效应的合适内标,而 L-苯丙氨酸-d 或咖啡因-d 作为 IS 用于校正这些毒素的 ME 并不有效,这是预期的结果。目标神经毒素的方法检测限(MDL)范围为 0.6-15 ng/L,足以检测水华淡水样品中这些毒素的存在。所开发的方法成功应用于当地水体中这些神经毒素的常规监测。监测结果表明,ATX-a、CYN 和 HATX-a 在水样中普遍存在,浓度范围为 70-24600 ng/L。

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