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[超高效液相色谱-串联质谱法同时测定血浆和尿液中的12种亲脂性贝类毒素]

[Simultaneous determination of 12 lipophilic shellfish toxins in plasma and urine by ultra-high performance liquid chromatography-tandem mass spectrometry].

作者信息

Lin Qiang, Yang Chao, Li Meili, Wang Jia, Hou Hanran, Shao Bing, Niu Yumin

机构信息

Beijing Yanqing District Center for Disease Control and Prevention, Beijing 102100, China.

Beijing Center for Disease Control and Prevention, Beijing 100013, China.

出版信息

Se Pu. 2021 Apr 8;39(4):399-405. doi: 10.3724/SP.J.1123.2020.11001.

DOI:10.3724/SP.J.1123.2020.11001
PMID:34227760
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC9404129/
Abstract

Lipophilic shellfish toxins pose significant threats to the health of seafood consumers and public health. The symptoms of these kinds of toxins include severe diarrhea, abdominal cramps, nausea and gastrointestinal disorders. These symptoms could be hardly distinguished with many other symptoms of food poisoning and diseases. Therefore, a fast and accurate determination method in human biological samples is urgently needed for the accurate judgement of food poisoning incident, which is important for the investigation of public health emergencies and clinical treatment of poisoned patients. However, there were several flaws of the previous studies reported on the analysis of lipophilic shellfish toxins: (1) limited target compounds were covered; (2) the pre-treatment process was complex; (3) the sensitivity of the compound was low. In this study, a simple extraction method coupled with ultra-high performance liquid chromatography-tandem mass spectrometry (UPLC-MS/MS) was developed for the simultaneous determination of 12 lipophilic shellfish toxins, including azaspir acid 1 (AZA1), azaspir acid 2 (AZA2), azaspir acid 3 (AZA3), dinophysistoxin 1 (DTX1), dinophysistoxin 2 (DTX2), gymnodimine (GYM), hyessotoxin (HYTX), okadaic acid (OA), pinnatoxin (Pntx), pectenotoxins 2 (PTX2), spirolides 1 (SPX1), yessotoxin (YTX), in plasma and urine. Firstly, the instrument conditions were optimized. Different additions in mobile phase were compared and 0.05% (v/v) ammonia solution was selected since it can improve the peak shape of YTX and HYTX, and increase the respondence by four times. Secondly, the volume of acetonitrile (0.2, 0.4, 0.6, 0.8, 1.0 mL) use for the extraction of the target compounds in plasma was optimized. Satisfactory recoveries were obtained when 0.6 mL of acetonitrile was used. At the same time, satisfactory recoveries were obtained when 0.9 mL of acetonitrile was used in urine samples. Finally, under the optimized conditions, the 12 compounds in plasma and urine samples were ultrasonically extracted with acetonitrile. Chromatographic separation was performed on a Phenomenex Kinetex C18 column (50 mm×3 mm, 2.6 μm) with 90% (v/v) acetonitrile aqueous solution and water containing 0.05% (v/v) ammonia as mobile phases. Gradient elution with a flow rate of 0.40 mL/min was employed. The 12 compounds were monitored in the multiple reactions monitoring (MRM) mode with electrospray ionization (ESI) under both positive and negative conditions. The matrix effects of the 12 compounds ranged from 0.8 to 1.1. Therefore, external standard calibration curves were used for the quantification. The 12 shellfish toxins showed good linear relationship in the range of 0.03-36.25 μg/L with the correlation coefficients greater than 0.995. The limits of detection (LODs, =3) were 0.08-0.21 ng/mL for the urine samples and 0.10-0.28 μg/L for the plasma samples, respectively. The limit of quantitations (LOQs, =10) were 0.23-0.63 μg/L for the urine samples and 0.31-0.84 μg/L for the plasma samples, respectively. The recoveries of the 12 compounds were in the range of 72.7%-124.1% at three spiked levels (i. e., LOQ, three times LOQ, and ten times LOQ). The intra-day and inter-day precisions were 2.1%-20.0% and 2.1%-15.3%, respectively. The method was applied in the detection of the 12 lipophilic shellfish toxins in the urine and plasma samples of healthy humans and mice previously injected with the 12 shellfish toxins intraperitoneally. None of the 12 toxins were found in the samples from healthy human, while all of the 12 lipophilic shellfish toxins were found in the urine and plasma samples collected from the poisoned mice in the range of 1.14-2.35 μg/L and 1.01-1.17 μg/L, respectively. The established method has the advantages of sensitive, quick, easy to operate, and of low sample volume. It can be used for the simultaneous determination of 12 lipophilic shellfish toxins in urine and plasma samples.

摘要

亲脂性贝类毒素对海鲜消费者的健康和公众健康构成重大威胁。这类毒素的症状包括严重腹泻、腹部绞痛、恶心和胃肠道紊乱。这些症状很难与许多其他食物中毒和疾病的症状区分开来。因此,迫切需要一种在人体生物样本中快速准确的测定方法,以准确判断食物中毒事件,这对于公共卫生突发事件的调查和中毒患者的临床治疗至关重要。然而,先前关于亲脂性贝类毒素分析的研究存在几个缺陷:(1)涵盖的目标化合物有限;(2)预处理过程复杂;(3)化合物的灵敏度低。在本研究中,开发了一种简单的提取方法,结合超高效液相色谱-串联质谱(UPLC-MS/MS),用于同时测定血浆和尿液中的12种亲脂性贝类毒素,包括氮杂螺旋酸1(AZA1)、氮杂螺旋酸2(AZA2)、氮杂螺旋酸3(AZA3)、鳍藻毒素-1(DTX1)、鳍藻毒素-2(DTX2)、裸甲藻毒素(GYM)、海兔毒素(HYTX)、冈田酸(OA)、扇贝毒素(Pntx)、pectenotoxins 2(PTX2)、螺旋藻毒素1(SPX1)、岩沙海葵毒素(YTX)。首先,优化了仪器条件。比较了流动相中不同的添加剂,选择了0.05%(v/v)氨水溶液,因为它可以改善YTX和HYTX的峰形,并使响应增加四倍。其次,优化了用于提取血浆中目标化合物的乙腈体积(0.2、0.4、0.6、0.8、1.0 mL)。当使用0.6 mL乙腈时,获得了满意的回收率。同时,当在尿液样本中使用0.9 mL乙腈时,也获得了满意的回收率。最后,在优化条件下,用乙腈对血浆和尿液样本中的12种化合物进行超声提取。在Phenomenex Kinetex C18柱(50 mm×3 mm, 2.6 μm)上进行色谱分离,以90%(v/v)乙腈水溶液和含有0.05%(v/v)氨的水作为流动相。采用梯度洗脱,流速为0.40 mL/min。在正、负条件下,通过电喷雾电离(ESI)在多反应监测(MRM)模式下监测这12种化合物。这12种化合物的基质效应范围为0.8至1.1。因此,采用外标校准曲线进行定量。这12种贝类毒素在0.03 - 36.25 μg/L范围内呈现良好的线性关系,相关系数大于0.995。尿液样本的检测限(LODs,=3)分别为0.08 - 0.21 ng/mL,血浆样本的检测限为0.10 - 0.28 μg/L。定量限(LOQs,=10)尿液样本分别为0.23 - 0.63 μg/L,血浆样本为0.31 - 0.84 μg/L。在三个加标水平(即定量限、三倍定量限和十倍定量限)下,这12种化合物的回收率在72.7% - 124.1%范围内。日内和日间精密度分别为2.1% - 20.0%和2.1% - 15.3%。该方法应用于检测健康人和先前腹腔注射这12种贝类毒素的小鼠的尿液和血浆样本中的12种亲脂性贝类毒素。健康人的样本中未发现这12种毒素中的任何一种,而从中毒小鼠收集的尿液和血浆样本中分别在1.14 - 2.35 μg/L和1.01 - 1.17 μg/L范围内发现了所有12种亲脂性贝类毒素。所建立的方法具有灵敏、快速、操作简便、样品用量少的优点。它可用于同时测定尿液和血浆样本中的12种亲脂性贝类毒素。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/de58/9404129/b3cd312bdfaf/cjc-39-04-399-img_3.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/de58/9404129/4b94bbeb89f0/cjc-39-04-399-img_1.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/de58/9404129/2bd9fca1d012/cjc-39-04-399-img_2.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/de58/9404129/b3cd312bdfaf/cjc-39-04-399-img_3.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/de58/9404129/4b94bbeb89f0/cjc-39-04-399-img_1.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/de58/9404129/2bd9fca1d012/cjc-39-04-399-img_2.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/de58/9404129/b3cd312bdfaf/cjc-39-04-399-img_3.jpg

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