尿中3-喹啉苄基苯甲酸酯的测定

G. Byrd, L. Sniegoski, E. White
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引用次数: 5

摘要

化合物3-quinuclidinyl benzilate (BZ)是一种有效的毒蕈碱类胆碱能拮抗剂,在非常小的剂量下就能导致失能[1,2]。因此,它可以作为一种强大的心理化学战剂。鉴于美国军方计划销毁BZ库存以及工作人员接触BZ的可能性增加,我们的实验室开发了一种针对人类接触BZ的特定确认测试。该测试确定了尿液中母体化合物的含量,以及两种主要代谢物,喹啉二醇(Q)和苯甲酸(BA),它们通过水解形成,如图1所示。我们实验室先前的工作表明,基于建议的可接受暴露水平,BA和Q可以在尿液中以5 ng/mL的目标浓度进行检测。这里描述的工作证明了母体化合物从尿液中恢复到其目标水平,并将该方法纳入BZ暴露的总体测试中。预计在接触者的尿液中只会发现一小部分未代谢的BZ。根据建议的可接受暴露水平估计,尿液中苯甲醚的检出限为0.5纳克/毫升。由于尿液基质的复杂性和个体之间尿液的差异,在这种水平上测量尿液中的BZ提出了一个具有挑战性的分析问题。建立了固相萃取-同位素稀释气相色谱/质谱联用法测定尿液中BZ的方法。在此过程中,取20ml尿液样品制成碱性样品,通过固相萃取将BZ去除到C1 g样品制备柱上。用水和40%乙腈溶液洗涤色谱柱,用甲醇洗脱BZ。将洗脱液吹干,在衍生化剂中重组,形成三甲基硅基衍生物,用于GC/MS分析。在m/z 255处使用单离子监测片段离子(C6 H5)2COTMS',在m/z 260处使用同位素标记的内标物(3-quinuclidinyl-' 8 o - benzil酸-d 5)进行测量。我们已经能够测定尿液中浓度低于0.5 ng/mL的BZ。图2描绘了离子色谱图,显示在0.5 ng/mL时检测到BZ作为其TMS衍生物。该方法被纳入BZ暴露的总体测试,以确定尿液中BZ, BA和Q的浓度。通过观察8个不同的尿液样本,该测试得到了验证。这些样本被分为几个亚样本,其中一些添加了已知浓度的分析物,而另一些则空白。在分析BZ、BA和Q的18个亚样本中,9个亚样本的浓度达到或略低于目标浓度水平,5个亚样本的浓度约为目标浓度的10倍,4个亚样本为空白。亚样本的峰值达到目标水平的10倍,目的是为实际接触时预期浓度水平的尿液样本提供信息。空白尿液样本提供了有关背景干扰的信息,这些干扰与测试中几种不同的尿液有关。对这些样本的验证测试结果以图形形式总结在图3中。对于所有三种分析物,我们认为测量值接近峰值水平。根据确定的目标水平,在四种空白尿液中,三种分析物均未出现假阳性。对于峰值接近目标水平的样品,没有测量值低于峰值值的80%。在此基础上,没有明显的假阴性。该方法在GC/MS测量、样品制备和尿-尿变异性方面的不精密度基本均匀分布,单次测量的不精密度约为15%。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Determination of 3-Quinuclidinyl Benzilate in Urine
The compound 3-quinuclidinyl benzilate (BZ) is a potent muscarinic cholinergic antagonist that can produce incapacitation at very small doses [1,2]. As such it can be used as a powerful psychochemical warfare agent. In response to the scheduled destruction of U.S. military stockpiles of BZ and the increased potential for worker exposure, our laboratory has developed a specific confirmatory test for human exposure to BZ. The test determines the amount of the parent compound in the urine as well as the two major metabolites, quinuclidinol (Q) and benzilic acid (BA) which are formed by hydrolysis as shown in figure 1. Previous work in our laboratory demonstrated that BA and Q could be determined in urine at their target concentration of 5 ng/mL as based on a proposed acceptable exposure level. The work described here demonstrates the recovery of the parent compound from urine at its target level and the incorporation of this method into an overall test for exposure to BZ. Only a small percentage of unmetabolized BZ is expected to be found in the urine of exposed persons. Estimates based on the proposed acceptable exposure level require detection limits for BZ in urine of 0.5 ng/mL. Because of the complexity of the urine matrix and the variation of urine from one individual to the next, the measurement of BZ in urine at this level presents a challenging analytical problem. A method using solid phase extraction and isotope dilution GC/MS was developed to measure BZ in urine. In the procedure, a 20 mL urine sample is made basic and the BZ is removed by solid phase extraction onto a C1 g sample preparation column. The column is washed with water and a 40% acetonitrile solution and the BZ is eluted with methanol. The eluent is blown to dryness and reconstituted in a derivatizing agent to form the trimethylsilyl derivative for analysis by GC/MS. Measurements are performed using single ion monitoring for the fragment ion (C6 H5 )2COTMS' at m/z 255 and the analogous ion from the isotopically labeled internal standard (3-quinuclidinyl-' 8 O-benzilate-d 5) at m/z 260. We have been able to determine BZ in urine at concentrations less than 0.5 ng/mL. Figure 2 depicts an ion chromatogram showing detection of BZ as its TMS derivative at 0.5 ng/mL. This method was incorporated into the overall test for exposure to BZ which determines the concentration of BZ, BA, and Q in urine. The test was validated by looking at eight different urine samples which were divided into subsamples, some spiked with known concentrations of the analytes and others left blank. Of the 18 subsamples that were analyzed for BZ, BA, and Q, nine were spiked at or just below the target concentration level, five at approximately 10 times the target level, and four were blank. The subsamples spiked at 10 times the target level were to provide information for urine samples with concentration levels that would be expected in the event of an actual exposure. The blank urine samples provided information regarding background interferences with the test over several different urines. The results of the validation test on these samples are summarized graphically in figure 3. For all three analytes we considered the measured values close to the spiked levels. Based on the established target levels no false positives occurred for any of the three analytes in any of the four blank urines. For samples spiked near the target levels no measured value was less than 80% of the spiked value. On this basis, no false negatives were apparent. The imprecisions in the method with regard to GC/MS measurement, sample preparation, and urine-to-urine variability were more or less evenly distributed and the imprecision of a single measurement was about 15%.
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