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使用气相色谱法对叠氮化物和氰化物进行叠氮化物中毒的毒理学分析。

Toxicological analysis of azide and cyanide for azide intoxications using gas chromatography.

机构信息

Department of Pharmacy & Pharmacology, The Netherlands Cancer Institute, Amsterdam, The Netherlands.

Division of Pharmacology, The Netherlands Cancer Institute, Amsterdam, The Netherlands.

出版信息

Basic Clin Pharmacol Toxicol. 2021 Mar;128(3):534-541. doi: 10.1111/bcpt.13523. Epub 2020 Nov 3.

DOI:10.1111/bcpt.13523
PMID:33090684
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC7984282/
Abstract

Azide is a highly toxic chemical agent to human being. Accidental, but also intentional exposure to azide occurs. To be able to confirm azide ingestion, we developed a method to identify and quantify azide in biological matrices. Cyanide was included in the method to evaluate suggested in vivo production of cyanide after azide ingestion. Azide in biological matrices was first derivatized by propionic anhydride to form propionyl azide. Simultaneously, cyanide was converted into hydrogen cyanide. After thermal rearrangement of propionyl azide, ethyl isocyanate was formed, separated together with hydrogen cyanide by gas chromatography (GC) and detected using a nitrogen phosphorous detector (NPD). The method was linear from 1.0-100 µg/mL for both analytes, and azide was stable in human plasma at -20°C for at least 49 days. Azide was measured in the gastric content of two cases of suspected azide ingestion (case 1:1.2 mg/mL, case 2:1.5 mg/mL). Cyanide was only identified in the gastric content of case 1 (approximately 1.4 µg/mL). Furthermore, azide was quantified in plasma (19 µg/mL), serum (24 µg/mL), cell pellet (21 µg/mL) and urine (3.0 µg/mL) of case 2. This method can be used to confirm azide and cyanide exposure, and azide concentrations can be quantified in several biological matrices.

摘要

叠氮化物对人类是一种剧毒化学物质。意外的,也有意的暴露于叠氮化物中发生。为了能够确认叠氮化物的摄入,我们开发了一种在生物基质中鉴定和定量叠氮化物的方法。氰化物被包含在该方法中,以评估摄入叠氮化物后体内氰化物的产生情况。生物基质中的叠氮化物首先与丙酸酐反应,形成丙酰叠氮化物。同时,氰化物转化为氢氰酸。丙酸酰叠氮化物热重排后,形成乙基异氰酸酯,与氢氰酸一起通过气相色谱(GC)分离,并使用氮磷检测器(NPD)检测。该方法对两种分析物均呈 1.0-100μg/mL 的线性关系,叠氮化物在人血浆中于-20°C 至少稳定 49 天。在两例疑似叠氮化物摄入的胃内容物中测量到了叠氮化物(病例 1:1.2mg/mL,病例 2:1.5mg/mL)。氰化物仅在病例 1 的胃内容物中被鉴定出来(约 1.4μg/mL)。此外,还在病例 2 的血浆(19μg/mL)、血清(24μg/mL)、细胞沉淀(21μg/mL)和尿液(3.0μg/mL)中定量了叠氮化物。该方法可用于确认叠氮化物和氰化物暴露情况,并定量几种生物基质中的叠氮化物浓度。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4712/7984282/65291b94ca84/BCPT-128-534-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4712/7984282/e73618a77c39/BCPT-128-534-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4712/7984282/65291b94ca84/BCPT-128-534-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4712/7984282/e73618a77c39/BCPT-128-534-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4712/7984282/65291b94ca84/BCPT-128-534-g001.jpg

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Sci Rep. 2021 Jul 30;11(1):15568. doi: 10.1038/s41598-021-95104-5.
法医毒理学科学工作组(SWGTOX)法医毒理学方法验证的标准操作规程。
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