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采用 LC/ESI-MS-MS 同位素稀释法检测小鼠和大鼠尿液中 1,4-双(N-乙酰-S-半胱氨酸)-2-丁酮,作为 1,3-丁二烯体外代谢物 1-氯-2-羟基-3-丁烯的生物标志物。

Isotope dilution LC/ESI-MS-MS quantitation of urinary 1,4-bis(N-acetyl-S-cysteinyl)-2-butanone in mice and rats as the biomarker of 1-chloro-2-hydroxy-3-butene, an in vitro metabolite of 1,3-butadiene.

机构信息

Institute of Environmental Pollution and Health, School of Environmental and Chemical Engineering, Shanghai University, Shanghai, 200444, China.

Institute of Environmental Pollution and Health, School of Environmental and Chemical Engineering, Shanghai University, Shanghai, 200444, China.

出版信息

Chem Biol Interact. 2019 Sep 25;311:108760. doi: 10.1016/j.cbi.2019.108760. Epub 2019 Jul 23.

Abstract

1-Chloro-2-hydroxy-3-butene (CHB) is a possible metabolite of 1,3-butadiene, a carcinogenic air pollutant. To demonstrate its formation in vivo, it is desirable to develop a practical biomarker and the corresponding analysis method. CHB can undergo alcohol dehydrogenase- and cytochromes P450 enzymes (P450)-mediated oxidation to yield 1-chloro-3-buten-2-one (CBO), which readily forms glutathione conjugates. We hypothesized that CBO-derived mercapturic acids, which are the expected biotransformed products of CBO-glutathione conjugates, could be used as CHB biomarkers. Thus, in the present study, we investigated the in vivo biotransformation of CHB into CBO-derived mercapturic acids. Because the reaction of CBO with N-acetyl-l-cysteine yields two products, 1,4-bis(N-acetyl-S-cysteinyl)-2-butanone (NC1) and 1-chloro-4-(N-acetyl-S-cysteinyl)-2-butanone (NC2), we first developed an isotope dilution LC/ESI-MS-MS method to quantitate urinary NC1 and NC2, and then determined their concentrations in urine of C57BL/6 mice and Sprague-Dawley rats administered CHB. Since no NC2 was detected in samples, the LC/ESI-MS-MS method was optimized specifically for NC1. NC1 was enriched through solid phase extraction with the recovery being 75-82%. The limits of detection and quantitation were 6.8 and 34 fmol/0.1 mL for mouse urine, and 4.5 and 7.1 fmol/0.1 mL for rat urine, respectively. In urine of animals before CHB administration, no NC1 was detected; in mice administered CHB at 10 and 30 mg/kg, and rats at 5 and 15 mg/kg, NC1 was detected and its concentrations in urine from animals given higher doses were 3-6 fold higher than those given lower doses. Moreover, the NC1 concentrations in urine during 0-8 h were 4-6 fold and 10-11 fold higher than those during 8-24 h for mice and rats, respectively. The results demonstrated that CHB could be in vivo biotransformed into NC1, which could be used as a practical CHB biomarker.

摘要

1-氯-2-羟基-3-丁烯(CHB)是 1,3-丁二烯的一种可能的代谢物,1,3-丁二烯是一种致癌的空气污染物。为了证明其在体内的形成,理想情况下需要开发一种实用的生物标志物及其相应的分析方法。CHB 可经醇脱氢酶和细胞色素 P450 酶(P450)介导氧化生成 1-氯-3-丁烯-2-酮(CBO),后者易与谷胱甘肽形成轭合物。我们假设 CBO 衍生的硫醚尿酸盐(CBO-谷胱甘肽轭合物的预期生物转化产物)可用作 CHB 生物标志物。因此,在本研究中,我们研究了 CHB 体内转化为 CBO 衍生的硫醚尿酸盐。由于 CBO 与 N-乙酰-L-半胱氨酸反应生成两种产物,即 1,4-双(N-乙酰-S-半胱氨酰基)-2-丁酮(NC1)和 1-氯-4-(N-乙酰-S-半胱氨酰基)-2-丁酮(NC2),我们首先开发了一种同位素稀释 LC/ESI-MS-MS 方法来定量测定尿中的 NC1 和 NC2,然后测定了给予 CHB 的 C57BL/6 小鼠和 Sprague-Dawley 大鼠尿中的浓度。由于在样品中未检测到 NC2,因此专门对 LC/ESI-MS-MS 方法进行了优化以用于 NC1。NC1 通过固相萃取进行富集,回收率为 75-82%。检测限和定量限分别为 6.8 和 34 fmol/0.1 mL 用于小鼠尿液,4.5 和 7.1 fmol/0.1 mL 用于大鼠尿液。在给予 CHB 之前的动物尿液中未检测到 NC1;在给予 10 和 30 mg/kg 的小鼠和 5 和 15 mg/kg 的大鼠中,检测到 NC1,并且给予较高剂量的动物的尿液中 NC1 的浓度比给予较低剂量的动物高 3-6 倍。此外,小鼠和大鼠尿液中 0-8 小时的 NC1 浓度分别比 8-24 小时高 4-6 倍和 10-11 倍。结果表明,CHB 可以在体内转化为 NC1,NC1 可用作实用的 CHB 生物标志物。

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