Kotapati Srikanth, Sangaraju Dewakar, Esades Amanda, Hallberg Lance, Walker Vernon E, Swenberg James A, Tretyakova Natalia Y
Department of Medicinal Chemistry and the Masonic Cancer Center, University of Minnesota, Minneapolis, MN 55455, USA, Sealy Center for Environmental Health and Medicine (SCEHM) and the Department of Preventive Medicine and Community Health, University of Texas Medical Branch at Galveston, Galveston, TX 77555, USA, Department of Pathology, University of Vermont, Burlington, VT 05405, USA and Department of Environmental Sciences and Engineering, University of North Carolina at Chapel Hill, Chapel Hill, NC 27599, USA.
Sealy Center for Environmental Health and Medicine (SCEHM) and the Department of Preventive Medicine and Community Health, University of Texas Medical Branch at Galveston, Galveston, TX 77555, USA.
Carcinogenesis. 2014 Jun;35(6):1371-8. doi: 10.1093/carcin/bgu047. Epub 2014 Feb 14.
Human carcinogen 1,3-butadiene (BD) undergoes metabolic activation to 3,4-epoxy-1-butene (EB), hydroxymethylvinyl ketone (HMVK), 3,4-epoxy-1,2-butanediol (EBD) and 1,2,3,4-diepoxybutane (DEB). Among these, DEB is by far the most genotoxic metabolite and is considered the ultimate carcinogenic species of BD. We have shown previously that BD-exposed laboratory mice form 8- to 10-fold more DEB-DNA adducts than rats exposed at the same conditions, which may be responsible for the enhanced sensitivity of mice to BD-mediated cancer. In the present study, we have identified 1,4-bis-(N-acetyl-L-cystein-S-yl)butane-2,3-diol (bis-BDMA) as a novel DEB-specific urinary biomarker. Isotope dilution high-performance liquid chromatography-electrospray ionization-tandem mass spectrometry was employed to quantify bis-BDMA and three other BD-mercapturic acids, 2-(N-acetyl-L-cystein-S-yl)-1-hydroxybut-3-ene/1-(N-acetyl-L-cystein-S-yl)-2-hydroxy-but-3-ene (MHBMA, from EB), 4-(N-acetyl-L-cystein-S-yl)-1,2-dihydroxybutane (DHBMA, from HMVK) and 4-(N-acetyl-L-cystein-S-yl)-1,2,3-trihydroxybutane (THBMA, from EBD), in urine of confirmed smokers, occupationally exposed workers and BD-exposed laboratory rats. Bis-BDMA was formed in a dose-dependent manner in urine of rats exposed to 0-200 p.p.m. BD by inhalation, although it was a minor metabolite (1%) as compared with DHBMA (47%) and THBMA (37%). In humans, DHBMA was the most abundant BD-mercapturic acid excreted (93%), followed by THBMA (5%) and MHBMA (2%), whereas no bis-BDMA was detected. These results reveal significant differences in metabolism of BD between rats and humans.
人类致癌物1,3 - 丁二烯(BD)会经历代谢活化,生成3,4 - 环氧 - 1 - 丁烯(EB)、羟甲基乙烯基酮(HMVK)、3,4 - 环氧 - 1,2 - 丁二醇(EBD)和1,2,3,4 - 二环氧丁烷(DEB)。其中,DEB是迄今为止最具遗传毒性的代谢产物,被认为是BD的最终致癌物质。我们之前已经表明,暴露于BD的实验小鼠形成的DEB - DNA加合物比在相同条件下暴露的大鼠多8至10倍,这可能是小鼠对BD介导的癌症敏感性增强的原因。在本研究中,我们鉴定出1,4 - 双 -(N - 乙酰 - L - 半胱氨酸 - S - 基)丁烷 - 2,3 - 二醇(双 - BDMA)作为一种新型的DEB特异性尿生物标志物。采用同位素稀释高效液相色谱 - 电喷雾电离 - 串联质谱法对双 - BDMA和其他三种BD - 巯基尿酸进行定量,这三种巯基尿酸分别是2 -(N - 乙酰 - L - 半胱氨酸 - S - 基)- 1 - 羟基丁 - 3 - 烯/1 -(N - 乙酰 - L - 半胱氨酸 - S - 基)- 2 - 羟基丁 - 3 - 烯(MHBMA,来自EB)、4 -(N - 乙酰 - L - 半胱氨酸 - S - 基)- 1,2 - 二羟基丁烷(DHBMA,来自HMVK)和4 -(N - 乙酰 - L - 半胱氨酸 - S - 基)- 1,2,3 - 三羟基丁烷(THBMA,来自EBD),这些物质存在于确诊吸烟者、职业暴露工人以及暴露于BD的实验大鼠的尿液中。通过吸入0 - 200 ppm BD暴露的大鼠尿液中,双 - BDMA以剂量依赖的方式形成,尽管与DHBMA(47%)和THBMA(37%)相比它是一种次要代谢产物(1%)。在人类中,排泄出的BD - 巯基尿酸中DHBMA含量最高(93%),其次是THBMA(5%)和MHBMA(2%),而未检测到双 - BDMA。这些结果揭示了大鼠和人类在BD代谢方面存在显著差异。