Hilton Donald C, Trinidad Debra A, Hubbard Kendra, Li Zheng, Sjödin Andreas
Centers for Disease Control and Prevention, 4770 Buford Highway, Atlanta, GA 30341, USA.
Centers for Disease Control and Prevention, 4770 Buford Highway, Atlanta, GA 30341, USA.
Chemosphere. 2017 Dec;189:365-372. doi: 10.1016/j.chemosphere.2017.09.077. Epub 2017 Sep 18.
Biomonitoring of exposure to polycyclic aromatic hydrocarbons (PAHs) typically uses measurement of metabolites of PAHs with four or less aromatic rings, such as 1-hydroxypyrene, even though interest may be in exposure to larger and carcinogenic PAHs, such as benzo[a]pyrene (B[a]P). An improved procedure for measuring two tetrol metabolites of B[a]P has been developed. Using 2 mL urine, the method includes enzymatic deconjugation of the tetrol conjugates, liquid-liquid extraction, activated carbon solid phase extraction (SPE) and Strata-X SPE, and gas chromatography-electron capture negative ionization-tandem mass spectrometric determination. Limits of detection were 0.026 pg/mL (benzo[a]pyrene-r-7,t-8,t-9,c-10-tetrahydrotetrol, BPT I-1) and 0.090 pg/mL (benzo[a]pyrene-r-7,t-8,c-9,c-10-tetrahydrotetrol, BPT II-1). We quantified BPT I-1 and BPT II-1 in urine from a volunteer who consumed one meal containing high levels of PAHs (barbequed chicken). We also measured urinary concentrations of BPT I-1 and BPT II-1 in smokers and nonsmokers, and compared these concentrations with those of monohydroxy PAHs (OH-PAHs) and cotinine. Urinary elimination of BPT I-1 and BPT II-1 as a function of time after dietary exposure was similar to that observed previously for OH-PAHs. While the median BPT I-1 concentration in smokers' urine (0.069 pg/mL) significantly differs from nonsmokers (0.043 pg/mL), BPT I-1 is only weakly correlated with cotinine. The urinary concentration of BPT I-1 shows a weaker relationship to tobacco smoke than metabolites of smaller PAHs, suggesting that other routes of exposure such as for example dietary routes may be of larger quantitative importance.
多环芳烃(PAHs)暴露的生物监测通常采用对具有四个或更少芳环的PAHs代谢物进行测量,比如1-羟基芘,尽管人们可能关注的是更大的致癌性PAHs暴露,例如苯并[a]芘(B[a]P)。现已开发出一种改进的方法来测量B[a]P的两种四醇代谢物。该方法使用2 mL尿液,包括四醇缀合物的酶促去结合、液液萃取、活性炭固相萃取(SPE)和Strata-X SPE,以及气相色谱-电子捕获负电离-串联质谱测定。检测限分别为0.026 pg/mL(苯并[a]芘-r-7,t-8,t-9,c-10-四氢四醇,BPT I-1)和0.090 pg/mL(苯并[a]芘-r-7,t-8,c-9,c-10-四氢四醇,BPT II-1)。我们对一名食用了一顿富含高浓度PAHs(烤鸡)餐食的志愿者尿液中的BPT I-1和BPT II-1进行了定量分析。我们还测量了吸烟者和非吸烟者尿液中BPT I-1和BPT II-1的浓度,并将这些浓度与单羟基PAHs(OH-PAHs)和可替宁的浓度进行了比较。饮食暴露后,BPT I-1和BPT II-1随时间的尿排泄情况与先前观察到的OH-PAHs情况相似。虽然吸烟者尿液中BPT I-1的中位数浓度(0.069 pg/mL)与非吸烟者(0.043 pg/mL)有显著差异,但BPT I-1与可替宁的相关性较弱。BPT I-1的尿液浓度与烟草烟雾的关系比小分子PAHs代谢物更弱,这表明其他暴露途径,例如饮食途径,在数量上可能具有更大的重要性。