Lutier Simon, Maître Anne, Bonneterre Vincent, Bicout Dominique J, Marques Marie, Persoons Renaud, Barbeau Damien
EPSP-TIMC (CNRS UMR 5525), Université Grenoble Alpes, TIMC-IMAG, F-38000 Grenoble, France.
EPSP-TIMC (CNRS UMR 5525), Université Grenoble Alpes, TIMC-IMAG, F-38000 Grenoble, France; Laboratoire de Toxicologie Professionnelle et Environnementale, DBTP, CHU de Grenoble, France.
Environ Res. 2016 May;147:469-79. doi: 10.1016/j.envres.2016.02.035. Epub 2016 Mar 11.
Polycyclic aromatic hydrocarbons (PAHs) are ubiquitous carcinogenic pollutants emitted in complex mixtures in the ambient air and contribute to the incidence of human cancers. Taking into account all absorption routes, biomonitoring is more relevant than atmospheric measurements to health risk assessment, but knowledge about how to use biomarkers is essential. In this work, urinary elimination kinetic of 1-hydroxypyrene (1-OHP) and 3-hydroxybenzo(a)pyrene (3-OHBaP) were studied in six electrometallurgy workers after PAHs exposure. Spot samples were collected on pre- and post-shift of the last workday then the whole urinations were separately sampled during the weekend. Non-linear mixed effects models were built to study inter- and intra-individual variability of both urinary metabolites toxicokinetic and investigate diuresis correction ways. Comparison of models confirmed the diuresis correction requirement to perform urinary biomonitoring of pyrene and BaP exposure. Urinary creatinine was found as a better way than specific gravity to normalize urinary concentrations of 1-OHP and as a good compromise for 3-OHBaP. Maximum observed levels were 1.0 µmol/mol creatinine and 0.8nmol/mol creatinine for 1-OHP and 3-OHBaP, respectively. Urinary 1-OHP concentrations on post-shift were higher than pre-shift for each subject, while 3-OHBaP levels were steady or decreased, and maximum urinary excretion rates of 3-OHBaP was delayed compared to 1-OHP. These results were consistent with the sampling time previously proposed for 3-OHBaP analysis, the next morning after exposure. Apparent urinary half-life of 1-OHP and 3-OHBaP ranged from 12.0h to 18.2h and from 4.8h to 49.5h, respectively. Finally, inter-individual variability of 1-OHP half-life seemed linked with the cutaneous absorption extent during exposure, while calculation of 3-OHBaP half-life required the awareness of individual urinary background level. The toxicokinetic modeling described here is an efficient tool which could be used to describe elimination kinetic and determine diuresis correction way for any other urinary biomarkers of chemicals or metals exposure.
多环芳烃(PAHs)是环境空气中以复杂混合物形式排放的普遍存在的致癌污染物,会导致人类癌症的发生。考虑到所有吸收途径,生物监测比大气测量对于健康风险评估更为相关,但了解如何使用生物标志物至关重要。在这项工作中,研究了六名电冶金工人在接触多环芳烃后1-羟基芘(1-OHP)和3-羟基苯并(a)芘(3-OHBaP)的尿排泄动力学。在最后一个工作日的班前和班后采集即时样本,然后在周末分别采集全天尿液样本。建立非线性混合效应模型以研究两种尿代谢物毒代动力学的个体间和个体内变异性,并研究利尿校正方法。模型比较证实了进行芘和苯并(a)芘暴露的尿生物监测需要进行利尿校正。发现尿肌酐作为标准化1-OHP尿浓度的方法比比重更好,对于3-OHBaP而言是一个不错的折衷方法。1-OHP和3-OHBaP的最大观察水平分别为1.0微摩尔/摩尔肌酐和0.8纳摩尔/摩尔肌酐。每个受试者班后的尿1-OHP浓度均高于班前,而3-OHBaP水平稳定或下降,并且3-OHBaP的最大尿排泄率比1-OHP延迟。这些结果与先前提出的3-OHBaP分析采样时间(接触后第二天早晨)一致。1-OHP和3-OHBaP的表观尿半衰期分别为12.0小时至18.2小时和4.8小时至49.5小时。最后,1-OHP半衰期的个体间变异性似乎与接触期间的皮肤吸收程度有关,而计算3-OHBaP半衰期需要了解个体尿背景水平。这里描述的毒代动力学模型是一种有效的工具,可用于描述消除动力学并确定任何其他化学物质或金属暴露的尿生物标志物的利尿校正方法。