Department of Occupational and Environmental Health, University of Milan and Fondazione IRCCS Ospedale Maggiore Policlinico, Mangiagalli e Regina Elena, via S. Barnaba, 8 20122 Milan, Italy.
Toxicol Lett. 2010 Jan 15;192(1):40-4. doi: 10.1016/j.toxlet.2009.02.004. Epub 2009 Feb 11.
The aim of this work is to compare several short-term biomarkers of styrene exposure, namely urinary styrene (StyU), mercapturic acids (M1+M2), mandelic acid (MA), phenylglyoxylic acid (PGA), phenylglycine (PHG), and 4-vinylphenol conjugates (VP), for use as biomarkers of exposure in epidemiologic studies. A repeated measurements protocol (typically 4 measurements per worker over 6 weeks) was applied to measure airborne styrene (StyA) and urinary biomarkers in 10 varnish and 8 fiberglass reinforced plastic workers. Estimated geometric mean personal exposures to StyA were 2.96mg/m(3) in varnish workers and 15.7mg/m(3) in plastic workers. The corresponding levels of StyU, M1+M2, MA, PGA, MA+PGA, PHG and VP were 5.13microg/L, 0.111, 38.2, 22.7, 62.6, 0.978, and 3.97mg/g creatinine in varnish workers and 8.38microg/L, 0.303, 146, 83.4, 232, 2.85 and 3.97mg/g creatinine in plastic workers. Within-worker (sigma(wY)(2)) and between-worker (sigma(bY)(2)) variance components were estimated from the log-transformed data as were the corresponding fold ranges containing 95% of the respective lognormal distributions of daily levels ((w)R(0.95)) and subject-specific mean levels ((b)R(0.95)). Estimates of (w)R(0.95) (range: 4-26) were generally smaller than those of (b)R(0.95) (range: 5-790) for both environmental and biological markers; this indicates that exposures varied much more between workers than within workers in these groups. Since attenuation bias in an estimated exposure-response relationship increases with the variance ratio lambda=sigma(wY)(2)/sigma(bY)(2), we estimated values of lambda for all exposure measures in our study. Values of lambda were typically much less than one (median=0.220) and ranged from 0.089 for M1+M2 in plastic workers to 1.38 for PHG in varnish workers. Since values of lambda were 0.147 and 0.271 for StyA in varnish workers and plastic workers, respectively, compared to 0.178 and 0.210 for MA in the same groups, our results suggest that either air measurements or conventional biomarker measurements (urinary MA) would be comparable surrogates for individual exposures in epidemiologic studies.
这项工作的目的是比较几种苯乙烯短期暴露生物标志物,即尿中苯乙烯(StyU)、硫醚氨酸(M1+M2)、马尿酸(MA)、苯乙醛酸(PGA)、苯甘氨酸(PHG)和 4-乙烯基苯酚缀合物(VP),作为流行病学研究中暴露的生物标志物。在 10 名清漆工和 8 名玻璃纤维增强塑料工人中应用了重复测量方案(通常每个工人在 6 周内进行 4 次测量),以测量空气中的苯乙烯(StyA)和尿生物标志物。估计的个人苯乙烯(StyA)暴露的几何平均水平在清漆工人中为 2.96mg/m(3),在塑料工人中为 15.7mg/m(3)。相应的 StyU、M1+M2、MA、PGA、MA+PGA、PHG 和 VP 水平分别为 5.13μg/L、0.111、38.2、22.7、62.6、0.978 和 3.97mg/g 肌酐在清漆工人中,以及 8.38μg/L、0.303、146、83.4、232、2.85 和 3.97mg/g 肌酐在塑料工人中。从对数转换数据中估计了个体内(sigma(wY)(2))和个体间(sigma(bY)(2))方差分量,以及相应的包含各自日水平((w)R(0.95))和个体特异性平均水平((b)R(0.95))的 95%正态分布的折叠范围。(w)R(0.95)(范围:4-26)的估计值通常小于(b)R(0.95)(范围:5-790)对于这两组环境和生物标志物;这表明在这些组中,暴露在工人之间的变化比在工人内部的变化大得多。由于估计的暴露-反应关系中的衰减偏差随方差比 lambda=sigma(wY)(2)/sigma(bY)(2)增加,因此我们估计了我们研究中所有暴露测量的 lambda 值。lambda 值通常远小于 1(中位数=0.220),范围从塑料工人中 M1+M2 的 0.089 到清漆工人中 PHG 的 1.38。由于 StyA 在清漆工人和塑料工人中的 lambda 值分别为 0.147 和 0.271,而同一组中 MA 的 lambda 值分别为 0.178 和 0.210,我们的结果表明,空气测量或常规生物标志物测量(尿液 MA)均可在流行病学研究中作为个体暴露的可比替代物。