Gong Jicheng, Zhu Tong, Kipen Howard, Rich David Q, Huang Wei, Lin Wan-Ting, Hu Min, Zhang Junfeng Jim
Duke University, Nicholas School of the Environment and Duke Global Health Institute, Durham, NC, USA; University of Southern California, Keck School of Medicine, Department of Preventive Medicine, Los Angeles, CA, USA.
Peking University, College of Environmental Sciences and Engineering and the Center for Environmental Health, Beijing, China.
Environ Int. 2015 Dec;85:104-10. doi: 10.1016/j.envint.2015.09.003. Epub 2015 Sep 16.
1-Nitro-pyrene has been considered a compound specific to diesel combustion emission, while 1- and 2-nitro-napthalene are mainly produced through photochemical conversion of naphthalene released to the atmosphere. Metabolites of these compounds may serve as biomarkers of exposure to traffic related pollutants. We collected urine samples from 111 healthy and non-smoking subjects within (i.e., during the Beijing Olympics) and outside (i.e., before and after the Olympics) a traffic control regime to improve Beijing's air quality. Urines were analyzed for the sum of 1&2-amino-naphthalene (metabolites of 1- and 2-nitro-naphthalene) and 1-amino-pyrene (a metabolite of 1-nitro-pyrene), using an HPLC-fluorescence method. Within the same time periods, PM2.5 mass and constituents were measured, including elemental carbon, sulfate, nitrate, PAHs, carbon monoxide, nitrogen dioxide, sulfur dioxide, ozone, and particle number concentrations. The associations between the urinary metabolites and air pollutants were analyzed using linear mixed-effects models. From the pre- to during-Olympic period, 1&2-amino-naphthalene and 1-hydroxy-pyrene decreased by 23% (p=0.066) and 16% (p=0.049), respectively, while there was no change in 1-amino-pyrene (2% increase, p=0.892). From during- to post-Olympic period, 1&2-amino-naphthalene, 1-amino-pyrene and 1-hydroxy-pyrene concentrations increased by 26% (p=0.441), 37% (p=0.355), and 3% (p=0.868), respectively. Furthermore, 1&2-amino-naphthalene and 1-hydroxy-pyrene were associated with traffic related pollutants in a similar lag pattern. 1-amino-pyrene was associated more strongly with diesel combustion products (e.g. PN and elemental carbon) and not affected by season. Time-lag analyses indicate strongest/largest associations occurred 24-72h following exposure. 1&2-amino-naphthalene and 1-hydroxy-pyrene can be used as a biomarker of exposure to general vehicle-emitted pollutants. More data are needed to confirm 1-amino-pyrene as a biomarker of exposure to diesel combustion emissions. Controlling creatinine as an independent variable in the models will provide a moderate adjusting effect on the biomarker analysis.
1-硝基芘一直被认为是柴油燃烧排放特有的一种化合物,而1-硝基萘和2-硝基萘主要是通过释放到大气中的萘的光化学转化产生的。这些化合物的代谢产物可作为接触交通相关污染物的生物标志物。我们收集了111名健康且不吸烟的受试者在交通管制期间(即北京奥运会期间)和管制期外(即奥运会前后)的尿液样本,此次交通管制旨在改善北京的空气质量。采用高效液相色谱-荧光法分析尿液中1&2-氨基萘(1-硝基萘和2-硝基萘的代谢产物)和1-氨基芘(1-硝基芘的一种代谢产物)的总量。在同一时间段内,测量了PM2.5的质量和成分,包括元素碳、硫酸盐、硝酸盐、多环芳烃、一氧化碳、二氧化氮、二氧化硫、臭氧和颗粒物数量浓度。使用线性混合效应模型分析尿液代谢产物与空气污染物之间的关联。从奥运会前到奥运会期间,1&2-氨基萘和1-羟基芘分别下降了23%(p = 0.066)和16%(p = 0.049),而1-氨基芘没有变化(增加了2%,p = 0.892)。从奥运会期间到奥运会后,1&2-氨基萘、1-氨基芘和1-羟基芘的浓度分别增加了26%(p = 0.441)、37%(p = 0.355)和3%(p = 0.868)。此外,1&2-氨基萘和1-羟基芘与交通相关污染物的关联模式相似。1-氨基芘与柴油燃烧产物(如颗粒物数量和元素碳)的关联更强,且不受季节影响。时间滞后分析表明,最强/最大的关联发生在接触后的24 - 72小时。1&2-氨基萘和1-羟基芘可作为接触一般车辆排放污染物的生物标志物。需要更多数据来确认1-氨基芘作为接触柴油燃烧排放物生物标志物的有效性。在模型中控制肌酐作为自变量将对生物标志物分析提供适度的校正作用。