Environmental Chemistry and Technology Program , University of Wisconsin-Madison , Madison , Wisconsin 53706 , United States.
Institute for Health and Social Policy and Department of Epidemiology, Biostatistics, and Occupational Health , McGill University , Montreal , Quebec H3A 1A3 , Canada.
Environ Sci Technol. 2019 Mar 5;53(5):2788-2798. doi: 10.1021/acs.est.8b05120. Epub 2019 Feb 25.
The chemical constituents of fine particulate matter (PM) vary by source and capacity to participate in redox reactions in the body, which produce cytotoxic reactive oxygen species (ROS). Knowledge of the sources and components of PM may provide insight into the adverse health effects associated with the inhalation of PM mass. We collected 48 h household and personal PM exposure measurements in the summer months among 50 women/household pairs in a rural area of southwestern China where daily household biomass burning is common. PM mass was analyzed for ions, trace metals, black carbon, and water-soluble organic matter, as well as ROS-generating capability (oxidative potential) by one cellular and one acellular assay. Crustal enrichment factors and a principal component analysis identified the major sources of PM as dust, biomass burning, and secondary sulfate. Elements associated with the secondary sulfate source (As, Mo, Zn) had the strongest correlation with increased cellular oxidative potential (Spearman r: 0.74, 0.68, and 0.64). Chemical markers of biomass burning (water-soluble potassium and water-soluble organic matter) had negligible oxidative potential, suggesting that these assays may not be useful as health-relevant exposure metrics in populations that are exposed to high levels of smoke from household biomass burning.
细颗粒物 (PM) 的化学成分因来源和在体内参与氧化还原反应的能力而有所不同,这些反应会产生细胞毒性的活性氧 (ROS)。了解 PM 的来源和成分可以深入了解与吸入 PM 质量相关的不良健康影响。我们在中国西南部一个农村地区的 50 对女性/家庭中收集了夏季 48 小时的家庭和个人 PM 暴露测量数据,那里每天都有家庭生物量燃烧。对 PM 质量进行了离子、痕量金属、黑碳和水溶性有机物分析,以及通过一种细胞和一种非细胞测定法分析了 ROS 生成能力(氧化电位)。地壳富集因子和主成分分析确定了 PM 的主要来源为灰尘、生物质燃烧和二次硫酸盐。与二次硫酸盐来源相关的元素(As、Mo、Zn)与细胞氧化电位升高呈最强相关性(Spearman r:0.74、0.68 和 0.64)。生物质燃烧的化学标志物(水溶性钾和水溶性有机物)的氧化电位可忽略不计,这表明在暴露于高水平家庭生物量燃烧烟雾的人群中,这些测定法可能不适用于与健康相关的暴露指标。