School of Public Health, North China University of Science and Technology, No. 21 Bohai Road, Caofeidian, Tangshan, 063210, Hebei, People's Republic of China.
Department of Occupational and Environmental Health, Tianjin Medical University, Tianjin, 300041, People's Republic of China.
Environ Geochem Health. 2021 Aug;43(8):3067-3081. doi: 10.1007/s10653-021-00819-z. Epub 2021 Jan 27.
Humans spend most of their time in indoor environments, thus a thorough understanding of indoor and outdoor PM-bound polycyclic aromatic hydrocarbons (PAHs) origins for accurate assessment of health risks is required. In the present study, 84 pairs of PM samples from indoor (laboratory) and outdoor (campus) locations were collected from April to December 2018 in Caofeidian, China. The annual median concentration of PM outdoors was 90.80 µg/m, 9.08 times higher than the annual standard of WHO guideline (10 µg/m). Indoor PM annual median concentration (41.80 µg/m) was also higher than the annual standard of ASHRAE guideline (15 µg/m). The annual median concentrations of ∑PAHs indoors (44.23 ng/m) and outdoors (189.6 ng/m) were highest in winter and descended in the order of autumn > spring > summer. Contrary to summer and autumn, indoor/outdoor concentration ratios were less than 1 in spring and winter, indicating that the contribution of outdoor particle infiltration was more significant than that of indoor sources. The positive matrix factorization model suggested that indoor PAHs came from three sources: vehicle emissions (43%), biomass burning (37%), industry emissions, and coal combustion (20%). Outdoor PAHs came from four sources: petroleum volatilization (39%), vehicle emissions (30%), coal combustion (18%), and biomass burning (13%). The incremental lifetime cancer risk values of indoor and outdoor PAHs in winter exceeded the acceptable level (10), and the carcinogenic risk of adults was higher than that of children and teenagers. These results indicated that simultaneous monitoring of indoor and outdoor PAHs is recommended for accurate assessment of health risk, and the analysis in the current work should be helpful to formulate policies to reduce PAHs emissions.
人类大部分时间都在室内环境中度过,因此需要深入了解室内和室外 PM 结合态多环芳烃(PAHs)的来源,以便准确评估健康风险。本研究于 2018 年 4 月至 12 月在中国曹妃甸采集了 84 对室内(实验室)和室外(校园)PM 样本。室外 PM 的年中值浓度为 90.80μg/m³,是世界卫生组织指导值(10μg/m³)的 9.08 倍。室内 PM 的年中值浓度(41.80μg/m³)也高于美国采暖、制冷与空调工程师学会指导值(15μg/m³)。室内(44.23ng/m)和室外(189.6ng/m)∑PAHs 的年中值浓度在冬季最高,随后呈秋季>春季>夏季的递减顺序。与夏季和秋季不同,春季和冬季室内/室外浓度比小于 1,表明室外颗粒物渗透的贡献比室内源更显著。正矩阵因子模型表明,室内 PAHs 来自三个来源:车辆排放(43%)、生物质燃烧(37%)、工业排放和煤炭燃烧(20%)。室外 PAHs 来自四个来源:石油挥发(39%)、车辆排放(30%)、煤炭燃烧(18%)和生物质燃烧(13%)。冬季室内和室外 PAHs 的增量终生癌症风险值超过了可接受水平(10),成人的致癌风险高于儿童和青少年。这些结果表明,为了准确评估健康风险,建议同时监测室内和室外 PAHs,本研究中的分析应有助于制定减少 PAHs 排放的政策。