State Key Laboratory of Environmental Aquatic Chemistry, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, PR China; National Engineering Laboratory for VOCs Pollution Control Material & Technology, University of Chinese Academy of Sciences, Beijing 101408, PR China.
State Key Laboratory of Environmental Aquatic Chemistry, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, PR China; CSD (Beijing) Water Service Co., Ltd., Beijing 100192, China.
Ecotoxicol Environ Saf. 2019 Mar;169:161-168. doi: 10.1016/j.ecoenv.2018.11.018. Epub 2018 Nov 14.
The characteristics of bioaerosol emissions from wastewater treatment plants (WWTPs) have attracted extensive attention. The anaerobic-anoxic-oxic (AO) process, which uses the activated sludge approach to wastewater treatment, is the most widely used process in WWTPs. Concentration, size distribution, population, and exposure risk from bacteria and fungi in bioaerosols of WWTPs using the AO process were studied in this work. The results showed that the maximum concentration of airborne bacteria (1.00 × 10 Colony Forming Units per cubic meter (CFU m)) and fungi (1.44 ×10 CFU m) occurred from the facility's aerobic tank, in summer. As one of the main factors affecting bioaerosol exposure risk, particle size distribution was related to season. The study found that particles larger than 3.3 µm in diameter were detected mainly in spring and summer, while particles less than 3.3 µm were detected mainly in autumn and winter, whether bacterial aerosol or fungal aerosol. In addition, pathogenic bacteria were observed in bioaerosols from WWTPs, with 18 of the 65 species of bacteria detected found to be potentially or opportunistically pathogenic, such as Chryseobacterium, Stenotrophomonas, Alcaligenes, Micrococcus, Pantoea, Enterobacter and Escherichia-Shigella. The presence of these pathogens further increased the exposure risk from bioaerosols. The results of an inhalation risk assessment for airborne bacteria and fungi indicated that potential adverse health risks for adults mainly occurred in spring, summer, and autumn. On this basis, it was concluded that WWTP operators should set up effective bioaerosol controls as soon as possible to protect the health of workers, and of residents near the plant.
本研究调查了采用活性污泥法处理污水的污水处理厂(WWTP)中厌氧-缺氧-好氧(AO)工艺产生的生物气溶胶的浓度、粒径分布、菌群和细菌及真菌暴露风险。结果表明,夏季,好氧池的空气细菌(1.00×10 个菌落形成单位/立方米(CFU/m3))和真菌(1.44×10 CFU/m3)浓度最高。作为影响生物气溶胶暴露风险的主要因素之一,粒径分布与季节有关。研究发现,春夏季主要检测到粒径大于 3.3μm 的颗粒,秋冬季主要检测到粒径小于 3.3μm 的颗粒,无论是细菌气溶胶还是真菌气溶胶。此外,污水处理厂的生物气溶胶中观察到了病原菌,在所检测的 65 种细菌中,有 18 种被认为具有潜在或机会致病性,如黄杆菌属、寡养单胞菌属、产碱杆菌属、微球菌属、潘多拉菌属、肠杆菌属和埃希氏-志贺氏菌属。这些病原体的存在进一步增加了生物气溶胶的暴露风险。空气中细菌和真菌吸入风险评估的结果表明,成年人主要在春季、夏季和秋季面临潜在的不良健康风险。在此基础上,研究人员得出结论,WWTP 操作人员应尽快建立有效的生物气溶胶控制措施,以保护工人和工厂附近居民的健康。