Qiao Meng, Qi Wei-xiao, Zhao Xu, Liu Hui-juan, Qu Jiu-hui
Huan Jing Ke Xue. 2016 Apr 15;37(4):1451-9.
Substituted polycyclic aromatic hydrocarbons (SPAHs) can be emitted to the environment not only through the incomplete combustion, but also through the transformation from parent polycyclic aromatic hydrocarbons (PAHs) by photo chemical and biological processes. The toxicities of some SPAHs are higher than their corresponding PAHs. Samples were collected from the wastewater treatment plants in Beijing. Three types of SPAHs, including oxy-PAHs (OPAHs), methyl-PAHs (MPAHs) and nitro-PAHs (NPAHs), as well as 16 PAHs were analyzed, in order to study the occurrence and behavior of these compounds during the wastewater biological treatment process. MPAHs, OPAHs and PAHs were detected in the influent and effluent, but no NPAHs. The concentrations of PAHs in the influent in both the aquatic and particulate phases ranged from 1.94 to 4.34 µg · L⁻¹, and SPAHs from 1.16 to 2.20 µg · L⁻¹. The concentrations of PAHs in the effluent were between 0.77 and 0.98 µg · L⁻¹, and SPAHs from 0.39 to 0.45 µg · L⁻¹. The concentrations of the MPAHs were lower than their corresponding PAHs, while OPAHs were higher. The removal efficiencies of all the compounds ranged from 53% to 83%. PAHs and SPAHs were mainly removed by adsorption and biodegradation during the activated sludge treatment processes. Some OPAHs could be transformed from PAHs, and could be accumulated. The PAHs were mainly originated from incomplete combustion of wood and coal, and some from combustion of petroleum, while only a little from the discharge of petroleum. The concentrations of PAHs and SPAHs in the effluent were higher in autumn than summer and winter. Most of the SPAHs and PAHs were discharged to the agriculture area through the river-water irrigation, which might pose potential risk to the humans. As a result, it is necessary to upgrade the wastewater treatment process to improve the removal efficiency of PAHs and SPAHs.
取代多环芳烃(SPAHs)不仅可通过不完全燃烧排放到环境中,还可通过光化学和生物过程由母体多环芳烃(PAHs)转化而来。一些SPAHs的毒性高于其相应的PAHs。从北京的污水处理厂采集了样本。分析了三种类型的SPAHs,包括含氧多环芳烃(OPAHs)、甲基多环芳烃(MPAHs)和硝基多环芳烃(NPAHs),以及16种PAHs,以研究这些化合物在废水生物处理过程中的存在情况和行为。在进水和出水中检测到了MPAHs、OPAHs和PAHs,但未检测到NPAHs。水相和颗粒相中进水的PAHs浓度范围为1.94至4.34 μg·L⁻¹,SPAHs浓度范围为1.16至2.20 μg·L⁻¹。出水的PAHs浓度在0.77至0.98 μg·L⁻¹之间,SPAHs浓度在0.39至0.45 μg·L⁻¹之间。MPAHs的浓度低于其相应的PAHs,而OPAHs的浓度则较高。所有化合物的去除效率范围为53%至83%。在活性污泥处理过程中,PAHs和SPAHs主要通过吸附和生物降解去除。一些OPAHs可由PAHs转化而来,并可积累。PAHs主要来源于木材和煤炭的不完全燃烧,部分来源于石油燃烧,而仅有少量来源于石油排放。出水的PAHs和SPAHs浓度秋季高于夏季和冬季。大多数SPAHs和PAHs通过河水灌溉排放到农业区,这可能对人类构成潜在风险。因此,有必要升级废水处理工艺以提高PAHs和SPAHs的去除效率。