Liu Shu-Hui, Tian Wei-Jun, Zhou Jian-Ren, Zhao Jing, Wang Zhe
College of Environmental Science and Engineering, Ocean University of China, Qingdao 266100, China.
Key Laboratory of Marine Environmental Science and Ecology, Ministry of Education, Qingdao 266100, China.
Huan Jing Ke Xue. 2019 Feb 8;40(2):747-753. doi: 10.13227/j.hjkx.201807099.
While polycyclic aromatic hydrocarbons (PAHs) are an important persistent toxic organic contaminant, the toxicities of substituted polycyclic aromatic hydrocarbons (SPAHs) are much higher than PAHs. Water and sludge samples were collected from the Qingdao Chengyang Sewage Treatment Plant (STP). The distribution and removal of 16 PAHs and nitro-PAHs (NPAHs), methyl-PAHs (MPAHs), and oxy-PAHs (OPAHs) in the SBR/MBBR process were analyzed. The results showed that 16 PAHs and 13 SPAHs were detected. In the influent water, the total concentrations of PAHs and SPAHs were 3835.14 ng·L and 6889.46 ng·L, respectively, which were much higher than those of STPs in other regions. In the effluent, the total concentrations of PAHs and SPAHs were 1148.18 ng·L and 1724.57 ng·L, respectively, and the removal rates were up to 70.06% and 74.97%, respectively. The SBR/MBBR process presented a more effective removal capacity for PAHs and SPAHs. The removal of PAHs was mainly by the biodegradation of low-ring polycyclic aromatic hydrocarbons (LMW-PAHs)in the aqueous phase; while the removal of PAHsin the particle phase mainly relied on the adsorption and precipitation of LMW-PAHs in the primary sedimentation tank and the biosorption of high-ring polycyclic aromatic hydrocarbons (HMW-PAHs) in the bio-unit. For SPAHs, the removal efficiency of MPAHs (up to 89.15%) was the best under the functions ofparticle adsorption and biodegradation. The removal rate of OPAHs was 63.36%, which was mainly removed by the adsorption of primary particles in the aqueous phase and the biosorption from the biological treatment unit in the particlephase, and the removal rate of NPAHs was 48.85% and largely occurred in the biological treatment unit. The removal mechanism of SPAHs in SBR/MBBR process was not the same. Therefore, STPs should take adequate control measures according to the distribution characteristics of PAHs and SPAHs in different treatment units. Additionally, the concentrations of PAHs and SPAHs in sludge were higher than those in the effluent. Thus, the management of PAHs and SPAHs in sludge should be improved.
虽然多环芳烃(PAHs)是一种重要的持久性有毒有机污染物,但取代多环芳烃(SPAHs)的毒性比PAHs高得多。从青岛城阳污水处理厂(STP)采集了水和污泥样本。分析了序批式活性污泥法/移动床生物膜反应器(SBR/MBBR)工艺中16种PAHs以及硝基多环芳烃(NPAHs)、甲基多环芳烃(MPAHs)和含氧多环芳烃(OPAHs)的分布及去除情况。结果表明,检测到了16种PAHs和13种SPAHs。进水水中,PAHs和SPAHs的总浓度分别为3835.14 ng·L和6889.46 ng·L,远高于其他地区的污水处理厂。出水水中,PAHs和SPAHs的总浓度分别为1148.18 ng·L和1724.57 ng·L,去除率分别高达70.06%和74.97%。SBR/MBBR工艺对PAHs和SPAHs表现出更有效的去除能力。PAHs的去除主要通过水相中低环多环芳烃(LMW-PAHs)的生物降解;而颗粒相中PAHs的去除主要依赖于初沉池中LMW-PAHs的吸附和沉淀以及生物单元中高环多环芳烃(HMW-PAHs)的生物吸附。对于SPAHs,MPAHs在颗粒吸附和生物降解作用下的去除效率最佳(高达89.15%)。OPAHs的去除率为63.36%,主要通过水相中初级颗粒的吸附以及颗粒相中生物处理单元的生物吸附去除,NPAHs的去除率为48.85%,且主要发生在生物处理单元。SBR/MBBR工艺中SPAHs的去除机制不尽相同。因此,污水处理厂应根据不同处理单元中PAHs和SPAHs的分布特征采取适当的控制措施。此外,污泥中PAHs和SPAHs的浓度高于出水。因此,应加强对污泥中PAHs和SPAHs的管理。