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人工湿地处理垃圾渗滤液的动力学和质量平衡分析

Kinetic and mass balance analysis of constructed wetlands treating landfill leachate.

作者信息

Sawaittayothin V, Polprasert C

机构信息

School of Environment, Resources and Development, Asian Institute of Technology (AIT), P.O. Box 4, Klong Luang, Pathumthani 12120, Thailand.

出版信息

Environ Technol. 2006 Dec;27(12):1303-8. doi: 10.1080/09593332708618750.

Abstract

Experiments were conducted to investigate the feasibility of applying constructed wetlands to treat a sanitary landfill leachate containing high nitrogen (TN) and bacterial contents. Two-pilot scale subsurface-flow constructed wetland (SFCW) units located at the Asian Institute of Technology, Thailand, campus, were fed with a synthetic wastewater and landfill leachate collected from a nearby sanitary landfill. Under the tropical conditions (temperature of about 30 degrees C), the SFCW units operating at the hydraulic retention time(HRT) of 8 days yielded the best treatment efficiencies with BOD, removal of 91%, TN removal of 96%, total and fecal coliforms (TC and FC) removal of more than 99% and cadmium removal of 99.7%. The treatment performance was found to follow first-order reaction rate, in which the k20 values of BOD5, COD, TN, TC, FC and Cd were 0.201, 0.121, 0.247, 0.346, 0.354 and 0.690 d(-1), respectively. Mass balance analysis, based on TN contents of the plant biomass and dissolved oxygen (DO) and oxidation- reduction potential (ORP) values, suggested that 88% of the input TN were uptaken by the plant biomass; 8% removed by nitrification-denitrification reactions and adsorption on the wetland media, while the remaining 4% were discharged with the effluent.

摘要

开展了实验以研究应用人工湿地处理含有高氮(总氮)和细菌含量的卫生填埋渗滤液的可行性。位于泰国亚洲理工学院校园内的两个中试规模的潜流人工湿地(SFCW)单元,分别用合成废水和从附近卫生填埋场收集的填埋渗滤液进行喂养。在热带条件下(温度约为30摄氏度),水力停留时间(HRT)为8天运行的SFCW单元产生了最佳处理效率,生化需氧量(BOD)去除率为91%,总氮去除率为96%,总大肠菌群和粪大肠菌群(TC和FC)去除率超过99%,镉去除率为99.7%。发现处理性能遵循一级反应速率,其中BOD5、化学需氧量(COD)、总氮、TC、FC和镉的k20值分别为0.201、0.121、0.247、0.346、0.354和0.690 d(-1)。基于植物生物量的总氮含量以及溶解氧(DO)和氧化还原电位(ORP)值的质量平衡分析表明,输入总氮的88%被植物生物量吸收;8%通过硝化反硝化反应和湿地介质吸附去除,而其余4%随流出物排放。

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