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垂直流微电解耦合人工湿地强化处理生活污水的研究
引用本文:张漓杉,涂立俊,钟山,谢沅汕,夏睿泽,田开放.垂直流微电解耦合人工湿地强化处理生活污水的研究[J].环境污染与防治,2019,41(1):1-5,9.
作者姓名:张漓杉  涂立俊  钟山  谢沅汕  夏睿泽  田开放
作者单位:珍稀濒危动植物生态与环境保护省部共建教育部重点实验室,广西 桂林 541006;广西师范大学环境与资源学院,广西 桂林 541004;珍稀濒危动植物生态与环境保护省部共建教育部重点实验室,广西 桂林 541006;广西师范大学环境与资源学院,广西 桂林 541004;珍稀濒危动植物生态与环境保护省部共建教育部重点实验室,广西 桂林 541006;广西师范大学环境与资源学院,广西 桂林 541004;珍稀濒危动植物生态与环境保护省部共建教育部重点实验室,广西 桂林 541006;广西师范大学环境与资源学院,广西 桂林 541004;珍稀濒危动植物生态与环境保护省部共建教育部重点实验室,广西 桂林 541006;广西师范大学环境与资源学院,广西 桂林 541004;珍稀濒危动植物生态与环境保护省部共建教育部重点实验室,广西 桂林 541006;广西师范大学环境与资源学院,广西 桂林 541004
基金项目:国家自然科学基金资助项目;广西科技攻关计划项目;桂林市科技计划项目
摘    要:比较了普通垂直流人工湿地、上升垂直流微电解耦合人工湿地和复合垂直流微电解耦合人工湿地处理生活污水的效果。结果表明,两种微电解耦合人工湿地的启动时间比普通垂直流人工湿地缩短近一半。3种人工湿地对氨氮的去除率无显著差异。对COD和总磷的去除率大小均表现为:复合垂直流微电解耦合人工湿地>上升垂直流微电解耦合人工湿地>普通垂直流人工湿地。3种人工湿地对COD和总磷的去除率随水力停留时间(HRT)的延长而升高。HRT为3d时,上升垂直流微电解耦合人工湿地和复合垂直流微电解耦合人工湿地的出水COD平均质量浓度分别为29.06、19.86mg/L,总磷分别为0.46、0.39mg/L,均达到《城镇污水处理厂污染物排放标准》(GB 18918—2002)的一级A排放要求。由于复合垂直流微电解耦合人工湿地结构复杂、造价高,相比上升垂直流微电解耦合人工湿地对COD和总磷的去除率提高又不明显,故推荐使用上升垂直流微电解耦合人工湿地。

关 键 词:微电解  人工湿地  生活污水  COD  总磷  氨氮

Micro-electrolysis combined vertical flow constructed wetland to enhance domestic wastewater treatment
ZHANG Lishan,TU Lijun,ZHONG Shan,XIE Yuanshan,XIA Ruize,TIAN Kaifang.Micro-electrolysis combined vertical flow constructed wetland to enhance domestic wastewater treatment[J].Environmental Pollution & Control,2019,41(1):1-5,9.
Authors:ZHANG Lishan  TU Lijun  ZHONG Shan  XIE Yuanshan  XIA Ruize  TIAN Kaifang
Institution:(Key Laboratory of Ecology of Rare and Endangered Species and Environmental Protection(Guangxi Normal University),Ministry of Education,Guilin Guangxi 541006;College of Environment and Resources,Guangxi Normal University,Guilin Guangxi 541004)
Abstract:The effects of normal vertical flow constructed wetland,upflow vertical flow micro-electrolysis constructed wetland and composite vertical flow micro-electrolysis constructed wetland on domestic wastewater were compared.Results showed that the start-up time of the two micro-electrolysis constructed wetlands shortened about one half compared with that of normal vertical flow constructed wetland.All the 3 constructed wetlands had little difference to remove ammonia nitrogen.However,for COD and TP,the removal rate showed composite vertical flow micro-electrolysis constructed wetland >upflow vertical flow micro-electrolysis constructed wetland >normal vertical flow constructed wetland.COD and TP removal rates of the 3 constructed wetlands all increased with hydraulic retention time(HRT).When HRT was 3 d,effluent mass concentrations of COD for upflow vertical flow micro-electrolysis constructed wetland and composite vertical flow micro-electrolysis constructed wetland were 29.06 and 19.86 mg/L,and that of TP were 0.46 and 0.39 mg/L,meeting the class 1A of“Discharge standard of pollutants for municipal wastewater treatment plant”(GB 18918-2002).Since the composite vertical flow micro-electrolysis constructed wetland had more complex structure and needed more management,but contributed little to remove COD and TP,therefore,the upflow vertical flow micro-electrolysis constructed wetland was recommended.
Keywords:micro-electrolysis  constructed wetland  domestic wastewater  COD  TP  ammonia nitrogen
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