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铁矿石和生物炭添加对潜流人工湿地污水处理效果及温室气体排放的影响
引用本文:邹旭青, 郝庆菊, 赵茂森, 陈世杰, 赵仲婧, 熊维霞, 曾唯, 江长胜. 铁矿石和生物炭添加对潜流人工湿地污水处理效果及温室气体排放的影响[J]. 环境工程学报, 2021, 15(2): 588-598. doi: 10.12030/j.cjee.202005025
作者姓名:邹旭青  郝庆菊  赵茂森  陈世杰  赵仲婧  熊维霞  曾唯  江长胜
作者单位:1.西南大学资源环境学院,西南山地生态循环农业国家级培育基地,重庆 400715; 2.西南大学含弘学院,重庆 400715
基金项目:重庆市基础研究与前沿探索项目;重庆市基础研究与前沿探索项目;国家自然科学基金;重庆市大学生创新训练项目
摘    要:
人工湿地是温室气体的重要排放源,为了探索减少其温室气体排放的措施,通过在温室内构建了空白-人工湿地(湿地Ⅰ)、铁矿石-人工湿地(湿地Ⅱ)、生物炭-人工湿地(湿地Ⅲ)和铁矿石+生物炭-人工湿地(湿地Ⅳ)4组湿地,研究了铁矿石和生物炭基质的添加对潜流人工湿地污水处理效果和温室气体排放的影响.结果表明,4组湿地的平均出水CO...

关 键 词:潜流人工湿地  铁矿石  生物炭  污染物去除  温室气体
收稿时间:2020-05-07

Effects of hematite and biochar addition on sewage treatment and greenhouse gases emissions in subsurface flow constructed wetland
ZOU Xuqing, HAO Qingju, ZHAO Maosen, CHEN Shijie, ZHAO Zhongjing, XIONG Weixia, ZENG Wei, JIANG Changsheng. Effects of hematite and biochar addition on sewage treatment and greenhouse gases emissions in subsurface flow constructed wetland[J]. Chinese Journal of Environmental Engineering, 2021, 15(2): 588-598. doi: 10.12030/j.cjee.202005025
Authors:ZOU Xuqing  HAO Qingju  ZHAO Maosen  CHEN Shijie  ZHAO Zhongjing  XIONG Weixia  ZENG Wei  JIANG Changsheng
Affiliation:1.State Cultivation Base of Eco-Agriculture for Southwest Mountainous Land, College of Resources and Environment, Southwest University, Chongqing 400715, China; 2.Institute of Hanhong, Southwest University, Chongqing 400715, China
Abstract:
Constructed wetland is an important source of greenhouse gas emissions. In order to explore measures to reduce their greenhouse gases emissions, in this study, four groups of wetlands, including blank constructed wetland (wetland I), hematite constructed wetland (wetland II), biochar constructed wetland (wetland III) and hematite-biochar constructed wetland (wetland IV) were built to investigate the effect of hematite or biochar addition on the sewage treatment and greenhouse gas emissions of subsurface flow constructed wetlands. The results showed that the average effluent COD concentrations of the four wetlands were (34.99±1.60), (35.57±1.69), (30.87±1.65) and (27.52±2.37) mg·L−1, respectively, and all the COD removal rates reached higher than 90%. The average TN concentrations of the four wetland systems were (24.75±0.96), (24.99±0.72), (15.04±0.61) and (15.63±0.61) mg·L−1, respectively, and the average TN removal rates of wetland III and wetland IV were 65.73% and 64.41%, respectively, both of them were higher than those of wetland I (43.61%) and wetland II (43.08%). Similar to TN, the ${rm{NH}}_4^ + $-N removal rates of the four wetland systems were 45.04%, 43.92%, 67.52% and 65.19%, respectively. The addition of hematite-biochar also had a certain effect on the reduction of CH4 and N2O emissions in the system. With a GWP of 1 g·m−2 CO2 as 1, the average integrated global warming potential (GWP) values of the wetland Ⅱ and wetland Ⅲ systems were 69.88 and 22.73, respectively, and they decreased by 32.39% and 78.01% compared with wetland (103.36), respectively. The GWP value of the CH4 and N2O emissions of wetland IV was similar to that of wetland III with the addition of biochar alone, which was 24.62. Compared with hematite, the addition of biochar caused better sewage treatment effect and lower CH4 and N2O emissions. The biochar in the hematite-biochar wetland plays a major role in removing pollutants and reducing greenhouse gas emissions. This study can provide effective suggestions for the improvement of constructed wetlands.
Keywords:subsurface constructed wetlands  hematite  biochar  pollutant removal  greenhouse gases
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