污水中抗生素生化去除研究进展
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摘要
综述了活性污泥法、膜生物反应器、人工湿地等国内外常见抗生素生化去除方法的优缺点与适用范围,通过工艺对比发现,膜生物反应器和人工湿地能有效去除污水中的抗生素,活性污泥法对抗生素的去除率不高,且选择性较强;污泥龄和水力停留时间对抗生素的去除率有着显著影响,多数情况下反应器的运行改进也能提高抗生素的去除效果。针对抗生素污染问题,提出了采取加强型的复合式处理工艺、开展分区研究、出台相关管理政策等建议。
This paper summarized the merits and demerits,and the scope of application of usual biochemical methods for antibiotics removal at home and abroad,such as activated sludge method,membrane bioreactor,constructed wetlands,etc. Membrane bioreactor and constructed wetland were more effective than activated sludge on removing antibiotics in sewage by comparison their technologies. Activated sludge method had high selectivity. SRT and HRT had significant effects on the removal rate. In most cases,improving the reactor operation could raise the removal efficiency. In view of antibiotic pollution,it gave some suggestions on adopting enhanced compound treatment process,carrying out partition studies and issuing related management policies etc.
This paper summarized the merits and demerits,and the scope of application of usual biochemical methods for antibiotics removal at home and abroad,such as activated sludge method,membrane bioreactor,constructed wetlands,etc. Membrane bioreactor and constructed wetland were more effective than activated sludge on removing antibiotics in sewage by comparison their technologies. Activated sludge method had high selectivity. SRT and HRT had significant effects on the removal rate. In most cases,improving the reactor operation could raise the removal efficiency. In view of antibiotic pollution,it gave some suggestions on adopting enhanced compound treatment process,carrying out partition studies and issuing related management policies etc.
引文
[1] XU W H,YAN W,LI X D,et al. Antibiotics in riverine runoff of the Pearl River Delta and Pearl River Estuary,China:concentrations,mass loading and ecological risks[J]. Environmental Pollution,2013,182(6):402-407.
[2]孙雨,丁剑楠,卢婕,等.长江南京段新兴污染物污染特征及风险评估[J].环境监测管理与技术,2017,29(2):25-30.
[3]高俊红,王兆炜,张涵瑜,等.兰州市污水处理厂中典型抗生素的污染特征研究[J].环境科学学报,2016,36(10):3765-3773.
[4]闾幸.生猪养殖废水及地表水中兽用抗生素污染现状与处理技术研究[D].上海:上海师范大学,2013.
[5]刘晓晖,卢少勇,王炜亮,等.环境中药品和个人护理品的复合污染风险[J].环境监测管理与技术,2016,28(2):10-13.
[6] ZHOU L J,YING G G,LIU S,et al. Occurrence and fate of eleven classes of antibiotics in two typical wastewater treatment plants in South China[J]. Science of the Total Environment,2013,452-453(5):365-376.
[7] MICHAEL I,RIZZO L,MCARDELL C S,et al. Urban wastewater treatment plants as hotspots for the release of antibiotics in the environment:a review[J]. Water Research,2013,47(3):957-995.
[8] RADJENOVIC'J,PETROVIC'M,BARCELO D. Fate and distribution of pharmaceuticals in wastewater and sewage sludge of the conventional activated sludge(CAS)and advanced membrane bioreactor(MBR)treatment[J]. Water Research,2009,43(3):831-841.
[9] YANG S,CARLSON K H. Solid-phase extraction-high-performance liquid chromatography-ion trap mass spectrometry for analysis of trace concentrations of macrolide antibiotics in natural and waste water matrices[J]. Journal of Chromatography A,2004,1038(1-2):141-155.
[10] LI B,ZHANG T. Mass flows and removal of antibiotics in two municipal wastewater treatment plants[J]. Chemosphere,2011,83(9):1284-1289.
[11]柴玉峰,张玉秀,陈梅雪,等.冀西北典型北方小城镇污水处理厂中抗生素的分布和去除[J].环境科学,2018,39(6):2724-2731.
[12] ABEGGLEN C,JOSS A,MCARDELL C S,et al. The fate of selected micropollutants in a single-house MBR[J]. Water Research,2009,43(7):2036-2046.
[13] XIA S,JIA R,FENG F,et al. Effect of solids retention time on antibiotics removal performance and microbial communities in an A/O-MBR process[J]. Bioresource Technology,2012,106(2):36-43.
[14]王琛,李梦凯,阎荣雷,等.紫外/真空紫外反应器对磺胺类抗生素的去除研究[J].中国给水排水,2016,32(9):53-57.
[15]吴曲丽.电化学-臭氧-SBR系统处理水中盐酸环丙沙星的效能[D].哈尔滨:哈尔滨工业大学,2016.
[16] TELSCHER M J H,SCHULLER U,SCHMIDT B,et al. Occurrence of a nitro metabolite of a defined nonylphenol isomer in soil/sewage sludge mixtures[J]. Environmental Science&Technology,2005,39(20):7896-7900.
[17] LUPRANO M L,DE S M,DEL M G,et al. Antibiotic resistance genes fate and removal by a technological treatment solution for water reuse in agriculture[J]. Science of the Total Environment,2016,571:809-818.
[18]罗玉,黄斌,金玉,等.污水中抗生素的处理方法研究进展[J].化工进展,2014,33(9):2471-2477.
[19]贾仁勇,夏四清,张善发.两种MBR工艺处理含抗生素污水效果及反应器内微生物群落结构[J].净水技术,2011,30(5):28-33.
[20]王肖.复合MBR强化去除污水中残留抗生素的效果研究[D].南京:东南大学,2015.
[21]刘红丽,谢文军,王新华. UASB/MBR组合工艺处理抗生素废水的研究[J].中国给水排水,2009,25(15):52-54.
[22] NGUYEN T T,BUI X T,LUU V P,et al. Removal of antibiotics in sponge membrane bioreactors treating hospital wastewater:Comparison between hollow fiber and flat sheet membrane systems[J]. Bioresource Technology,2017,240:42-49.
[23]阿丹.人工湿地对14种常用抗生素的去除效果及影响因素研究[D].广州:暨南大学,2012.
[24] ZHANG S,YANG X L,LI H,et al. Degradation of sulfamethoxazole in bioelectrochemical system with power supplied by constructed wetland-coupled microbial fuel cells[J]. Bioresource Technology,2017,244(1):345-352.
[25]牛瑞华.人工湿地对磺胺类抗生素的去除效果及影响因素研究[D].上海:东华大学,2014.
[26]荣婧.水生植物对水中磺胺嘧啶和左炔诺孕酮去除机理研究[D].重庆:重庆大学,2011.
[27] CHEN J,WEI X D,LIU Y S,et al. Removal of antibiotics and antibiotic resistance genes from domestic sewage by constructed wetlands:Optimization of wetland substrates and hydraulic loading[J]. Science of the Total Environment,2016,565:240-248.
[28] HUANG X,ZHENG J,LIU C,et al. Removal of antibiotics and resistance genes from swine wastewater using vertical flow constructed wetlands:effect of hydraulic flow direction and substrate type[J]. Chemical Engineering Journal,2017,308:692-699.
[29] CHOI Y J,KIM L H,ZOH K D. Removal characteristics and mechanism of antibiotics using constructed wetlands[J]. Ecological Engineering,2016,91:85-92.
[30] QIN Q,WU X,CHEN L,et al. Simultaneous removal of tetracycline and Cu(Ⅱ)by adsorption and coadsorption using oxidized activated carbon[J]. Rsc Advances,2018,8(4):1744-1752.
[31]宋奇轩.改性多壁碳纳米管的制备及对磺胺甲恶唑的吸附研究[D].济南:济南大学,2016.
[32]庄珍珍.高级氧化技术对水中磺胺类抗生素的去除研究[D].赣州:江西理工大学,2015.
[33] WAN Z,WANG J L. Removal of sulfonamide antibiotics from wastewater by gamma irradiation in presence of iron ions[J].核技术(英文版),2016,27(5):104-108.
[2]孙雨,丁剑楠,卢婕,等.长江南京段新兴污染物污染特征及风险评估[J].环境监测管理与技术,2017,29(2):25-30.
[3]高俊红,王兆炜,张涵瑜,等.兰州市污水处理厂中典型抗生素的污染特征研究[J].环境科学学报,2016,36(10):3765-3773.
[4]闾幸.生猪养殖废水及地表水中兽用抗生素污染现状与处理技术研究[D].上海:上海师范大学,2013.
[5]刘晓晖,卢少勇,王炜亮,等.环境中药品和个人护理品的复合污染风险[J].环境监测管理与技术,2016,28(2):10-13.
[6] ZHOU L J,YING G G,LIU S,et al. Occurrence and fate of eleven classes of antibiotics in two typical wastewater treatment plants in South China[J]. Science of the Total Environment,2013,452-453(5):365-376.
[7] MICHAEL I,RIZZO L,MCARDELL C S,et al. Urban wastewater treatment plants as hotspots for the release of antibiotics in the environment:a review[J]. Water Research,2013,47(3):957-995.
[8] RADJENOVIC'J,PETROVIC'M,BARCELO D. Fate and distribution of pharmaceuticals in wastewater and sewage sludge of the conventional activated sludge(CAS)and advanced membrane bioreactor(MBR)treatment[J]. Water Research,2009,43(3):831-841.
[9] YANG S,CARLSON K H. Solid-phase extraction-high-performance liquid chromatography-ion trap mass spectrometry for analysis of trace concentrations of macrolide antibiotics in natural and waste water matrices[J]. Journal of Chromatography A,2004,1038(1-2):141-155.
[10] LI B,ZHANG T. Mass flows and removal of antibiotics in two municipal wastewater treatment plants[J]. Chemosphere,2011,83(9):1284-1289.
[11]柴玉峰,张玉秀,陈梅雪,等.冀西北典型北方小城镇污水处理厂中抗生素的分布和去除[J].环境科学,2018,39(6):2724-2731.
[12] ABEGGLEN C,JOSS A,MCARDELL C S,et al. The fate of selected micropollutants in a single-house MBR[J]. Water Research,2009,43(7):2036-2046.
[13] XIA S,JIA R,FENG F,et al. Effect of solids retention time on antibiotics removal performance and microbial communities in an A/O-MBR process[J]. Bioresource Technology,2012,106(2):36-43.
[14]王琛,李梦凯,阎荣雷,等.紫外/真空紫外反应器对磺胺类抗生素的去除研究[J].中国给水排水,2016,32(9):53-57.
[15]吴曲丽.电化学-臭氧-SBR系统处理水中盐酸环丙沙星的效能[D].哈尔滨:哈尔滨工业大学,2016.
[16] TELSCHER M J H,SCHULLER U,SCHMIDT B,et al. Occurrence of a nitro metabolite of a defined nonylphenol isomer in soil/sewage sludge mixtures[J]. Environmental Science&Technology,2005,39(20):7896-7900.
[17] LUPRANO M L,DE S M,DEL M G,et al. Antibiotic resistance genes fate and removal by a technological treatment solution for water reuse in agriculture[J]. Science of the Total Environment,2016,571:809-818.
[18]罗玉,黄斌,金玉,等.污水中抗生素的处理方法研究进展[J].化工进展,2014,33(9):2471-2477.
[19]贾仁勇,夏四清,张善发.两种MBR工艺处理含抗生素污水效果及反应器内微生物群落结构[J].净水技术,2011,30(5):28-33.
[20]王肖.复合MBR强化去除污水中残留抗生素的效果研究[D].南京:东南大学,2015.
[21]刘红丽,谢文军,王新华. UASB/MBR组合工艺处理抗生素废水的研究[J].中国给水排水,2009,25(15):52-54.
[22] NGUYEN T T,BUI X T,LUU V P,et al. Removal of antibiotics in sponge membrane bioreactors treating hospital wastewater:Comparison between hollow fiber and flat sheet membrane systems[J]. Bioresource Technology,2017,240:42-49.
[23]阿丹.人工湿地对14种常用抗生素的去除效果及影响因素研究[D].广州:暨南大学,2012.
[24] ZHANG S,YANG X L,LI H,et al. Degradation of sulfamethoxazole in bioelectrochemical system with power supplied by constructed wetland-coupled microbial fuel cells[J]. Bioresource Technology,2017,244(1):345-352.
[25]牛瑞华.人工湿地对磺胺类抗生素的去除效果及影响因素研究[D].上海:东华大学,2014.
[26]荣婧.水生植物对水中磺胺嘧啶和左炔诺孕酮去除机理研究[D].重庆:重庆大学,2011.
[27] CHEN J,WEI X D,LIU Y S,et al. Removal of antibiotics and antibiotic resistance genes from domestic sewage by constructed wetlands:Optimization of wetland substrates and hydraulic loading[J]. Science of the Total Environment,2016,565:240-248.
[28] HUANG X,ZHENG J,LIU C,et al. Removal of antibiotics and resistance genes from swine wastewater using vertical flow constructed wetlands:effect of hydraulic flow direction and substrate type[J]. Chemical Engineering Journal,2017,308:692-699.
[29] CHOI Y J,KIM L H,ZOH K D. Removal characteristics and mechanism of antibiotics using constructed wetlands[J]. Ecological Engineering,2016,91:85-92.
[30] QIN Q,WU X,CHEN L,et al. Simultaneous removal of tetracycline and Cu(Ⅱ)by adsorption and coadsorption using oxidized activated carbon[J]. Rsc Advances,2018,8(4):1744-1752.
[31]宋奇轩.改性多壁碳纳米管的制备及对磺胺甲恶唑的吸附研究[D].济南:济南大学,2016.
[32]庄珍珍.高级氧化技术对水中磺胺类抗生素的去除研究[D].赣州:江西理工大学,2015.
[33] WAN Z,WANG J L. Removal of sulfonamide antibiotics from wastewater by gamma irradiation in presence of iron ions[J].核技术(英文版),2016,27(5):104-108.
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