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PHBV生物滤池深度脱氮过程中抗生素环丙沙星的同步去除规律及影响因素

迮思文 王宇晖 宋新山 黄威 许中硕 张志兰

迮思文,王宇晖,宋新山,等.PHBV生物滤池深度脱氮过程中抗生素环丙沙星的同步去除规律及影响因素[J].环境工程技术学报,2023,13(1):222-231 doi: 10.12153/j.issn.1674-991X.20210619
引用本文: 迮思文,王宇晖,宋新山,等.PHBV生物滤池深度脱氮过程中抗生素环丙沙星的同步去除规律及影响因素[J].环境工程技术学报,2023,13(1):222-231 doi: 10.12153/j.issn.1674-991X.20210619
ZE S W,WANG Y H,SONG X S,et al.Simultaneous removal of ciprofloxacin in PHBV biofilter denitrification process and its influencing factors[J].Journal of Environmental Engineering Technology,2023,13(1):222-231 doi: 10.12153/j.issn.1674-991X.20210619
Citation: ZE S W,WANG Y H,SONG X S,et al.Simultaneous removal of ciprofloxacin in PHBV biofilter denitrification process and its influencing factors[J].Journal of Environmental Engineering Technology,2023,13(1):222-231 doi: 10.12153/j.issn.1674-991X.20210619

PHBV生物滤池深度脱氮过程中抗生素环丙沙星的同步去除规律及影响因素

doi: 10.12153/j.issn.1674-991X.20210619
基金项目: 上海市科技兴农重点攻关项目(2020-02-08-00-07-F01483);上海市“扬帆计划”(20YF1400200);国家重点研发计划项目(2019YFC0408603);国家自然科学基金项目(31900097)
详细信息
    作者简介:

    迮思文(1997—),女,硕士研究生,研究方向为污水生物脱氮,zsw1997zinnia@163.com

  • 中图分类号: X703

Simultaneous removal of ciprofloxacin in PHBV biofilter denitrification process and its influencing factors

  • 摘要:

    固相碳源是反硝化生物滤池深度脱氮过程中抗生素被同步去除的关键影响因素之一。选取典型抗生素环丙沙星(CIP)为研究对象,搭建固相碳源-聚羟基丁酸戊酸酯(PHBV)反硝化生物滤池,重点考察不同浓度CIP条件下系统的出水水质和微生物群落结构特征变化。结果表明:秋季适宜温度(3~27 ℃)条件下,当进水CIP浓度低于300 μg/L 时,NO3 -N和CIP去除率均超过了95%;冬季低温(−8~12 ℃)条件下,当进水CIP浓度为1 000 μg/L时,NO3 -N和CIP去除率分别为60%和49%。微生物群落结构特征分析显示,变形菌门(Proteobacteria)和丙型变形菌纲(Gammaproteobacteria)分别为最优势门和纲,其中Gammaproteobacteria良好分泌胞外聚合物的特征使其对抗生素具有耐药性。尽管系统长期暴露于CIP中,系统中反硝化菌属物种依然保持较高的相对丰度,其中最优势反硝化菌属脱氯单胞菌(Dechloromonas)在系统纵向沿程中的相对丰度均超过5%,最高达10%。研究证实PHBV反硝化生物滤池是实现深度脱氮并同步去除抗生素的有效技术,同时也为反硝化生物滤池在实际工程中低温运行提供一定的数据支撑。

     

  • 图  1  PHBV反硝化生物滤池装置示意

    Figure  1.  Schematic diagram of PHBV supported denitrification biofilter

    图  2  进出水DO、ORP、pH以及COD变化特征

    Figure  2.  Variation characteristics of effluent DO, ORP, pH and COD

    图  3  PHBV反硝化生物滤池系统的CIP三维荧光特征

    Figure  3.  EEM characteristics of CIP influent and effluent in PHBV supported denitrification biofilter

    图  4  PHBV反硝化生物滤池系统进出水CIP浓度变化

    Figure  4.  Variation of CIP concentrations in influent and effluent in PHBV supported denitrification biofilter

    图  5  PHBV反硝化生物滤池系统NO3 -N浓度变化

    Figure  5.  Nitrate removal performance in PHBV supported denitrification biofilter

    图  6  PHBV反硝化生物滤池系统各阶段进出水NH4 +-N浓度变化

    Figure  6.  Concentration of NH4 +-N in influent and effluent during different phases in PHBV supported denitrification biofilter

    图  7  门水平、纲水平以及属水平上微生物群落相对丰度

    Figure  7.  Relative abundance of microbial communities at phylum, class and genus levels

    表  1  PHBV反硝化生物滤池进水水质特征和运行条件

    Table  1.   Influent characteristics and operation parameters in PHBV supported denitrification biofilter

    阶段运行时间/d温度/℃水力停留时间(HRT)/h进水pHNO3 -N浓度/(mg/L)CIP浓度/(μg/L)
    1~2113~27246.85±0.3115.60~17.030
    22~428~24307.02±0.1115.53~16.740
    43~529~27307.07±0.1415.83~17.58100
    53~723~19307.15±0.2415.44~17.42300
    73~92−5~16307.23±0.1315.20~17.00500
    93~112−8~12307.24±0.1115.03~16.261 000
    下载: 导出CSV

    表  2  PHBV反硝化生物滤池纵向沿程水质变化特征

    Table  2.   Characteristics of water quality along the longitudinal profile in PHBV supported denitrification biofilter

    沿程采样点DO浓度/(mg/L)ORP/mVpHCOD/(mg/L)NO3 -N浓度/(mg/L)NH4 +-N浓度/(mg/L)NO2 -N浓度/(mg/L)CIP浓度/(μg/L)
    进水9.39275.007.768.3515.390.560.011 000.00
    出水口①7.18203.207.3992.5812.860.990.04916.01
    出水口②4.77232.307.2657.5811.100.900.04852.90
    出水口③4.66251.607.3253.6210.180.960.06816.40
    出水口④4.49208.307.4018.228.960.930.04759.03
    出水口⑤4.35214.007.0763.935.940.970.05607.10
    出水3.57162.907.2523.594.311.070.20500.06
    下载: 导出CSV

    表  3  PHBV反硝化生物滤池系统的微生物多样性指数

    Table  3.   Microbial diversity index of PHBV supported denitrification biofilter

    样品编号 Chao1指数 Shannon指数
    a1 3 496.29 8.94
    a2 4 863.72 9.65
    a3 3 766.92 7.52
    a4 4 101.46 7.93
    a5 4 074.57 9.32
    a6 2 192.23 4.77
    下载: 导出CSV
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