基于微生物电化学技术的萘普生高盐废水处理

王思祺, 严伟富, 赵峰, 卢小泉. 基于微生物电化学技术的萘普生高盐废水处理[J]. 环境化学, 2020, (4): 1137-1144. doi: 10.7524/j.issn.0254-6108.2019083103
引用本文: 王思祺, 严伟富, 赵峰, 卢小泉. 基于微生物电化学技术的萘普生高盐废水处理[J]. 环境化学, 2020, (4): 1137-1144. doi: 10.7524/j.issn.0254-6108.2019083103
WANG Siqi, YAN Weifu, ZHAO Feng, LU Xiaoquan. Treatment of naproxen high-salt wastewater based on microbial electrochemical technology[J]. Environmental Chemistry, 2020, (4): 1137-1144. doi: 10.7524/j.issn.0254-6108.2019083103
Citation: WANG Siqi, YAN Weifu, ZHAO Feng, LU Xiaoquan. Treatment of naproxen high-salt wastewater based on microbial electrochemical technology[J]. Environmental Chemistry, 2020, (4): 1137-1144. doi: 10.7524/j.issn.0254-6108.2019083103

基于微生物电化学技术的萘普生高盐废水处理

    通讯作者: 卢小泉, E-mail: luxq@nwnu.edu.cn
  • 基金项目:

    国家自然科学基金(21777155)资助.

Treatment of naproxen high-salt wastewater based on microbial electrochemical technology

    Corresponding author: LU Xiaoquan, luxq@nwnu.edu.cn
  • Fund Project: Supported by the National Natural Science Foundation of China (21777155).
  • 摘要: 制药废水是环境中萘普生的主要来源之一,因废水中含盐量较高,传统生物法对其中萘普生的去除效果有限,因此研究如何快速去除制药废水中的萘普生污染以及如何获得高盐废水中快速降解萘普生的功能菌群对生态环境具有重要意义.本研究基于长期驯化的混菌,研究微生物电化学技术在0.3%—3.0%不同盐度下对萘普生的去除效果.驯化后的混菌在108 h对8 mg·L-1萘普生的去除率达到75%以上,并且在3.0%的高盐度下经过108 h去除率可达98%.通过高通量测序技术分析发现,发现相比于原始接种源,在门水平上,驯化后的微生物群落中厚壁菌门(Firmuicutes)和拟杆菌门(Bacteroidales)相对丰度显著增加;而在属水平,在0.3%—1.0%盐度下,真细菌属(Eubacterium spp.)的丰度显著增加至27.9%—50.5%,BacteroidesDysgonomonas等也分别从0.05%、0.03%增加至2.7%—6.8%和10.0%—19.9%;值得注意的是,CastellaniellaPseudomonas在3.0%的高盐度下显著富集至6.9%和37.3%.本研究表明,EubacteriumDysgonomonasBacteroides等菌属能够耐受较低的盐度(0.3%—1.0%),且可能在降解转化萘普生体系中发挥作用;CastellaniellaPseudomonas会在3.0%的高盐环境下富集,可能是两类较好耐盐性且具有较强萘普生降解能力的功能微生物.
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  • [1] GUO N, WANG Y, TONG T, et al. The fate of antibiotic resistance genes and their potential hosts during bio-electrochemical treatment of high-salinity pharmaceutical wastewater[J]. Water Research, 2018, 133:79-86.
    [2] 刘奇,魏东斌,陈振斌,等.医药品和个人护理用品(PPCPs)类污染物氯化转化行为研究进展[J].环境化学,2012,31(3):278-286.

    LIU Q, WEI D B, CHEN Z B, et al. A review on transformation behaviors of PPCPs in chlorination process[J]. Environmental Chemistry, 2012, 31(3):278-286(in Chinese).

    [3] RODRIGUEZ-NARVAEZ O M, MANUEL PERALTA-HERNANDEZ J, GOONETILLEKE A, et al. Treatment technologies for emerging contaminants in water:A review[J]. Chemical Engineering Journal, 2017, 323:361-380.
    [4] 庄榆佳,高阳俊,邓玉君,等.微生物固化曝气技术对养殖废水的深度处理[J].环境化学,2015,34(7):1356-1362.

    ZHUANG Y J, GAO Y J, DENG Y J, et al. Advanced treatment of swine wastewater by the immobilized-microorganism and aeration technology[J]. Environmental Chemistry, 2015, 34(7):1356-1362(in Chinese).

    [5] PETRIE B, BARDEN R, KASPRZYK-HORDERN B. A review on emerging contaminants in wastewaters and the environment:Current knowledge, understudied areas and recommendations for future monitoring[J]. Water Research, 2015, 72:3-27.
    [6] RIVERA-UTRILLA J, SANCHEZ-POLO M, ANGELES FERRO-GARCIA M, et al. Pharmaceuticals as emerging contaminants and their removal from water. A review[J]. Chemosphere, 2013, 93:1268-1287.
    [7] MARCHLEWICZ A, DOMARADZKA D, GUZIK U, et al.Bacillus thuringiensis B1(2015b) is a gram-positive bacteria able to degrade naproxen and ibuprofen[J]. Water Air and Soil Pollution, 2016, 227(6):197-205.
    [8] DOMARADZKA D, GUZIK U, HUPERT-KOCUREK K, et al. Cometabolic degradation of naproxen by Planococcus sp Strain S5[J]. Water Air and Soil Pollution, 2015, 226(9):297-305.
    [9] YAN W, XIAO Y, YAN W, et al. The effect of bioelectrochemical systems on antibiotics removal and antibiotic resistance genes:A review[J]. Chemical Engineering Journal, 2019, 358:1421-1437.
    [10] 梁胜娜,杨俏,高超,等.毒性物质在微生物燃料电池中不同响应的研究进展[J].环境化学, 2018, 37(4):740-752.

    LIANG S N, YANG Q, GAO C, et al. Different responses of toxic substances in microbial fuel cells[J]. Environmental Chemistry, 2018, 37(4):740-752(in Chinese).

    [11] 谢静怡,李永峰,孙彩玉,等.微生物燃料电池耦合连续搅拌反应系统(CSTR)低温下处理"糖蜜-电镀"废水[J].环境化学, 2015, 34(4):786-791.

    XIE J Y, LI Y F, SUN C Y, et al. Microbial fuel cell with continuous stirred reactor system (CSTR) for continuous flow processing of "Molasses-Electroplating" wastewater at low temperatures[J]. Environmental Chemistry, 2015, 34(4):786-791(in Chinese).

    [12] FENG H, ZHANG X, GUO K, et al. Electrical stimulation improves microbial salinity resistance and organofluorine removal in bioelectrochemical systems[J]. Applied and Environmental Microbiology, 2015, 81:3737-3744.
    [13] ZHANG J, ZHANG Y, QUAN X. Electricity assisted anaerobic treatment of salinity wastewater and its effects on microbial communities[J]. Water Research, 2012, 46:3535-3543.
    [14] LOVLEY D R, PHILLIPS E J P. Novel mode of microbial energy-metabolism-organic-carbon oxidation coupled to dissimilatory reduction of iron or manganese[J]. Applied and Environmental Microbiology, 1988, 54:1472-1480.
    [15] XIAO Y, WU S, ZHANG F, et al. Promoting electrogenic ability of microbes with negative pressure[J]. Journal of Power Sources, 2013, 229:79-83.
    [16] CAMPO R, DI PRIMA N, FRENI G, et al. Start-up of two moving bed membrane bioreactors treating saline wastewater contaminated by hydrocarbons[J]. Water Science and Technology, 2016, 73:716-724.
    [17] YAN W, GUO Y, XIAO Y, et al. The changes of bacterial communities and antibiotic resistance genes in microbial fuel cells during long-term oxytetracycline processing[J]. Water Research, 2018, 142:105-114.
    [18] KIELY P D, RADER G, REGAN J M, et al. Long-term cathode performance and the microbial communities that develop in microbial fuel cells fed different fermentation endproducts[J]. Bioresource Technology, 2011, 102:361-366.
    [19] AMORIM C L, MAIA A S, MESQUITA R B R, et al. Performance of aerobic granular sludge in a sequencing batch bioreactor exposed to ofloxacin, norfloxacin and ciprofloxacin[J]. Water Research, 2014, 50:101-113.
    [20] ZHANG Q, ZHANG Y, LI D. Cometabolic degradation of chloramphenicol via a meta-cleavage pathway in a microbial fuel cell and its microbial community[J]. Bioresource Technology, 2017, 229:104-110.
    [21] LEFEBVRE O, VASUDEVAN N, THANASEKARAN K, et al. Microbial diversity in hypersaline wastewater:The example of tanneries[J]. Extremophiles, 2006, 10:505-513.
    [22] WANG L Q, MESELHY M R, LI Y, et al. The heterocyclic ring fission and dehydroxylation of catechins and related compounds by Eubacterium sp strain SDG-2, a human intestinal bacterium[J]. Chemical&Pharmaceutical Bulletin, 2001, 49:1640-1643.
    [23] JIANG Y B, ZHONG W H, HAN C, et al. Characterization of electricity generated by soil in microbial fuel cells and the isolation of soil source exoelectrogenic bacteria[J]. Frontiers in Microbiology, 2016, doi:10.3389/fmicb.2016.01776.
    [24] ALEXANDRINO D A M, MUCHA A P, ALMEIDA C M R, et al. Biodegradation of the veterinary antibiotics enrofloxacin and ceftiofur and associated microbial community dynamics[J]. Science of the Total Environment, 2017, 581:359-368.
    [25] MARTINS M, SANCHES S, PEREIRA I A C. Anaerobic biodegradation of pharmaceutical compounds:New insights into the pharmaceutical-degrading bacteria[J]. Journal of Hazardous Materials, 2018, 357:289-297.
    [26] ZHANG K, LIU Y, LUO H, et al. Bacterial community dynamics and enhanced degradation of di-n-octyl phthalate (DOP) by corncob-sodium alginate immobilized bacteria[J]. Geoderma, 2017, 305:264-274.
    [27] JIANG X-W, LIU H, XU Y, et al. Genetic and biochemical analyses of chlorobenzene degradation gene clusters in Pandoraea sp strain MCB032[J]. Archives of Microbiology, 2009, 191:485-492.
    [28] HERZOG B, LEMMER H, HORN H, et al. Characterization of pure cultures isolated from sulfamethoxazole-acclimated activated sludge with respect to taxonomic identification and sulfamethoxazole biodegradation potential[J]. Bmc Microbiology, 2013, 13:276-286.
    [29] ELABED H, GONZALEZ-TORTUERO E, IBACACHE-QUIROGA C, et al. Seawater salt-trapped pseudomonas aeruginosa survives for years and gets primed for salinity tolerance[J]. Bmc Microbiology, 2019, 19:142-155.
    [30] LI X, ZHAO L, ADAM M. Biodegradation of marine crude oil pollution using a salt-tolerant bacterial consortium isolated from Bohai Bay, China[J]. Marine Pollution Bulletin, 2016, 105:43-50.
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  • 收稿日期:  2019-08-31

基于微生物电化学技术的萘普生高盐废水处理

    通讯作者: 卢小泉, E-mail: luxq@nwnu.edu.cn
  • 1. 西北师范大学地理与环境科学学院, 兰州, 730070;
  • 2. 甘肃省生物电化学与环境分析重点实验室, 兰州, 730070;
  • 3. 中国科学院城市环境研究所, 中国科学院城市污染物转化重点实验室, 厦门, 361021
基金项目:

国家自然科学基金(21777155)资助.

摘要: 制药废水是环境中萘普生的主要来源之一,因废水中含盐量较高,传统生物法对其中萘普生的去除效果有限,因此研究如何快速去除制药废水中的萘普生污染以及如何获得高盐废水中快速降解萘普生的功能菌群对生态环境具有重要意义.本研究基于长期驯化的混菌,研究微生物电化学技术在0.3%—3.0%不同盐度下对萘普生的去除效果.驯化后的混菌在108 h对8 mg·L-1萘普生的去除率达到75%以上,并且在3.0%的高盐度下经过108 h去除率可达98%.通过高通量测序技术分析发现,发现相比于原始接种源,在门水平上,驯化后的微生物群落中厚壁菌门(Firmuicutes)和拟杆菌门(Bacteroidales)相对丰度显著增加;而在属水平,在0.3%—1.0%盐度下,真细菌属(Eubacterium spp.)的丰度显著增加至27.9%—50.5%,BacteroidesDysgonomonas等也分别从0.05%、0.03%增加至2.7%—6.8%和10.0%—19.9%;值得注意的是,CastellaniellaPseudomonas在3.0%的高盐度下显著富集至6.9%和37.3%.本研究表明,EubacteriumDysgonomonasBacteroides等菌属能够耐受较低的盐度(0.3%—1.0%),且可能在降解转化萘普生体系中发挥作用;CastellaniellaPseudomonas会在3.0%的高盐环境下富集,可能是两类较好耐盐性且具有较强萘普生降解能力的功能微生物.

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