用户名: 密码: 验证码:
曝气生物滤池处理城市污水的主要影响因素及细菌多样性研究
详细信息    本馆镜像全文|  推荐本文 |  |   获取CNKI官网全文
摘要
本文以青岛麦岛污水处理厂的曝气生物滤池(BAF)为研究对象,分析其在处理以生活污水为主的典型城市污水时的处理效能。首先,考察了不同工艺运行条件与参数对曝气生物滤池净化效能的影响;然后,运用PCR分子生物学技术手段,通过构建16S rDNA基因文库,对青岛麦岛污水处理厂曝气生物滤池中滤料表面生物膜内的细菌多样性进行了系统发育分析;最后,给出了曝气生物滤池有机物降解动力学模型。
     青岛市麦岛污水处理厂的曝气生物滤池对主要污染物COD、NH3-N和SS的年平均去除率分别为58.8%、56.2%和67.6%,处理效能稳定,出水水质能够达到《城镇污水处理厂污染物排放标准》(GB18918-2002)的一级B排放标准,显示了该工艺具有良好的污水处理能力。
     对曝气生物滤池处理城市污水的关键影响因素的研究结果表明,当滤池进水COD和NH3-N质量浓度分别为60-260mg/L和22-65 mg/L时,水力负荷范围为2.5-3.2 m3/m2·h;有机负荷范围为2.2-3.3 kg/m3 d;氨氮负荷范围为0.4-0.8 kg/m3 d;气水比为5:1;温度为15-28℃。NH3-N去除率与进水COD和NH3-N负荷负相关。
     曝气生物滤池滤料表面生物膜内的细菌多样性研究结果表明,滤料表面的优势菌群分别是兼具呼吸/发酵代谢方式的β-变形菌、γ-变形菌和以发酵为主要代谢方式的拟杆菌属。细菌优势顺序为:β-proteobacterium类群(占38.6%),γ-proteobacterium类群(占18.2%),Bacteroidetes类群(占13.6%),α-proteobacterium类群(占9.1%),δ-proteobacterium类群和Nitrospirae类群(各占4.5%),Firmicutes类群(占2.3%),同时还存在9.1%的未知类群。滤池中主要的有机物去除功能菌是食酸假单胞菌、球衣菌、黄单胞菌和黄杆菌;优势亚硝化细菌为亚硝化单胞菌,优势硝化细菌为硝化螺菌;主要的反硝化细菌为生丝微菌和丛毛单胞菌。对测序得到的26个OUT用MEGA软件进行系统发育分析,同样表明滤料表面细菌多样性较强。
     推导得出了曝气生物滤池去除有机物动力学模型,通过对有机底物降解动力学的分析和建模试,得出有机物降解模型为
In this paper, the Biological Aerated Filter (BAF) which was used in Qingdao Maidao sewage treatment plant was studied to analyze its treatment efficiency in treating typical municipal sewage which mainly composed of domestic sewage.First, focused on the influence of different operating conditions and process parameters on the performance of biological aerated filter purify effectiveness;Then, With the help of molecular ecology techniques, such as PCR, with constructing 16S rDNA gene library, bacteria diversity of BAF filter surface biofilm in Qingdao Maidao sewage treatment plant was analyzed by phylogenetic; Finally, BAF kinetics models of removing organic was given.
     BAF was used in Qingdao Maidao Wastewater Treatment Plant for municipal wastewater treatment, major pollutants COD,NH3-N and SS removal rates of the annual average was 58.8%,56.2% and 67.6%, respectively. Processing performance and stability, the effluent indexes are better than the I-B criteria specified in Discharge Standard of Pollution for Municipal Wastewater Treatment Plant(GB18198-2002),shows that the process has a good capacity of sewage treatment.
     Research on Affecting Performance of Biological Aerated Filter for Municipal Wastewater Treatment, the results showed that when COD and NH3-N in influent were between 60-260mg/L and 22-65 mg/L, respectively, the optimum hydraulic loading was between 2.5-3.2m3/(m2h),the optimum COD loading in influent was between 2.2-3.3kg/(m3d),and the optimum NH3-N loading was between 0.4-0.8kg/(m3 d).The optimum gas to liquid ratio was 5:1.The optimum temperature was between 15-28℃. The removal rate was negatively related to COD and NH3-N loading in influent.
     BAF bacterial diversity within the biofilm surface was studied;the results show that the dominant microorganisms of the filter surface areβ-proteobacteria, y-proteobacteria and bacteroidetes.Order of dominance isβ-proteobacterium sp. (accounting for 38.6%),γ-proteobacterium sp.(accounting for 18.2%),bacteroidetes sp. (accounting for 13.6%),α-proteobacterium sp.(accounting for 9.1%), 8-proteobacterium sp. and Nitrospirae sp.(each accounting for 4.5%),Firmicutes sp. (accounting for 2.3%),while there are still 9.1% of unknown groups.In the BAF, Pseudomonas,Sphaerotilus,Xanthomonas and Flavobacterium are dominant microorganisms to remove organic pollutants,Nitrosomonas sp.are advantage nitrosation bacteria, Nitrospira sp.are advantage nitrification bacteria, Hyphomicrobium and Comamonas sp.are advantage denitrifying bacteria.26 OUT phylotypes received from sequencing were analyzed with MEGA, the result also demonstrated that the bacterium on the filter surface in Biological Aerated Filter (BAF) have great diversity.
     The kinetic model of removing organic of Biological Aerated Filter can be obtained through analyzing removal kinetic model of organic esterase:
引文
[1]陶俊杰,于军亭,陈振选等.城市污水处理技术与工程事例[M].化学工业出版社,2005
    [2]邹家华.关于检查<中华人民共和国水污染防治法>实施情况的报告.环境保护,2002,(1)
    [3]吴瑞林.生命之水·生命之源.http://www.grengz.cn.2005-03-24
    [4]王金南等.中国水污染防治体制与政策[M].北京:中国环境科学出版社,2003
    [5]蔡秀萍,王芳,吴启堂.一种同步化学脱氮除磷的碱性活性污泥法废水处理工艺[J].农业环境科学学报,2008,27(5):2002-2007
    [6]乔海兵,王淑莹,李桂荣.连续流间歇曝气氧化沟处理生活污水脱氮除磷研究[J].环境污染治理技术与没备,2006,7(7):11-14
    [7]刘小英,赵红梅,彭党聪,穗贤杰.SBR中生物除磷颗粒污泥的反硝化聚磷研究[J].环境科学,2008,29(8):2254-2259
    [8]王宝贞,王琳.水污染治理新技术.北京:科学出版社,2004.44.55
    [9]郑俊,吴浩汀编著.曝气生物滤池工艺的理论与工程应用.北京:化学工业出版社,2005:325-326
    [10]熊志斌,邵林广.曝气生物滤池技术研究进展[J].当代化工,2009.38(1):61-64
    [11]崔福义,张兵,唐利.曝气生物滤池技术研究与应用进展[J].环境污染治理技术与设备,2005,6(10):1-7.
    [12]刘灿灿,沈耀良.曝气生物滤池的工艺特性及运行控制[J].工业用水与废水,2008,39(2):20-23
    [13]王炜亮,毕学军,张波.曝气生物滤池的特点、应用及发展[J].青岛建筑工程学院学报,2004,25(4):62-67
    [14]刘明坤,郑俊,汪荣.曝气生物滤池的调试及运行[J].中国给水排水,2008,24(4):100-102
    [15]Xiaojun Wang, Sili Chen, Xiaoyang Gu, et al.Pilot study on the advanced treatment of landfill leachate using a combined coagulation, fenton oxidation and biological aerated filter process[J].Waste Management, (2008), doi:10.1016/j.wasman.2008.10.006.
    [16]史一欣,倪晋仁.曝气生物滤池对晚期垃圾渗滤液的短程脱氮研究[J].中国给水排水,2007,23(13):69-75
    [17]Bo Liu, Dongdong Yan, Qi Wang, Song Li, Shaogui Yang, Wenfei Wu, Feasibility of a two-stage biological aerated filter for depth processing of electroplating-wastewater[J], Bioresource Technology,2009,100(17):3891-3896
    [18]董佳,黄瑞敏,高武龙.BAF-微絮凝工艺用于印染废水回用预处理[J].工业用水与废水,2008,39(5):45-52
    [19]李凯,张华伟,曹文平等.BAF工艺预处理微污染水源水的研究[J].中国资源综合利 用,2008,26(7):17-18
    [20]J.A.Herrera Melian, A.Ortega Mendez, J.Arana, etc.Degradation and detoxification of formalin wastewater with aerated biological filters and wetland reactors [J]. Process Biochemistry,2008,43:1432-1435
    [21]Won-Seok Chang, Hung-Thuan Tran, Doo-Hyun Park, Rui-Hong Zhang, Dae-Hee Ahn, Ammonium nitrogen removal characteristics of zeolite media in a Biological Aerated Filter (BAF) for the treatment of textile wastewater[J],Journal of Industrial and Engineering Chemistry, 2009,15(4):524-528,
    [22]Xin Zhao, Yanming Wang, Zhengfang Ye, et al.Oil field wastewater treatment in Biological Aerated Filter by immobilized microorganisms[J].Process Biochemistry,2006,41:1475-1483
    [23]杨金水,刘伟杰,吴佳莲等.曝气生物滤池处理生物质废水及降解菌分析[J].环境科学,2008,29(11):3133-3137
    [24]G. Farabegoli,A.Chiavola, E. Rolle, The Biological Aerated Filter (BAF) as alternative treatment for domestic sewage.Optimization of plant performance[J].Journal of Hazardous Materials,2009,171(15):1126-1132
    [25]Yaqin Zhao, Qinyan Yue, Renbo Li, Min Yue, Shuxin Han, Baoyu Gao, Qian Li,Hui Yu, Research on sludge-fly ash ceramic particles (SFCP) for synthetic and municipal wastewater treatment in biological aerated filter (BAF) [J].Bioresource Technology,2009,100(21):4955-4962
    [26]易彪,陶涛,朱鹏.曝气生物滤池处理城市污水的工程应用[J].中国给水排水,2007,23(20):60-62
    [27]黄绪达,王琳,王洪辉.麦岛污水处理厂BIOSTYR高效生物滤池设计[J].中国给水排水,2008,24(4):51-54
    [28]郑家麒,梁敬斌,王达.曝气生物滤池在生活污水处理中的技术应用.冶金动力,2008,1:79-82
    [29]L. G. Mendoza-Espinosa, T. Stephenson. Organic and Hydraulic Shock Loading on a Biological Aerated Filter. Environmental Technology,2001,22(3):321-330
    [30]Hu Yongyou, Wang Lili.Effect of media heights on the performance of biological aerated filter [J].J Environ Sci.2005,17(2):281-284
    [31]Xie Shuguang, Zhan Xiaojian, Wang Zhansheng. Thermolability of nitrifying activity in biological aerated filter[J].Acta Sci Natural Univ Pekinen,2005,41(2):282-288
    [32]Yanzhen Yu, Yan Feng,Liping Qiu, Wenwen Han, Lipang Guan.Effect of grain-slag media for the treatment of wastewater in a biological aerated filter [J].Bioresource Technology,2007, doi:10.1016/j.biortech.2007.09.001
    [33]Yaqin Zhao, Qinyan Yue, Renbo Li,et al.Research on sludge-fly ash ceramic particles (SFCP) for synthetic and municipal wastewater treatment in biological aerated filter(BAF) [J]. Bioresource Technology,2009,100:4955-4962.
    [34]Xiaojun Wang,Xiaoyang Gu, Dexian Lin, et al.Treatment of acid rose dye containing wastewater by ozonizing e biological aerated filter [J].Dyes and Pigments,2007,74:736-740.
    [35]裴圣,程寒飞,陈祥宏.不同流向BAF硝化影响因素的对比试验[J].环境工程学报,2009,3(2):285-288
    [36]张红品,龙腾锐,何强,曹艳晓.侧向流曝气生物滤池中的生物膜特征分析[J].环境工程学报,2008,2(11):1451-1456
    [37]李微,傅金祥,和娟娟.曝气生物滤池后置反硝化效能研究[J].工业用水与废水,2008,39(6):30-32
    [38]曾正中,王厚成,李勃.曝气生物滤池两种填料挂膜的对比试验[J].环境工程,2008,26(1):21-23
    [39]张薇,史开武,孔惠.曝气生物滤池(BAF)的发展与现状[J].北京石油化工学院学报,2005,13(3):24-30.
    [40]刘灿灿,金吴云,沈耀良,袁煦.陶粒曝气生物滤池处理生活污水影响因素的研究.苏州科技学院学报(工程技术版),2008,21(3):27-32
    [41]黄绪达,王琳.麦岛污水处理厂BIOSTYR高效生物滤池设计[J].中国给水排水,2008,24(4):17-19
    [42]付丹,刘柳.填料对曝气生物滤池影响的概述.环境科学与管理,2008,33(3):101-103
    [43]罗舒君,周培国,张齐生,俞芳芳.竹炭曝气生物滤池去除水中有机物的研究.水处理技术,2009,35(3):86-98
    [44]贾亚梅,徐哲明,许明.曝气生物滤池中COD去除影响因素试验分析.环境科技,2009,2(22):13-16
    [45]郝晓地,魏丽,仇付国.内循环强化曝气生物滤池脱氮性能的研究.中国给水排水,2008,24(19):20-24
    [46]杨文澜.升流式曝气生物滤池处理农村生活污水性能参数的研究.安徽农业科学,2008,36(25):11047-11048,1159
    [47]孙颖,王红芳,门贵斌.轻质陶粒曝气生物滤池处理城市污水厂二级出水的试验研究.中国环境管理干部学院学报,2009,19(1):83-87
    [48]熊集兵,高冲,白向玉,丁杰.低温条件下组合式人工生态系统对二级出水中氮磷的去除效应研究.农业环境科学学报2009,28(3):575-580
    [49]Hill VR,Kahler AM,Jothikumar N,et al.Multi-State evaluation of an ultrafihration-based procedure for simultaneous recovery of enteric microbes in 100-L tap water samples. Appl Environ Microbiol.2007,73(13):4218-4225
    [50]Koizumi Yoshikacu, Kojima Hisaya, Fukui Manabu.Characterization of depth-related microbial community structure in lake sediment by denaturing gradient gel electrophoresis of amplified 16S rDNA and reversely transcribed 16S rRNA fragments.FEMS Microbiology Ecology.2003,46:147-157
    [51]石芳永,宋奔奔,傅松哲.竹子填料海水曝气生物滤器除氮性能和硝化细菌群落变化研究.渔业科学进展,2009,30(1):92-96
    [52]Adler M.Immuno-PCR a clinical laboratory tool.Adv Clin Chem.2006,39:239-292
    [53]He J Z, Xu Z H,Jane H.Prelysis washing improves DNA extraction from a forest soil.Soli Biology Biochemistry.2005,37:2337-2341
    [54]林山杉,金玉花,付丽丽等.砾间接触氧化反应器中填料表面细菌多样性及其主要功能.吉林大学学报(地球科学版).2007,37(2):361-366
    [55]陈接锋,许旭萍,李惠珍.球衣菌属的研究概况.环境科学与技术.2002,25(6):43-46
    [56]王春荣,李军,王宝贞,张国柱.2种不同填料曝气生物滤池处理生活污水的经验模型.环境污染治理技术与设备,2005,6(12):56-60
    [57]Pirt S.J. The maintenance energy of bacteria in growing culture, Proc.R. Soc. London. SerB,1965,163:224-231

© 2004-2018 中国地质图书馆版权所有 京ICP备05064691号 京公网安备11010802017129号

地址:北京市海淀区学院路29号 邮编:100083

电话:办公室:(+86 10)66554848;文献借阅、咨询服务、科技查新:66554700