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开云全站APP-AAO+流态化生物载体工艺的菌群结构分析 作者:刘敏, 房阔, 王凯军(清华大学环境学院 环境模拟与污染控制国家重点联合实验室,北京 100084)
当前位置: 首页 行业资讯 水业新闻 正文AAO+流态化生物载体工艺的菌群布局阐发 作者:刘敏, 房阔, 王凯军(清华年夜学情况学院 情况摹拟与污染节制国度重点结合尝试室,北京 100084)发布日期:2023-10-07来历:AAO+流态化生物载体工艺的菌群布局阐发 作者:刘敏, 房阅读次数:90焦点提醒:[1]刘敏,房阔,王凯军.AAO+流态化生物载体工艺的菌群布局阐发[J].中国给水排水,2023,39(19):11-18. LIUMin,FANGKuo,WANGKai-jun.Analysis on Microbial Community Composition of AAO+FBC/MBBR System[J].China Water & Wastewater,2023,39(19):11-18.点击复制AAO+流态化生物载体工艺的菌群布局阐发中国给水排水[ISSN:1000-4062/[1]刘敏,房阔,王凯军.AAO+流态化生物载体工艺的菌群布局阐发[J].中国给水排水,2023,39(19):11-18. LIUMin,FANGKuo,WANGKai-jun.Analysis on Microbial Community Composition of AAO+FBC/MBBR System[J].China Water Wastewater,2023,39(19):11-18.点击复制AAO+流态化生物载体工艺的菌群布局阐发中国给水排水[ISSN:1000-4062/CN:12-1073/TU] 卷: 第39卷 期数: 2023年第19期 页码: 11-18 栏目: 出书日期: 2023-10-01Title:Analysis on Microbial Community Composition of AAO+FBC/MBBR System作者:刘敏, 房阔, 王凯军(清华年夜学情况学院 情况摹拟与污染节制国度重点结合尝试室,北京 100084)Author(s):LIU Min, FANG Kuo, WANG Kai-jun(State Key Joint Laboratory of Environmental Simulation and Pollution Control, School of Environment, Tsinghua University, Beijing 100084, China)要害词:城市污水; 脱氮除磷; FBC/MBBR工艺; 菌群布局; 宏基因组阐发Keywords:municipal wastewater; removal of nitrogen and phosphorus; FBC/MBBR process; community composition; metagenomic analysis摘要:为进一步提高脱氮除磷效力,某污水处置厂在好氧池投加填料,将生化段工艺进级为改良型AAO+流态化生物载体工艺(FBC/MBBR)。为考查工艺不变运行后的微生物菌群布局和功能,采取宏基因组测序方式对缺氧池夹杂液、好氧池填料和夹杂液样本进行阐发。成果注解,在门程度上,缺氧池夹杂液、好氧池填料和夹杂液中的优势类群均为变形菌门(Proteobacteria)、放线菌门(Actinobacteria)和绿弯菌门(Chloroflexi)。检测到的聚磷菌(PAO)首要为Accumulibacter(0.81%~0.99%)、Tetrasphaera(0.35%~0.75%)、Mycobacterium(1.00%~1.54%);在好氧池填料上检测到较高品貌的Nitrosomonas(2.8%)和Nitrospira(2.8%);反硝化功能菌首要包罗Dechloromonas、Flavobacterium等。另外,还量化比力阐发了与硝化、反硝化、厌氧氨氧化等脱氮进程相干的功能基因。Abstract:To improve the removal efficiency of nitrogen and phosphorus, the biochemical treatment of a full-scale wastewater treatment plant was renovated into improved AAO and fluidized biological carrier process (FBC/MBBR) by adding fillers to an aerobic tank. In order to investigate the composition and function of the microbial community under stable operation, metagenomic analysis was used to further analyze the samples from anoxic tank, aerobic tank filler and aerobic tank in this wastewater treatment system. Taxonomic analysis showed that the dominant bacterial phyla were Proteobacteria, Actinobacteria and Chloroflexi. The dominant polyphosphate accumulating organism (PAO) found were Accumulibacter (0.81%-0.99%), Tetrasphaera (0.35%-0.75%) and Mycobacterium (1.00%-1.54%). The relative abundance of ammonia-oxidizing bacteria (AOB) and nitrite-oxidizing bacteria (NOB) bacteria were enriched in aerobic biofilm, and the typical AOB and NOB were Nitrosomonas (2.8%) and Nitrospira (2.8%), respectively. The denitrification functional bacteria detected mainly included Dechloromonas, Flavobacterium and so on. Otherwise, various key enzymes related to nitrification, denitrification and Anammox during nitrogen removal were annotated and quantified.类似文献/References:[1]张玲玲,曹洋,顾淼,等.高排放尺度下城市污水深度脱氮手艺研究[J].中国给水排水,2021,37(13):27. ZHANG Ling-ling,CAO Yang,GU Miao,et al.Advanced Nitrogen Removal Technology of Municipal Wastewater under High Discharge Standard[J].China Water Wastewater,2021,37(19):27.[2]阮超,张延军,李胡爽,等.武汉年夜东湖城市污水深隧布局健康监测系统研究[J].中国给水排水,2021,37(20):126. RUAN Chao,ZHANG Yan-jun,LI Hu-shuang,et al.Research on Structure Health Monitoring System of Dadonghu Urban Sewage Deep Tunnel in Wuhan[J].China Water Wastewater,2021,37(19):126.[3]黄良波,黄世浏,曹贵华,等.ABR-AO生化沉淀一体化污水处置工艺设计[J].中国给水排水,2022,38(2):54. HUANG Liang-bo,HUANG Shi-liu,CAO Gui-hua,et al.Design of ABR-AO Biochemical Sedimentation Integrative Wastewater Treatment Process[J].China Water Wastewater,2022,38(19):54.[4]郑晓英,徐智,张远,等.纳米氧化铈对好氧污泥颗粒化历程的影响[J].中国给水排水,2022,38(3):21. ZHENGXiao-ying,XUZhi,ZHANGYuan,et al.Effect of Cerium Oxide Nanoparticles on Aerobic Granulation Process[J].China Water Wastewater,2022,38(19):21.[5]王雄伟,张国珍,武福平,等.两级A/O生物滤池与微絮凝过滤组合处置二级出水[J].中国给水排水,2022,38(5):65. WANGHong-wei,ZHANGGuo-zhen,WU Fu-ping,et al.Two?stage A/O Biofilter Combined with Micro-flocculation Filtration for Secondary Effluent Treatment[J].China Water Wastewater,2022,38(19):65.[6]崔涛,李胜,田敏,等.氧化沟型A2/O工艺脱氮除磷机能评价[J].中国给水排����ȫվAPP水,2022,38(7):75. CUITao,LISheng,TIANMin,et al.Evaluation of Nitrogen and Phosphorus Removal Performance in an Oxidation Ditch Based A2/O Process[J].China Water Wastewater,2022,38(19):75.[7]曾晓岚,尹嘉豪,陈亮,等.电化学工艺处置滇池流域农业面源污水[J].中国给水排水,2022,38(13):105. ZENGXiao-lan,YINJia-hao,CHENLiang,et al.Electrochemical Process for Treatment of Agricultural Non-point Source Sewage in Dianchi Basin[J].China Water Wastewater,2022,38(19):105.[8]何春求,周少奇.改进A2/O MBR工艺仿真摹拟和运行优化[J].中国给水排水,2022,38(15):90. HEChun-qiu,ZHOUShao-qi.Simulation of Modified A2/O-MBR Process and Its Operation Optimization[J].China Water Wastewater,2022,38(19):90.[9]刘流,倪黄蕾,梁军,等.二沉池分歧径向散布活性污泥对脱氮除磷的影响[J].中国给水排水,2022,38(15):104. LIULiu,NIHuang-lei,LIANGJun,et al.Effect of Different Radial Distribution of Activated Sludge on Nitrogen and Phosphorus Removal in Secondary Settling Tank[J].China Water Wastewater,2022,38(19):104.[10]李易寰,董玉明,高芳.AAOA-MBR工艺在污水厂提标扩建中的利用[J].中国给水排水,2022,38(18):114. LIYi-huan,DONGYu-ming,GAOFang.Application of AAOA-MBR Process in Sewage Treatment Plant Upgrading and Expansion[J].China Water Wastewater,2022,38(19):114.更新日期/Last Update: 2023-10-01
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