期刊文献+

城市污水管网中产甲烷菌的分布特性规律 被引量:3

Distribution Characteristics of Methanogens in Urban Sewer System
原文传递
导出
摘要 实验通过一套1200 m的 PVC 管式反应器来模拟城市污水管网,利用气相色谱法、液相色谱法和454高通量测序等手段,研究了城市污水管网中产甲烷过程中的物质变化和产甲烷菌分布特性规律。结果表明,管网中甲烷含量沿程升高,说明管网中存在产甲烷菌;产甲烷菌主要包含甲烷八叠球菌属(Methanosarcina)、广古菌门中的菌属(Euryarchaeota unclassified)和甲烷杆菌科中的菌属(Methanobacteriaceae unclassified)这3种优势菌属,且在管网800~1000 m处有广古菌门中的菌属(Euryarchaeota unclassified)取代甲烷八叠球菌属(Methanosarcina)成为第一优势菌属的演替现象;管网中产甲烷可利用基质有甲酸、甲醇、甲胺、乙酸,其中乙酸为主要基质,这些基质在管网中先增加后降低的变化趋势导致了管网中产甲烷菌演替现象的发生。 A study was conducted through a 1 200 m-PVC-pipe-reactor, which was used to simulate the urban sewer system. Gas chromatography, liquid chromatography and 454 high-throughput sequencing were utilized to study the variation of substrates during the methanogenic process and the distribution characteristics of methanogens in the sewer system. The results showed that the concentration of methane increased along the sewer system, which illustrated that methanogens existed in the sewer network. The methanogens mainly contained Methanosarcina, Euryarchaeota unclassified and Methanobacteriaceae unclassified. The distinct succession which Euryarchaeota unclassified replaced Methanosarcina to be the first dominant microbial genus between 800-1 000 m of the sewer system. Formic acid, methanol, methylamine, acetic acid and hydrogen were available substrates for methanogens. Among these substrates, acetic acid was the primary substrate for methanogen. The variation trends of these substrates were first increasing and then decreasing along the length of the sewer system, which led to the succession phenomenon of methanogens in the sewer system.
出处 《环境科学》 EI CAS CSCD 北大核心 2016年第6期2252-2258,共7页 Environmental Science
基金 国家水体污染控制与治理科技重大专项(2012ZX07313001) 新世纪优秀人才项目(NCET-12-1043) 陕西省创新团队项目(IRT 2013KCT-13)
关键词 城市污水管网 454 高通量测序 甲烷 产甲烷菌 演替现象 urban sewer system 454 high-throughput sequencing methane methanogens succession phenomenon
  • 相关文献

参考文献31

  • 1Mohanakrishnan J, Sharma K R, Meyer R L, et al. Variation in biofilm structure and activity along the length of a rising main sewer[ J ]. Water Environment Research, 2009, 81 (8) : 800- 808.
  • 2Tanaka N, Takenaka K. Control of hydrogen sulfide and degradation of organic matter by air injection into a wastewaterforce main[J]. Water Science and Technology, 1995, 31 (7) : 273-282.
  • 3Leu H G, Ouyang C F, Su J L. Effects of flow velocity changes on nitrogen transport and conversion in an open channel flow[ J]. Water Research, 1996, 30(9) : 2065-2071.
  • 4Raunkjer K, Nielsen P H, Hvitved-Jacobsen T. Acetate removal in sewer biofilms under aerobic conditions[ J]. Water Research, 1997, 31(11) : 2727-2736.
  • 5Warith M A, Kennedy K, Reitsma R. Use of sanitary sewers as wastewater pre-treatment systems [ J ]. Waste Management, 1998, 18(4) : 235-247.
  • 6Gasperi J, Gromaire M C, Karl M, et al. Contributions of wastewater, runoff and sewer deposit erosion to wet weather pollutant loads in combined sewer systems[ J]. Water Research, 2010, 44(20) : 5875-5886.
  • 7. Chen G H, Leung D H W. Utilization of oxygen in a sanitary gravity sewer[ J]. Water Research, 2000, 34 ( 15 ) : 3813-3821.
  • 8Chen G H, Leung D H W, Huang J C. Removal of dissolved organic carbon in sanitary gravity sewer [ J ]. Journal of Environmental Engineering, 2001, 127(4) : 295-301.
  • 9Chen G H, Leung D H W, Hung J C. Biofilm in the sediment phase of a sanitary gravity sewer[ J]. Water Research, 2003, 37 (11) : 2784-2788.
  • 10iEsCy A, Storfjell M, Mellgren L, et al. A comparison of biofilm growth and water quality changes in sewers with anoxic and anaerobic (septic) conditions [ J ]. Water Science and Technology, 1997, 36( 1 ) : 303-310.

二级参考文献93

共引文献64

同被引文献25

引证文献3

二级引证文献6

相关作者

内容加载中请稍等...

相关机构

内容加载中请稍等...

相关主题

内容加载中请稍等...

浏览历史

内容加载中请稍等...
;
使用帮助 返回顶部