期刊文献+

温度和游离氨对颗粒与絮状污泥硝化性能影响的对比研究 被引量:4

Effects of Temperature and Free Ammonia Concentration on Nitrification Between the Aerobic Granular and the Floccular Sludges
下载PDF
导出
摘要 采用批式试验,考察了不同温度(10、15、20、25、30℃)及室温下不同游离氨质量浓度(1.76、8.23、14.68、26.52、46.23、90.00 mg/L)对好氧颗粒污泥和絮状污泥硝化作用的影响.结果表明,随着温度的升高,好氧颗粒污泥和絮状污泥的比氨氧化速率均增大,而在相同温度下,好氧颗粒污泥的硝化能力更强,比氨氧化速率分别是絮状污泥的4.5倍(10℃)和2.5倍(30℃).游离氨的试验表明,在游离氨质量浓度为90.00 mg/L时,游离氨对颗粒污泥硝化性能无明显抑制作用,但对絮状污泥抑制作用明显,比氨氧化速率比上一梯度减小了约43%,原因是氨氧化菌均布于絮状污泥中,与氨氮接触充分,易受到抑制,而好氧颗粒污泥的表面生物特征影响氨氮传质速率,使其具有抗高氨氮负荷冲击的优势,可见颗粒污泥在维持生物脱氮系统稳定方面具有较大潜力. Using batch tests, the nitrifying performances were investigated at different temperatures (10, 15, 20, 25, 30 ℃) and free ammonia (FA) concentration p(FA) (1.76, 8.23, 14.68, 26.52, 46.23, 90.00 mg/L) between the Aerobic granular sludge (AGS) and the Floccular sludge (FS). Results show that the specific ammonia oxidation rates of AGS and FS significantly increase with the temperature, however, at the same temperature, the ammonia oxidation rate of AGS is 4.5 times( 10 ℃ ) and 2.5 times (30 % ) of that of FS. When p (FA) = 90.00 mg/L, experiments show that FA has no significant inhibitory effect on AGS but FS, the ammonia oxidation rate of FS decreases by 43% compared with last FA level. This is because the stronger resistance of AGS to the transfer of ammonia into the bacterial aggregates may make it appear to be more tolerant to FA. But in the FS, distributing throughout the entire aggregates, the ammonia oxidizing bacteria (AOB) are more possibly inhibited under high FA loading rate. It can be concluded that the AGS has great potential in withstanding high ammonia loading and maintaining the stability of the biological nitrogen removal performance.
出处 《北京工业大学学报》 CAS CSCD 北大核心 2013年第2期297-303,共7页 Journal of Beijing University of Technology
基金 国家自然科学基金资助项目(50808004) 北京市教委科技创新平台项目
关键词 颗粒污泥 絮状污泥 活化能 游离氨 比氨氧化速率 Aerobic granular sludge floccular sludge activate energy free ammonia (FA) specific ammonia oxidation rate
  • 相关文献

参考文献2

二级参考文献6

共引文献65

同被引文献48

  • 1Sun, HongWei, Yang, Qing, Dong, GuoRi, Hou, HongXun, Zhang, ShuJun, Yang, YingYing, Peng, YongZhen.Achieving the nitrite pathway using FA inhibition and process control in UASB-SBR system removing nitrogen from landfill leachate[J].Science China Chemistry,2010,53(5):1209-1215. 被引量:8
  • 2徐继荣,王友绍,殷建平,孙翠慈,张凤琴,王清吉,何磊,董俊德.大亚湾海域沉积物中的硝化与反硝化作用[J].海洋与湖沼,2007,38(3):206-211. 被引量:22
  • 3GB17378.4-2007.海洋监测规范[S].
  • 4徐敏,牛越,昌晶,王玮,闫逊,张士兵,宋志文.几种理化因子对海洋硝化细菌去除氨氮效果的影响[J].微生物学杂志,2007,27(5):65-69. 被引量:15
  • 5LU S M, LIAO MJ, XIE C X. Removing ammonium from aquaculture ponds using suspended biocarrier-irnmobilized am?monia-oxidizing microorganisms[J]. Annals of Microbiology, 2015, 65 (4) : 2041-2046.
  • 6JAMESJ P, MARTIN T A. Nitrification in the water column and sediment of a hypereutrophic lake and adjoining river system[J]. Water Research, 2000,34(4): 1247-1254.
  • 7WANG C, ZHAI W Y, YIN W, et al. The limiting role of oxygen penetration in sediment nitrification[J]. Environ?mental Science and Pollution Research, 2015,22(14): 10910-10918.
  • 8WANG L, LI T. Effects of seasonal temperature variation on nitrification, anammox process, and bacteria involved in a pilot-scale constructed wetland[J]. Environmental Science and Pollution Research, 2015,22(5): 3774-3783.
  • 9FONTENOT Q, BONVILLAIN C, KILGEN M, et al. Effects of temperature, salinity, and carbon: nitrogen ratio on sequencing batch reactor treating shrimp aquaculture wastewater[J]. Bioresource Research, 2007, 98 ( 9) : 1700-1703.
  • 10YOO H, AHN K H, LEE HJ, et al. Nitrogen removal from synthetic wastewater by simultaneous nitrification and deni?trification (SND) via nitrite in an intermittently-aerated reactor[J]. Water Research, 1999, 33( 1): 145-154.

引证文献4

二级引证文献22

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