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海洋厌氧氨氧化菌的富集培养及其脱氮特性
引用本文:冯莉,于德爽,李津,单晓静,杨振琳. 海洋厌氧氨氧化菌的富集培养及其脱氮特性[J]. 环境科学, 2017, 38(6): 2435-2443
作者姓名:冯莉  于德爽  李津  单晓静  杨振琳
作者单位:青岛大学环境科学与工程学院, 青岛 266071,青岛大学环境科学与工程学院, 青岛 266071,青岛大学环境科学与工程学院, 青岛 266071,青岛大学环境科学与工程学院, 青岛 266071,青岛大学环境科学与工程学院, 青岛 266071
基金项目:国家自然科学基金项目(51278258,51478229);山东省自然科学基金项目(BS2015HZ007);山东省高等学校科技计划项目(J15LC61)
摘    要:采用ASBR厌氧氨氧化反应器,通过接种胶州湾底泥,研究了海洋厌氧氨氧菌的富集培养及其脱氮特性.实验结果表明:海洋厌氧氨氧化菌的富集培养可分为4个阶段:菌体自溶期(1~15 d)、迟滞期(16~152 d)、活性提高期(153~183 d)与稳定运行期(184~192 d).与淡水厌氧氨氧化相比,其迟滞期(137 d)较长,活性提高期(30 d)较短,对基质浓度与HRT的变化更敏感,且由进出水导致的菌活性延迟时间为5 h,远长于淡水厌氧氨氧化菌,因此海洋厌氧氨氧化菌对新环境的适应能力更弱,更难富集培养.经过192 d运行,对NH_4~+-N与NO-2-N的去除率分别达到96.98%与95.66%,三氮转化比n(NH_4~+-N)∶n(NO-2-N)∶n(NO-3-N)为1∶(1.2±0.2)∶(0.22±0.06),接近理论比(1∶1.32∶0.26),NRRNH_4~+-N升至0.080 kg·(m~3·d)-1,海洋厌氧氨氧化菌活性显著提高,这标志着海洋厌氧氨氧化菌富集成功.反应器运行过程中,污泥逐渐由黑色泥状变为砖红色颗粒状,扫描电镜观察,该砖红色颗粒为表面光滑,排列紧密、有类似火山口形状的球状菌相互黏聚而成的菌团.

关 键 词:海洋厌氧氨氧化菌  富集培养  脱氮效能  高盐废水  污泥性状
收稿时间:2016-11-21
修稿时间:2016-12-10

Enrichment and Nitrogen Removal Characteristics of Marine Anaerobic Ammonium Oxidizing Bacteria
FENG Li,YU De-shuang,LI Jin,SHAN Xiao-jing and YANG Zhen-lin. Enrichment and Nitrogen Removal Characteristics of Marine Anaerobic Ammonium Oxidizing Bacteria[J]. Chinese Journal of Environmental Science, 2017, 38(6): 2435-2443
Authors:FENG Li  YU De-shuang  LI Jin  SHAN Xiao-jing  YANG Zhen-lin
Affiliation:School of Environmental Science and Engineering, Qingdao University, Qingdao 266071, China,School of Environmental Science and Engineering, Qingdao University, Qingdao 266071, China,School of Environmental Science and Engineering, Qingdao University, Qingdao 266071, China,School of Environmental Science and Engineering, Qingdao University, Qingdao 266071, China and School of Environmental Science and Engineering, Qingdao University, Qingdao 266071, China
Abstract:In this work, enrichment and nitrogen removal characteristics of marine anaerobic ammonium oxidizing bacteria were investigated by seeding sediment sludge from the Jiaozhou bay. Experimental results showed that the whole process could be divided into four phases:bacterial lysis phase (1-15 d), lag phase (16-152 d), exponential growth phase (153-183 d) and stationary phase (184-192 d). Compared to freshwater anaerobic ammonium oxidizing bacteria, the lag phase (137 d) was longer. However, the exponential growth phase (30 d) was shorter. Besides, marine anaerobic ammonium oxidizing bacteria were more sensitive to variation in substrate concentration and HRT. The activity delay time caused by inflow and effluent was 5 h, which was far longer than fresh anaerobic ammonium oxidizing bacteria. As a result, the adaptive ability of marine anaerobic ammonium oxidizing bacteria was weaker and it was harder to enrich. After successful enrichment of 192 d, the removal rates of ammonia nitrogen and nitrite nitrogen were 96.98% and 95.66%, respectively. n(NH4+-N):n(NO2--N):n(NO3--N) was 1:(1.2±0.2):(0.22±0.06), which was close to the theoretical ratio. NRRNH4+-Nwas 0.080 kg·(m3·d)-1, which indicated that the activity of marine anaerobic ammonium oxidizing bacteria increased significantly. The enrichment of marine anaerobic ammonium oxidizing bacteria was achieved. The sludge characteristics changed from black to red. SEM observation confirmed that the red granule was cenobium, which consisted of closely spaced micrococcus with smooth surface and crateriform shape.
Keywords:marine anaerobic ammonium oxidizing bacteria  enrichment  nitrogen removal efficiency  high saline wastewater  sludge characteristics
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