C/N比对ANAMMOX与反硝化协同脱氮性能影响及其动力学
Influence of C/N on nitrogen removal performance and kinetics characteristics of ANAMMOX/denitrification synergistic interaction
-
摘要: 采用ASBR厌氧氨氧化(ANAMMOX)反应器,考察了不同C/N(NH4+-N)比时厌氧氨氧化与反硝化协同脱氮性能表现,并与无机环境下反应器的脱氮性能相比较。研究结果表明,C/N比决定了ANAMMOX/反硝化耦合反应的发展方向。当C/N4+-N和NO2--N的去除率分别为92%、95%、COD去除率大于96%,实现了氨氮及COD的同时去除;当C/N=1.33时,反硝化反应逐渐占据优势;当C/N>2.96时,反硝化作用成为主导反应,厌氧氨氧化反应受到明显抑制,氨氮去除率下降。采取批次实验方法研究了厌氧氨氧化与反硝化协同反应的动力学特性。用基质抑制动力学Haldane模型拟合不同基质浓度下的厌氧氨氧化活性,得到氨氮最大比增长速率为0.09 kg/(kg·d)(以VSS计),半饱和常数为8.4 mg/L、半抑制常数为1 198.2 mg/L;亚硝态氮最大比增长速率为0.27 kg/(kg·d)(以VSS计),半饱和常数为10.2 mg/L、半抑制常数为300.1 mg/L。采用Monod模型和Haldane模型分别拟合不同COD浓度和亚硝酸盐浓度下的反硝化性能,得到反硝化亚硝态氮最大比增长速率为0.2 kg/(kg VSS·d),半饱和常数为17.4 mg/L、半抑制常数为128.4 mg/L,COD半饱和常数为83.3 mg/L。Abstract: The effect of different C/N(NH4+-N) on nitrogen removal performance by ANAMMOX/denitrification synergistic interaction in anaerobic sequencing batch reactor was investigated. Apart from the ANAMMOX performance under inorganic conditions, the results indicate that C/N ratio determines the direction of development of the ANAMMOX/denitrification synergistic interaction. ANAMMOX is the dominant reaction when the ratio of C/N is less than 0.33. The optimal ratio of C/N is 0.67, and the ammonium and nitrite removal efficiencies were 92% and 95%, respectively. The removal efficiency of COD was also higher than 96%. When the ratio of C/N is higher than 1.33, denitrification reaction share the advantage gradually. When the ratio of C/N is higher than 2.96, denitrification becomes the dominant reaction, and the decreasing removal efficiencies of ammonium indicate the weakening of ANAMMOX reaction. The kinetic characteristics of ANAMMOX/denitrification synergistic interaction were studied through batch tests. The kinetic characteristics of ANAMMOX can be described by the Haldane model as ammonia and nitrite can both inhibit the ANAMMOX biomass. The kinetic parameters were determined, where the maximum specific growth rate of ammonia was 0.09 kg/(kg·d) (calculated as VSS). The half saturation constants and the half inhibition constants of ammonium were 8.4 mg/L and 1 198.2 mg/L, respectively. The maximum specific growth rate of nitrite was 0.27 kg/(kg·d)(calculated as VSS), and the half saturation constants and half inhibition constants for nitrite were 10.2 mg/L and 300.1 mg/L, respectively. The Monod model and the Haldane model were used to determine the kinetic characteristics of COD and nitrite, respectively. The results showed that the maximum specific growth rate of nitrite was 0.2 kg/(kg·d)(calculated as VSS). The half saturation constant of nitrite was 17.4 mg/L, and the half inhibition constant of nitrite was 128.4 mg/L. The half saturation constant of COD was 83.3 mg/L.
-
Key words:
- ANAMMOX /
- denitrification /
- synergistic reaction /
- reaction kinetics /
- C/N
-
-
[1] Mulder A., van de Graaf A. A., Robertson L. A., et al. Anaerobic ammonium oxidation discovered in a denitrifying fluidized bed reactor. FEMS Microbiology Ecology, 1995, 16(3): 177-184 [2] Jetten M. S. M., Cirpus I., Kartal B., et al. 1994-2004: 10 years of research on the anaerobic oxidation of ammonium. Biochemical Society Transactions, 2005, 33(1): 119-123 [3] Ahn Y. H., Hwang I. S., Min K. S. ANAMMOX and partial denitritation in anaerobic nitrogen removal from piggery waste. Water Science and Technology, 2004, 49(5-6): 145-153 [4] 朱静平, 胡勇有, 闫佳. 有机碳源条件下厌氧氨氧化ASBR反应器中的主要反应. 环境科学, 2006, 27(7): 1353-1357 Zhu Jingping, Hu Yongyou, Yan Jia. Main reactions in anaerobic ammonium oxidation reactor under organic carbon condition. Environmental Science, 2006, 27(7): 1353-1357(in Chinese) [5] 秦玉洁, 周少奇, 朱明石. 厌氧氨氧化反应器微生态的研究. 环境科学, 2008, 29(6): 1638-1643 Qin Yujie, Zhou Shaoqi, Zhu Mingshi. Microecology of the anaerobic ammonium oxidation reactor. Environmental Science, 2008, 29(6): 1638-1643(in Chinese) [6] 赖杨岚, 周少奇. 厌氧氨氧化与反硝化的协同作用特性研究. 中国给水排水, 2010, 26(13): 6-10 Lai Yanglan, Zhou Shaoqi. Study on synergism characteristics of ANAMMOX and denitrification. China Water & Wastewater, 2010, 26(13): 6-10(in Chinese) [7] 唐崇俭, 郑平. 厌氧氨氧化膨胀污泥床反应器的化学计量学特性. 中国环境科学, 2010, 30(11): 1446-1452 Tang Chongjian, Zheng Ping. Stoichiometric characteristics of anammox expanded sludge bed reactor. China Environmental Science, 2010, 30(11): 1446-1452(in Chinese) [8] 于德爽, 李伟刚, 李津. ASBR反应器厌氧氨氧化脱氮Ⅰ: 工艺特性与控制策略. 中国环境科学, 2013, 33(12): 2176-2183 Yu Deshuang, Li Weigang, Li Jin. Nitrogen removal in the anammox sequencing batch reactor Ⅰ: Performance and control strategies. China Environmental Science, 2013, 33(12): 2176-2183(in Chinese) [9] 国家环境保护局. 水和废水监测分析方法(第4版). 北京: 中国环境科学出版社, 2002: 258-282 [10] Strous M., Kuenen J. G., Jetten M. S. M. Key physiology of anaerobic ammonium oxidation. Applied and Environmental Microbiology, 1999, 65(7): 3248-3250 [11] Tang Chongjian, Zheng Ping, Chai Liyuan, et al. Thermodynamic and kinetic investigation of anaerobic bioprocesses on ANAMMOX under high organic conditions. Chemical Engineering Journal, 2013, 230: 149-157 [12] 胡勇有, 梁辉强, 朱静平, 等. 有机碳源环境下的厌氧氨氧化批式实验. 华南理工大学学报(自然科学版), 2007, 35(6): 116-119 Hu Yongyou, Liang Huiqiang, Zhu Jingping, et al. Batch experiments of anaerobic ammonium oxidation process with organic carbon. Journal of South China University of Technology (Natural Science Edition), 2007, 35(6): 116-119(in Chinese) [13] Chamchoi N., Nitisoravut N., Schmidt J. E. Inactivation of ANAMMOX communities under concurrent operation of anaerobic ammonium oxidation (ANAMMOX) and denitrification. Bioresource Technology, 2008, 99(9): 3331-3336 [14] Ni Shouqing, Ni Jianyuan, Hu Deliang, et al. Effect of organic matter on the performance of granular anammox process. Bioresource Technology, 2012, 110: 701-705 -

计量
- 文章访问数: 3237
- HTML全文浏览数: 2694
- PDF下载数: 1328
- 施引文献: 0