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Effect of organic compounds on the SAD and its mathematical simulation |
YANG Jing-yue1, LI Jun1, ZHENG Zhao-ming1, DU Jia1, MA Jing2, BIAN Wei1, WANG Wen-xiao1 |
1. College of Architecture and Civil Engineering, Beijing University of Technology, Beijing 100124, China;
2. Beijing Municipal Engineering Professional Design Institute Co., Ltd, Beijing 100037, China |
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Abstract The denitrification performance of simultaneous anammox and denitrification (SAD) granular sludge under different C/N was studied by batch test. The coupled system granular sludge was cultured in a UASB reactor with sufficient nitrogen,and it had high anammox activity and denitrification activity. Using glucose as carbon source, when the C/N were 1, 2, 4, there was no significant difference in the activity of ANAMMOX, and the denitrification activity increased gradually. The maximum rate of NO2--N degradation was 0.265, 0.345, and 0.453kgN/(kgVSS·d), respectively. When sodium acetate was used as the carbon source and the C/N ratios were 1, 2, and 4, respectively, neither of the ANAMMOX activity or the denitrification activity was affected. Under the same C/N, the activity of ANAMMOX with glucose as the carbon source was higher, while the denitrification activity with sodium acetate as the carbon source was higher.When C/N was 1, 2 and 4, the maximum degradation rate of NH4+-N with glucose as organic matter was 1.15, 1.19, 1.58times of sodium acetate respectively. The maximum degradation rate of NO2--N with sodium acetate as organic matter was 1.89, 1.48 and 1.15times of glucose, respectively. The mathematical simulation results of the experiment showed that the models can accurately predict the trend of nitrogen change during the experiment. There was no significant change in the ANAMMOX activity of the granular sludge in the coupled system when the C/N ratio was 1~4.
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Received: 07 May 2018
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[1] |
金仁村,胡宝兰,郑平,等.厌氧氨氧化反应器性能的稳定性及其判据[J]. 化工学报, 2006,57(5):1166-1170.
|
[2] |
李泽兵,刘常敬,赵白航,等.多基质时厌氧氨氧化菌、异养反硝化污泥活性及抑制特征[J]. 中国环境科学, 2013,33(4):648-654.
|
[3] |
Kalyuzhnyi S, Gladchenko M, Mulder A, et al. New anaerobic process of nitrogen removal.[J]. Water Science & Technology A Journal of the International Association on Water Pollution Research, 2006,54(8):163-170.
|
[4] |
周少奇.厌氧氨氧化与反硝化协同作用化学计量学分析[J]. 华南理工大学学报(自然科学版), 2006,34(5):1-4.
|
[5] |
Strous M, Heijnen J J, Kuenen J G, et al. The sequencing batch reactor as a powerful tool for the study of slowly growing anaerobic ammonium-oxidizing microorganisms[J]. Applied Microbiology and Biotechnology, 1998,50(5):589-596.
|
[6] |
朱泽沅,于德爽,李津. C/N比对ANAMMOX与反硝化协同脱氮性能影响及其动力学[J]. 环境工程学报, 2016,10(6):2813-2818.
|
[7] |
刘常敬,李泽兵,郑照明,等.不同有机物对厌氧氨氧化耦合反硝化的影响[J]. 中国环境科学, 2015,35(1):87-94.
|
[8] |
管勇杰,于德爽,李津,等.有机碳源作用下厌氧氨氧化系统的脱氮效能[J]. 环境科学, 2017,38(2):654-664.
|
[9] |
毕贞. Anammox菌的金属暴露响应及其耦合脱氮的数学模拟[D]. 大连理工大学, 2015.
|
[10] |
Gujer W, Henze M, Mino T, et al. Activated sludge model No.3[J]. Water Science & Technology, 1999,39(1):183-193.
|
[11] |
Hiatt W C, Jr G C. An updated process model for carbon oxidation, nitrification, and denitrification.[J]. Water Environment Research A Research Publication of the Water Environment Federation, 2008, 80(11):2145-2156.
|
[12] |
Hao X, Heijnen J J, Van Loosdrecht M C. Model-based evaluation of temperature and inflow variations on a partial nitrification-ANAMMOX biofilm process[J]. Water Research, 2002,36(19):4839.
|
[13] |
Ni B J, Chen Y P, Liu S Y, et al. Modeling a granule-based anaerobic ammonium oxidizing (ANAMMOX) process.[J]. Biotechnology & Bioengineering, 2009,103(3):490-499.
|
[14] |
Bi Z, Takekawa M, Park G, et al. Effects of the C/N ratio and bacterial populations on nitrogen removal in the simultaneous anammox and heterotrophic denitrification process:Mathematic modeling and batch experiments[J]. Chemical Engineering Journal, 2015,280:606-613.
|
[15] |
Jenni S, Vlaeminck S E, Morgenroth E, et al. Successful application of nitritation/anammox to wastewater with elevated organic carbon to ammonia ratios[J]. Water Research, 2014,49:316-326.
|
[16] |
刘金苓,钟玉鸣,谢志儒,等.厌氧氨氧化微生物在有机碳源条件下的代谢特性[J]. 环境科学学报, 2009,29(10):2041-2047.
|
[17] |
Zhu W, Zhang P, Dong H, et al. Effect of carbon source on nitrogen removal in anaerobic ammonium oxidation (anammox) process[J]. Journal of Bioscience and Bioengineering, 2017,123(4):497-504.
|
[18] |
刘常敬,李泽兵,郑照明,等.厌氧氨氧化耦合异养反硝化的脱氮性能及污泥性状[J]. 环境工程学报, 2014,8(8):3137-3142.
|
[19] |
马静,郑照明,王朝朝,等.抗生素对厌氧氨氧化颗粒污泥脱氮性能的影响[J]. 中国环境科学, 2017,37(4):1315-1321.
|
[20] |
Yang X, Wang S, Zhou L. Effect of carbon source, C/N ratio, nitrate and dissolved oxygen concentration on nitrite and ammonium production from denitrification process by Pseudomonas stutzeri D6[J]. Bioresource Technology, 2012,104(1):65-72.
|
[21] |
徐亚同.不同碳源对生物反硝化的影响[J]. 环境科学, 1994, (2):29-32.
|
[22] |
张诗颖,吴鹏,宋吟玲,等.厌氧氨氧化与反硝化协同脱氮处理城市污水[J]. 环境科学, 2015,36(11):4174-4179.
|
[23] |
Elefsiniotis P, Li D. The effect of temperature and carbon source on denitrification using volatile fatty acids[J]. Biochemical Engineering Journal, 2006,28(2):148-155.
|
[24] |
阎宁,金雪标,张俊清.甲醇与葡萄糖为碳源在反硝化过程中的比较[J]. 上海师范大学学报(自然科学版), 2002,31(3):41-44.
|
[25] |
Van D G A, De Brujin P, Robertson L A, et al. Autotrophic growth of anaerobic ammonium-oxidising micro-organisms in a fluidised bed reactor[J]. Microbiology, 1996,142(8):2187-2196.
|
[26] |
操沈彬,王淑莹,吴程程,等.有机物对厌氧氨氧化系统的冲击影响[J]. 中国环境科学, 2013,33(12):2164-2169.
|
[27] |
杨胤,李冬,梁瑜海,等.可降解硝态氮的歧化厌氧氨氧化颗粒污泥的驯化[J]. 中国给水排水, 2014,(23):6-10.
|
[28] |
傅金祥,童颖,于鹏飞,等.有机物对厌氧氨氧化的双向影响及抑制解除[J]. 工业水处理, 2014,34(7):19-22.
|
[29] |
吕永涛,陈祯,吴红亚,等.有机物浓度对厌氧氨氧化脱氮性能影响试验研究[J]. 环境工程学报, 2009,3(7):1189-1192.
|
[30] |
郑照明,李军,杨京月,等.不同C/N比和碳源种类条件下的SNAD生物膜脱氮性能[J]. 中国环境科学, 2017,37(4):1331-1338.
|
|
|
|