Modeling kinetics of ammonium oxidation and nitrite oxidation under simultaneous inhibition by free ammonia and free nitrous acid

被引:268
作者
Park, Seongjun [2 ]
Bae, Wookeun [1 ]
机构
[1] Hanyang Univ, Dept Civil & Environm Engn, Ansan 425791, Gyunggi Do, South Korea
[2] Arizona State Univ, Ctr Environm Biotechnol, Biodesign Inst, Tempe, AZ 85287 USA
关键词
Partial nitrification; Nitrite oxidation; Free ammonia; Free nitrous acid; Inhibition kinetics; Modeling; ENRICHED NITROBACTER CULTURE; DIRECT LINEAR PLOT; WASTE-WATER; NITROSOMONAS-EUROPAEA; ENERGY GENERATION; GROWTH-PROCESSES; SHARON PROCESS; MIXED CULTURE; REMOVAL; NITRIFICATION;
D O I
10.1016/j.procbio.2009.02.002
中图分类号
Q5 [生物化学]; Q7 [分子生物学];
学科分类号
071010 ; 081704 ;
摘要
Inhibition of ammonium oxidation and nitrite oxidation by free ammonia (FA) and free nitrous acid (FNA) was studied using three different sludges. An uncompetitive inhibition model fit the experimental data well when the reactions were under FA inhibition, whereas a noncompetitive model fit well under FNA inhibition. The estimates of the inhibition constant (K-1) of nitrite oxidation were 46 mu M for FA and 1.7-6.8 mu M for FNA, each of which was significantly smaller than that of ammonium oxidation, which were 290-1600 mu M for FA and 12 mu M for FNA. The much smaller values of K, for nitrite oxidation reflected the susceptibility of that reaction to inhibition by FA and FNA, which could lead to accumulation of nitrite during nitrification. A kinetic model for simultaneous inhibition by FA and FNA was derived. The model predicted that nitrite oxidation should be affected more seriously than ammonium oxidation by the simultaneous inhibition, which would accelerate the accumulation of nitrite in a strong nitrogenous wastewater treatment. It also indicated that a complete removal of ammonia could be achieved with high accumulation of nitrite in a sequencing batch reactor, which is impossible in a continuous-flow reactor. (C) 2009 Elsevier Ltd. All rights reserved.
引用
收藏
页码:631 / 640
页数:10
相关论文
共 40 条
[21]   Model based design of a novel process for nitrogen removal from concentrated flows [J].
Hellinga, C ;
Van Loosdrecht, MCM ;
Heijnen, JJ .
MATHEMATICAL AND COMPUTER MODELLING OF DYNAMICAL SYSTEMS, 1999, 5 (04) :351-371
[22]  
Henze M., 2000, ACTIVATED SLUDGE MOD, P121, DOI DOI 10.1007/S13398-014-0173-7.2
[23]   HYDROXYLAMINE OXIDOREDUCTASE FROM NITROSOMONAS - INACTIVATION BY HYDROGEN-PEROXIDE [J].
HOOPER, AB ;
TERRY, KR .
BIOCHEMISTRY, 1977, 16 (03) :455-459
[24]   PHOTOINACTIVATION OF AMMONIA OXIDATION IN NITROSOMONAS [J].
HOOPER, AB ;
TERRY, KR .
JOURNAL OF BACTERIOLOGY, 1974, 119 (03) :899-906
[25]  
Jetten MSM, 1998, FEMS MICROBIOL REV, V22, P421, DOI 10.1111/j.1574-6976.1998.tb00379.x
[26]   A model for the simulation of the SHARON process:: pH as a key factor [J].
Magri, A. ;
Corominas, Ll. ;
Lopez, H. ;
Campos, E. ;
Balaguer, M. ;
Colprim, J. ;
Flotats, X. .
ENVIRONMENTAL TECHNOLOGY, 2007, 28 (03) :255-265
[27]   A REVIEW OF LITERATURE ON INORGANIC NITROGEN METABOLISM IN MICROORGANISMS [J].
PAINTER, HA .
WATER RESEARCH, 1970, 4 (06) :393-+
[28]   Empirical model of the pH dependence of the maximum specific nitrification rate [J].
Park, Seongjun ;
Bae, Wookeun ;
Chung, Jinwook ;
Baek, Seung-Cheon .
PROCESS BIOCHEMISTRY, 2007, 42 (12) :1671-1676
[30]  
Strous M, 1999, APPL ENVIRON MICROB, V65, P3248