NH4+-N was one of the important substrate for ANAMMOX bacteria. But instable nitrogen removal process often occurred and microbial activity even had inhibited by using ANAMMOX bacteria, because of high substrate concentration. In order to effectively avoid NH4+-N inhibition to anammox bacteria activity, the effect of NH4+-N on the activity of anammox bacteria was analysis by inhibitor morphology, main influence factors and inhibiting regularity. The results showed that temperature and pH were important impact on morphology and concentration changes between NH4+-N and FA. The ANAMMOX activity was recovered after 44h operation when the pH was decreased from 7.9 to 7.3under the influent concentration of NH4+-N was fixed at 500mg/L. Half maximal inhibitory concentration (IC50) of FA on ANAMMOX was different when the influent concentration of NH4+-N was variety. IC50 of FA and inhibitory time under different NH4+-N concentrations have relationship (y=732.38x-0.89). Thus, we avoided the effect of FA on activity of anammox bacteria by changing the pH when the influent concentration of NH4+-N was constant. Besides pH decreased, HRT can also be shortened to avoid the effect of FA on activity of ANAMMOX bacteria, when the influent concentration of NH4+-N was fluctuate.
Han Ping, Gu Ji-Dong. Further Analysis of Anammox Bacterial Community Structures Along an Anthropogenic Nitrogen-Input Gradient from the Riparian Sediments of the Pearl River Delta to the Deep-Ocean Sediments of the South China Sea[J]. Geomicrobiology Journal, 2015,32(9):789-798.
[2]
Wang S Y, Zhu G B, Peng Y Z, et al. Anammox Bacterial Abundance, Activity, and Contribution in Riparian Sediments of the Pearl River Estuary[J]. Environmental Science Technology, 2012,46(16):8834-8832.
[3]
Osaka T, Kimura Y, Otsubo Y, et al. Temperature dependence for anammox bacteria enriched from freshwater sediments[J]. Journal of Bioscience and Bioengineering, 2012,114(4):429-434.
HumbertS, Zopfi J, Tarnawski S. Abundance of anammox bacteria in different wetland soils[J]. Environmental Microbiology Reports, 2012,4(5):484-490.
[6]
Ding Z J, Ventorino V, Panico A, et al. Enrichment of Anammox Biomass from Different Seeding Sludge:Process Strategy and Microbial Diversity[J]. Water Air Soil Pollution, 2017,228(1):108-119.
[7]
Ni S Q, Meng J. Performance and inhibition recovery of anammox reactors seeded with different types of sludge[J]. Water Science Technology, 2015,63(4):710-718.
[8]
Nakajima J, Sakka M, Kimura T, et al. Enrichment of anammox bacteria from marine environment for the construction of a bioremediation reactor[J]. Applied Microbiology and Biotechnology, 2008,77(5):1159-1166.
[9]
kawagoshi Y, Nakamura Y, Kawashima H, et al. Enrichment culture of marine anaerobic ammonium oxidation (anammox) bacteria from sediment of sea-based waste disposal site[J]. Journal of bioscience and bioengineering, 2009,107(1):61-63.
郝晓地,仇付国,van der Star WRL,等.厌氧氨氧化技术工程化的全球现状及展望[J]. 中国给水排水, 2007,30(18):15-19.
[12]
Jung J Y, Kang S H, Chung Y C, et al. Factors affecting the activity of Anammox bacteria during start up in the continuous culture reactor[J]. Water Science Technology, 2007,55(1):459-468.
[13]
Jaroszynski L W, Cicek N, Sparling, et al. Impact of free ammonia on anammox rates (aNOxic ammonium oxidation) in a moving bed biofilm reactor[J]. Chemosphere, 2012,88(2):188-195.
Awata T, Tanabe K, Kindaichi T, et al. Influence of temperature and salinity on microbial structure of marine anammox bacteria[J]. Water Science Technology, 2012,66(5):958-964.
[17]
He S L, Zhang Y L, Niu Q G, et al. Operation stability and recovery performance in an Anammox EGSB reactor after pH shock[J]. Ecological Engineering, 2016,90:50-56.
Cema G, Piaza E, Trela J, et al. Dissolved oxygen as a factor influencing nitrogen removal rates in a one-stage system with partial nitritation and Anammox process[J]. Water Science Technology, 2011,64(5):1009-1015.
[20]
Lotti T, van der Star W R L, Kleerebezem R, et al. The effect of nitrite inhibition on the anammox process[J]. Water Research, 2012,46(8):2559-2569.
Anthonisen A C, Loehr R C, Prakasam T B S, et al. Inhibition of nitrification by ammonia and nitrous acid[J]. Journal of Water Pollution Control Federation, 1976,48(5):835-852.
[23]
van der Star W R, Dijkema C, Waard P, et al. An intracellular pH gradient in the anammox bacterium Kuenenia stuttgartiensis as evaluated by 31P NMR[J]. Applied Microbiology and Biotech-nology, 2010,86(1):311-317.
[24]
Kim J H, Guo X J, Park H S. Comparison study of the effects of temperature and free ammonia concentration on nitrification and nitrite accumulation[J]. Process Biochemistry, 2008,43(2):154-160.
[25]
Cema G, PlazaE, Surmacz-Gorska J, et al. Study onevaluation of kinetic parameters for Anammox process[J]. In:IWA 2005 Proceed-ing Specialty Conference, 2005. Krakow, Poland, September 18-21.
[26]
Dapena-Mora A, Fernadez I, Campos JL, et al. Evaluation of activity and inhibition effects on Anammox process by batch tests based on the nitrogen gas production[J]. Enzyme & Microbial Technology, 2006,40(4):859-865.
[27]
Fernández I, Dosta J, Fajardo C, et al. Short and long-term effects of ammonium and nitrite on the Anammox process[J]. Journal of Environmental Management, 2012,95:170-174.
[28]
Niu Q G, He S L, Zhang Y L, et al. Process stability and the recovery control associated with inhibition factors in a UASB-anammox reactor with a long-term operation[J]. Bioresource Technology, 2016,203:132-141.