• 상하수도학회지
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• 제10권3호
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• pp.55-63
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• 1996

Nitrification reaction consists of two reactions: nitritification which oxidizes ammonia nitrogen to nitrite nitrogen and nitratification which oxidizes nitrite nitrogen to nitrate nitrogen. Each reaction is carried out by Nitrosomonas and Nitrobacter, respectively. The effective maximum growth rates for both bacteria have to be determined to design aeration tank whenever the aeration tanks have to nitrify ammonia nitrogen in influent. And these values are very important to use mathematical models such as IAWPRC model to simulate nitrification in activated sludge. There are several methods to determine these valves, however, the Fed-Batch experiments can determine these values within 72 hours. In this study, the mathematical equations and experimental procedures for Fed-Batch test are presented. Also, the experimental data and reported values are compared. The estimated mean values of maximum specific growth rates for Nitrosomonas and Nitrobacter are $0.5010day^{-1}$ and $0.6704day^{-1}$, respectively.

• Journal of Microbiology and Biotechnology
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• 제15권4호
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• pp.772-779
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• 2005

Ammonia-oxidizing bacteria (AOB) were enriched by repeating fed-batch cultivations in an AOB-selective medium of activated sludges from a domestic wastewater treatment plant. Enriched culture showed strong capabilities of ammonia oxidation [0.810 mg $NH_4^+$-N/mg mixed liquor suspended solids (MLSS)$\cdot$day] as well as $NO_x^-$-N production (0.617 mg $NO_x^-$-N/ mg MLSS$\cdot$day). Degree of enrichment was examined through fluorescent in situ hybridization (FISH) analyses using an AOB-specific Cy3-labeled oligonucleotide probe (NSOl90) and terminal-restriction fragment length polymorphism (T-RFLP) analyses. FISH analyses confirmed that the fraction of AOB among 4',6-diamidino-2-phenylindole (DAPI)-stained cells increased from about less than $0.001\%$ to approximately $42\%$ after enrichment of AOB, and T-RFLP analyses showed that bacterial community became simpler as enrichment was continued. When the enriched culture of AOB was added (150 mg/l as dry suspended solid) to the normal activated sludge (3,000 mg/l as dry suspended solid), nitrification efficiencies were improved from 0.020 mg $NO_x^-$-N/mg MLSS$\cdot$day to 0.041 mg $NO_x^-$-N/mg MLSS$\cdot$day in a synthetic wastewater and also from 0.0007 mg $NO_x^-$-N/mg MLSS$\cdot$day to 0.0918 mg $NO_x^-$-N/mg MLSS$\cdot$day in a real domestic wastewater. Therefore, it is expected that this enrichment method could be used for improving efficiency of nitrification in wastewater treatment plants.

• 한국물환경학회지
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• 제34권1호
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• pp.96-108
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• 2018

Large efforts have recently been made on research and development of sustainable and energy-efficient short-cut nitrogen removal processes owing to strong attention to the energy neutral/positive wastewater treatment system. Anaerobic ammonium oxidizing bacteria (anammox bacteria) have been highlighted since 1990's due to their unique advantages including 60% less energy consumption, nearly 100% reduction for carbon source requirement, and 80% less sludge production. Side-stream short-cut nitrogen removal using anammox bacteria and partial nitritation anammox (PN/A) has been well established, whereas substantial challenges remain to be addressed mainly due to undesired main-stream conditions for anammox bacteria. These include low temperature, low concentrations of ammonia, nitrite, free ammonia, free nitrous acid or a combination of those. In addition, an anammox side-stream nitrogen management is insufficient to reduce overall energy consumption for energy-neutral or energy positive water resource recovery facility (WRRF) and at the same time to comply with nitrogen discharge regulation. This implies the development of the successful main-stream anammox based technology will accelerate a conversion of current wastewater treatment plants to sustainable water and energy recovery facility. This study discusses the status of the research, key mechanisms & interactions of the protagonists in the main-stream PN/A, and control parameters and major challenges in process development.

• 한국물환경학회지
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• 제29권3호
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• pp.377-382
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• 2013

Enriching anammox bacteria (AMX) in a lab-scale granular sequencing batch reactor using local digester centrate, we observed the significant enrichment of the filamentous-like bacterial population. These bacteria were revealed as novel bacterial species (termed CHL) belonging to Chlorobi/Bacteroidetes phyla via Denaturing Gradient Gel Electrophoresis (DGGE). Further, niche differentiation of AMX and CHL quantification was observed in granule and filament biomass, suggesting AMX was dominant in the granule and CHL was dominant in the filament. Therefore, it was confirmed the structural role of CHL was indeed to aid the granule formation of the AMX. In parallel, the physiological role of CHL was suspected to degrade biopolymers in the digester centrate using nitrate as an electron acceptor.

• 한국환경과학회지
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• 제14권9호
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• pp.811-815
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• 2005

The activated sludge from the aeration basin of the Su-yeong municipal wastewater treatment plant which has operated by a standard activated sludge process in Busan, Korea was investigated during April 2004 and January 2005 with several bio-indicators. The number of bacteria and fungi per gram of dry weight of MLSS were estimated to be $3.1\times10^6\sim1.5\times10^8\;and\;l.1\times10^3\sim1.1\times10^5$ colony forming units, respectively, by the plate agar method. By cultivation-independent methods, such as 4',6-diamidino-2-phenylindole stain and fluorescence in situ hybridization, the ratio of eubacteria to the entire biomass was evaluated by more than $80\%$ (v/v). The ratio of ammonia-oxidizing bacteria and nitrite-oxidizing bacteria to the total eubacteria was detennined to be $7.0\sim9.8\%\;and\;3.3\sim6.2\%$ without heavy variation in spite of a period of relatively low temperature in the basin. It would be expected that the nitrification would occur or at least co-exist throughout the year in the sludge of many municipal WWTP with influents that contain the sufficient nitrogen sources although the WWTP does not have any specialized processes for the removal of nitrogen.

• 상하수도학회지
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• 제26권6호
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• pp.797-805
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• 2012

Contribution of immobilized media with bacteria to the odor removal was evaluated in a lab scale bio-filter compared to that with sponge or ceramic media without the immobilized bacteria. Candida tropicalis for volatile organic compounds and ammonium oxidizing bacteria (AOB) for inorganic compounds were used as seeds in lab-scale bio-reactors. Three different type of media in the bio-reactors that immobilized bioreactor (IBR), sponge bioreactor (SBR), and ceramic bioreactor (CBR) were examined, respectively. An empty bed contact time (EBCT) of the bio-filters was fixed as 60 seconds, and the inlet concentration of toluene was changed from 20 ppm to 200 ppm to observe the removal efficiency depending on the concentrations. As a result, the maximum elimination capacities of IBR, SBR, and CBR were 166 $g/m^3/hr$, 138 $g/m^3/hr$, and 138 $g/m^3/hr$, respectively. In addition, toluene as an organic compound and ammonia as an inorganic compound were applied together with different inlet concentrations varied from 80 ppm to 250 ppm of toluene and from 2.5 ppm to 40 ppm of ammonia. The toluene maximum elimination capacities in IBR, SBR, and CBR were 97.4 $g/m^3/hr$, 59.5 $g/m^3/hr$, and 81.9 $g/m^3/hr$, respectively. The ammonia maximum elimination capacities were reached as 7.2 $g/m^3/hr$ in IBR, 6.6 $g/m^3/hr$ in SBR, and 7.0 $g/m^3/hr$ in CBR.

• 생태와환경
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• 제35권3호통권99호
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• pp.152-159
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• 2002

농업용 저수지로 축조된 문천지에서 질소순환에 관여하는 질화세균의 연중변화를 현장그대로의 세균상을 반영하는 FISH법으로 정량분석하였다. 아울러 질화세균군의 계절적인 변화와 이화학적인 환경요인과의 상관성을 규명해보기 위해 수온,pH,용존 유기물(DOC),chi-a등이 측정되었다. 총세균수는 정점 1에서 3월에 급격히 상승한 경우를 제외하고는 정점간의 큰 차이가 없이 $0.8{\sim}1.5{\times}10^6\;cells/ml$ 범위에서 변화하였고 eubacteria의 총세균수에 대한 비율는 $44.9{\sim}79.5%$, 질화세균이 eubacteria에서 차지하는 비율은 $1.0{\sim}7.4%$에 그쳤다. 암모니아산화세균은 큰 계절적인 변동이 없이 $1.1{\sim}3.0{\times}10^4\;cell/ml$범위에서 변화한 반면에 아질산산화세균은　정점에 관계없이 겨울철에 증가하는 양상을 나타냈다($1.3{\sim}5.7{\times}10^4\;cells/ml$).또한 암모니아산화세균보다 아질산산화세균이 대체적으로 더 많은 개체수를 나타냈다. 아울러 이화학적인 환경요인 중,　수온은 총세균수와 양의 상관성 (r=0.355, p<0.05),　그리고 아질산산화세균과는 음의 상관성 (r= -0.416, p<0.05)을 보였다. 마찬가지로 아질산산화세균은 pH와도 음의 상관성 (r= -0.568,p<0.01)을 나타냈다. 아울러 DOC는 총세균수(r = 0.586,p<0.000), 　eubacteria (r = 0.448, p<0.01)와 긴밀한 상관관계에 있는 것으로 나타났다. 따라서 문천지에서는 수온, DOC 그리고 pH가 수계 세균군집구조를 변화시키는　중요한 요인으로 작용함을 알 수 있었다. 또한 FISH법은 느리게 성장하는 질화세균군을 정량 분석할 수 있는　유용한 기법으로 평가된다.기간동안 강우의 빈도 및 강도는 하천의 육수학적 현상 변화와 패턴에 중요한 요소로서 작용하며, 이는 동아시아몬순기후대에 속하는 하천들에서 유사하게 발생하는 하천의 중요한 특성으로 사료된다.다. 정화효율과 수리학적조건간의 상관계수($R^2$)는 수리학적 체류시간과 0.016-0.731,일처리유량과는 0.015-0.868을 나타내었으며, 시간당 정화량과 수리학적 조건간의 상관계수($R^2$)는 수리학적 체류시간과는 0.173-0.763,일처리유량과는 0.209-0.770의 범위를 나타내었다. 정화효율과 수리학적 부하조건간의 상관계수($R^2$)Tt 0.5 이상을 나타내는 각 수생식물 습지별 수질항목은 체류시간과 일처리유량에 대해각각 20%,정화속도와 수리학적 조건간의 상관계수는 체류시간에 대해 53%, 일처리유량에 대해73%가 0.5이상을 보이고 있어 시간당 정화량과 수리학적 조건간의 상관관계가 정화효율과의 상관관계보다 좀더 유의성 있게 나타났다. 이것은 높은 수리학적 부하조건이 영양염류 등의 정화효율에는 크게 영향을 미치지 않음을 보여주고 있으며, 따라서 비교적 낮은 농도의 영양염류를 가지고 있고, 많은 처리수량을 요구하는 부영양화된 저수지의 수질개선을 위해서는 높은 수리학적 부하조건에서 시간당 정화량을 늘리는 관리방법이 경제적이며, 이에 초점을 맞추어 나가야 할 것으로 사료된다.도로 검출되어 이를 고려한정수공정의 관리가 필요하리라 생각된다.$yr^{-1}$)의 71%가 감소되어야 할 필요성이 제기되었다. 또한 여름철 심층 산소 고갈이 야기되었고, 이 시기에 퇴적물로 용출된 인이 식물플랑크톤 성장에 이용될 수 있기때문에 퇴적물에 대한 관리도 수행될 필요가 있다.rsity)지수는 2000년 7월에 2.22로 가장 높았으며, 생물량도 조사기간중 36,640 cells ${\cdot}\;mL^{-1}$로 가장 많았다.

• 한국환경농학회지
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• 제33권4호
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• pp.314-320
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• 2014

BACKGROUND: Run off from agricultural sites contaminates water bodies with nitrogen which is toxic and causes eutrophication when excessively accumulated. Hence, the interest in monitoring nitrogen toxicity in aquatic environment has been continuously increasing. METHODS AND RESULTS: To detect a real time toxicity of various nitrogen compounds, we applied biomonitoring method (biosensor) based on sulfur-oxidizing bacteria (SOB). The toxicity biomonitoring test was conducted in semi-continuous mode in a reactor filled with sulfur particles (2~4 mm diameter) under aerobic condition. Relative toxicity was simply determined by measuring the change in electrical conductivity (EC). Various nitrogenous compounds at different concentrations were evaluated as a potential toxic substance. Nitrite was found to be very toxic to SOB with a 90% inhibition even when the concentration as low as 3 mg/L. However, nitrate and ammonia have any inhibitory effect on SOB's activity. CONCLUSION: The biosensor based on SOB responded sensitively to nitrite even at substantially low concentrations. Therefore, it can be used as a reliable biological alarm system for rapid detection of contaminants due to its simplicity and sensitive nature.

• 미생물학회지
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• 제42권1호
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• pp.26-33
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• 2006

생물학적 질소 제거(Biological nitrogen removal; BNR) 시스템의 효율적인 처리 공정을 이재하기 위하여 질산화 반응조 내 세균 군집 구조를 16S rRNA 유전자의 PCR 및 terminal restriction fragment length polymorphism (T-RELP)방법을 이용하여 분석하였다. 본 연구에서 사용한 BNR 시스템은 국내에서 비교적 많이 적용되고 있는 부상여재를 이용한 고도처리 시스템, Nutrient Removal Laboratory 시스템, 반추기법을 이용한 영양염류 처리 Sequencing Batch Reactor (SBR)시스템이었고, 실험 결과 모든 시료에서 암모니아 산화 세균과 $\beta-proteobacteria$에 해당되는 말단 단편을 확인할 수 있었다. 암모니아 산화세균 군집에서 유래된 말단 단편의 염기서열을 분석한 결과 SBR공정에서는 Nitrosomonas와 Nitrosolobus에 속하는 군집 이 우점종임을 확인할 수 있었다. 그러나 다른 두 공정들에서는 $\beta-proteobacteria$에 속하는 미배양 균주와 Cardococcus australiensis와 염기서열 유사도가 높은 군집이 우점하였다. 또한, 암모니아산화 세균군집을 분석한 결과, SBR 공정이 암모니아 산화세균의 농화 배양에 가장 효과적인 것으로 나타났다. 이러한 결과는 각 BNR 시스템에 동일한 폐수가 유입되었음에도 불구하고 서로 다른 세균 군집 구조를 형성하고 있음을 의미한다.

• 한국물환경학회지
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• 제23권6호
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• pp.920-926
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• 2007

The upflow Biobead$^{(R)}$ process, one of biological aerated filters (BAF), which was used commercially, invented for removal of organic materials and nitrification. This process was modified to enhance the ability of denitrification through the induction of pre-anoxic tank. In this research, we investigated the effects of hydraulic retention time (HRT) and backwashing period in aerobic tank. The characteristics of nitrifying bacteria, which are composed of ammonia-oxidizing bacteria (AOB) and nitrite-oxidizing bacteria (NOB), also investigated using fluorescence in situ hybridization (FISH). Even though the HRT was shortened, the efficiency of nitrification was not decreased when the organic loading rate and ammonium-nitrogen loading rate were $2.10kg/m^3/day$ and $0.25kg/m^3/day$, respectively. And then the distribution ratios of AOB and NOB showed the similar patterns. However, when the backwashing period was lengthened from 12 hours to 24 hours in aerobic 1 tank, the nitrification efficiency was decreased to 63.9% from 89.2%. The results of FISH explained that this decrease of nitrification efficiency was caused by the decrease of distribution ratio of AOB in aerobic 1 tank. The nitrification efficiencies of aerobic 1 and aerobic 2 tank were increased when the backwashing period was lengthened because of relative high distribution ratios of nitrifying bacteria.