• 상하수도학회지
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• 제26권2호
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• pp.265-273
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• 2012

Anaerobic sewage treatment is drawing attentions due to high energy consumptions and sludge production associated with aerobic treatment. This study evaluates the treatment characteristics and energy balance of a fluidized bed reactor (FBR) for treating domestic sewage at $20^{\circ}C{\sim}25^{\circ}C$ for 245 days. Sewage fed to the FBR was a primary clarifier effluent of a domestic sewage treatment plant with COD of 99-301 mg/L and $BOD_{5}$ of 37-149 mg/L. Effluent $SBOD_{5}$ and its removal efficiency at HRT of 1~3 h were 6~15 mg/L and 73.4~85.5%, respectively, achieving high removal efficiency for soluble organic substances even at short HRTs. COD removal efficiency and its effluent concentration were 53.8~75.9% and 51~83 mg/L, respectively. The energy production potential from gaseous methane was 0.009-0.028 kWh/$m^{3}$, which satisfies the energy required for the FBR operation.

• 대한환경공학회지
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• 제35권1호
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• pp.1-9
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• 2013

혐기성 연속 회분식 반응조(Anaerobic sequencing batch reactor; ASBR)를 이용하여 혼합배양을 통한 장기간의 수소생산특성을 조사하였다. 실험에 사용된 기질은 글루코오스(8,250 mg/L)였고, pH 5.5, 온도 $37^{\circ}C$, 교반속도 150 rpm으로 설정하여 160일 동안 반응조를 운전하였다. 운전초기에 F/M비 2로 유지되어 수소생산 수율은 0.8 mol $H_2/mol$ glucose의 수소가 생산되었고, 운전 80일째 수소생산수율은 2.68 mol $H_2/mol$ glucose까지 증가하였다. 그러나 그 이후로 수소 생산량이 지속적으로 감소하여 운전 130일경 이후 수소의 생산은 없는 것으로 나타났다. PCR-DGGE분석을 통해 반응조내 미생물은 일반적인 수소생성 균으로 알려지고 있는 Clostridium sp.가 검출되었으나 반응조 운전 조건의 변화가 수소생산 저감의 주된 원인으로 밝혀졌다. 즉 반응조의 MLSS 농도가 증가함에 따라 F/M비가 감소하고 생산된 수소는 propionic acid의 생성으로 소모되는 것으로 추정할 수 있고 이는 반응조의 F/M비 0.5와 propionic acid 농도는 2,130 mg/L로 높게 유지된 것으로 확인하였다.

• 대한환경공학회지
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• 제27권2호
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• pp.215-223
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• 2005

본 연구는 세 가지 다른 형태의 플라즈마 반응기 (SD, DBD, PDC)를 이용한 기상의 스타이렌 분해실험을 통하여 최적 플라즈마 반응기에 대하여 고찰하였다. 각 플라즈마 반응기에 대한 비교평가를 위하여 스타이렌 분해효율, 탄소수지, 반응 생성물의 동정, 생성물의 수율 및 선택성 등의 항목을 평가하였다. 스타이렌의 전환과정은 오존과의 반응이 중요하며, PDC 반응기보다 오존생성량이 많은 SD와 DBD 반응기가 스타이렌의 전환율이 더 높은 것으로 나타났다. 한편, PDC 반응기는 탄소수지, COx ($CO+CO_2$)의 수율 및 선택성에 있어서, SD와 DBD 반응기 보다 훨씬 더 뛰어난 것으로 판명되었다. 스타이렌 초기농도를 100ppmv로 하였을 때, PDC 반응기와 플라즈마 단독공정에서 탄소수지 100%를 달성하기 위해 필요한 비투입 에너지는 각각 110 J/L와 420 J/L로, PDC 반응기가 훨씬 더 낮은 에너지로 스타이렌의 완전분해가 가능하였다. 스타이렌의 분해과정에서 생성되는 주된 생성물로는 CO와 $CO_2$가 있으며 HCOOH가 미량 성분으로 관찰되었다. 이러한 반응 생성물의 수율에는 차이가 나타나지만 이들의 분포는 플라즈마 반응기의 종류와 관계없이 거의 동일한 것으로 나타났다. 이상적인 스타이렌 분해 성성물인 $CO_2$의 선택성에 있어서 SD와 DBD 반응기는 $39.5{\sim}60%$ 정도를 나타내었으나 PDC 반응기에서는 $68.5{\sim}75.5%$ 정도로 훨씬 더 높은 것으로 나타났다.

• 한국환경과학회지
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• 제3권3호
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• pp.263-271
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• 1994

A detachment of biofilm was investigated in an inverse fluidized bed biofilm reactor(IFRBR). The biofilm thickness, 5 and the bioparticle density, Pm were decreased by the increase of Reynolds number, Re and the decrease of biomass concentration, h. The correlations were expressed as $\delta$=6l.6+16.33$b_c$-0.004Re and Ppd=0.3+0.027$b_c$- 2.93x$l0^{-5}$ no by multiple linear regression analysis method. Specific substrate removal rate, q was derived by F/M ratio and biofilm thickness as q=0.44.+0.82F/M-5.Ix10$-4^{$\delta$}$. Specific biofilm detachment rate, bds was influenced by FIM ratio and Reynolds number as $b_{ds}$=-0.26+0.26F/M+ 2.17$\times$$10^{-4}$Re. Specific biofilm deachment rate in an IFBBR was higher than that in a FBRR(fluidized bed biofilm reactor) because of the friction between air bubble and the bioparticles.

• 대한환경공학회지
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• 제35권10호
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• pp.724-729
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• 2013

동시 질산화 탈질은 미세 용존 산소하에 한 반응조내에서 일어난다. 따라서, 본 연구에서는 인 방출을 위해 공기가 공급되는 MBR 전단에 혐기성 존을 만들어주었으며, 높은 DO 농도에서 탈질효율을 향상시켜 주기 위해서는 MBR 내에 배플을 설치하여 무산소 존이 이루어지게 하였다. 그리고 인 제거를 위한 테스트는 MBR 전단의 혐기성 반응조에 알럼 응집제를 투입하여 수행하였다. 질소 제거를 위한 SND의 최적 DO 농도 도출은 MBR 내 DO 농도를 2.0, 1.5, 1.0, 0.75 mg/L의 다양한 조건에서의 운전을 통해 수행하였다. 심지어 높은 알칼리성 하수라 알럼 응집제를 투입하였을 때 알칼리 용액 첨가 없이도 pH는 7.0~8.0로 유지되었다. TCODcr와 $NH_4^+$-N의 제거 효율은 모든 DO 농도에서 90% 이상이었다. DO 농도 2.0, 1.5, 1.0, 0.75 mg/L에서의 TN 제거효율은 각각 50, 51, 54, 66%이었다. DO 농도 0.75 mg/L 조건에서 알럼을 첨가한 결과 TN 제거효율은 54%로 감소하였다. 혐기성 반응조에 알럼을 투입한 결과 TP 제거효율은 29%에서 95%로 향상되었다. 그리고 알럼 투입 후 분리막 모듈의 화학적 세정 주기는 15~20일부터 40~50일으로 늘어났다.

• 한국미생물·생명공학회지
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• 제25권1호
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• pp.68-74
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• 1997

The conversion of D-sorbitol to L-sorbose by Gluconobater suboxydans was analyzed, and continuous production of L-sorbose was carried out in immobilized cell reactors. L-Sorbose production by high densities of resting cells was more effective than by conventional batch fermentations. Sorbitol dehydrogenase, an enzyme converting D-sorbitol to L-sorbose, did not suffer from substrate inhibition, but from product inhibition. When L-sorbose production was carried out with Ca-alginate-immobilized cells, about 60 g/l of L-sorbose was obtained. On the other hand, when the corn steep liquor (CSL) concentration of medium was reduced to 0.08%, 80 g/l of L-sorbose was obtained. Outgrowth inside the immobilized carriers was thought to block the pores of the carriers so that substrate could not easily diffuse through the carriers. Continuous production of L-sorbose was well accomplished in a bubble column reactor, and 6. 5 g/l.h of productivity and 81.2% of yield were obtained at a substrate feeding rate of 0.08h$^{-1}$ under the optimum conditions with carrier volume of 55% and aeration rate of 3 vvm.

• 한국환경보건학회지
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• 제22권4호
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• pp.10-15
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• 1996

Treatment of a synthetic wastewater was made for the purpose of evaluating the performance of a pilot scale of an IFBBR. The particles used in this experiment were circular shaped polystyrene whose density was lower than that of water. The reactor volume was 400 l and the SCOD removal efficiency was more than 90% at HRT of 5 hrs. The IFBBR was successfully operated for 5 months without any significant problems. And it whs certained that IFBBR had a potential capability for treating wastewater.

• 한국신재생에너지학회:학술대회논문집
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• 한국신재생에너지학회 2008년도 춘계학술대회 논문집
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• pp.210-213
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• 2008

The purpose of this study is to investigate the performances of organic removal and methane recovery in the full scale two-phase anaerobic system. The full scale two-phase anaerobic system was consists of an acidogenic ABR (Anaerobic Baffled Reactor) and a methanognic UASB (Upflow Anaerobic Sludge Blanket) reactor. The volume of acidogenic and methanogenic reactors is designed to 28.3 $m^3$ and 75.3 $m^3$. The two-phase anaerobic system represented 60-82% of COD removal efficiency when the influent COD concentration was in the range of 7,150 to 16,270 mg/L after screening (average concentration is 10,280 mg/L). After steady-state, the effluent COD concentration in the methanogenic reactor showed 2,740 $\pm$ 330 mg/L by representing average COD removal efficiency was 71.4 $\pm$ 8.1% when the operating temperature was in the range of 19-32$^{\circ}C$. The effluent SCOD concentration was in the range of 2,000-3,000 mg/L at the steady state while the volatile fatty concentration was not detected in the effluent. Meanwhile, the COD removal efficiency in the acidogenic reactor showed less than 5%. The acidogenic reactor played key roles to reduce a shock-loading when periodic shock loading was applied and to acidify influent organics. Due to the high concentration of alkalinity and high pH in the effluent of the methanogenic reactor, over 80% of methane in the biogas was produced consistently. More than 70 % of methane was recovered from theoretical methane production of TCOD removed in this research. The produced gas can be directly used as a heat source to increase the reactor temperature.

• 한국물환경학회지
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• 제21권3호
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• pp.256-262
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• 2005

The purpose of this study is to investigate the performances of organic removal and methane recovery by using a full scale two-phase anaerobic system. The full scale two-phase anaerobic process was consists of an acidogenic anaerobic baffled reactor (ABR) and a methanognic upflow anaerobic sludge blanket (UASB) reactor. The volumes of acidogenic and methanogenic reactors were designed to $28.3m^3$ and $75.3m^3$. The two-phase anaerobic system represented 60-82% of COD removal efficiency when the influent COD concentration was in the range of 7,150 to 16,270 mg/L after screening (average concentration is 10,280 mg/L). After steady-state, the effluent COD concentration in the methanogenic reactor showed $2,740{\pm}330 mg/L$ by representing average COD removal efficiency was $71.4{\pm}8.1%$ when the operating temperature was in the range of $19-32^{\circ}C$. The effluent SCOD concentration was in the range of 2,000-3,000 mg/L at the steady state while the volatile fatty acid concentration was not detected in the effluent. Meanwhile, the COD removal efficiency in the acidogenic reactor showed less than 5%. The acidogenic reactor played key roles to reduce a shock-loading when periodic shock loading was applied and to acidify influent organics. Due to the high concentration of alkalinity and high pH in the effluent of the methanogenic reactor, over 80% of methane in the biogas was produced consistently. More than 70% of methane was recovered from theoretical methane production of TCOD removed in this research. The produced gas can be directly used as a heat source to increase the reactor temperature.

• Biotechnology and Bioprocess Engineering:BBE
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• 제2권2호
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• pp.90-93
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• 1997

Recombinant exoinulinase was partially purified form the culture supernatant of S.cerevisiae by(NH4)2SO4 precipitation and PEG treatment. The purfied inulinase was immobilized onto Amino-cellulofine with glutaraldeyde as a cross-linking agent. Immobilization yield based on the enzyme activity was about 15%. Optimal pH and temperature of immobilized enzyme were found to be 5.0 and 6$0^{\circ}C$, respectively. The enzyme activity was stably maintained in the pH ranges of 4.5 to 6.0 at 6$0^{\circ}C$. 100% of enzyme activity was observed even after incubation for 24 hr at 6$0^{\circ}C$. In the operation of a packed-bed reactor containing 412U inulinase, dahalia inulin of 7.5%(w/w) concentration was completely hydrolyzed at flow rate of 2.0mL/min at 6$0^{\circ}C$, resulting in a volumetric productivity of 693 g-reducing sugars/L/h. Under the reaction conditions of 1.0mL/min flow rate with 2.5% inulin at 6$0^{\circ}C$, the reactor was successfully operated over 30 days without loss ofinulinase activity.