• Membrane Journal
• /
• v.7 no.4
• /
• pp.175-182
• /
• 1997

Membrane-bioreactor process which combines anaerobic-aerobic bioreactor and membrane process, was used to remove refractory organic susbstances and dye molecule in textile wastewater effectively. Direct feeding of raw feed water to membrane process caused serious fouling on membrane. On the other hand, pretreated feed by bioreactor before the membrane process remarkably reduced the fouling and prolonged the membrane life. Removal efficiency and fouling were more dependent on the material property of the membrane rather than the membrane pore size and structure. Operation mode of hollow fiber membrane module and linear velocity in the hollow fiber influenced the ramoval efficiency and the water flux of the membrane. The combined membrane- bioreactor process was more effective in treating the textile wastewater than each single process.

• Journal of Wetlands Research
• /
• v.23 no.2
• /
• pp.183-188
• /
• 2021

In the case of small-scale sewage treatment plants, it is reported that the amount of inflow fluctuates and it is difficult to operate the sewage treatment due to the inflow of unknown water due to the aging of sewage pipes. In particular, there are many overall operational problems due to the decrease in water temperature in winter. In this study, the operation status of small-scale sewage treatment facilities located in mountainous areas and water quality changes according to temperature were analyzed. It was found that the concentration of BOD, COD, and SS in effluent water was greatly changed depending on the temperature, and it was found that COD was particularly affected. Accordingly, the water level of the bioreactor was raised by 0.4m in order to temporarily apply measures to lower the water temperature in winter. As a result of comparing and analyzing the results when the bioreactor was covered and operated, a significant improvement effect occurred. In addition, a plan to improve the treatment efficiency of the bioreactor in winter is to extend the residence time of the bioreactor, a plan to expand the bioreactor specification, a new flow control tank and transport it to the outside, and an oxygen-free air diffuser to be used as an aerobic tank in case of an emergency in winter. The improvement plan was suggested. The results of this study are expected to be used as basic data for the operation plan of small-scale sewage treatment facilities in winter.

• Journal of Korean Society of Environmental Engineers
• /
• v.38 no.6
• /
• pp.279-290
• /
• 2016

The performance of upflow anaerobic bioelectrochemical reactor (UABE), equipped with electrodes (anode and cathode) inside the upflow anaerobic reactor, was compared to that of upflow anaerobic sludge blanket (UASB) reactor for the treatment of acidic distillery wastewater. The UASB was stable in pH, alkalinity and VFAs until the organic loading rate (OLR) of 4.0 g COD/L.d, but it became unstable over 4.0 g COD/L.d. As a response to the abrupt doubling in OLR, the perturbation in the state variables for the UABE was smaller, compared to the UASB, and quickly recovered. The UABE stability was better than the UASB at higher OLR of 4.0-8.0 g COD/L.d, and the UABE showed better performance in specific methane production rate (2,076mL $CH_4/L.d$), methane content in biogas (66.8%), and COD removal efficiency (82.3%) at 8.0 g COD/L.d than the UASB. The maximum methane yield in UABE was about 407mL/g $COD_r$ at 4.0 g COD/L.d, which was considerably higher than about $282mL/g\;COD_r$ in UASB. The rate limiting step for the bioelectrochemical reaction in UABE was the oxidation of organic matter on the anode surface, and the electrode reactions were considerably affected by the pH at 8.0 g COD/L.d of high OLR. The maximum energy efficiency of UABE was 99.5%, at 4.0 g COD/L.d of OLR. The UABE can be an advanced high rate anaerobic process for the treatment of acidic distillery wastewater.

• 종축개량
• /
• v.19 no.3
• /
• pp.73-84
• /
• 1997

• Journal of the Korea Academia-Industrial cooperation Society
• /
• v.11 no.10
• /
• pp.4055-4068
• /
• 2010

In this study, validity of wastewater treatment system with advanced treatment processes was evaluated by studying its operational conditions by applying the advanced treatment to the wastewater treatment system which was operating for last several years. Study indicated a fair result for the removal efficiencies of BOD, T-P, and T-N for each unit operation. BOD removal efficiencies for primary clarifier, bioreactor, final effluent are 35, 87, and 48 % respectively. T-P(T-N) removal efficiencies for primary clarifier, bioreactor, final effluent are 18(23), 40(38), and 25(25) % respectively. Further investigation of bioreactor showed that various microorganism such as bacteria, protozoa, and metazoa is present in the bioreactor, and the main function of the media, adhesion (adsorption) of microorganism onto the media, is stabilized. Final effluent quality was lower than the regulation, and BOD, COD, SS, T-N, T-P were 5.5, 9.9, 4.6, 11.8, 0.99 mg/L respectively.

• Journal of Korean Society of Environmental Engineers
• /
• v.36 no.10
• /
• pp.679-684
• /
• 2014

Many burial sites were constructed to suppress the spread of foot and mouth disease during outbreak. Defected burial sites were removed when leachate leak is presumed and carcasses were moved to the circular storage tanks. However, carcasses were not decomposed possibly due to low water content, low microbial activities, and poor mixing. In this research, storage tank containing carcasses in it was modified to bioreactor to accelerate stabilization. Liquids with nutrients were added and circulated to maintain the optimum water content while extraneous microorganisms were augmented. Settlement was used as the primary index for assessing stabilization rate, and the consolidation theory was utilized to estimate the expected final settlement. 30% of carcasses is expected to be decomposed and removed from the storage tank for five years of bioreactor operation.

• Proceedings of the Korea Water Resources Association Conference
• /
• 2022.05a
• /
• pp.396-396
• /
• 2022

생물전기화학적 혐기성소화(Bioelectrochemical anaerobic digestion; BEAD)는 소량의 전압공급을 통해 고농도 하·폐수의 효과적인 처리 및 에너지 회수가 가능한 처리방법으로, 기존 하·폐수처리공정(활성슬러지 및 그 변법)에서 벗어나기 위한 방법 중 하나로 연구되고 있지만, 내부저항 및 전극구조에 따른 물질전달저해로 인해 소규모 연구 위주로 진행되었다. 하지만 stainless steel(SS) 등 내부저항을 완화할 수 있는 전극재료 및 전극구조 개선 연구가 진행됨에 따라 BEAD 적용규모가 증가하는 추세이며, 본 연구에서는 100 L의 용량에서 전극재질 및 구조에 따른 적용적합성을 에너지효율 비교를 통해 평가하였다. 반응조는 비교를 위한 AD, 반응조 내부에 전극을 설치한 BEAD, 반응조 외부에 전극이 포함된 반응조를 추가한 ABEAD로 구성하였으며, AD 및 BEAD는 기계적 교반, ABEAD는 기계적 교반 및 펌프를 통한 bulk 용액 순환으로 물질전달이 이뤄졌다. 또한 BEAD는 탄소계 전극, ABEAD는 SS계 전극을 사용하였으며 두 반응조 모두 0.4 V의 전압을 공급하였다. 실험조건은 유효용량 100 L, 유기물부하율 3 kg/m³/d, HRT 20 days 및 중온소화(35℃)으로 운전하였다. 실험결과 AD, BEAD 및 ABEAD의 유기물제거율은 각각 평균 68.1 %, 68.9 %, 74.9 %로 전극 및 반응조의 분리를 통해 물질전달을 개선한 ABEAD에서 증가하였다. 에너지 생성량의 경우 AD에 비해 BEAD는 평균 229 kJ/d, ABEAD는 309 kJ/d가 추가 생성되었으며 유기물제거율이 높은 ABEAD에서 더 높은 에너지생산이 이뤄졌다. 마지막으로 전압공급으로 인한 에너지소비량은 BEAD는 평균 3.4 kJ/d, ABEAD는 평균 0.9 kJ/d로 전극의 낮은 생물적합성으로 인해 전극에서의 생화학반응이 적은 ABEAD가 에너지소비량이 낮았다. 따라서 본 연구에서는 SS 전극의 사용가능성 및 전극구조 개선에 따른 에너지효율성 향상을 확인할 수 있었으며, 추후 연구에 활용할 수 있을 것으로 기대된다.

• Proceedings of the Membrane Society of Korea Conference
• /
• 2000.07b
• /
• pp.111-121
• /
• 2000

• Journal of Korean Society of Environmental Engineers
• /
• v.29 no.8
• /
• pp.922-929
• /
• 2007

The complete oxidation of ammonia to nitrate is a distinctive two-step process divided into the oxidation of ammonia to nitrite(nitritation) by Nitrosomonas and the oxidation of nitrite to nitrate(nitratation) by Nitrobacter. The nitrogen removal via nitrite accumulation offers several advantages such as saving costs for aeration, saving carbon source and finally reduction of sludge discharge. In this work a suspended bioreactor coupled with membrane filtration(MBR) was used to find the process conditions of nitrite build-up. The MBR enables to reach sufficient nitrifying bacteria in the bioreactor, although the autotrophic bacteria can be easily washed out due to their lower growth rate. The dissolved oxygen concentration $c'_{O2}$ and ammonia concentration $c_{NH3}$ in the reactor were varied and investigated as parameters for nitrite accumulation. As a result the higher ammonia concentration in the reactor is very effective for starting nitrite build-up and the effect was strengthened in combination with lower dissolved oxygen concentration. With lower $c'_{O2}<0.3$ $mgL^{-1}$ $O_2$ and high $c_{NH3}=6.3\sim14.9$ $mgL^{-1}$ $NH_3N$ the 74% of the nitrite accumulation was achieved. Specially, it was found that the nitrite accumulation could occur not only in biofilm reactor as many references showed but also in the membrane bioreactor carried out in this study.

• Journal of the Korea Organic Resources Recycling Association
• /
• v.24 no.1
• /
• pp.31-40
• /
• 2016

In this study, mesophilic anaerobic digestion of source separated food waste was carried out by leachate recirculation system and methane gas was produced. Two systems - system A and B were fabricated and placed within water bath to maintain $36^{\circ}C$. Each system was comprised of an anaerobic bioreactor and a leachate tank. Leachate in bioreactor was separated through the screen located at 30 mm above the bottom and a pump was installed to transfer collected leachate to the leachate tank. Everyday, 2.5 L of the leachate was pumped from the bioreactor to the leachate tank for 30 min and transferred leachate was pumped back to the top of the bioreactor for 30min, sequentially. Source separated food waste used for this experiment was washed by water before transferring to the laboratory. Transferred food waste was warmed to $36^{\circ}C$ before being fed to bioreactors. System A was fed to 49.1 g VS (Volatile Solids) and System B was fed to 54.0 g VS at every two weeks, respectively. $NH_4{^+}-N$ and salinity were monitored to see the inhibition toward anaerobic bioreaction and it was found that concentrations of these materials were not high enough to affect the bioreaction. Although the food waste was fed biweekly for 112 days and 140 days at system A and B, respectively, there was no sludge withdrawal from each system. Average methane productions rates were 0.439 L $CH_4/g$ VS and 0.368 L $CH_4/g$ VS for system A and B, respectively.