• 기술사
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• 제18권3호
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• pp.28-35
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• 1985

As the paper industry consumes much water in process and discharge wastewater containing suspended solid and COD(chemical oxygen demand), relevant law against this discharge has been set up to limit the total containment of COD in discharge. This study has been carried out to improve the treatment method for the soluble COD in wastewater produced during the process of paste-board production, which is made of semichemical pulp and waste paper. Applicated methods are, O$_2$AS : O$_2$ activated sludge process DAS : Deep well activated sludge process SAS : standard activated sludge process and proper combination of DAS and SAS 1) As a result of this experiment, we get the following conclusion between in COD sludge loading "X" and COD removable rate in the process of treating waste-water. COD removable rate(％)=(0.778+0.0146/X)${\times}$100(％)……(7) 2) In case that the COD sludge loading is high, it has been cleared out that the COD removable rate shall become low due to unknown unsoluble substances contained in the process. Meanwhile, to increase the efficiency rate of treatment, it is thought to be necessary, to provide long-time contacts with activated sludge. 3) Once the COD of original waste-water and the target COD of treated water are decided, COD sludge loading is obtained from equation(7), and capacity of aeration tank in the effective systems such as O$_2$AS, DAS, to bet the required COD removable rate can be decided. Therefore the choice among SAS, O$_2$AS, DAS methods is made in consideration of required COD removable rate and allowable installation area. 4) In the sedimentation tank with sludge bulking, it is possible to increase the COD removable rate by 3～7％ but still there exist many obstacles to manage this operation.

• 환경위생공학
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• 제8권2호
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• pp.65-84
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• 1993

This study reviewed the current status and problems of sewerage system in Korea and then proposed possible methods to correct the problems. Also, evaluation of future development in sewerage system is included. It can be summarized as follows : 1. Investment in sewerage system is relatively low . 0.23% of GNP, Considering that the investment portion is 0.35% in OECD and 0.63% in Japan, it should be increased further. 2. The reasons wily the investment in sewerage system is low can be ' (1) Low priority is given to the investment in sewerage system. Local government builds and operates its own wastewater treatment plant. Local government as well as residents prefer to invest their money in roadwork, housing and parks to in wastewater treatment facilities because of greater investment effects. (2) Besides capital investment, more maintenance cost is needed for sewerage system. Proper operation of wastewater treatment facilities requires a well-trained operator. Because of public conception that operation of wastewater treatment facility is a dirty job, it is difficult to find a well-trained operator. (3) It is difficult to estimate the effect of sewerage system (4) Cost required to build and maintain wastewater treatment facility should be paid by people, who benefit from the facility. People to benefit are sometimes different from people to pay. 3. Advanced treatment is necessary to protect the bay aura and raw water source as well as to prevent eutrophication of lakes and ponds. 4. Wastewater treatment facility were mainly build in big cities during the decade of 1980. Followings should be solved first to expand the facilities. (1) Rapid repair and construction of sewer. (2) Technical development of wastewater treatment . Prevention of efficient and economical wastewater . Development of efficient and economical wastewater treatment techniques . Development of high-efficiency treatment using bioreactor . Reuse of wastewater treatment plant effluent (3) Sludge treatment and disposal . Composting of sludge cakes . Development of techniques to reduce the volume of sludge cake : incineration and reuse of sludge ash and slag. (4) Utilization of wastewater treatment facilities . Construction of community parks or sports families(ie, on the tops of the covered aeration tanks and sedimention tanks) Construction of wastewater treatment facilities under ground and of parking facilities and community parks above ground. (5) Education of wastewater treatment personal.

• 한국생물공학회:학술대회논문집
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• 한국생물공학회 2000년도 추계학술발표대회 및 bio-venture fair
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• pp.229-232
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• 2000

본 연구에서는 균주의 배양과 동시에 생산물을 회수할 수 있는 동시추출공정을 건조질량의 $15{\sim}75%$의 탄화수소를 생산한다고 알려진 B. braunii 배양에 적용하고자 한다. 일반적인 two-phase 동시추출공정의 적용시 B. braunii의 경우 생산된 탄화수소가 균주 외벽의 matrix에 강하게 부착되어 있기 때문에, two phase 추출공정 적용시 bubble column내에서 단지 폭기에 의한 교반만으로는 충분한 탄화수소의 회수율을 얻을 수가 없었다. 본 연구에서는 배양액과 유기용매층의 접촉기회를 증대시킨 two-stage 동시추출 공정을 개발하여 기존의 two-phase 동시추출 공정보다 2배 이상 높은 56.2%의 탄화수소 회수율을 얻을 수가 있었다.

• 대한토목학회논문집
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• 제14권6호
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• pp.1365-1373
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• 1994

난류전단 흐름에서의 기포 크기분포를 예측하기 위하여 개발된 Monte-Carlo 모의모형을 실험실 크기의 문제에 적용하였다. 각종 모형 매개변수 및 물리적 변수들에 대한 민감도 분석을 수행하였으며, 실험 관측치와의 비교를 통하여 모형의 실제 적용성에 관하여 조사하였다. 공기와 물의 유량비 또는 마찰계수가 증가함에 따라 기포의 크기가 커지는 것으로 나타났다. 평균유속이 증가함에 따라 가포의 크기는 작아지지만, 폭기구간내 기포의 총표면적은 거의 일정함을 보였다. 모형의 종방향 거리증분에 따른 기포 크기분포의 변화는 거의 없었으며, 횡방향 거리중분을 크게 할수록 기포가 크거나 작은 쪽으로 치우쳐 중간정도의 크기를 갖는 기포의 수가 감소하였다. 기포의 크기분포는 그 초기분포 및 공기의 주입위치에 크게 영향을 받는 것으로 나타났다. 기포의 충돌과 응집을 구분하기 위하여 충돌효율을 도입하였다.

• 상하수도학회지
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• 제25권3호
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• pp.383-390
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• 2011

In this study, a process combined biofiltration with sulfur-utilizing autotrophic denitrification and membrane separation was proposed to examine the efficiency of nitrogen removal. As an experimental device, hollow-fiber module was installed in the center of reactor to generate the flux forward sulfur layer in the cylinder packed with granular sulfur. In addition, a simple module was installed in activated sludge aeration tank which inside and outside of sulfur-using denitrification module was covered with microfilter and the module was considered as an alternative of clarifier. The experiment for developing new MBR process was carried out for three years totally. As the results of first two-year experiment, successful nitrogen removal performance was revealed with lab-scale test and pliot scale plant using artificial wastewater and actual plating wastewater. In this year, pilot scale test using actual domestic wastewater was performed to prove field applicability. As the results, high-rate nitrogen removal performance was confirmed with about 0.19 kg ${NO_3}^--N/m^3$ day of rate. Also significant fouling and pressure increase were not found during the experiment. And, the production ratio of sulfate and the consumption ratio of alkalinity showed a slightly higher value about 311 mg ${SO_4}^{2-}/L$ and 369 mg $CaCO_3$/L, respectively. In conclusion, the developed MBR process can be utilized as an alternative for retrofiting existing wastewater plants as well as new construction of advanced sewage wastewater treatment plants, with cost-effective merit.

• KSBB Journal
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• 제8권2호
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• pp.150-155
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• 1993

난분해성인 색소를 대사분해할 수 있는 미생물을 분리하여, 색소분해의 최적조건을 조사하였다. 미생물은 폐수처리공장의 폭기조에서 채취한 폐수로부터 agar media에서 순수분리하였다. 이 균주들을 glu­c cose, peptone, $Na_2HPO_45, KCI, MgSO_4, KH_2PO_4, NaCI, CaCI_2$와 dye(azo계, reactive red계 ) lOppm 을 함유한 액체 배지에서 dye의 분해력이 강하였으 며, 이때의 최적 pH는 중성 또는 약알칼리성이고, 최적 온도는 $30^{\circ}C$ 전후이다. 이 조건에서 10ppm의 m mono-azo(Lot No. 180), di-azo(Lot No. 138), re­a active red(Lot No.2)는 약 2일에 거의 분해되었고, di-azo(Lot No. 151), reactive red(Lot No. 34, L Lot No. 00166)는 약 5일에 거의 분해되었고, 최적 배지조건하에서 산소의 영향은 D.O를 50%로 유지 시켰을 경우보다 혐기성 배양의 경우가 reactive d dye(Lot No.2)의 분해도가 훨씬 높았다.

• Membrane and Water Treatment
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• 제11권1호
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• pp.41-48
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• 2020

Lead is a highly toxic heavy metal that causes serious health problems. Nonetheless, it is increasingly being used for industrial applications and is often discharged into the environment without adequate purification. In this study, Pb(II) was removed by powdered waste sludge (PWS) based on the biosorption mechanism. Different PWSs were collected from a submerged moving media intermittent aeration reactor (SMMIAR) and modified Ludzack-Ettinger (MLE) processes. The contents of extracellular polymeric substances were similar, but the surface area of MLE-PWS (2.07 ㎡/g) was higher than that of SMMIAR-PWS (0.82 ㎡/g); this is expected to be the main parameter determining Pb(II) biosorption capacity. The Bacillaceae family was dominant in both PWSs and may serve as the major responsible bacterial group for Pb(II) biosorption. Pb(II) biosorption using PWS was evaluated for reaction time, salinity effect, and isotherm equilibrium. For all experiments, MLE-PWS showed higher removal efficiency. At a fixed initial Pb(II) concentration of 20 mg/L and a reaction time of 180 minutes, the biosorption capacities (q_e) for SMMIAR- and MLE-PWSs were 2.86 and 3.07 mg/g, respectively. Pb(II) biosorption using PWS was rapid; over 80% of the maximum biosorption capacity was achieved within 10 minutes. Interestingly, MLE-PWS showed enhanced Pb(II) biosorption with salinity values of up to 30 g NaCl/L. Linear regression of the Freundlich isotherm revealed high regression coefficients (R² > 0.968). The fundamental Pb(II) biosorption capacity, represented by the K_F value, was consistently higher for MLE-PWS than SMMIAR-PWS.

• 멤브레인
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• 제24권1호
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• pp.20-30
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• 2014

C/N 비가 낮은 농촌마을 하수의 고도처리를 위하여 $0.4{\mu}m$의 세공크기를 갖고 있는 평막이 침지된 연속회분식 반응기를 사용하였다. 분말활성탄의 투입, 폭기량 및 유입 유기물 농도가 처리효율과 여과 성능에 미치는 영향을 조사하였다. 54일 이내의 조업 초기에서는 C/N 비가 증가할수록 COD, T-N 및 T-P의 제거율과 MLSS 농도는 증가하였다. 조업 89일 후의 COD, T-N 및 T-P의 제거율은 각각 97.1%, 75.0% 및 48.3%이었다. 막여과에 의해 처리수에서 SS는 검출되지 않았으며, T-P의 제거율이 낮게 나온 이유는 과잉의 슬러지를 배출하지 않았기 때문이다. 분말활성탄을 투여한 경우 조업이 진행됨에 따라 분말활성탄의 혼합강도와 충돌빈도가 증가하여 슬러지의 입자크기가 감소하였으며, 이로 인해 분말활성탄을 투여하지 않은 경우에 비해 TMP 상승이 크게 나타났다.

• 한국생물공학회:학술대회논문집
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• 한국생물공학회 2002년도 생물공학의 동향 (X)
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• pp.112-115
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• 2002

본 연구에서는 균주의 배양과 동시에 생산물을 회수할 수 있는 동시추출공정을 건조질량의 $15{\sim}75$ %의 탄화수소를 생산한다고 알려진 B. braunii 배양에 적용하고자 한다. 일반적인 tow-phase 동시 추출공정의 적용시 B. braunii의 경우 생산된 탄화수소가 균주 외벽의 matrix에 강하게 부착되어 있기 때문에, two phase 추출공정 적용시 bubble solumn내에서 단지 폭기에 의한 교반만으로는 충분한 탄화수소의 회수율을 얻을 수가 없었다. 본 연구에서는 배양액과 유기용매층의 접촉기회를 증대시킨 two-stage 동시추출 공정을 개발하여 기존의 two-stage 동시추출 공정보다 2배 이상 높은 57 %의 탄화수소 회수율을 얻을 수가 있었고, 이를 회분배양후 후속분리공정으로 이용할 경우 6시간 추출후 62 %의 회수율을 얻을 수가있었다.

• 한국물환경학회지
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• 제22권2호
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• pp.203-208
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• 2006

A continuous feed and cyclic draw SBR process was developed to overcome flow rate fluctuation and to maximize organic matters utilization efficiency for nitrogen and phosphorus removal. The developed SBR process was operated with two parallel reactors. Influent was supplied to one reactor which was not obligately aerated. At the same time, the other reactor was just aerated without supplying influent. In addition this mode was changed periodically. Cycle time was 6hr and aeration time ratio($t_{aer}/t_{total}$) was 0.33, respectively. $COD_{cr}$ and SS removal efficiencies of 95% or higher were achieved. Nitrogen removal was so greatly influenced by influent $COD_{cr}/T-N$ ratio. At influent $COD_{cr}/T-N$ ratio of 5.7, removal efficiencies of ammonia-N, T-N and T-P were 96%, 78% and 55%, respectively. Influent $COD_{cr}/T-N$ of 4 or higher ratio was necessary to achieve 60% or higher nitrogen removal. Organic matters of influent was efficiently utilized in denitrification reaction and consumed COD has a good correlation with removed T-N(about 6.5 mgCOD/mgTN). Continuous feed and cyclic draw SBR process could be one of alternative processes for the removal of nutrients in rural area where $COD_{cr}/T-N$ ratio was low and fluctuation of flow rate was severe.