• 한국환경농학회지
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• 제17권1호
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• pp.70-75
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• 1998

실험결과 최종처리수의 $BOD_5$를 30mg/l 이하로 유지하는 것이 충분히 가능하다. 최종처리수의 총질소와 총인은 축산폐수처리시설의 방류수 수질기준보다 월등히 낮다. 연못상층에서 조류(Algae)가 성장하면서 질소와 인을 흡수하기 때문이다. 연못시스템은 질소와 인을 동시에 제거하는 장점이 있다. 최종처리수의 평균 SS가 $30mg/{\ell}$ 보다 다소 높아 2차처리 수준의 방류수 수질기준을 충족시키지 못하는 경우가 발생할 수 있으나 연못상층의 조류(Algae) 성장에 원인이 있어 문제가 되지 않는다. 2차연못과 3차연못의 SS는 거의 조류가 차지하고 있다. 조류를 회수하여 사료로 사용하거나 처리수를 유기농업 관수로 이용하여 조류를 비료로 이용하는 재활용 방법이 바람직하다. 실험 연못시스템의 모델은 연못의 수, 연못의 종류, 각 연못의 크기, 유입폐수의 $BOD_5$ 부하량을 적절히 조절하면 액상폐수(뇨${\cdot}$오수)뿐아니라 분${\cdot}$뇨${\cdot}$오수를 동시에 처리할 수 있다. 국내 여건에서는 중소규모 축산시설의 폐수를 처리하는데 연못시스템이 적합하며, 토지확보가 가능하면 대형 축산폐수 공동처리시설로 사용할 수 있다. 대부분 축산농가에 설치되어 있는 간이정화조와 산화구를 연못시스템으로 대치하여 이들의 낮은 처리효율의 문제점을 해결할 수 있다고 사료된다. 다른 처리기법에 비해 연못시스템은 관리운영에 적은 인력과 경비가 소요하여 노동력이 부족한 농촌지역에 적합하다.

• 한국환경생태학회지
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• 제16권2호
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• pp.179-187
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• 2002

유기물이 함유된 공업용 폐수(2차처리수)의 수질을 정화하기 위해 2000년 7～10월에 친환경적인 방법인 식물정화조를 조성하여 하천의 수질 및 지하수를 보전하고 공업단지내에서 생물서식공간과 휴게공간을 제공하고자 본 실험을 진행하였다 식물정화조의 크기는 10m$\times$6m(상부면)로 1일 처리용량은 2.5㎥였다. 폐수는 1일 4회, 6시간 간격으로 0.625㎥씩 나누어 처리하였다. 처리효율을 높이기 위해 수직흐름방식을 채택하였고, 배수층은 모래와 자갈을 2:1의 비율로 혼합하여 깊이 1.0m로 조성하였다. 식물정화조 내에는 갈대, 부들, 골풀, 노랑꽃창포 등의 다년생 정수식물을 20본/㎥ 식재하였다. 처리수 재활용 차원에서 생물종다양성을 증진시키는 자연형 연못을 조성하였으며, 이를 환경교육장으로 활용하기 위해 관찰데크, 안내해설판 등을 도입하였다. 실험결과 BOD$_{5}$, COD, T-N, T-P 등의 제거에 상당한 효과가 있는 것으로 나타났고, 생태계 모니터링 결과, 생물서식공간(비오톱)으로서의 기능이 점진적으로 향상되고 있는 것으로 나타났다.

• 한국환경보건학회지
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• 제19권3호
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• pp.1-16
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• 1993

This paper describes an investigation to determine whether the activated sludge (AS) process could be used for the treatment of wastewater at the Union Carbide Coporation (UCC) plant in Seadrift, Texas. This plant presently utilizes a waste stabilization pond (WSP) system for treatment of the wastewater. The treatment system consists of an in-plant primary WSP and two off-plant WSPs (secondary and tertiary WSPs), run in series. The total hydraulic detention time of the WSP system is approximately 150 days. Several laboratory-based treatability studies have been conducted to evaluate the performace of the WSP system and the degradability of specific chemical compounds. From an additional study, it was determined that the WSP system was stressed and occasionally operating near the limit of its treatment capacity. The existing primary WSP plays an important role in the overall treatmemt system, because it not only functions as a pH and organic-strength equalization basin, but also serves as a "preconditioning" basin by fermenting high strength organic wastes to volatile organic acids for subsequent degradation in the escondary WSP. However, in view of pending RCRA legislatin conerning the "proposed organic toxicity characteristics limits" (40 CFR Part261: Federal Register, July, 1988), it is possible that the primary WSP will have to be abandoned in favor of alternative treatment options. Therefore the main purpose of this study was to perform activated sludge treatability evaluations for the development of an alternative to the existing primary WSP treatment ststem. In addition, another purpose was to determine the degradability of bis(2-chloroethyl)ether (Chlorex or CX) and benzene(BZ) in the activated sludge process. The presence of these two chemicals in the wastewater of the plant prompted the question of whatedether they could be degraded in an activated sludge system.

• 대한환경공학회지
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• 제27권2호
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• pp.198-205
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• 2005

본 연구에서는 marsh와 pond의 조합으로 구성된 회분식과 연속식 습지 반응조를 이용하여 화약물질인 TNT(2,4,6-trinitrotoluene)를 처리하는 실험을 수행하였다. 회분식 실험결과 10 mg/L의 TNT가 20일 이내에 marsh와 pond 반응조 내에서 모두 제거되었다. TNT의 분해에 따른 주요 분해 부산물들은 2,4-diamino-6-nitrotoluene(2,4-DANT), 2,6-diamino-4-nitrotoluene(2,6-DANT), 4-diamino-2,6-nitrotoluene(4-ADNT), 그리고 2-diamino-4,6-nitrotoluene(2-ADNT)이었으며 시간이 경과하면서 이들 부산물도 점차 감소하는 경향을 보였다. 다음으로 Marsh와 pond의 조합으로 이루어진 연속식 반응조를 이용하여 TNT를 처리한 결과 회분식 반응조와 비슷한 경향을 보였으며, 2일 이내에 수중에서 거의 모든 TNT가 제거되었다. 주요 부산물은 marsh와 pond 단일조합 반응조에서는 ADNT(mono amino-dinitrotoluene)계열의 부산물이었던 반면, marsh-pond, pond-marsh 연속식 반응조에서는 분해가 된 DANT(diamino-mononitrotoluene)가 주된 부산물로 관찰되어 혐기성과 호기성 조건을 동시에 가지는 연속식 조합 습지 시스템이 TNT의 분해에 더 효과적임을 알 수 있었다. 또한 습지의 유입수와 처리수의 독성을 평가하기 위해 Microtox Assay를 통하여 분석한 결과, marsh와 pond의 연속식 복합 반응조의 처리수는 $EC_{50}$를 계산할 수 없을 정도로 독성이 감소됨을 알 수 있었다. 이들 실험결과를 통하여 marsh와 pond의 조합으로 혐기성과 호기성을 동시에 마련한 인공습지 시스템을 이용하여 수중에 존재하는 TNT를 안정적으로 처리할 수 있었다.

• 한국환경보건학회지
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• 제30권3호
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• pp.214-220
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• 2004

The microcosm type wetland systems were constructed in order to treat wastewater contaminated with parathion. The microcosm reactor consisted of marsh and pond type. The experiment was carried out using batch (marsh or pond) and continuous (marsh-pond and pond-marsh type) systems. In the batch reactor, marsh-type wetland completely removed parathion in water within 8 days, while pond reactor removed 97% of parathion during the same period. During parathion degradation, the amount of 4-nitrophenol production, one of the metabolites from parathion degradation, was higher in marsh-type batch reactor. In the continuous systems, both marsh-pond and pond-marsh combination systems effectively removed parathion from water, and the production of 4-nitrophenol was also minimal. In the extraction experiment, the parathion and its metabolite were not found in the wetland soil and the plant. In order to achieve both aerobic and anaerobic conditions, the continuous wetland system combining marsh and pond type can be the alternative for the non-point source pollutants such as parathion pesticide.

• 한국수자원학회:학술대회논문집
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• 한국수자원학회 2008년도 학술발표회 논문집
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• pp.2127-2131
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• 2008

본 연구는 자연생태하에서 지속가능한 태양에너지와 생태계작용에 의한 수질개선기법을 개발하기 위하여 생태연못을 설치하여 수질부하가 발생함에 따라 생태연못에 에너지를 순환시켜 생태적 수질정화 기능을 강화하는데 목적을 두었다. 본 연구에서 생태연못(Eco-Pond) 시스템의 수질개선 원리는 수중(유입수)의 침전, 유기산 생성, 메탄 발효, 호기성 산화, 광합성 산소배출 및 병원균 제거 등을 촉진시키기 위한 목적으로 축산농가 및 마을단위의 축산 및 생활하수 유입부에서 생태연못을 두어 수질을 개선하는 공법 즉, 산화조(Oxidation Pond)에 SolaBee 시스템을 결합한 모델을 제안하였다. 에너지 순환장치를 이용한 수질개선 방안으로는 태양열 연못 내에 물순환장치를 만들어 수체를 효율적으로 순환시키고 공기를 혼합시켜 부영양화가 진행되는 연못이 수질을 자연친화적으로 개선시키도록 하였다. 따라서 연구결과 태양에너지는 다른 자연에너지(풍력 등)에 비해서 에너지 밀도는 낮지만 지역의존성이 적고 그 양이 방대하여 21세기 중요한 에너지원으로 사용가능성을 확인할 수 있었다. 본 연구에서 제시된 에너지 순환구조를 가진 생태연못 시스템은 우리나라 중소규모의 농촌 및 축산농가에 보급 될 수 있는 수질개선 시스템이다.

• 환경위생공학
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• 제14권3호
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• pp.123-129
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• 1999

The utilization methods of algae biomass have been studied constantly in whole world. These are $\circled1$the wastewater treatment if waste stabilization pond and oxidation ditch etc. and $\circled2$the biosorption of heavy metals and recovery of strategic' precious metals and $\circled3$the single-celled protein production and the production of chemicals like coloring agent and $\circled4$the production of electric energy through methane gasification. The culture system also has been developed constantly in relation with such utilization method developments. In the result of experimental operation under continuous and cyclic irradiation of light, using high rate algae biomass culture pond(HRABCP), which had been made so as to be an association system with the various items which had been managed to have high efficiency for algae culture, the algae production of the 12 hours-irradiance pond was 41.48 Chlorophyll-a ${\mu}g/L$ only in spite of having the more chance of $CO_2$ synthesis to algae cell than the 24 hours-irradiance pond. This means that the energy supply required for dark-reaction of photosynthesis is very important like this. The difference of algae production between continuous and cyclc irradiation explains that the dark-reaction of photosynthesis acts on algae production as the biggest primary factor. The continuous irradiance on HRABCP made the good algae-production($1403.97{\;}{\mu}g$ Chlorophyll-a/mg) and the good oxygen-production(5.8 mg $O_2/L$) and the good solid-liquid seperation. especially, DO concentration through the oxygen-production was enough to fishes' survival.

• 한국환경복원기술학회지
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• 제7권4호
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• pp.61-68
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• 2004

The purpose of this study was to develop environmentally friendly constructed wetland system in order to improve the environment. This system was constructed with two constructed wetlands andone pond. The size of the first and second wetland was 2.5m in length, 2.5m in width and 0.7m in depth for the first wetland and 0.6m in depth for the second wetland. Those were filled with pebbles with about 16~32mm in diameter from bottom to 20cm depth and onto the pebbles with about 0.5 mm in diameter sand in depth 40cm. The first constructed Wetland was planted with pragmites communis. The second was planted with Iris pseudoacorus and Acorus calamus var. aneustatus.A vertical flow system was used in the first constructed wetland and a horizontal flow system in the second. The water of outflow from the second wetland flowed into the pond. This system was installed in Yangpyeong, Kyunggi Province. The Quality of inflow and outflow were analyzed at the first time from May 20 to May 30, 2002 and at second time from June 10 to July 18, 2002. At the second period wetland was implanted with microbes in order to improve the efficiency of constructed wetlands. Following standard methods for wastewater, BOD, COD, SS, T-N and T-P were analyzed. This system was effective in reducing COD, BOD, SS, T-N and T-P level. The result shows that wastewater was purified through constructed wetland system with plants and highly purified with microbes especially in T-P. The Average total phosphorous concentration of influent and effluent in constructed wetland with microbes was 2.8mg/${\ell}$ L and 0.21mg/${\ell}$ respectively. This system can be used in rural community because this is not only effective on purification of sewage but also is harmonized with the surrounding nature.

• 상하수도학회지
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• 제21권6호
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• pp.727-735
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• 2007

The use of water by cities is increasing owing to industrialization, the concentration of population, and the enhancement of the standard of living. Accordingly, the amount of waste water is also increasing, and the degree of pollution of the water system is rising. In order to solve this problem, it is necessary to remove organisms and suspended particles as well as the products of eutrophication such as nitrates and phosphates. This study developed a high-end treatment engineering solution with maximum efficiency and lower costs by researching and developing a advanced treatment engineering solution with the use of Biosorption. As a result, the study conducted a test with a $50m^3/day$ Pilot Scale Plant by developing treatment engineering so that only the secondary treatment satisfies the standard of water quality and which provided optimal treatment efficiency along with convenient maintenance and management. The removal of organisms, which has to be pursued first for realizing nitrification during the test period, was made in such a way that there would be no oxidation by microorganisms in the reactor while preparing oxygen as an inhibitor for the growth of microorganism in the course of moving toward the primary settling pond. The study introduced microorganisms in the endogeneous respiration stage to perform adhesion, absorption, and filtering by bringing them into contact with the inflowing water with the use of a sludge returning from the secondary settling pond. Also a test was conducted to determine how effective the microorganisms are as an inner source of carbon. The HRT(Hydraulic Retention Time) in the nitrification tank (aerobic tank) could be reduced to two hours or below, and the stable treatment efficiency of the process using the organisms absorbed in the NAR reactor as a source of carbon could be proven. Also, given that the anaerobic condition of the pre-treatment tank becomes basic in the area of phosphate discharge, it was found that there was excellent efficiency for the removal of phosphate when the pre-treatment tank induced the discharge of phosphate and the polishing reactor induced the uptake of phosphate. The removal efficiency was shown to be about 94.4% for $BOD_5$. 90.7% for $COD_{Cr}$ 84.3% for $COD_{Mn}$, 96.0% for SS, 77.3% for TN, and 96.0% for TP.

• 환경위생공학
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• 제11권1호
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• pp.83-91
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• 1996

It is not too much to say that the territorial inhabitants' concerns are wholly c concentrated on the environmental preservation-problem and development-problem in Korea given effect to the local self-government system. At a time like this I was studied the effect on nutrients removal through lighting period in aerobic high rate pond and we know that waste stabilization pond method is the most economical and energy saving wastewater treatment technology than others. At the results which was studied through operating the reactor-l artifically main-tained at a temperature, $25^{\circ}C$, a light intensity, 3000lux, and a lighting period, 24hrs and the reactor-2 artifically maintained at a tern야rature, $25^{\circ}C$ and a light intensity 3000lux, and a lighting period period, 12hrs, It has appeared for 24hrs.-lighting period -reactor-1 to be prior to the reactor-2. The attained results are that 1. reactor-1 is prior to reactor-2 on oxygen-generation 2. reactor-1 is prior to reactor-2 on algal production 3. COD removal efficiency, 90.76%, T-N removal efficiency, 80%, T-P removal e efficiency, 74.47 % in reactor-2, in reactor-1 COD removal efficiency, 94.85 %, T-N removal efficiency, 98.07%, T-P removal efficiency, 72.13% are, so the treatment efficiency of reactor-1 is more excellent than things of reactor-2 4. it appeared that the detention time is 8, 9days.