KR100391937B1 - Water treatment system by high-rate oxidation pond with filamentous algae mat - Google Patents

Water treatment system by high-rate oxidation pond with filamentous algae mat Download PDF

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KR100391937B1
KR100391937B1 KR10-2000-0064587A KR20000064587A KR100391937B1 KR 100391937 B1 KR100391937 B1 KR 100391937B1 KR 20000064587 A KR20000064587 A KR 20000064587A KR 100391937 B1 KR100391937 B1 KR 100391937B1
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algae
treatment
sewage
agricultural drainage
filamentous algae
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KR20020033998A (en
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김완중
김영철
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농업기반공사
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
    • C02F3/322Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae use of algae
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/06Aerobic processes using submerged filters
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/10Packings; Fillings; Grids
    • C02F3/101Arranged-type packing, e.g. stacks, arrays
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/10Packings; Fillings; Grids
    • C02F3/109Characterized by the shape
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/007Contaminated open waterways, rivers, lakes or ponds

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  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Microbiology (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Biotechnology (AREA)
  • Botany (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

본 발명은 분산형 농촌마을의 오수 및 소하천수·농경배수의 처리시스템에 관한 것으로, 기계·토목적 처리구조를 갖추지 않고 사상성조류매트가 증식되는 고속산화지와 수생식물조 및 유출제어조를 설치함으로써 고효율의 영양염류의 제거가 가능한 수처리가 이루어지도록 한 것이다.The present invention relates to a treatment system for sewage, small river and agricultural drainage in a decentralized rural village, and by installing a high speed oxidized land, an aquatic plant tank and an outflow control tank in which a filamentous algae mat is grown without a mechanical or civil treatment structure. The water treatment to remove nutrients of high efficiency is made.

이러한 본 발명은 오수 및 소하천수·농경배수의 처리에 있어 수심 50㎝ 이내로 유지되는 무교반식 고속산화지에서 사상성조류매트를 증식시키고, 고속산화지 전후에 수생식물조와 유출제어조를 배열시킴으로써 이루어지며, 본 시스템은 유휴농경지나 하천부지를 이용하여 간단히 설치할 수 있다.The present invention is made by multiplying filamentous algae mat in an agitated fast oxidation paper maintained within a depth of 50 cm in the treatment of sewage, small river water and agricultural drainage, and arranging aquatic plant tanks and outflow control tanks before and after the high speed oxidation paper. The system can be simply installed using idle farmland or riverbeds.

Description

사상성조류매트 산화지를 이용한 농촌형 소하천수, 농업배수 처리공법{Water treatment system by high-rate oxidation pond with filamentous algae mat}Water treatment system by high-rate oxidation pond with filamentous algae mat

본 발명은 농촌마을의 소하천수·농경배수의 처리에 있어서, 특별한 토목구조물의 제작과 기계적인 처리구조를 갖추지 않고, 논과 같은 유휴농경지를 고속산화지로 활용하여 수처리가 이루어지도록 한 농촌형 오수 및 소하천수·농경배수 처리공법에 관한 것이다.In the present invention, in the treatment of small rivers and agricultural drainage in rural villages, rural sewage and small river waters are made without using special engineering structures and mechanical treatment structures, and utilizing idle agricultural lands such as rice fields as high-speed oxidation sites. It relates to the agricultural drainage treatment method.

일반적으로 수처리 시설은 (1) 부유물질의 제거, (2) 유기물질의 제거, (3) 영양염류의 제거, (4) 미생물학적으로 안전한 처리수질의 확보, (5) 독성물질(중금속 포함)의 제거등의 목표를 가지고 설계하게 되는데, 대부분은 상기된 몇몇 목표 또는 아래에 제시한 전체목표를 달성하기 위하여 설계하게 된다.In general, water treatment facilities require (1) removal of suspended solids, (2) removal of organic substances, (3) removal of nutrients, (4) ensuring microbiologically safe treatment water quality, and (5) toxic substances (including heavy metals). It is designed to achieve the goal of elimination of, and most are designed to achieve some of the above goals or the overall goal set out below.

기계적인 요소가 많은 공학적인 처리시스템(engineered processes)에서는 상기한 처리목표에 따라 1차처리, 2차처리, 3차처리로 분류하며, 지난 30여년간 상기와 같은 목표를 달성하고자 각 단위공정을 정형화/배열화 하는 수많은 노력을 기울여 왔으며, 일반적으로 도시하수를 처리할 경우 각 처리목표를 달성하기 위해서 부가적인 단위공정을 추가하는 것이 보통이나 이는 막대한 재정이 요구된다.Engineered processes with many mechanical factors are classified into primary treatment, secondary treatment and tertiary treatment according to the above treatment goals. For each of the last three decades, each unit process is formalized. There has been a lot of effort to make / arrangements, and in general, when treating municipal sewage, it is common to add additional unit processes to meet each treatment goal, but this requires a significant amount of finance.

그러나 농어촌지역(읍, 면, 리)에서는 농어촌지역 수계의 수질관리를 위해서 앞서 제시한 처리목표중 일부를 달성하고자 할 때 흔히 도시지역에서 건설/운영하고 있는 고비용의 환경기초시설을 설치하는데는 재원조달의 문제가 있어 현실적으로 불가능하며, 또한 유기물 농도에 비해 상대적으로 높은 영양염류를 제어하기 위한 고도처리기법의 도입이 매우 어려운 실정이다.However, in rural areas (Eup, Myeon, Lee), when they want to achieve some of the above treatment goals for water quality management in rural areas, they often have the resources to install expensive environmental foundations that are being constructed and operated in urban areas. There is a problem of procurement, which is not practical, and it is very difficult to introduce advanced treatment techniques for controlling nutrients which are relatively higher than organic concentration.

최근 들어 오수나 하천수·농경배수중에 포함된 질소와 인을 제거하기 위하여 자연정화원리를 활용한 인공습지나 산화지 공법이 많이 활용되고 있으나, 대부분 대량의 토지면적을 요구하는 공법의 특성상 우리나라에 전반적으로 활용하기에는 많은 어려움이 있다.Recently, many artificial wetlands and oxidized geotechnologies using natural purification principles have been used to remove nitrogen and phosphorus contained in sewage, river water, and agricultural drainage. There are many difficulties to use.

본 발명은 오수 및 농경배수·소하천수에서 특히 문제시 되는 영양염류의 제거를 위한 처리시스템을 개발한 것으로, 가급적 기존 자연처리공법에 비해 토지요구도가 작고 토목구조의 설치나 혼합을 위한 기계적 요소를 배제하는 동시에 유지관리가 용이하도록 한 것이다.The present invention has developed a treatment system for the removal of nutrients, which is particularly problematic in sewage, agricultural drainage, and small river water. Wherever possible, land requirements are smaller than existing natural treatment methods and mechanical elements for installation or mixing of civil structures Excluded and easy to maintain.

본 발명은 농촌 지역의 오수, 오염된 소하천수나 농경배수중의 영양염류 제거뿐만 아니라 병원성 미생물 제거 등에 탁월한 효과를 가지는 고속산화지를 이용할 때 배출수중의 과다 조류유출로 인한 2차오염을 제어하기 위한 목적으로 고속산화지내에 사상성조류를 증식시킴으로써 처리시설의 관리를 매우 용이하도록 한 것이다.The present invention aims to control secondary pollution due to excess algae in the discharged water when using high speed oxidizing paper which has an excellent effect on removing pathogenic microorganisms as well as removing nutrients from sewage, polluted sewage or agricultural drainage in rural areas. In this way, the growth of filamentous algae in high-speed oxidized land is made very easy.

이러한 본 발명은 고속산화지 전단에 부유물질의 제어 및 부유성 조류 증식억제를 위한 수생식물조를 설치하고 고속산화지 후단에는 조류유출을 방지하지 위한 유출제어조(침전조)를 설치함으로써 이루어지는 것으로 수생식물조에는 개구리밥 등 부유식물을 식재하여 수표면 전체를 피복시킬 수 있도록 하고, 유출제어조에는 미나리나 부레옥잠 등을 식재하여 뿌리나 줄기에 의해 산화지에서 유출된 조류군체를 효과적으로 제어하는 동시에 태양광을 차단시킴으로써 조류의 추가증식을 억제하여 처리시스템 배출수질의 안정성을 확보하는 것이다.The present invention is made by installing an aquatic plant tank for the control of suspended solids and floating algae growth inhibition on the front end of the high-speed oxidation paper, and the outflow control tank (sedimentation tank) to prevent algae outflow at the rear end of the high-speed oxidation paper in the aquatic plant tank Planting floating plants such as duckweed to cover the entire water surface, and planting buttercups and water hyacinths in the outflow control tank to effectively control algae colonies leaked from the oxidized ground by roots and stems, while blocking sunlight. The additional growth of algae is suppressed to ensure the stability of treatment system effluent quality.

도 1 은 본 발명의 사상성조매트산화지(FAMP ; Filamentous Algae Mat Ponds), 수생식물조(APB ; Aqutic Plant Basin), 유출제어조(ACB ; Algae Control Basin)등의 처리공정도1 is a process chart of a filamentous algae mat ponds (FAMP), an aquatic plant basin (APB), an outflow control tank (ACB), and the like of the present invention.

도 2 와 도 3 은 본 발명에 의해 처리된 소하천수·농경배수 처리결과 그래프2 and 3 are graphs of small river water and agricultural drainage treatment results treated by the present invention.

도 3 은 본 발명의 고속산화지(FAMP)에서의 사상성조류의 증식형태를 보인 사진Figure 3 is a photograph showing the growth mode of filamentous algae in the fast oxidation paper (FAMP) of the present invention

[도면의 주요부분에 대한 부호 설명][Description of symbols on the main parts of the drawings]

1. 사상성조류매트 산화지 2. 수생식물조 3 유출제어조1. Filamentous algae mat oxidation paper 2. Aquatic plant tank 3 Outflow control tank

본 발명의 수처리는 도 1 에 도시된 바와 같이 부유물질의 영향을 최소화하고 부유성 조류 증식을 억제하기 위하여 오수 및 농경배수·소하천수가 수생식물조(1)를 거친후 고속산화지(2)를 거쳐 유출제어조(3)를 거치도록 한 것으로, 가급적 농촌지역 특히 분산형 마을에서 큰 재정지원 없이 설치 가능하도록 한 것이다.이러한 본 발명은 생활오수 및 소하천수, 농경배수의 처리에 있어서, 오수 및 소하천수, 농경배수를 부유물질의 제거 및 부유성조류 증식 억제를 위하여 수생식물조(1)로 유입하여 처리시키는 단계와, 상기 수생식물조(1)에서 일정시간 체류된 오수 및 소하천수, 농경배수를 사상성조류를 증식하여 매트리스화 시킨 고속산화지(2:또는 고효율산화지)로 유입 처리하는 단계와, 상기 고속산화지(2)에서 처리된 처리수를 유출제어조(3)로 유입하여 조류 유출을 방지한 후 방류하므로서 이루어지는 것으로, 이하 본 발명을 실시예에 의거 상세히 살펴본다.The water treatment of the present invention, after minimizing the effects of suspended solids and suppressing the growth of floating algae, as shown in Figure 1, after the sewage and agricultural drainage, small river water through the aquatic plant tank (1) through a fast oxidation paper (2) The spill control tank 3 is intended to be installed in rural areas, particularly in distributed villages, without significant financial support. The present invention provides sewage and small rivers in the treatment of domestic sewage and small rivers and agricultural drainage. Inflow and treatment of water and agricultural drainage to the aquatic plant tank (1) for removal of suspended solids and suppression of floating algae, and sewage, small river water, and agricultural drainage stayed in the aquatic plant tank (1) for a certain time. Inflow treatment of the filamentous algae into high-speed oxidation paper (2: or high-efficiency oxidation paper) in which the mattress is formed, and the treated water treated in the high-speed oxidation paper (2) flows into the outflow control tank (3). It is made by discharge after preventing the algae outflow, the present invention will be described in detail based on the following examples.

실 시 예. 1Example. One

오염된 하천수와 농경배수를 이용하여 처리실험을 수행한 결과 본 발명을 이루는 각 공정은 다음과 같은 기능과 역할을 수행하는 것으로 밝혀졌다.As a result of treatment experiments using contaminated river water and agricultural drainage, each process constituting the present invention was found to perform the following functions and roles.

수생식물조 (APB)Aquatic Plant (APB) 사상성조류매트 산화지 (FAMP)Filamentous Algal Oxide Paper (FAMP) 유출제어조 (FAMCB)Outflow Control Tank (FAMCB) 수생식물은 개구리밥 등 수표면을 완전 피복하는 부엽식물이 적절함.수생식물의 뿌리 등에 의해 유입수중의 부유물질이 부착 또는 침전 제거됨.태양광을 차단함으로써 부유성 조류 증식을 억제함.식물생체량의 수확/재이용For aquatic plants, the side plants that completely cover the surface of the water, such as frog rice, are suitable. Floating substances in the inflow water are attached or precipitated by the roots of aquatic plants.Inhibiting floating algae by blocking sunlight. Harvest / Reuse Spirogyra sp.를 우점종으로 하는 사상성조류군을 증식시킴.조류합성에 의한 용존성 인/질소의 제거높은 pH 조건으로 인한 병원성 미생물의 사멸효과높은 pH로 인한 인산염 인의 화학적 침전제거용존산소의 공급으로 전 시스템에서 충분한 호기상태 유지.Proliferation of filamentous algae, predominant species of spirogyra sp. Elimination of dissolved phosphorus / nitrogen by algae synthesis. Killing effect of pathogenic microorganisms due to high pH conditions. Chemical precipitation of phosphate due to high pH. Maintain sufficient exhalation in the system. 수생식물은 미나리나 부레옥잠의 식재가 적절함.유출된 조류의 침전 및 부착 제거과도하게 상승된 pH를 조정함으로써 유출수의 화학적 안정도모식물생체량의 회수/재이용Aquatic plants are suitable for planting buttercups and water hyacinths. Chemical stability of effluents by adjusting the elevated pH with precipitation and removal of adherent algae.

실 시 예. 2Example. 2

본 발명의 처리시스템을 이용하여 분산마을형 오수 및 소하천수·농경배수의 수처리실험에서 영양염류의 유입수질을 오염된 하천수나 농경배수 수준인 T-N 3∼9 ㎎/L, T-P 0.3∼0.7 ㎎/L로 운전하였을 때 도 2 에 나타난 바와 같이 수리학적 체류시간 4∼5일에서 처리수질은 평균 T-N 0.67 ㎎/L, T-P 0.068 ㎎/L 였다.Using the treatment system of the present invention, TN 3-9 mg / L, TP 0.3-0.7 mg /, which is the level of contaminated river water or agricultural drainage, in the water treatment experiment of distributed village sewage and small river and agricultural drainage. As shown in FIG. 2, the treated water quality at the hydraulic retention time of 4-5 days was TN 0.67 mg / L and TP 0.068 mg / L.

본 처리시스템 전체의 영양염류 제거효율은 T-N 89.3%, T-P 85.8%였으며, FAMP에서의 효율은 T-N 88.1%, T-P 80.4% 였다.The nutrient removal efficiencies of the whole treatment system were T-N 89.3% and T-P 85.8%, and the efficiency in FAMP was T-N 88.1% and T-P 80.4%.

특히 영양염류 처리를 위해 공학적 처리시설에서 흔히 요구되는 추가의 탄소원공급이 전혀 필요없이 처리수질을 부영양화 유발기준 이하로 유지할 수 있으며, 특별한 동력원이나 시설물의 관리인력이 불필요하였다.In particular, the treatment water quality could be kept below eutrophication criteria without the need for additional carbon sources, which are often required in engineering treatment facilities for the treatment of nutrients, and no special power source or management personnel were needed.

한편 온도가 저하되는 동절기에는 시스템의 온상화 또는 비닐하우스 등을 설치하여 온도저하를 방지할 경우 처리의 안정성이 크게 향상된다.On the other hand, in winter, when the temperature is lowered, the stability of the treatment is greatly improved when the system is warmed or a vinyl house is installed to prevent the temperature decrease.

또한 본 발명의 시스템을 현장에 적용할 경우 대상 수체에 적절한 운전조건을 찾아내기 위하여 도 3 과 같이 시운전결과를 통하여 수리학적 체류시간(HRT), 수온(Temp.), pH와 T-N, T-P와의 관계를 분석하여 적절한 운전조건을 찾을 수 있다.In addition, when the system of the present invention is applied to the site, the relationship between the hydraulic retention time (HRT), the water temperature (Temp.), PH, TN, and TP through the test operation results as shown in FIG. The proper operating conditions can be found by analyzing.

실 시 예. 3Example. 3

본 발명 수처리 시스템의 주요기능인 사상성 조류의 증식은 전체시스템을 완전한 호기성 조건을 유지할 수 있도록 한다. 사상성 조류군이 매트를 형성하면서 주간동안 광합성 활동을 통하여 발생된 산소 기포는 도 4 의 사진과 같이 조류매트내에 포획하고 있었다.The growth of filamentous algae, a major function of the present water treatment system, allows the entire system to maintain complete aerobic conditions. Oxygen bubbles generated through photosynthetic activity during the day as the filamentous algae group formed a mat were captured in the algae mat as shown in FIG. 4.

기존에 개발되어 있는 고속산화지의 원리는 전 수층에 걸쳐 조류합성이 일어나고 야간에 호흡으로 인한 무산소 상태를 방지할 수 있도록 기계적인 교반시설을 주로 설치하고 있다. 그러나 본 발명 수처리 시스템에서는 조류매트내에 포획된 산소공급으로 야간의 무산소상태가 일어나지 않으므로 기계적인 혼합은 필요 없으므로 본 발명 시스템은 무교반식으로 설계된다.The principle of high speed oxidizing paper, which has been developed previously, is mainly installing mechanical stirring facilities to prevent algae synthesis and prevent anoxic conditions due to breathing at night. However, in the water treatment system of the present invention, the oxygen supply trapped in the algae mat does not occur at night, so no mechanical mixing is necessary, so the present invention system is designed without stirring.

또한 사상성 조류군은 매트를 형성하고 있기 때문에 고속산화지(2)에서 조류유출(2차오염)은 거의 찾아볼 수 없으며 고속산화지(2)에서 과도증식된 사상성조류군은 매트가 갈변하기 시작하는 시점에서 회수함으로써 최종적으로 영얌염류의 제거가 완성되는 것으로 매트의 회수시기는 3∼4주에 1회가 적당하며, 회수작업은 갈퀴 등을 이용하여 인력으로 쉽게 가능하다.In addition, since filamentous algae form mats, algae outflow (secondary pollution) is hardly found in the fast oxidation sheet (2), and the filamentous algae group that overproliferates in the fast oxidation sheet (2) starts to brown. Finally, the elimination of Young-Yam salts is completed by recovering from the mat. The recovery time of the mat is suitable every three to four weeks, and the recovery operation can be easily performed by manpower using a rake.

회수된 조류생체량중 VS 함량은 약 88% 로써 유기질 함량이 높아 조류의 퇴비화 등 재활용에 적합하다.VS content in recovered algae biomass is about 88%, which is suitable for recycling such as composting of algae due to high organic content.

또한 사상성조류매트산화지(2)(FAMP)에서 사상성 조류군의 질소와 인 흡수능력은 각각 37.7 ㎎rem.N/d·㎡, 31.2 ㎎rem.P/d·㎡ 로 산정되어, 본 발명 시스템에 적용된 사상성 조류군의 영양염류 흡수능력은 개구리밥이나 부레옥잠, 미나리 등의 수생식물에 의한 효과보다도 월등히 크다.In addition, the filamentous algae group had 37.7 mg rem. N / d · m 2, 31.2 mg rem. The nutrient absorption capacity of the filamentous algae group, which is calculated as P / d · m 2, applied to the system of the present invention, is much greater than the effect of aquatic plants such as duckweed, water hyacinth, and parsley.

본 발명은 농촌지역의 오수나 오염된 소하천수, 농경배수중의 영양염류 제거시스템으로써, 재정적인 지원이 적은 실정에서 기계적인 요소나 토목구조물의 설치를 가급적 배제하고도 영양염류의 높은 제거효율을 얻을 수 있다.The present invention is a system for removing nutrients from sewage, polluted sewage and agricultural drainage in rural areas. In the absence of financial support, the present invention provides high removal efficiency of nutrients even if eliminating mechanical elements or civil structures. You can get it.

또한 본 발명에 의한 처리부지 역시 분산형 농촌마을에서 유휴농경지(주로 논)나 하천부지, 저수지 홍수면을 활용하여 간단히 설치할 수 있으며, 처리수질이 부영양화 유발기준 이하로 발생되므로 농업용수원의 관리에 매우 적합한 것이다.In addition, the treatment site according to the present invention can also be easily installed in a decentralized rural village by utilizing idle farmland (mainly paddy fields), riverbeds, and reservoir floodplain, and because the treated water quality is generated below the eutrophication standard, it is very useful for the management of agricultural water sources. It is suitable.

Claims (2)

생활오수 및 소하천수, 농경배수의 처리에 있어서, 오수 및 소하천수, 농경배수를 부유물질의 제거 및 부유성조류 증식 억제를 위하여 수생식물조(1)로 유입하여 처리시키는 단계;In the treatment of domestic sewage and small river water, agricultural drainage, the step of treating the sewage and small river water, agricultural drainage into the aquatic plant tank (1) for the removal of suspended substances and suppressing the growth of floating algae; 상기 수생식물조(1)에서 일정시간 체류된 오수 및 소하천수, 농경배수를 사상성조류를 증식하여 매트리스화 시킨 고속산화지(2)로 유입 처리하는 단계;Inflowing and treating the sewage, small river water, and agricultural drainage in the aquatic plant tank (1) into a fast oxidation paper (2) where the filamentous algae are grown and mattressed; 상기 고속산화지(2)에서 처리된 처리수를 유출제어조(3)로 유입하여 조류 유출을 방지한 후 방류하는 것을 특징으로 하는 사상성조류매트 산화지를 이용한 농촌형 소하천수, 농업배수 처리공법.Rural type river water, agricultural drainage treatment method using filamentous algae mat oxidized paper, characterized in that the treated water from the high-speed oxidizing paper (2) flows into the outflow control tank (3) to prevent algae outflow. 제 1 항에 있어서, 고속산화지(2)는 사상성조류를 이용하여 사상성조류매트를 형성시켜 조류유출에 의한 2차오염을 방지하며, 동시에 무교반식으로 운전되는 것을 특징으로 하는 사상성조류매트 산화지를 이용한 농촌형 소하천수, 농업배수 처리공법.The method of claim 1, wherein the fast oxidation paper 2 uses filamentous algae to form a filamentous algae mat to prevent secondary contamination due to algae spillage, and at the same time, it is operated in an agitated manner. Rural small river water, agricultural drainage treatment method.
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US5137625A (en) * 1990-12-28 1992-08-11 Wolverton Billy C Aquatic plant/microbial water purification system
JPH05154498A (en) * 1991-12-09 1993-06-22 Meiji Milk Prod Co Ltd Treatment of drainage and equipment thereof
JPH06182384A (en) * 1992-12-22 1994-07-05 Dam Suigenchi Kankyo Seibi Center Equipment for purifying inflow water
JPH07303897A (en) * 1994-03-17 1995-11-21 Pub Works Res Inst Ministry Of Constr Water purifying apparatus using filamentary algae

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5137625A (en) * 1990-12-28 1992-08-11 Wolverton Billy C Aquatic plant/microbial water purification system
JPH05154498A (en) * 1991-12-09 1993-06-22 Meiji Milk Prod Co Ltd Treatment of drainage and equipment thereof
JPH06182384A (en) * 1992-12-22 1994-07-05 Dam Suigenchi Kankyo Seibi Center Equipment for purifying inflow water
JPH07303897A (en) * 1994-03-17 1995-11-21 Pub Works Res Inst Ministry Of Constr Water purifying apparatus using filamentary algae

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