KR20010037974A - Circular Waterway Type Waste Water Treatment System for Nitrogen & Phosphorous Removal - Google Patents
Circular Waterway Type Waste Water Treatment System for Nitrogen & Phosphorous Removal Download PDFInfo
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- KR20010037974A KR20010037974A KR1019990045760A KR19990045760A KR20010037974A KR 20010037974 A KR20010037974 A KR 20010037974A KR 1019990045760 A KR1019990045760 A KR 1019990045760A KR 19990045760 A KR19990045760 A KR 19990045760A KR 20010037974 A KR20010037974 A KR 20010037974A
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/30—Aerobic and anaerobic processes
- C02F3/302—Nitrification and denitrification treatment
- C02F3/305—Nitrification and denitrification treatment characterised by the denitrification
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/30—Aerobic and anaerobic processes
- C02F3/302—Nitrification and denitrification treatment
- C02F3/303—Nitrification and denitrification treatment characterised by the nitrification
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/30—Aerobic and anaerobic processes
- C02F3/308—Biological phosphorus removal
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
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- Y10S—TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y10S210/00—Liquid purification or separation
- Y10S210/902—Materials removed
- Y10S210/903—Nitrogenous
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
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- Y10S—TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y10S210/00—Liquid purification or separation
- Y10S210/902—Materials removed
- Y10S210/906—Phosphorus containing
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Abstract
Description
본 발명은 하수 또는 폐수로부터 유기물과 영양염류를 제거하는 장치 및 방법에 관한 것으로, 침전지내장형 또는 외장형의 산화구에 혐기성반응조와 호기성반응조를 설치하고, 상기 혐기성 반응조에서는 인방출반응이 이루어지며 상기 무산소반응조에서는 탈질반응이 이루어지고, 산화구에서는 인의 초과섭취와 질산화 및 유기물의 호기성분해가 이루어지므로 내부순환펌프 및 관로를 생략하고서도 경제적으로 질소와 인을 제거할수 있는 고도하폐수처리시스템에 관한 것이다.The present invention relates to an apparatus and a method for removing organic matter and nutrients from sewage or wastewater. An anaerobic reaction tank and an aerobic reaction tank are installed in a sedimentation built-in type or an external type of oxidizing sphere, and in the anaerobic reaction tank, a phosphorus release reaction is performed and the oxygen-free reaction tank is performed. In the denitrification reaction, the oxidative sphere is ingested in excess of phosphorus, nitrification and aerobic decomposition of organic matter, so it is related to the advanced sewage treatment system that can remove nitrogen and phosphorus economically without omitting the internal circulation pump and pipeline.
하폐수중의 오염물질에는 유기물과 영양염류인 질소와 인이 주종을 이루고 있으며 생물학적 질소제거는 질산화(Nitrification)반응을 위한 호기성반응조(Aerobic Reactor)와 탈질(Denitrification)반응을 위한 무산소반응조(Anoxic Reactor)로 분리된 2조이상의 반응조에서 질산화반응과 탈질반응이 이루어진다. 또한 생물학적 방법에 의하여 인을 효과적으로 제거하기 위해서는 활성슬러지로부터 인이 방출되는 혐기성반응조(Anaerobic Reactor)가 추가되어야 한다.Contaminants in sewage water are mainly composed of organic matter and nutrients nitrogen and phosphorus, and biological nitrogen removal is aerobic reactor for nitrification reaction and anoxic reactor for denitrification reaction. Nitrification and denitrification occur in two or more tanks separated by. In addition, in order to effectively remove phosphorus by a biological method, an anaerobic reactor that releases phosphorus from activated sludge should be added.
질소산화물이 환원되는 탈질반응의 형태는 유입하폐수에 함유된 유기물을 이용하는 전탈질방법과 외부에서 유기물을 공급해야 되는 후탈질방법으로 분류되며, 유입하폐수중의 유기물을 이용하는 전탈질방법이 경제적으로 유리한 측면이 있으나 장치의 구성이 복잡하고 내부순환에 따른 동력소요가 큰 문제점이 있다.Types of denitrification in which nitrogen oxides are reduced are classified into total denitrification method using organic substances contained in influent wastewater and post denitrification method using organic materials from outside, and total denitrification method using organic substances in influent wastewater is economically advantageous. Although there is a side, the configuration of the device is complicated and there is a big problem of power consumption due to internal circulation.
종래의 기술중 본 발명에서와 같은 전탈질방법으로서 대표적인 공법에 해당되는 A2O공법(Anaerobic Anoxic Oxic Process)과 장치의 구성에 대하여 좀더 자세히 설명하면, 도1에서와 같이 혐기성반응조(101)에서는 침전지(111)에서 반송되는 활성슬러지로부터 인방출반응이 이루어지고, 무산소반응조(102)에서는 탈질반응이, 호기성반응조(103)에서는 질산화와 유기물분해 및 인의 초과섭취가 이루어지는 공정으로 구성된다.The A 2 O method (Anaerobic Anoxic Oxic Process) and if greater detail the configuration of a device, the anaerobic tank 101, as shown in Figure 1, which is a typical method as before denitration method as in the invention of the prior art The phosphorus release reaction is carried out from the activated sludge returned from the settling basin 111, the denitrification reaction in the oxygen-free reaction tank 102, the nitrification and organic decomposition and the excess intake of phosphorus in the aerobic reactor (103).
호기성반응조(103)에는 유기물의 분해와 질산화 반응을 위하여 포기장치가 설치되며 반응액을 무산소반응조(102)로 내부순환시키기 위한 내부순환펌프(107)가 설치되어야 한다. 이와 같은 구성의 상기 A2O공법에서는 내부순환펌프(107)와 내부순환관로등이 설치되므로, 시설비와 동력비 측면에서 비경제적이며 유지관리면에서도 어려움이 많은 문제점이 있다.The aerobic reactor 103 is provided with an aeration device for decomposition and nitrification of organic matter, and an internal circulation pump 107 for circulating the reaction liquid into the oxygen-free reactor 102 should be installed. In the A 2 O method of the above configuration, since the internal circulation pump 107 and the internal circulation pipe are installed, there are many problems in terms of facility cost and power cost, which are uneconomical and difficult in maintenance.
또한 종래의 산화구는 순환거리가 비교적 긴 수로형의 반응조이므로 일부구간은 무산소조건 또는 혐기성조건이 형성되어 질소와 인이 효과적으로 제거될수 있는 것처럼 막연히 주장되기도 하였다. 그러나 산화구에서 슬러지가 침전되지 않기 위해서는 순환수류의 유속은 약 0.3m/sec(1ft/sec)가 유지되어야 하며 이러한 유속에서는 순환거리가 매우 긴 산화구, 예를 들면 순환거리가 100M인 대형 산화구에서도 1회 순환에 소요되는 시간은 6분미만이므로 호기성구간, 무산소구간 나아가서는 혐기성구간이 형성된다는 것은 거의 불가능하고 따라서 산화구 단일반응조에서의 질소와 인의 제거효율은 높지 못하였다.In addition, since the conventional oxidation sphere is a channel having a relatively long circulation distance, some sections have been vaguely claimed as nitrogen and phosphorus can be effectively removed by forming anoxic or anaerobic conditions. However, in order to prevent sludge settling in the oxidizing sphere, the flow rate of the circulating water must be maintained at about 0.3 m / sec (1 ft / sec), and at this flow rate, even in a large oxidizing sphere having a long circulating distance, for example, a large oxidizing sphere having a circulating distance of 100 M 1 Since the cycle time is less than 6 minutes, it is almost impossible to form aerobic, anaerobic, and anaerobic sections. Therefore, the removal efficiency of nitrogen and phosphorus in the oxidizing zone was not high.
산화구를 이용하여 질소, 인제거 효율을 크게하기 위하여 덴마트의 크뢰어사에서는 2개이상의 산화구와 외장형 침전지를 조합하여 유로변경 및 간헐포기방식으로 운영하는 PID공법을 개발하였으나 앞단계에는 인방출반응을 위하여 4조의 반응기를 거치는 구조이므로 공정이 매우 복잡하고 시설비 소요가 큰 문제점이 있다.In order to increase the efficiency of nitrogen and phosphorus removal using oxidizing spheres, Denmart Kreuer developed a PID method that operates by changing the flow path and intermittent aeration method by combining two or more oxidizing spheres and an external sedimentation basin. In order to pass through the four sets of reactors in order to process the process is very complicated and there is a large cost requirement.
출원인이 발명하여 PhiCD(Phased isolated intra Clarifier Ditch)시스템으로 명명한 한국특허 제225971호 질소·인제거를 위한 하폐수처리장치 및 방법은 2개이상의 침전지내장형산화구를 조합하여 유로변경 및 간헐포기방식으로 운영하는 하폐수처리시스템을 구성한 것으로 PID공법보다 공정이 단순하고 처리효율이 개선된 공법이다. 그러나 PID공법의 Phase B, Phase D에서는 한 개의 호기성조건의 산화구에서 하폐수의 유입과 유출이 이루어지므로 미생물의 생체에 합성되는 것을 제외하고는 별다른 질소·인제거 기능이 없어 질소와 인의 유출농도가 증가되기도 하며, 출원인이 발명한 상기 PhiCD공법에서도 (c)단계와 (f)단계에서는 PID에서와 같은 문제점이 발생된다.Apparatus and method for treating sewage and wastewater for nitrogen and phosphorus removal in Korea, which the applicant invented and named as PhiCD (Phased isolated intra Clarifier Ditch) system, combines two or more sedimentation-embedded oxidizing spheres and operates the channel change and intermittent aeration method. It is composed of sewage treatment system, which is simpler than PID method and has improved treatment efficiency. However, in the phase B and phase D of the PID method, the inflow and outflow of sewage water is carried out in one aerobic oxidizing sphere, so there is no nitrogen / phosphorus removal function except that it is synthesized in microorganisms. In the PhiCD method invented by the applicant, the same problem as in PID occurs in steps (c) and (f).
이에 본 발명은 상술한 제 문제점을 해소하기 위하여 안출된 것으로, 2조이상의 산화구를 조합하여 유로변경 및 간헐포기방식으로 운영하는 하폐수처리시스템의 모든 단계에서 질소·인제거 효율을 높게 유지할수 있음은 물론, 단일 산화구도 질소와 인 제거기능을 구비하고 별도의 내부순환시설을 생략할수 있는 경제적이고 효율적인 하폐수처리시스템을 제공하고자 한다.Accordingly, the present invention has been made to solve the above-mentioned problems, and it is possible to maintain high nitrogen and phosphorus removal efficiency at all stages of the wastewater treatment system operated by changing the flow path and intermittent aeration by combining two or more trillion oxide spheres. Of course, a single oxidation sphere also has a nitrogen and phosphorus removal function, and to provide an economical and efficient wastewater treatment system that can omit a separate internal circulation facility.
먼저 탈질목적을 달성하기 위하여 본 발명에서는 순환수로형의 호기성반응조인 산화구와 침전지로 구성된 하폐수처리시스템에서, 상기 산화구의 내부에 벽체를 설치하고 무산소반응조를 구성하여 상기 무산소반응조에 하폐수와 반송슬러지가 유입되도록 하고 상기 산화구에서 순환하는 반응액의 일부도 상기 무산소반응조로 유입되도록 하여 탈질이 완료된 반응액은 상기 산화구로 유출되는 구조이다.First, in order to achieve the purpose of denitrification, in the present invention, a wastewater treatment system composed of an oxidizing sphere and a sedimentation basin, which is an aerobic reaction tank of a circulating water channel, is provided with a wall inside the oxidizing sphere, and an anoxic reaction tank is formed to treat wastewater and return sludge in the anoxic reactor. A part of the reaction solution circulated in the oxidizing sphere is also introduced into the anoxic reaction tank so that the denitrification completes the reaction liquid to the oxidizing sphere.
이와 같은 구조의 하폐수처리시스템의 작용을 설명하면, 상기 무산소반응조에서는 미생물이 유입유기물을 이용하여 산화구에서 유입되는 순환수류중의 질소산화물을 환원시키는 탈질반응이 이루어지게 되며, 상기 산화구에서는 호기성조건에서 질산화와 유기물의 분해가 이루어지게 된다. 이때 무산소반응조에 순환수류가 과다하게 유입되면 체류시간이 부족되고 무산소조건의 유지가 어렵게 되므로 순환수류의 유입량을 조절할수 있도록 상기 무산소반응조의 유입구에는 수문등을 설치하는 것이 바람직하다.Referring to the operation of the wastewater treatment system having such a structure, in the anoxic reaction tank, the denitrification reaction is performed in which the microorganisms reduce nitrogen oxides in the circulating water stream flowing from the oxidizing port using the inflowing organic matter, and in the oxidizing sphere under aerobic conditions. Nitrification and decomposition of organic matter are achieved. At this time, if the circulating water flows excessively into the anoxic reaction tank, the residence time is insufficient and it is difficult to maintain the anoxic condition. Therefore, it is preferable to install a water gate at the inlet of the anoxic reaction tank to control the inflow of the circulating water.
또한 탈질기능에 탈인기능을 추가하기 위하여 상기 무산소반응조 앞단계에 혐기성반응조를 추가로 설치하고 하폐수와 반송슬러지는 상기 혐기성반응조로 유입시키고 상기 혐기성반응조의 유출수와 산화구의 순환수류는 상기 무산소반응조로 유입되도록 구성한다. 생물학적 질소·인 제거기능을 병행할수 있는 하폐수처리시스템의 작용을 설명하면, 상기 혐기성반응조에서는 활성슬지로부터 인방출이 이루어지고 상기 무산소반응조에서는 탈질반응이 이루어지며 상기 산화구에서는 질산화 반응과 인의 초과섭취 및 유기물의 호기성 분해가 각각 이루어지게 된다.In addition, in order to add dephosphorization function to the denitrification function, an anaerobic reaction tank is additionally installed in the front stage of the anoxic reaction tank, and sewage and return sludge flow into the anaerobic reaction tank, and the effluent and anaerobic circulation flow of the anaerobic reaction tank are introduced into the anoxic reaction tank. Configure to Referring to the action of the sewage water treatment system which can perform the biological nitrogen and phosphorus removal function, the anaerobic reaction tank is phosphorus discharge from the activated sludge, the anoxic reaction tank is denitrification reaction, the oxidation sphere nitrification reaction and excess intake of phosphorus and Aerobic decomposition of organics is achieved respectively.
이와 같이 반응액이 순환하는 순환수로형의 반응조인 산화구의 내부에 무산소반응조를 설치하거나 또는 혐기성반응조와 무산소반응조를 함께 설치하므로서 내부순환펌프 및 관로를 생략하고서도 종래의 AO 또는 A2O공법에서와 같이 질소와 인을 제거할 수 있게 된다.In this way, an oxygen-free reaction tank is installed inside the oxidizing sphere, which is a circulating channel type reaction tank in which the reaction solution circulates, or an anaerobic reaction tank and an oxygen-free reaction tank are installed together, so that the internal circulation pump and the pipe are omitted, and the conventional AO or A 2 O method is used. Likewise, nitrogen and phosphorus can be removed.
또한 침전지가 내장된 침전지내장형산화구에 상기 무산소반응조를 설치하거나 혐기성반응조와 무산소반응조를 함께 설치하게 되면 슬러지 수집장치 또는 슬러지반송펌프 및 관로시설도 불필요하게 되므로 더욱 경제적이다. 특히 본 발명에 의한 방법은 이미 건설이 완료되어 가동중인 재래식 산화구와 침전지내장형산화구에도 용이하게 적용하여 고도처리공법으로 변경시킬수 있으며, 종래 PID공법 또는 출원인이 발명한 PhiCD공법에 적용하여 질소와 인의 제거효율을 향상시킬수 있다.In addition, when the anoxic reaction tank is installed in the sedimentation basin built-in oxidizing sphere in which the sedimentation basin is built, or when the anaerobic reaction tank and the anoxic reaction tank are installed together, the sludge collecting device or the sludge conveying pump and the pipe line facility are also unnecessary, which is more economical. In particular, the method according to the present invention can be easily applied to conventional oxidized spheres and sedimentation-type oxidized spheres which have already been constructed and operated, and can be changed to a high-treatment method, and applied to the conventional PID method or the PhiCD method invented by the applicant to remove nitrogen and phosphorus. It can improve the efficiency.
본 발명에 따른 산화구를 2조이상 조합하여 유로변경 및 간헐포기방식으로 구성 및 운영하는 하폐수고도처리시스템을 구성하므로서 종래의 PID공법의 (B)Phase와 (D)Phase 그리고 PhiCD공법의 (C)단계와 (F)단계에서 질소와 인의 유출농도를 감소시킬수 있게 되어 처리효율을 향상시키게 된다.(B) Phase and (D) Phase and PhiCD method of the conventional PID method by constructing the wastewater advanced water treatment system which is configured and operated in the channel change and intermittent aeration method by combining two or more sets of oxidation spheres according to the present invention. In step and (F) it is possible to reduce the outflow concentration of nitrogen and phosphorus to improve the treatment efficiency.
도 1은 종래의 전탈질방법에 의한 질소, 인 제거 시스템의 흐름도,1 is a flow chart of a nitrogen, phosphorus removal system by a conventional total denitrification method,
도 2는 본 발명에 따른 질소 제거기능이 구비된 하폐수처리시스템의 개략 구성도,2 is a schematic configuration diagram of a wastewater treatment system equipped with a nitrogen removal function according to the present invention;
도3은 본 발명에 따른 질소, 인 제거기능이 구비된 하폐수처리시스템의 개략 구성도,3 is a schematic configuration diagram of a wastewater treatment system equipped with a nitrogen and phosphorus removing function according to the present invention;
도4는 본 발명에 따른 질소, 인 제거기능이 구비되고 침전지가 내장된 하폐수처리시스템의 개략 구성도이다.Figure 4 is a schematic diagram of the sewage treatment system equipped with a nitrogen, phosphorus removal function and built-in sedimentation basin according to the present invention.
*도면의 주요부분에 대한 부호의 설명** Description of the symbols for the main parts of the drawings *
1 : 산화구 2 : 침전지1: Oxidized sphere 2: Sedimentation basin
3 : 혐기성반응조 4 : 무산소반응조3: anaerobic reactor 4: anaerobic reactor
5 : 벽체 6 : 수 문5: wall 6: male door
7 : 내장형 침전지 11 : 순환수류7: built-in sedimentation basin 11: circulating water flow
이하, 본 발명의 구성 및 작용을 첨부된 예시도면을 통하여 상세하게 설명한다.Hereinafter, the configuration and operation of the present invention will be described in detail through the accompanying drawings.
도2는 본 발명에 따른 탈질반응을 위한 무산소반응조가 구비된 순환수로형 하폐수처리시스템의 평면도이다.2 is a plan view of a circulating water channel type sewage treatment system equipped with an oxygen-free reaction tank for denitrification according to the present invention.
순환수로형의 호기성반응조인 산화구(1)와 침전지(2)로 구성된 하폐수처리시스템에서, 상기 산화구에 벽체(5)를 설치하여 무산소반응조(4)를 구성하고 유입하폐수 및 반송슬러지는 상기 무산소반응조로 유입되는 구조이다. 상기 산화구내의 순환수류(11)의 일부는 상기 무산소반응조로 유입되며 무산소반응조의 유입구에는 수문(6)을 설치하여 상기 순환수류의 유입량이 조절되도록 구성하였다.In the wastewater treatment system consisting of an oxidizing sphere (1) and a sedimentation basin (2), which are aerobic reaction tanks of circulation channel type, a wall (5) is installed in the oxidizing sphere to form an anaerobic reaction tank (4), and the influent wastewater and the return sludge are the anoxic reaction tank. Inflow to the structure. Part of the circulating water 11 in the oxidizing sphere flows into the anoxic reaction tank, and a water gate 6 is installed at the inlet of the anoxic reaction tank to control the inflow of the circulating water.
이와 같은 구조의 상기 하폐수처리시스템에서는 별도의 내부순환펌프가 없어도 상기 산화구에서의 순환수류가 순환유속에 의하여 상기 무산소반응조로 유입되므로 경제적으로 질소산화물의 탈질반응이 이루어지게 된다.In the wastewater treatment system having such a structure, even without a separate internal circulation pump, the circulating water flow in the oxidizing sphere flows into the anoxic reaction tank by the circulation flow rate, thereby economically denitrifying the nitrogen oxide.
도3은 본 발명에 따른 질소와 인을 동시에 제거할수 있도록 무산소반응조와 혐기성반응조가 함께 구비된 순환수로형 하폐수처리시스템의 평면도이다.Figure 3 is a plan view of the circulating channel type sewage treatment system equipped with an anoxic reactor and an anaerobic reactor to remove nitrogen and phosphorus simultaneously according to the present invention.
본 실시예에서는 탈질과 탈인을 병행하기 위하여 무산소반응조(4) 앞단계에 혐기성반응조(3)를 추가로 설치하고 하폐수와 반송슬러지는 상기 혐기성반응조로 유입시키고 상기 혐기성반응조의 유출수와 산화구의 순환수류(11)는 상기 무산소반응조로 유입되도록 구성하며 상기 혐기성반응조에는 상기 순환수류가 유입되지 않는 구조이다. 본 실시예의 작용을 설명하면, 상기 혐기성반응조에서는 활성슬러지로부터 인방출이 이루어지고 상기 무산소반응조에서는 산화구에서 순환유속에 의하여 유입되는 순환수류중의 질소산화물의 탈질반응이 이루어지며 상기 산화구에서는 질산화 반응과 인의 초과섭취 및 유기물의 호기성 분해가 각각 이루어지게 된다.In this embodiment, an anaerobic reaction tank (3) is additionally installed at the front of the anaerobic reaction tank (4) in order to perform denitrification and dephosphorization in parallel. Sewage and return sludge are introduced into the anaerobic reaction tank, and the effluent water of the anaerobic reaction tank and the circulating water flow of the oxidizing port. (11) is configured to flow into the anoxic reaction tank and the circulation water flow does not flow into the anaerobic reaction tank. Referring to the operation of the present embodiment, the anaerobic reaction tank is phosphorus discharge from the activated sludge, the anoxic reaction tank is denitrification reaction of the nitrogen oxide in the circulating water flow by the circulating flow rate from the oxidizing sphere and the nitrification reaction in the oxidizing sphere Excessive intake of phosphorus and aerobic decomposition of organics are achieved respectively.
도4는 본 발명에 따른 질소와 인을 제거하며 침전지가 내장된 순환수로형 하폐수처리시스템의 평면도이다. 본 실시예에서는 도2의 실시예에서 침전지(7)를 산화구(1)의 내부에 설치하여 침전지내장형산화구로 구성한 것으로 외장형 침전지를 사용하는 다른 실시예에서보다 경제적인 시설을 제공할수 있다.Figure 4 is a plan view of the circulating channel type sewage treatment system in which nitrogen and phosphorus are removed and a sedimentation basin is built according to the present invention. In this embodiment, in the embodiment of FIG. 2, the sedimentation basin 7 is installed inside the oxidation sphere 1, and the sedimentation basin built-in oxidization sphere is configured to provide a more economical facility than in the other embodiments using the external sedimentation basin.
상술한 바와 같이 본 발명의 순환수로형 고도하폐수처리시스템은, 별도의 내부순환펌프 및 관로시설을 생략하고서도 전탈질방법에 의한 질소제거가 가능하게 되므로 시설비와 동력비에서 경제적이며, 이미 건설이 완료되어 가동중인 산화구에 의한 하폐수처리시설에도 용이하게 적용하여 질소와 인을 높은 효율로 제거할수 있는 한편, 산화구에 의한 유로변경 및 간헐포기방식의 하폐수처리시스템과 침전지내장형산화구에도 광범위하게 적용하여 경제적이고 효율적으로 질소, 인 제거효율을 향상시킬수 있게 된다.As described above, the circulating waterway type advanced sewage treatment system of the present invention is economical in facility cost and power cost because nitrogen can be removed by total denitrification without omitting a separate internal circulation pump and pipeline facility. It can be easily applied to wastewater treatment facilities by oxidizing spheres to remove nitrogen and phosphorus with high efficiency, while it is widely applied to the wastewater treatment system of oxidized spheres and intermittent aeration wastewater treatment system and sedimentation built-in oxidizing spheres. As a result, nitrogen and phosphorus removal efficiency can be improved.
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CN101628775B (en) * | 2009-08-09 | 2011-07-27 | 江苏鼎泽环境工程有限公司 | Improved Carrousel oxidation ditch |
WO2021093214A1 (en) * | 2019-11-17 | 2021-05-20 | 凌志环保股份有限公司 | Oxidation ditch and moving bed biofilm reactor integrated sewage treatment equipment |
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US4548712A (en) * | 1977-11-04 | 1985-10-22 | Reid John H | Conservation of momentum in a barrier oxidation ditch |
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US4818391A (en) * | 1983-09-28 | 1989-04-04 | Love Leonard S | Integral Clarifier |
JPS60132700A (en) * | 1983-12-21 | 1985-07-15 | Sumitomo Jukikai Envirotec Kk | Biological denitrification treatment of sewage in recirculation water channel type aeration tank |
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CN101628775B (en) * | 2009-08-09 | 2011-07-27 | 江苏鼎泽环境工程有限公司 | Improved Carrousel oxidation ditch |
WO2021093214A1 (en) * | 2019-11-17 | 2021-05-20 | 凌志环保股份有限公司 | Oxidation ditch and moving bed biofilm reactor integrated sewage treatment equipment |
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