KR100989213B1 - Advanced treatment flotation method by dissolved nano air bubble water that do not need reaction, coagulation, neutralization tank (naf method) - Google Patents

Advanced treatment flotation method by dissolved nano air bubble water that do not need reaction, coagulation, neutralization tank (naf method) Download PDF

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KR100989213B1
KR100989213B1 KR1020100051131A KR20100051131A KR100989213B1 KR 100989213 B1 KR100989213 B1 KR 100989213B1 KR 1020100051131 A KR1020100051131 A KR 1020100051131A KR 20100051131 A KR20100051131 A KR 20100051131A KR 100989213 B1 KR100989213 B1 KR 100989213B1
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water
tank
flotation
nano
inlet
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한영교
한정석
한지연
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한영교
한지연
한정석
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/24Treatment of water, waste water, or sewage by flotation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D21/00Separation of suspended solid particles from liquids by sedimentation
    • B01D21/02Settling tanks with single outlets for the separated liquid
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/002Construction details of the apparatus
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/005Processes using a programmable logic controller [PLC]

Abstract

PURPOSE: An advanced treatment flotation method by dissolved a nano air bubble water that do not need reaction, coagulation, neutralization tank(NAF method) is provided to easily remove biologically recalcitrant substance, total nitrogen, total phosphorus. CONSTITUTION: A pressure pump(20) circulates processed water of a floating tank. A chemical injection pump discharges chemical from a chemical tank(52). A nano air bubble generator(100) expands and compress circulating water of an injector and supplies nano bubble to the inflowing water inlet of a division tank. A controller automatically control circulating water quantity, injected chemical quantity, and the level of the division tank and sludge rate.

Description

반응/응집/중화조가 필요없는 미세 기포에 의한 고도처리 부상분리장치 및 방법{Advanced treatment flotation method by dissolved nano air bubble water that do not need reaction, coagulation, neutralization tank (NAF method)}Advanced treatment flotation method by dissolved nano air bubble water that do not need reaction, coagulation, neutralization tank (NAF method)}

본 발명은 하/폐수 처리장에서 발생되는 하/폐수 중 고도처리(T-N, T-P제거) 및 슬러지 농축설비를 겸하여 저렴한 시설비와 간편한 처리장치 및 공정을 제공하는 부상분리장치 및 방법에 관한 것이다. The present invention relates to a flotation separation apparatus and method for providing a low cost of facilities and a simple treatment device and process by combining advanced treatment (T-N, T-P removal) and sludge thickening equipment in sewage / wastewater generated in the sewage / wastewater treatment plant.

하/폐수 고도 처리(T-N, T-P제거)의 방법으로는 생물학적 처리방법과 응집침전법, 부상분리방법 등이 있다. Advanced sewage / wastewater treatment (T-N, T-P removal) includes biological treatment, flocculation and sedimentation.

이 중, 생물학적 처리방법으로 AO, A2O, VIP, UCT, Bardenpho, SBR, NBR, Five Stage 등이 개발되어 이용되고 있으나, 생물학적 처리로는 그 한계(T-N : 20mg/ℓ, T-P : 1mg/ℓ 이하는 불가능)가 있으며, 처리수 중에 핀플록(Pin Floc) 상태의 미생물덩어리에 미생물의 핵의 구성요소인 인(P)이 내포되어 있으며, 용해성 인(P)도 잔존하므로, 이를 제거하기 위해서는 화학적 처리가 필수불가결하다. 이와 같이 생물학적 처리 방법은 하/폐수를 처리하여 재이용하는데 후속공정으로 여과시설, 흡착시설 등 여러 공정이 필요하므로 시설을 위하여 넓은 처리 장소가 요구되고 처리시간이 긴 문제점이 있었다.Among them, AO, A 2 O, VIP, UCT, Bardenpho, SBR, NBR, Five Stage, etc. have been developed and used as biological treatment methods, but the limits of biological treatment (TN: 20mg / ℓ, TP: 1mg / less than or equal to ℓ), and the lumps of microorganisms in the Pin Floc state contain phosphorus (P), which is a component of the nucleus of the microorganisms, and soluble phosphorus (P) remains. Chemical treatment is indispensable for this. As such, biological treatment methods require sewage / wastewater to be reused by various processes such as filtration facilities and adsorption facilities, and thus require a wide treatment site and a long treatment time.

그리고, 응집침전법에서는 반응조, 응집조, 응집침전조, 오니 농축조 등 여러 부대설비가 필요하고, 형성된 플록을 침전분리시키는데 체류 처리시간도 3시간 이상이 소요된다.In the flocculation sedimentation method, various auxiliary facilities such as a reaction tank, a flocculation tank, a flocculation sedimentation tank, a sludge concentration tank, etc. are required, and the residence treatment time also takes 3 hours or more to precipitate and separate the formed floc.

또한 하/폐수에 포함된 고형물을 부상시켜 제거하는 부상분리방법의 예로는 대한민국 공개특허 2000-37345호와 등록실용신안 20-0252229호 등이 공지되어 있으나, 이러한 종래의 부상분리방법은 유입수가 반응조, 응집조, 중화조 등을 거치면서 큰 플록으로 형성되므로 역시 설치를 위한 대량의 공간이 요구되고, 응집조에 투입된 약품에 의하여 플록을 형성하는데 약품이 고형질 내부로 침투하는데 시간이 오래걸려서 약품 사용량이 많아지게 되며, 유입수가 최종 부상분리조를 통과하는 데 있어서 최소 한 시간 이상이 필요하므로 처리시간이 오래 걸린다.In addition, examples of the flotation separation method for lifting and removing solids contained in the sewage / wastewater are known from Republic of Korea Patent Application Publication No. 2000-37345 and Utility Model No. 20-0252229. As it is formed into a large floc through the flocculation tank and the neutralization tank, a large amount of space is also required for installation, and it takes a long time for the chemical to penetrate into the solid to form the floc by the chemicals injected into the flocculation tank. In this case, the inflow water takes a long time because at least one hour is required to pass through the final flotation tank.

또한, 일반적인 부상분리방법에서 부상분리조로 기포를 공급하기 위해서 요구되는 가압수탱크(3분 정도 체류시간)는 3kg/㎠ 이상이면 2종 압력용기로 정기적인 검사를 반드시 받아야 하므로 유지 관리에도 번거로움이 있었다. In addition, if the pressurized water tank (3 minutes residence time) required to supply bubbles to the flotation tank in the normal flotation separation method is more than 3kg / ㎠, regular inspection is required with two kinds of pressure vessels, which is cumbersome for maintenance. There was this.

더욱이, 일반 가압부상법은 반응, 응집조에서 형성된 큰 플록 표면에 공기방울을 부착시켜 공기방울의 부력에 의하여 부상시키므로 플록이 커야되며, 가압수를 원수대비 30% 이상 필요하고 가압수 생성시간이 3분이 소요되면 부상분리시간이 30분 이상 소요되므로 총 소요시간이 1시간 이상으로 긴 문제점이 있었다.Moreover, in the case of general pressure flotation method, the flocs are attached to the surface of the large flocs formed in the reaction and flocculation tanks, so that the flocs must be floated. Therefore, the flocs must be large. If it takes 3 minutes, the separation time is 30 minutes or more, so the total travel time was longer than 1 hour.

본 발명은 상기와 같은 문제점을 해결하기 위해 발명한 것으로서 나노사이즈의 미세기포(Nano Air Bubble 수, 직경 50㎚ 이하)를 이용하여 유입수의 Pin-Floc 및 Colloid 상태까지 부상분리시키는 것으로 큰 Floc이 요구되지 않으므로 약품 종류와 량이 감소되도록 하면서 처리시간을 단축하고, 종래의 반응조, 중화조, 응집조 등이 요구되지 않도록 하는 부상분리장치 및 방법을 제공하는 데 목적이 있다.The present invention has been invented to solve the above problems, by using a nano-sized micro-bubbles (Nano Air Bubble number, diameter 50nm or less) to separate the inlet water to the Pin-Floc and Colloid state of a large floc is required Therefore, it is an object of the present invention to provide a flotation separation apparatus and method for shortening the treatment time while reducing the type and amount of chemicals and preventing the conventional reaction tank, the neutralization tank, the flocculation tank, and the like.

상기한 목적을 달성하기 위한 본 발명의 특징은, 유입수 투입구로 유입된 유입수에서 형성된 플록을 부상시켜 스키머로 제거하여 고도처리를 하고 처리수를 배출구로 배출하는 부상분리장치에 있어서, 상기한 부상분리조의 배출구측 저부와 관로로 연결되어 부상분리조의 처리수를 순환수로 순환시키는 가압펌프; 에어 컴프레셔; 유입수의 성분에 따라 유입수 처리에 필요한 약품을 약품탱크로부터 배출하는 약품 주입 펌프; 내경이 입구로부터 좁아졌다가 출구측으로 다시 넓어지게 형성된 중공부의 입구측에 상기한 가압펌프가 연결되고 내경이 좁아지는부분의 말단에 에어 컴프레셔 및 약품 주입 펌프와 관로를 통해서 연결된 약품투입구와 공기 투입구가 천공된 인젝터(Injector); 상기한 약품과 공기가 투입되어 인젝터로부터 배출되는 순환수를 팽창과 압축을 다수회 반복시켜 나노 기포수를 제조하여 부상분리조의 유입수 투입구측으로 공급하는 나노 기포수 발생장치; 상기 부상분리장치를 구성하는 각 부분들의 동작을 PLC 프로그래밍을 통하여 자동 제어하여 유입수량에 따라 순환수량 및 주입약품량과 처리수위 조절장치에 의한 부상분리조의 수위와 슬러지 함수율이 자동 제어되도록 하는 제어부(MCC); 를 포함하여 구성되어 종래의 반응조, 응집조, 중화조가 필요하지 않고 한 개의 조에서 유입수의 고도처리가 완료되도록 하는 부상 분리 장치에 있다.Features of the present invention for achieving the above object, in the flotation separation device for floating the floc formed in the inflow water introduced into the inflow water inlet to remove the skimmer by the advanced treatment and discharge the treated water to the outlet, the above-mentioned flotation separation A pressurized pump connected to the outlet side bottom of the tank by a pipe to circulate the treated water of the floating separation tank to the circulation water; Air compressors; A chemical infusion pump for discharging a chemical required for the influent treatment from the chemical tank according to a component of the influent; The pressurization pump is connected to the inlet side of the hollow portion which has an inner diameter narrowed from the inlet and widened to the outlet side, and a chemical inlet and an air inlet connected to the end of the portion where the inner diameter is narrowed through an air compressor, a chemical injection pump and a pipe line. Perforated injectors; Nano-bubble water generator for producing the nano-bubble water by repeating the expansion and compression of the circulating water discharged from the injector by the medicine and air is supplied to the inlet water inlet side of the flotation tank; Control unit to automatically control the operation of each part constituting the flotation separator through PLC programming to automatically control the water level and sludge water content of the flotation tank by the circulating water, the amount of injected chemicals and the treatment level according to the inflow water ( MCC); It is configured to include a conventional separation vessel, the flocculation tank, the neutralization tank is not necessary, and the floating separation device to complete the advanced treatment of the influent in one tank.

상기에서 부상분리조는 유입수 투입구 측 전방 하부에 부상분리조 내부의 적정 수면보다 낮은 격벽이 하나 이상 형성되고, 처리수 배출구측에는 스컴저장조를 그 외주면이 부상분리조 내주면과 이격되도록 설치하며, 상기한 스컴저장조의 설치로 인하여 처리수 배출구와 스컴저장조 사이에는 처리수만 보관되도록 처리수조가 자동으로 형성된다.In the above-mentioned floatation separation tank, at least one partition wall lower than the appropriate water level inside the floating separation tank is formed at the front lower portion of the inflow water inlet, and the scum reservoir is installed at the treated water outlet side so that its outer peripheral surface is spaced apart from the inner peripheral surface of the floating separation tank. Due to the installation of the reservoir, the treatment tank is automatically formed so that only the treatment water is stored between the treatment water outlet and the scum storage tank.

또한 상기한 나노 기포 발생장치는 U자형으로 형성되고 중심부가 인젝터의 출구와 연결되며 인젝터의 출구보다 넓은 내경을 갖고 인젝터와 연결된 일측에 순환수 흐름을 한방향으로만 제한하기 위한 제 1차단판이 형성된 제 1 팽창관과, 상기한 제 1팽창관의 양측을 서로 연결하며 제 1팽창관보다 내경이 작아서 순환수를 가압(수축)하는 다수개의 가압관과, 제1팽창관 내부에 설치되어 상기한 다수개의 가압관과 제 1팽창관을 순환수가 지그재그로 통과하도록 유로를 형성 및 차단하는 다수개의 차단판과, 상기한 제 1팽창관의 순환수 출구와 연결되며 제 1팽창관의 내경보다 큰 내경을 갖는 제 2팽창관 및, 상기한 제 2팽창관의 순환수 출구와 부상분리조를 연결하며 제 2팽창관보다 내경이 작은 관로를 포함하여 구성된다.
In addition, the nano-bubble generating device is formed of a U-shaped, the center is connected to the outlet of the injector, has a wider inner diameter than the outlet of the injector and the first blocking plate is formed on one side connected to the injector to limit the flow of circulating water in one direction only A plurality of pressurized tubes connecting the both sides of the first expansion tube to the first expansion tube and having a smaller inner diameter than the first expansion tube to pressurize (shrink) the circulating water; A plurality of blocking plates for forming and blocking a flow path for circulating water to pass through the two pressure pipes and the first expansion pipe in a zigzag manner, and an inner diameter that is connected to the circulation water outlet of the first expansion pipe and is larger than the internal diameter of the first expansion pipe. And a second expansion tube having a pipe, and a pipe line connecting the circulating water outlet of the second expansion tube to the floating separation tank and having an inner diameter smaller than that of the second expansion tube.

그리고, 본 발명의 다른 특징은 유입수로부터 형성된 플록을 부상시켜 스키머로 제거하여 고도처리를 하는 부상분리방법에 있어서, 부상분리조의 유입수 투입구측에 유입수에 따른 약품과 부상분리조의 처리수 및 공기가 포함된 순환수를 배출하면 순환수가 고압에서 부상분리조내부의 상압상태로 투입되면서 급속하게 확산되어 나노기포를 포함하는 나노 기포수가 되고, 상기한 나노 기포수에 의하여 유입수의 핀플록 및 콜로이드 상태까지 상부로 부상시켜, 상부로 부상된 플록은 스키머로 제거하도록 하며 처리수는 처리수 배출구로 배출하는 것이다.In addition, another feature of the present invention is a flotation separation method in which the floc formed from the inflow water is floated and removed with a skimmer for advanced treatment, wherein the chemical and flotation treatment water and air according to the inflow water are included in the inflow water inlet side of the flotation tank. When the discharged circulating water is discharged, the circulating water is rapidly introduced at high pressure inside the floating separation tank at high pressure, and rapidly diffuses into nano bubble water including nano bubbles, and the upper portion reaches the pin floc and colloidal state of the influent by the nano bubble water. The floc floated to the top is removed with a skimmer and the treated water is discharged to the treated water outlet.

상기에서 나노 기포수는 부상분리조에서 처리된 처리수를 순환수로 하여 가압펌프로 1차 가압하고, 1차가압된 순환수를 인젝터로 유입하되 인젝터 유입시 필요약품과 공기를 주입하여 다시 가압한 후, 관로의 대/소로 가압과 팽창을 다수회 반복시켜 공기 및 약품을 순환수에 최대한 용해시켜 부상분리조로 분출하면 고압에서 대기압상태로 되면서 부피가 팽창되어 나노 기포(Nano Air Bubble)수가 된다.
In the above, the nano-bubble water is pressurized by a pressurized pump with the treated water treated in the flotation tank as the circulating water, and the pressurized circulating water is introduced into the injector, and the necessary chemicals and air are injected when the injector is introduced again. After the pressurization and expansion of the pipe line are repeated many times, the air and chemicals are dissolved in the circulating water as much as possible and ejected into the flotation tank, whereby the volume is expanded to atmospheric pressure at high pressure to become nano air bubble water. .

이러한 장치 및 방법에 의하여 나노 기포수를 유입수와 혼합하면, 나노 기포수에 용해된 약품이 빠르게 부상분리조 내부에 확산되면서 반응/응집이 일어나 핀플록(Pin-Floc)이 형성되면서 부상분리조의 유속에 의하여 유수의 흐름 방향으로 흐르면서 T-N, T-P를 포함한 난분해성 물질과 반응하여 스컴(Scum)을 형성하므로 상부의 스키머로 제거하여 처리하게 된다.When the nanobubble water is mixed with the influent by this apparatus and method, the chemical dissolved in the nanobubble water rapidly diffuses into the flotation tank, causing reaction / agglomeration to form Pin-Floc, thereby forming the flow rate of the flotation tank. By reacting with the non-degradable material including TN, TP while flowing in the flow direction of the flow of water to form a scum (Scum) is removed by the upper skimmer to process.

이때, 상기한 나노 기포수가 고압(3~20kg/㎠)으로 분출되면서 물은 플로톤(H+)과 수산기(OH-)로 형성되어 수산기(OH-)가 핀플록의 내부에까지 침투하여 단백질 등을 파괴하여 탄산가스(CO2)로 방출시키므로 슬러지 발생량을 줄일 수 있고, 소량의 나노 기포수로도 부상분리시킬 수 있다. At this time, the number of the above-described nano-bubbles as ejected at a high pressure (3 ~ 20kg / ㎠) Water Flow ton (H +) and hydroxyl (OH -) are formed by hydroxyl (OH -) is to penetrate far inside the pin floc protein, etc. Destroys and releases carbon dioxide (CO 2 ) to reduce the amount of sludge generated, and can be separated by a small amount of nano-bubble water.

이는 기존의 가압부상법이 큰 플록 표면에 공기방울을 부착시켜 부상시키는 방법과는 이론적, 원리적으로 완전히 다른 방법이다. This method is theoretically and theoretically different from the existing method of floating flotation by floating air bubbles on a large floc surface.

또한 나노 기포수는 고압(3~20kg/㎠)에서 대기압으로 분출되므로 보일-샬의 법칙에 의하여 부피는 수십 배로 팽창되어 소량의 순환수(유입수 대비 : 5~20%)로도 핀플록 및 콜로이드 입자를 부상분리 시킨다. 더욱이 기포사이즈가 나노 사이즈이므로 부상시간이 종래의 큰 기포에 비하여 오래 걸리게 되므로 물의 가수분해가 잘 이루어지게 되고 유입수의 처리효율이 향상된다.In addition, since nano bubble water is ejected at high pressure (3 ~ 20kg / ㎠) to atmospheric pressure, the volume is expanded tens of times according to Boyle-Shal's law, so that pin floc and colloidal particles can be produced even with a small amount of circulating water (5 ~ 20% of influent). Separate the float. Moreover, since the bubble size is nano size, the floating time takes longer than that of the conventional large bubble, so that the hydrolysis of the water is performed well and the treatment efficiency of the influent is improved.

상기에서 핀플록(Pin-Floc)은 정체시켜도 가라앉거나 뜨지 않는 입자의 플록을 말하고, 콜로이드(Colloid)는 입자의 표면에 양전하(+)와 음전하(-)가 평형되어 안정한 상태로 있는 입자를 말한다.Pin-Floc is a floc of particles that do not sink or float even when stagnant. Colloid refers to particles in which the positive and negative charges are balanced on the surface of the particles and are in a stable state. Say.

이상과 같이 구성된 본 발명에 의하면 하/폐수 중의 난분해성 물질을 처리할 수 있으며, 총질소(T-N)는 30% 이상 제거되며, 총인(T-P)은 99%, BOD, CODMn가 50% 이상 제거되므로 지금까지 각종 하/폐수처리장에서 처리하는데 상당한 어려움이 있었던 난분해성 물질, 총질소(T-N), 총인(T-P)을 용이하게 처리할 수 있어 수질오염 예방 및 수질 환경개선에도 크게 도움을 줄 수 있다.According to the present invention configured as described above can treat the hardly decomposable substances in sewage / waste water, total nitrogen (TN) is removed more than 30%, total phosphorus (TP) 99%, BOD, COD Mn is removed more than 50% Therefore, it is possible to easily handle hardly decomposable substances, total nitrogen (TN) and total phosphorus (TP), which have been difficult to treat in various sewage / wastewater treatment plants so far, which can greatly help in preventing water pollution and improving the water environment. .

더욱이 유입수를 응집 등의 처리를 하지 않고 바로 부상분리조로 투입하고, 부상분리조 내부에서 체류시간이 5~20분 이내이므로, 응집조, 중화조, 반응조등이 필요하지 않고 부상분리조의 크기 또한 감소되므로 시설비, 운전비가 대폭 절감되는 효과가 있다.Moreover, the inflow water is directly put into the flotation tank without treatment such as flocculation, and the residence time within the flotation separation tank is within 5-20 minutes, so that no flocculation tank, neutralizing tank, reaction tank is required, and the size of the flotation tank is also reduced. As a result, facility costs and operating costs are greatly reduced.

또한, 기존 가압부상법은 부상조에 정체(30분 이상)시켜 큰 플록(Floc) 표면에 공기방울을 부착시켜 부상시키므로 큰 플록을 생성하는 시간과 가압부상 분리시간이 장시간(1.5시간 이상)이 요구되나, 본 발명은 부상분리조를 유속이 느린(유속 : 0.1 ~ 0.001m/sec) 관로 역할을 하게 하여 상부의 부상된 스컴(Scum)을 유수의 흐름 방향으로 모이게 하므로, 유입수 투입구로부터 흘러오면서 모여진 스컴만을 스키머가 제거하면 되므로 스키머(Skimmer)의 크기를 작게 할 수 있어서 시설비를 감소시키는 효과가 있다. In addition, the existing pressure flotation method causes stagnation (more than 30 minutes) in the floating tank and attaches air bubbles to the surface of the large floc, causing the flotation to take place, requiring a long time (more than 1.5 hours) to generate a large floe. However, the present invention serves to serve as a low-flow (flow rate: 0.1 ~ 0.001m / sec) pipe to the flotation tank to collect the injured scum in the upper flow direction, gathered while flowing from the inlet inlet Since only the scum needs to be removed by the skimmer, the size of the skimmer can be reduced, thereby reducing the facility cost.

도 1은 본 발명에 따른 부상분리장치를 나타내는 도면
도 2는 본 발명의 인젝터 및 나노 기포 발생 장치를 나타내는 도면
1 is a view showing a flotation separator according to the present invention;
2 is a view showing the injector and nano-bubble generating device of the present invention

이하 본 발명의 실시예를 첨부한 도 1 및 도 2를 참조하여 살펴본다.Hereinafter, an embodiment of the present invention will be described with reference to FIGS. 1 and 2.

본 발명에 따른 부상분리장치는 크게, 부상분리조(10), 가압펌프(20), 에어 컴프레셔(60), 약품 주입 펌프(50), 인젝터(110), 나노기포발생장치(100)를 포함하여 구성된다.Floating separation apparatus according to the present invention includes a floating separation tank 10, a pressure pump 20, an air compressor 60, a chemical injection pump 50, an injector 110, a nano bubble generator 100. It is configured by.

상기에서 부상분리조(10)는 유입수가 유량계에 의하여 일정량만큼 유입되는 유입수 투입구(12), 상기한 유입수 투입구(12) 반대측에 형성되어 처리가 완료된 처리수가 자동수량조절장치에 의하여 배출되는 배출구(14), 상기한 유입수 투입구(12)측 저부에 수직으로 돌출형성되며 부상분리조(10) 내부의 적정 수면보다 상종단이 낮게 배치되는 복수개의 격벽(16), 상기한 처리수 배출구(14) 측에 인접하게 설치되며 부상분리조 내주면과 그 외주면이 이격되게 설치되는 스컴저장조(30) 및 상기한 스컴저장조(30) 전방 상부에 설치되어 스컴을 부상분리조(10)에서 스컴저장조(30)로 이동시키는 스키머(40)를 포함하여 구성된다.In the above-mentioned floatation separation tank 10 is an inlet water inlet 12 through which the inlet water is introduced by a certain amount by the flow meter, the outlet formed in the opposite side of the inlet water inlet 12, the discharged water is discharged by the automatic water quantity adjusting device ( 14), the plurality of partitions 16 are formed to protrude perpendicularly to the bottom of the inlet 12, the upper end is lower than the proper surface of the water separation tank 10, the treatment water outlet 14 The scum storage tank 30 is installed adjacent to the side and the outer peripheral surface of the floating separation tank and the outer peripheral surface is installed in the scum storage tank 30 and the upper portion of the scum storage tank 30 in front of the scum storage tank 30 scum storage tank 30 It comprises a skimmer 40 to move to.

그리고, 상기한 가압펌프(20)는 상기한 부상분리조(10)의 처리수 배출구(14)측 저부와 관로로 연결되어 부상분리조(10)의 처리수를 순환수로 순환시킨다.In addition, the pressure pump 20 is connected to the bottom of the treated water outlet 14 side of the floating separation tank 10 by a pipe to circulate the treated water of the floating separation tank 10 to the circulating water.

그리고, 상기한 약품 주입 펌프(50)는 부상분리조(10)로 유입되는 유입수의 성분에 따라 유입수 처리에 필요한 약품이 저장된 약품 저장탱크(52)로부터 일정량씩 해당 약품을 배출한다.In addition, the chemical injection pump 50 discharges the chemicals by a predetermined amount from the chemical storage tank 52 in which the chemicals necessary for the inflow water treatment are stored according to the components of the inflow water introduced into the flotation separation tank 10.

상기한 가압펌프(20)와 에어 컴프레셔(60) 및 약품 주입 펌프(50)와 연결된 인젝터(110)는, 내경이 입구로부터 좁아졌다가 출구측으로 다시 넓어지게 형성된 중공부(112)의 입구측이 상기한 가압펌프(20)와 연결되고 에어 컴프레셔(60) 및 약품 주입 펌프(50)와 관로를 통해서 연결된 약품투입구(114)와 공기 투입구(116)가 내경이 좁아지는 부분의 말단에 천공된다.The injector 110 connected to the pressure pump 20, the air compressor 60, and the chemical injection pump 50 has an inlet side of the hollow part 112 formed to have an inner diameter narrowed from an inlet and widened to an outlet side again. The chemical inlet 114 and the air inlet 116 connected to the pressure pump 20 and connected to the air compressor 60 and the chemical infusion pump 50 are drilled at the end of the portion where the inner diameter is narrowed.

그리고, 나노기포발생장치(100)는 상기한 약품과 공기가 투입되어 인젝터(110)로부터 배출되는 순환수를 팽창과 압축을 다수회 반복시켜 부상분리조(10)의 유입수 투입구(12) 및 유입수 투입구(12) 측 저부로 나노사이즈 기포 형태로 투입하는 역할을 하는 것으로, 그 구성은 하기와 같다.In addition, the nano-bubble generating device 100 is introduced into the inlet 12 and the inlet of the floating separation tank 10 by repeating the expansion and compression of the circulating water discharged from the injector 110 by the above-mentioned chemicals and air is injected many times. It serves to inject in the form of nano-sized bubbles to the bottom of the inlet 12 side, the configuration is as follows.

상기한 나노기포발생장치(100)는 U형으로 형성되어 중심부(122)가 인젝터(110)의 출구와 연결되며 양측부(124)의 일측 종단은 막힌 상태이고 타측 종단은 개방형성되며 그 내경은 인젝터(110)의 출구보다 넓게 형성되고 인젝터(110)와 연결된 중심부 일측에 순환수 흐름을 제한하기 위한 제 1차단판(126)이 형성된 제 1 팽창관과, 상기한 제 1팽창관(120)의 양측부(124)를 서로 연결하며 제 1팽창관(120)보다 내경이 작아서 순환수를 가압(수축)하는 다수개의 가압관(130)과, 상기한 다수개의 가압관(130)과 제 1팽창관(120)을 순환수가 지그재그로 통과하여 출구로 배출도록 제 1팽창관(120) 내부에 설치되는 다수개의 다른 차단판(140)과, 상기한 제 1팽창관(120)의 순환수 출구와 연결되며 제 1팽창관(120)의 내경보다 큰 내경을 갖는 제 2팽창관(150) 및, 상기한 제 2팽창관(150)의 순환수 출구와 부상분리조(10)를 연결하며 제 2팽창관(150)보다 내경이 작은 관로(160)를 포함하여 구성된다.The nano-bubble generating device 100 is formed in a U-shape, the center 122 is connected to the outlet of the injector 110, one end of both sides 124 is blocked and the other end is open and the inner diameter is A first expansion tube formed wider than an outlet of the injector 110 and having a first blocking plate 126 formed on one side of a center connected to the injector 110 to restrict the flow of circulating water, and the first expansion tube 120 described above; A plurality of pressurizing pipes 130 connecting the two side portions 124 to each other and having a smaller inner diameter than the first expansion pipe 120 to pressurize (contract) the circulating water, and the plurality of pressurizing pipes 130 and the first A plurality of other blocking plates 140 installed inside the first expansion pipe 120 to discharge the expansion pipe 120 zigzag and discharge to the outlet, and the water outlet of the first expansion pipe 120 described above. And a second expansion tube 150 having an inner diameter greater than that of the first expansion tube 120 and the second expansion tube 150. Connecting the outlet and the water exchange floatation tank 10 and is configured to include a second expanded inner diameter of the tube is smaller than 150, the channel 160.

상기에서 제 1팽창관(120)의 막힌 종단은 형태 안정 및 차지하는 공간 축소를 위하여 제 2팽창관에 일체로 설치될 수도 있다.The closed end of the first expansion tube 120 may be integrally installed in the second expansion tube for shape stability and space reduction.

또한, 도면 중 PG와 G1,G2,G3 압력계를 나타내고, F1,F2,F3는 유량계를 나타내며, V1, V2,V3,V4는 밸브를 나타낸다.
In the figure, PG, G1, G2, and G3 pressure gauges are shown, F1, F2, and F3 indicate flow meters, and V1, V2, V3, and V4 indicate valves.

그리고, 상기한 부상 분리 장치를 이용하고 하/폐수 고도처리를 위한 부상분리 방법을 하기에서 살펴본다.And, using the above-mentioned flotation separation device and looks at the flotation separation method for advanced sewage / wastewater treatment.

본 발명에 따른 부상 분리 방법은, 부상분리조의 유입수 투입구와 유입수 투입구측 저부에 유입수에 따른 약품과 부상분리조의 처리수가 순환된 순환수를 포함하는 나노기포를 배출하여 나노기포가 이젝터를 통하여 순간적으로 고압(3~20kg/㎠)에서 부상분리조내부로 대기압(1kg/㎠)상태로 투입되면서 나노 기포수가 된다.The floating separation method according to the present invention discharges nanobubbles including circulating water circulated with the chemicals according to the inflow water and the treated water of the floating separation tank at the inflow inlet and the bottom of the inflow inlet of the floating separation tank, and the nanobubbles are instantaneously discharged through the ejector. At high pressure (3 ~ 20kg / ㎠) is introduced into the floating separation tank at atmospheric pressure (1kg / ㎠) state becomes nano bubble water.

그리고, 이러한 나노 기포수는 순간적으로 확산되면서 플로톤(H+)과 수산기(OH-)로 되어 콜로이드의 양전하는 수산기(OH-)와 결합하고 음전하(-)는 플로톤(H+)과 결합하여 핀플록이 형성되고, 핀플록 자체에 나노 기포가 내포되어 있어 부상분리된다.And, this nano number of bubbles while being instantaneously diffused into flows tone (H +) and hydroxyl (OH -) is in a colloid positively charged is a hydroxy group (OH -) - combined with the flow-tone (H +) and coupled to the negative charge () As a result, a pin floc is formed, and nano-bubbles are contained in the pin floc itself, and the flotation is separated.

또한, 생물학적으로 처리불가능한 난분해성물질은 나노 기포수의 플로톤(H+)과 수산기(OH-)가 파괴시켜 안정하게 처리하는 작용을 한다.In addition, the biologically unprocessable hardly decomposable substance acts to stably process by destroying the Floton (H + ) and the hydroxyl group (OH ) of the nano-bubble water.

이와 같이 나노 기포수가 유입수의 핀플록 및 콜로이드까지 상부로 부상시키게 되고, 상부로 부상된 플록은 스키머에 의하여 제거된다.In this way, the nanobubble water is floated upward to the pin floc and the colloid of the influent, and the floc floated upward is removed by the skimmer.

한편, 상기에서 약품은 소석회, 철염, 알미늄염 등이 유입수의 종류에 따라 선택적으로 사용된다.On the other hand, in the above chemicals, hydrated lime, iron salt, aluminum salt, etc. are selectively used according to the type of influent.

그리고, 상기한 나노 기포수는 부상분리조에서 처리된 처리수를 순환수로 하여 가압펌프로 1차 가압하고, 1차가압된 공기를 인젝터로 유입하되 인젝터 유입시 필요약품과 공기를 주입하여 다시 가압한 후, 관로의 대/소로 가압과 팽창을 다수회 반복시켜 공기 및 약품을 순환수에 최대한 용해시켜 부상분리조로 분출하면 고압에서 대기압상태로 되면서 부피가 팽창되어 나노 기포(Nano Air Bubble)수가 된다. In addition, the nano-bubble water is first pressurized with a pressurized pump using the treated water treated in the floating separation tank as a circulating water, and the first pressurized air is introduced into the injector, and the necessary chemicals and air are injected again when the injector is introduced. After pressurization, pressurization and expansion of the pipe line are repeated many times, dissolving the air and chemicals in the circulating water as much as possible, and ejecting them to the floating separation tank. do.

이때, 상기한 순환수(Q1) 및 약품(C1,C2)의 주입량은 유량계(F1)에 의하여 감지된 유입수(Q)의 수량에 맞게 조정되는데, 상기한 순환수(Q1)는 유량계(F2) 및 밸브(V1)를 통해서 약품(C1, C2)은 유량계(F3) 및 약품 주입 펌프(50)를 통해서 자동으로 조정되어 인젝터(110)로 투입한다. 그리고, 인젝터(110)로 주입되는 공기의 압력은 부상분리조(10)로 주입되는 나노기포와 약품이 포함된 순환수의 압력(G3)이 일정하게 유지되도록 에어 컴프레셔에 의하여 조정된다.At this time, the injection amount of the circulating water (Q1) and the chemicals (C1, C2) is adjusted according to the quantity of inflow water (Q) detected by the flow meter (F1), the circulating water (Q1) is a flow meter (F2) And through the valve (V1) chemicals (C1, C2) is automatically adjusted through the flow meter (F3) and the chemical injection pump 50 is injected into the injector 110. Then, the pressure of the air injected into the injector 110 is adjusted by the air compressor so that the pressure (G3) of the circulating water containing the nano-bubble and the drug injected into the flotation separation tank 10 is kept constant.

또한, 나노 기포수량은 유입수(Q)에 따라 순환수량(Q1)이 결정되어 일정비율로 자동밸브(V2, V3, V4)로 분배되며, 나노 기포수는 가압펌프(P1, P2)가 교대운전되면서 부상분리조 내부로 투입된다.In addition, the amount of nano bubble water is circulated water (Q1) is determined according to the inlet water (Q) is distributed to the automatic valves (V2, V3, V4) at a constant ratio, the nano bubble water in the pressure pump (P1, P2) alternate operation It is then introduced into the floatation tank.

그리고, 부상분리조(10)에서 처리되어 유출되는 수량은 자동수위 조절장치(V1)로 조절하는데, 이러한 과정을 통하여 부상분리조(10)의 수위조절과 상부에 부상하는 스컴의 두께가 조절된다. In addition, the amount of water discharged from the floating separation tank 10 is controlled by an automatic water level adjusting device V1. Through this process, the level of the floating water separation tank 10 and the thickness of the scum floating on the upper part are adjusted. .

그리고, 이러한 일련의 제어 공정은 PLC로 프로그래밍하여 제어부(MCC)에서 자동 제어되도록 하는데, 구체적으로 유입수량에 따라 순환수량 및 주입약품량과 처리수위 조절장치에 의한 부상분리조의 수위와 슬러지 함수율이 PLC프로그래밍을 통하여 제어부(MCC)에서 자동제어된다.
In addition, such a series of control processes are programmed by the PLC to be automatically controlled by the controller (MCC), specifically, the water level and the sludge water content of the flotation tank by the circulating water, the injected chemical amount, and the treatment level control device according to the inflow water Automatically controlled by the controller MCC through programming.

이러한 본 발명의 부상 분리 방법에 따른 유입수 처리 과정을 구체적으로 하기에서 살펴본다.The influent treatment process according to the flotation separation method of the present invention will be described in detail below.

우선, 부상분리조의 유입수 투입구에 Al+3과 나노 기포수를 주입하면 나노 기포수가 확산(고압 → 1atm)되면서 유입수와 나노 기포수를 교반하게 되고, 이 과정에서 불용성염인 AlPO4 플록을 형성하여 교착화 시킨다. First, when Al +3 and nano bubble water are injected into the inlet inlet of the flotation tank, the nano bubble water is diffused (high pressure → 1atm), and the influent and the nano bubble water are agitated. In this process, AlPO 4 floc, an insoluble salt, is formed. Deadlock.

이렇게 형성된 플록 내/외부에는 나노 기포수에 포함된 직경 50㎚이하의 나노 기포가 부착되어 있으므로 상기한 플록은 나노기포에 의하여 부상 분리된다. The flocs formed as described above are attached to the nano-bubbles having a diameter of 50 nm or less included in the nano-bubble water, and thus the flocs are separated and separated by the nano-bubbles.

이 과정에서 나노 기포수의 수산기(OH-)가 유출수에 포함된 미생물의 세포막을 침투하여 단백질을 산화분해시킴으로 슬러지 발생량을 작게 하며, 콜로이드 상태도 부상분리시킨다. In this process, a hydroxyl group (OH -) of the nano-bubbles can penetrate the cell membrane of the microorganism contained in the effluent and reduce the sludge production sikimeuro oxidative degradation of proteins, thereby also separating portion colloidal state.

부상된 슬러지는 함수율 95% 정도의 농축된 슬러지를 얻을 수 있으므로 별도의 슬러지 농축조가 필요 없으며, 이와 같이 부상된 슬러지에는 불용성염(AlPO4) 상태의 총인이 내포되어 있어 슬러지 처리로서 총인을 99% 제거한다. The flocculated sludge can obtain concentrated sludge with a water content of about 95%, so no separate sludge thickening tank is needed, and the flocculated sludge contains total phosphorus in the insoluble salt (AlPO 4 ) state, and the total phosphorus as sludge treatment is 99%. Remove

따라서, 상기한 본 발명의 나노기포수에 의한 부상분리 방법(NAF공법)은 Nano 기포(50㎚ 이하)를 이용하므로 부상분리시간이 10분이며, 분사 Nozzle 입구에 Alum을 주입하면 Nano Air Bubble수가 확산되면서 약액도 동시에 확산되어 반응되므로 반응조, 응집조가 필요 없고, Nano Air Bubble수 생성시간이 10~60초로 짧고, 부상분리시간도 5~20분으로 단축된다.Therefore, the floating separation method (NAF method) according to the nano-bubble water of the present invention uses a nano bubble (50 nm or less), so the floating separation time is 10 minutes, and when the Alum is injected into the injection nozzle inlet, the nano air bubble water As it is diffused, the chemical solution is also diffused and reacted at the same time, thereby eliminating the need for a reaction tank or agglomeration tank.

또한, 상부 Scum은 물은 아래 부상분리조로 빠져 농축된 슬러지를 얻을 수 있으므로 슬러지 농축조 등이 필요 없고, 슬러지 함수율을 조절할 수 있다.
In addition, the upper cum can be concentrated in the sludge flotation tank to obtain the sludge, so the sludge thickening tank is not required, and the sludge moisture content can be adjusted.

상기한 바와 같이 구성된 부상 분리 장치 및 방법에 의한 실시예를 살펴본다.Look at the embodiment by the flotation separation apparatus and method configured as described above.

Pilot Plant 실험에서 순환수 압력(G3)은 6atm, 순환수량(Q1)은 유입수대비 10%, 약품으로 알루미늄(Alum)을 사용할 때, 부상분리시간 10분, 나노기포수 생성시간은 20초, 스컴 함수율은 95%이며, 알루미늄 사용량에 따른 제거율은 아래와 같다.In the Pilot Plant experiment, the circulation water pressure (G3) was 6 atm, the circulation water volume (Q1) was 10% of the influent water, and when aluminum was used as a chemical, 10 minutes of flotation separation time, 20 seconds of nano bubble water generation, and scum The moisture content is 95%, and the removal rate according to the amount of aluminum used is as follows.

아래 표 1 내지 6에서 단위는 ppm이다.In Tables 1 to 6 below the units are ppm.

- Alum 20ppm 주입시-20 ppm injection of Alum

Figure 112010034935751-pat00001
Figure 112010034935751-pat00001

- Alum 25ppm 주입시-25ml injection of Alum

Figure 112010034935751-pat00002
Figure 112010034935751-pat00002

- Alum 30ppm 주입시-Alum 30ppm injection

Figure 112010034935751-pat00003
Figure 112010034935751-pat00003

- Alum 20ppm 주입시-20 ppm injection of Alum

Figure 112010034935751-pat00004
Figure 112010034935751-pat00004

- Alum 25ppm 주입시-25ml injection of Alum

Figure 112010034935751-pat00005
Figure 112010034935751-pat00005

- Alum 30ppm 주입시-Alum 30ppm injection

Figure 112010034935751-pat00006
Figure 112010034935751-pat00006

상기 실험에서 (예)로 T-P 2.0ppm일 때 Alum 20% 용액 25ppm 주입시 T-P 99%가 제거되므로 최적주입량이다. 이를 Al : P로는 1.9 : 1이다. In the above experiments, when T-P 2.0ppm (for example), the T-P 99% is removed at the time of injecting 25ppm of Alum 20% solution. This is 1.9: 1 with Al: P.

Nano Air Bubble수에 의한 부상분리는 Pin-Floc이 부상분리에 유리하고, 큰 Floc은 본 발명에 저해요인이 되며, 시설비, 운영관리비가 많이 소요될 뿐이다. Floating separation by Nano Air Bubble water, Pin-Floc is advantageous for floating separation, large Floc is a detrimental factor to the present invention, facility cost, operation management costs only a lot.

Polymer 같은 타약품은 사용하지 않는다. Do not use other drugs such as polymer.

본 발명은 상기 실시예에 한정되는 것이 아니고, 특허 청구범위와 발명의 상세한 설명 및 첨부한 도면의 범위 안에서 여러 가지로 변형하여 실시하는 것이 가능하고, 이 또한 본 발명에 속하는 것이다.
The present invention is not limited to the above embodiments, but can be modified and practiced in various ways within the scope of the claims and the detailed description of the invention and the accompanying drawings, which also belong to the invention.

10 : 부상분리조 20 : 가압펌프
30 : 에어 컴프레셔 50 : 약품 주입 펌프
110 : 인젝터 100 : 나노기포 발생장치
10: flotation tank 20: pressure pump
30: air compressor 50: chemical injection pump
110: injector 100: nano bubble generator

Claims (5)

유입수 투입구로 유입된 유입수에서 형성된 플록을 부상시켜 스키머로 제거하여 고도처리를 하고 처리수를 배출구로 배출하는 부상분리장치에 있어서,
상기한 부상분리조의 배출구측 저부와 관로로 연결되어 부상분리조의 처리수를 순환수로 순환시키는 가압펌프;
에어 컴프레셔;
유입수의 성분에 따라 유입수 처리에 필요한 약품을 약품탱크로부터 배출하는 약품 주입 펌프;
내경이 입구로부터 좁아졌다가 출구측으로 다시 넓어지게 형성된 중공부의 입구측에 상기한 가압펌프가 연결되고 내경이 좁아지는부분의 말단에 에어 컴프레셔 및 약품 주입 펌프와 관로를 통해서 연결된 약품투입구와 공기 투입구가 천공된 인젝터(Injector);
상기한 약품과 공기가 투입되어 인젝터로부터 배출되는 순환수를 팽창과 압축을 다수회 반복시켜 나노 기포수를 제조하여 부상분리조의 유입수 투입구측으로 공급하는 나노 기포수 발생장치;
상기 부상분리장치를 구성하는 각 부분들의 동작을 PLC 프로그래밍을 통하여 자동 제어하여 유입수량에 따라 순환수량 및 주입약품량과 처리수위 조절장치에 의한 부상분리조의 수위와 슬러지 함수율이 자동 제어되도록 하는 제어부(MCC); 를 포함하여 구성되는 것을 특징으로 하여,
반응/응집/중화조가 필요없이 한 개의 조에서 유입수의 고도처리가 완료되도록 하는 부상 분리 장치.
In the flotation device for flotation formed from inflow water flowing into the inflow water inlet, it is removed with a skimmer for advanced processing, and the treated water is discharged to the outlet.
A pressurized pump connected to the outlet side bottom of the floating separation tank by a pipe and circulating the treated water of the floating separation tank to circulating water;
Air compressors;
A chemical infusion pump for discharging a chemical required for the influent treatment from the chemical tank according to a component of the influent;
The pressurization pump is connected to the inlet side of the hollow portion which has an inner diameter narrowed from the inlet and widened to the outlet side, and a chemical inlet and an air inlet connected to the end of the portion where the inner diameter is narrowed through an air compressor, a chemical injection pump and a pipe line. Perforated injectors;
Nano-bubble water generator for producing the nano-bubble water by repeating the expansion and compression of the circulating water discharged from the injector by the medicine and air is supplied to the inlet water inlet side of the flotation tank;
Control unit to automatically control the operation of each part constituting the flotation separator through PLC programming to automatically control the water level and sludge water content of the flotation tank by the circulating water, the amount of injected chemicals and the treatment level according to the inflow water ( MCC); Characterized in that comprises a,
Flotation separation device to complete the advanced treatment of influent in one tank without the need for reaction / aggregation / neutralization tanks.
제 1항에 있어서, 상기한 부상분리조는 유입수 투입구 측 전방 하부에 부상분리조 내부의 적정 수면보다 낮은 격벽이 하나 이상 형성되고, 처리수 배출구측에는 스컴저장조를 그 외주면이 부상분리조 내주면과 이격되도록 설치하며, 상기한 스컴저장조의 설치로 인하여 처리수 배출구와 스컴저장조 사이에는 처리수만 보관되도록 처리수조가 자동으로 형성되도록 하는 것을 특징으로 하는 부상 분리 장치.The method of claim 1, wherein the flotation tank is formed at least one partition wall lower than the appropriate surface of the flotation tank in the front lower portion of the inlet inlet, the scum storage tank on the treated water outlet side so that its outer peripheral surface is spaced apart from the inner peripheral surface of the flotation tank And installing the scum storage tank so that the treatment water tank is automatically formed so that only the treated water is stored between the treated water outlet and the scum storage tank. 제 1항에 있어서, 상기한 나노 기포수 발생장치는 U자형으로 형성되고 중심부가 인젝터의 출구와 연결되며 인젝터의 출구보다 넓은 내경을 갖고 인젝터와 연결된 일측에 순환수 흐름을 한방향으로만 제한하기 위한 제 1차단판이 형성된 제 1 팽창관과,
상기한 제 1팽창관의 양측을 서로 연결하며 제 1팽창관보다 내경이 작아서 순환수를 가압(수축)하는 다수개의 가압관과,
제1팽창관 내부에 설치되어 상기한 다수개의 가압관과 제 1팽창관을 순환수가 지그재그로 통과하도록 유로를 형성 및 차단하는 다수개의 차단판과,
상기한 제 1팽창관의 순환수 출구와 연결되며 제 1팽창관의 내경보다 큰 내경을 갖는 제 2팽창관 및,
상기한 제 2팽창관의 순환수 출구와 부상분리조를 연결하며 제 2팽창관보다 내경이 작은 관로를 포함하여 구성되는 것을 특징으로 하는 부상 분리 장치.
According to claim 1, wherein the nano-bubble water generating device is formed in a U-shape, the center is connected to the outlet of the injector, and has a wider inner diameter than the outlet of the injector for limiting the circulating water flow in one direction connected to the injector in only one direction A first expansion pipe formed with a first blocking plate,
A plurality of pressure pipes connecting both sides of the first expansion pipe to each other and having a smaller inner diameter than the first expansion pipe to pressurize (shrink) the circulating water;
A plurality of blocking plates installed inside the first expansion pipe to form and block a flow path for circulating water to pass through the plurality of pressure pipes and the first expansion pipe in a zigzag manner;
A second expansion tube connected to the circulating water outlet of the first expansion tube and having an inner diameter larger than that of the first expansion tube;
Floating separator for connecting the circulating water outlet of the second expansion tube and the floating separation tank, and comprising a conduit having a smaller inner diameter than the second expansion tube.
유입수로부터 형성된 플록을 부상시켜 스키머로 제거하여 고도처리를 하는 부상분리방법에 있어서,
부상분리조의 유입수 투입구측에 유입수에 따른 약품과 부상분리조의 처리수 및 공기가 포함된 순환수를 배출하면 순환수가 고압에서 부상분리조내부의 상압상태로 투입되면서 급속하게 확산되어 나노기포를 포함하는 나노 기포수가 되고, 상기한 나노 기포수에 의하여 유입수의 핀플록 및 콜로이드 상태까지 상부로 부상시켜, 상부로 부상된 플록은 스키머로 제거하도록 하며 처리수는 처리수 배출구로 배출하며,
상기한 나노 기포수는 부상분리조에서 처리된 처리수를 순환수로 하여 가압펌프로 1차 가압하고, 1차가압된 순환수를 인젝터로 유입하되 인젝터 유입시 필요약품과 공기를 주입하여 다시 가압한 후, 관로의 대/소로 가압과 팽창을 다수회 반복시켜 공기 및 약품을 순환수에 최대한 용해시켜 부상분리조로 분출하면 고압에서 대기압상태로 되면서 부피가 팽창되어 나노 기포(Nano Air Bubble)수가 되는 것을 특징으로 하여,
반응/응집/중화조가 필요없이 한 개의 조에서 유입수의 고도처리가 완료되도록 하는 부상 분리 방법.
In the flotation separation method in which the floc formed from the influent is floated and removed with a skimmer to perform advanced processing.
When the circulating water containing the chemicals and the treated water and the air in the floating separation tank are discharged at the inlet water inlet of the floating separation tank, the circulating water is rapidly diffused from the high pressure into the atmospheric pressure inside the floating separation tank to contain nano bubbles. It becomes nano bubble water and floats up to the pin floc and colloidal state of the inflow water by the above-mentioned nano bubble water, so that the floc floating to the top is removed by skimmer and the treated water is discharged to the treated water outlet,
The nano-bubble water is pressurized first with a pressurized pump using the treated water treated in the floating separation tank as a circulating water, and the pressurized circulated water is introduced into the injector, and when the injector is introduced, the necessary chemicals and air are pressurized again. After the pressurization and expansion of the pipe line are repeated many times, the air and chemicals are dissolved in the circulating water as much as possible and spouted into the floating separation tank, and the volume is expanded to the atmospheric pressure at high pressure to become nano air bubble water. Characterized in that,
Flotation separation method that allows the advanced treatment of influent in one tank to be completed without the need for reaction / aggregation / neutralization tanks.
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KR101620261B1 (en) * 2015-01-19 2016-05-11 건양대학교산학협력단 Freshwater algea removal system using the micro-bubble
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