KR100949149B1 - Food Degreasing Solution - Google Patents

Food Degreasing Solution Download PDF

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KR100949149B1
KR100949149B1 KR1020090074961A KR20090074961A KR100949149B1 KR 100949149 B1 KR100949149 B1 KR 100949149B1 KR 1020090074961 A KR1020090074961 A KR 1020090074961A KR 20090074961 A KR20090074961 A KR 20090074961A KR 100949149 B1 KR100949149 B1 KR 100949149B1
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oil
separation
water
tank
liquid
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KR1020090074961A
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Korean (ko)
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이원택
은희영
박승원
최두형
이기옥
홍성택
최경춘
권혁성
김윤미
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전주시
(주)파인리포먼스
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    • 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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01FMIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
    • B01F23/00Mixing according to the phases to be mixed, e.g. dispersing or emulsifying
    • B01F23/20Mixing gases with liquids
    • B01F23/23Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids
    • B01F23/231Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids by bubbling
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • 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
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • 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
    • 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
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01FMIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
    • B01F2101/00Mixing characterised by the nature of the mixed materials or by the application field
    • B01F2101/305Treatment of water, waste water or sewage
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B2101/00Type of solid waste
    • B09B2101/02Gases or liquids enclosed in discarded articles, e.g. aerosol cans or cooling systems of refrigerators
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/20Waste processing or separation
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies

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  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Physical Water Treatments (AREA)

Abstract

PURPOSE: A processing method of food waste leachate is provided to maximize separation efficiency of solids and oil recovery rates by installing a floating tank for oil separation and a floating separation tank for solid-liquid separation. CONSTITUTION: A processing method of food waste leachate includes the following: separating oil included in food waste leachate which is pre-processed with microbubbles dissolved in pressurized and pressed water; storing separated oil; separating the oil and water by heating the stored oil in an oil storage tank(50); adjusting pH of the food waste on which oil is removed; producing floc by rapidly and slowly coagulating the food waste leachate; separating the produced floc; and circulating the processed water on each step.

Description

음식물 탈리액 처리방법{omitted}Food Desorption Method {omitted}

본 발명은 '남은 음식물 자원화 공정'에서 배출되는 고농도의 유기성 폐액인 '음식물 탈리액'을 처리하기 위한 음식물 탈리액 처리에 관한 것으로, 더욱 상세하게는 음식물 탈리액에 포함되어 있는 유분을 분리하기 위한 유수분리용 부상분리조와, 유기성 고형물을 분리하기 위한 고액분리용 부상분리조를 서로 분리하여 설치함으로써 유분회수율과 고형물 분리효율을 최대화한 음식물 탈리액 처리장치 및 방법에 관한 것이다.The present invention relates to a food desorption solution for treating 'food desorption liquid', which is a high concentration of organic waste liquid discharged from the 'remaining food resource recycling process', and more specifically, a wound for separation of oil and water for separating oil contained in the food desorption liquid. The present invention relates to a food desorption liquid treatment apparatus and method for maximizing oil recovery and solids separation efficiency by separately separating a separation tank and a floating separation tank for separation of solids for separating organic solids.

일반적으로 '음식물 탈리액'은 남은 음식물 자원화 공정에서 배출되는 고농도의 유기성 폐액을 말한다. 음식물 탈리액은 85% 이상의 수분을 함유하고 있고 쉽게 부패되는 유기성 물질을 포함하고 있으며, 고형물 함량(SS)이 100,000ppm을 넘는 악성 폐액이다. In general, 'food desorption liquid' refers to a high concentration of organic waste liquid discharged from the remaining food recycling process. Food desorption liquids contain more than 85% water, contain easily decaying organic matter, and are malignant waste fluids with a solids content (SS) of more than 100,000 ppm.

음식물 탈리액은 음식물 쓰레기의 특성과 크게 구별되지 않으며 수거지역의 특성 및 섭취하는 음식의 특성, 지역의 음식문화 등에 따라 매우 다르나 일반적으로 우리나라의 식생활 습관 등을 고려해 볼 때 염분이 많이 함유되어 있으며, 기타 BOD, COD, SS, T-N, T-P 등이 매우 높은 것으로 나타났고 특히 유기산 농도가 높고 pH가 낮다. Food desorption liquids are not very different from the characteristics of food waste and vary greatly depending on the characteristics of the collection area, the characteristics of the foods eaten and the local food culture, but in general, they contain a lot of salts in consideration of the dietary habits of Korea. BOD, COD, SS, TN, TP, etc. were found to be very high, especially high organic acid concentration and low pH.

음식물 탈리액은 직매립이 금지되어 있다. 또 음식물쓰레기의 직매립도 자치단체에서 금지하고 있다. 현재 음식물 탈리액은 함수율 92% 이하에서 해양투기 되거나 하수처리장에 반입하여 처리하고 있다. 그러나 해양투기는 런던협약에 의해 2013년부터 전면금지 될 것으로 예상되고, 고농도로 하수처리장에서 처리하는 경우 처리시설의 악영향과 악취로 인한 민원발생이 우려되고 있다. Food desorption liquids are prohibited from landfilling. Local governments also ban direct landfilling of food waste. Currently, food desorption liquids are disposed of at sea or under sewage treatment at 92% water content. However, dumping at sea is expected to be totally banned in 2013 under the London Convention, and there are concerns that complaints may arise due to the adverse effects of the treatment facilities and odors when the wastewater is treated at high concentrations.

이에 따라 최근에는 음식물 탈리액를 바로 버리거나 하수처리장으로 반입하지 않고, 혐기성 소화공정을 이용하여 바이오가스를 생산하거나 음식물 탈리액 처리장치를 이용해 하수처리장으로 유입되기 전에 유기물 함량을 최소화하고 있다. Accordingly, in recent years, the amount of organic matter is minimized before the food desorption solution is immediately discarded or brought into the sewage treatment plant, and biogas is produced using an anaerobic digestion process or the food desorption solution is introduced into the sewage treatment plant.

도 1은 종래의 음식물 탈리액 처리장치의 일 예를 보여준다. 도시된 바와 같이, 종래의 음식물 탈리액 처리장치는 1차 드럼스크린, 침사조, 그리고 부상분리조(1), 응집반응조(2) 및 2차 드럼스크린조(3)가 순차적으로 구성되어 있다.Figure 1 shows an example of a conventional food leaving solution. As shown, the conventional food desorption liquid treatment apparatus is composed of a primary drum screen, a sedimentation tank, and a floating separation tank (1), a flocculation reaction tank (2) and a secondary drum screen tank (3) sequentially.

따라서 음식물 탈리액은 1차 드럼스크린과 침사조 그리고 부상분리조(1)를 거치면서 비교적 크기가 큰 조대협잡물, 비중이 무거운 침전물 및 유분이 제거된다. 그리고 2차 드럼스크린(3)은 반응응집조(2)에서 응집된 고형물을 최종적으로 분리한다. Therefore, the food desorption liquid is removed from the large coarse coarse matter, heavy sediment and oil through the primary drum screen, sedimentation tank and flotation tank (1). And the secondary drum screen (3) finally separates the solid aggregated in the reaction agglomeration tank (2).

그리고 부상분리조(1)에서 분리된 유분은 유분저장조(5)에 저장되고, 2차 드럼스크린(3)에서 처리된 슬러지는 탈수기를 거쳐 퇴비화 공정으로 투입되며, 고액분리된 처리수는 방류조를 거쳐 방류된다. 즉, 유분회수 및 고형분 제거공정을 거 쳐 오염농도를 저감시킨 음식물 탈리액 처리수는 하수처리장으로 유입하여 연계처리 된다. And the oil separated in the floating separation tank (1) is stored in the oil storage tank (5), the sludge treated in the secondary drum screen (3) is introduced into the composting process through a dehydrator, the solid-liquid separated treatment water is discharged tank Discharged via In other words, the processed food desorption water, which has reduced the pollution concentration through the oil recovery and the solids removal process, flows into the sewage treatment plant and is linked.

이와 같이, 종래의 음식물 탈리액 처리장치는 하나의 부상분리조(1)에서 고형물과 함께 유분을 분리하도록 하고 있다. 그리고 부상분리조(1)에서 분리된 유분은 유분저장조(4)에 저장한다. 또한, 2차 드럼스크린(3)의 전방에 반응응집조(2)를 설치하여 2차 드럼스크린(3)에서 고액분리를 수행하고 있다. In this way, the conventional food desorption liquid treatment apparatus is to separate the oil together with the solids in one floating separation tank (1). And the oil separated from the flotation tank (1) is stored in the oil storage tank (4). In addition, the reaction agglomeration tank 2 is installed in front of the secondary drum screen 3 to perform solid-liquid separation in the secondary drum screen 3.

그러나 상기 부상분리조(1)로 유입되는 음식물 탈리액은 고형물(SS)이 다량으로 포함되어 있어 유수회수가 용이하지 않다. 즉, SS에 부착되어 있거나 에멀전화되어 있는 유분에 미세기포가 부착하여 수면위로 부상시켜야 하나 SS함량이 높은 탈리액은 미세기포가 잘 발생하지 않고 유분이 고형물로부터 쉽게 분리되지 않기 때문에 유분분리가 원활하지 않다. However, the food desorption solution flowing into the flotation tank 1 contains a large amount of solids (SS), and thus it is not easy to recover the water. In other words, microbubbles should be attached to the surface of the oil attached to the SS or emulsified to float on the surface of the water, but the separation of the oil with high SS content does not occur easily because the microbubbles are not easily generated and the oil is not easily separated from the solids. not.

그리고 분리된 유분은 수면위에 층을 이루고 있는데 종래의 부상분리조(1)는 스키머 작동으로 유분회수 시 수면층과 유분층이 혼합되어 회수된 유분의 질을 떨어뜨리는 문제가 있었다. In addition, the separated oil forms a layer on the surface of water, but the conventional flotation tank 1 has a problem of degrading the quality of oil recovered by mixing the water layer and the oil layer during oil recovery by skimmer operation.

또한, 유분이 많이 잔류하는 음식물 탈리액에 응집제를 투여할 경우, 유분이 미세 고형물을 감싸고 있기 때문에 거대 플럭이 형성되기 어렵다. 따라서 종래와 같이, 유분이 완전히 분리되지 않은 음식물 탈리액에 응집제를 투입하고 응집반응 후 제2 드럼스크린(3)을 통해 고액분리를 하면, 응집효율이 적절하지 않은 상태에서 드럼스크린 유입시 1mm보다 작은 SS가 처리수로 배출되어 처리수질이 불량하고 슬러지 성상도 불량하게 되는 문제가 있었다.In addition, when the flocculant is administered to the food desorption liquid having a large amount of oil, a large floc is hardly formed because the oil surrounds the fine solid. Therefore, as in the prior art, when a flocculant is added to a food desorption liquid in which oil is not completely separated and solid-liquid separation is carried out through the second drum screen 3 after the flocculation reaction, the flocculation efficiency is less than 1 mm when the drum screen flows in an unsuitable state. SS is discharged into the treated water has a problem that the treated water quality is poor and the sludge properties are also poor.

이와 같이 종래의 음식물 탈리액 처리장치는 고액분리 효율이 낮아 처리수질이 불량하고 슬러지의 성상이 수분을 많이 함유하고 있기 때문에 슬러지 발생부피가 크다. 또한, 하루에 발생되는 음식물 탈리액을 처리하기 위해서는 충분한 응집반응시설과 고액분리시설이 필요한데, 종래의 처리장치는 기본적인 용량이 작고 그로 인한 체류시간이 짧아 처리효율을 떨어졌다. 예를 들어, 종래 응집반응조의 경우 각조의 체류시간이 5분 남짓에 불과하다. 반대로 체류시간을 충분히 하기 위해서는 처리장치의 확대가 불가피하나 이 경우 추가적인 투자비용이 요구된다. Thus, the conventional food desorption liquid treatment apparatus has a low sludge generation efficiency due to low liquid-liquid separation efficiency and poor treatment water quality, and the sludge property contains a lot of water. In addition, a sufficient flocculation reaction facility and a solid-liquid separation facility are required to process the food desorption solution generated in a day, but the conventional treatment apparatus has a low basic capacity and a short residence time, thereby reducing treatment efficiency. For example, in the conventional flocculation tank, the residence time of each tank is only about 5 minutes. On the contrary, it is inevitable to expand the processing equipment in order to make the residence time sufficient, but in this case, additional investment cost is required.

아울러, 2차 드럼스크린(3)은 응집반응이 제대로 이루어지지 않은 많은 양의 음식물 탈리액이 유입되어 발생되는 슬러지의 함수율이 높다. 또, 최종 처리수 중의 유분 및 유기물의 함량과다로 하수처리장 연계처리 시 하수처리장의 안정적 운영에 악영향을 미치고 있다.In addition, the secondary drum screen (3) has a high water content of the sludge generated by the inflow of a large amount of food desorption solution in which the aggregation reaction is not properly performed. In addition, due to the excessive content of oil and organic matter in the final treated water, the sewage treatment plant linked treatment adversely affects the stable operation of the sewage treatment plant.

이와 같이 종래의 음식물 탈리액 처리장치는 고농도의 유기물과 유분 그리고 유기산을 포함하는 음식물 탈리액을 처리하는데 한계가 있으므로 새로운 형태의 음식물 탈리액 처리장치의 개발이 시급히 요청되고 있는 실정이다.As described above, since the conventional food desorption solution processing apparatus has a limitation in processing food desorption liquids containing a high concentration of organic matter, oil and organic acids, the development of a new food desorption solution processing system is urgently required.

본 발명은 종래 기술의 문제점을 해결하기 위한 것으로서, 본 발명의 주된 목적은, 음식물 탈리액의 처리효율을 개선하여 처리수질의 향상, 발생 슬러지의 함수율 저감 및 유분회수의 효율을 향상시킬 수 있는 새로운 형태의 음식물 탈리액 처리장치 및 방법을 제공하는 것이다. The present invention is to solve the problems of the prior art, the main object of the present invention is to improve the treatment efficiency of the food desorption solution to improve the quality of the treated water, to reduce the water content of the sludge generated, and to improve the efficiency of oil recovery It is to provide an apparatus and method for treating food desorption liquid.

본 발명의 다른 목적은, 음식물 탈리액에 포함되어 있는 유분을 분리하기 위한 유수분리용 부상분리조와, 유기성 고형물을 분리하기 위한 고액분리용 부상분리조를 서로 분리하여 설치하고, 고액분리용 부상분리조에서 배출되는 처리수 중 일부를 고압공기로 가압처리하여 미세기포가 용해된 가압처리수를 생성하고 이를 고액분리용 부상분리조 및 유수분리용 부상분리조로 순환 공급하여 유수분리용 부상분리조의 탈리액의 농도를 희석하고, 유분 분리를 최대화하며, 유분이 제거된 탈리액에 응집제를 주입하여 응집 반응시킨 후 고액분리용 부상분리조에서 고액분리하여 고액분리 효율을 최대화할 수 있는 음식물 탈리액 처리장치 및 방법을 제공하는 것이다.Another object of the present invention is to separate and install the flotation separation tank for oil and water separation to separate the oil contained in the food desorption liquid, and the solids separation separation tank for separating the organic solids, and in the flotation separation tank for solid-liquid separation Part of the discharged treated water is pressurized with high pressure air to generate pressurized water in which microbubbles are dissolved, and it is circulated and supplied to the solid-liquid separation flotation and the oil-water separation flotation tank to dilute the concentration of the desorbent in the flotation separation tank for oil-water separation. And, to maximize the separation of oil, the flocculant is injected into the desorbent from which the oil is removed, and the flocculation reaction to provide a food desorption liquid treatment apparatus and method that can maximize the solid-liquid separation efficiency by solid-liquid separation in the flotation separation tank for solid-liquid separation. .

본 발명의 또 다른 목적은, 분리가 어려운 남은 음식물의 고형분 및 유분을 체거름 및 부상분리 공정을 거쳐 효과적으로 제거함으로써 유분회수율을 극대화하고 하수처리연계시 하수처리장 운영에 미치는 영향을 최소화하는 음식물 탈리액 처리장치 및 방법을 제공하는 것을 목적으로 한다.Another object of the present invention is to effectively remove the solids and oil of the remaining food difficult to separate through the sieving and flotation separation process to maximize the oil recovery rate and minimize the effect on the operation of the sewage treatment plant during sewage treatment associated with It is an object to provide an apparatus and method.

상술한 본 발명의 목적을 달성하기 위하여, 본 발명에 따른 음식물 탈리액 처리장치는, 전처리된 음식물 탈리액에 포함되어 있는 유분을 가압처리수에 용해된 미세기포를 이용하여 분리하는 유수분리용 부상분리조와; 상기 유수분리용 부상분리조를 통해서 유분이 제거된 음식물 탈리액에 응집제를 투여하고 급속 및 완속 교반을 거쳐 플럭을 형성시키는 반응응집조와; 상기 반응응집조에서 생성된 플럭을 가압처리수에 용해된 미세기포를 이용하여 분리하는 고액분리용 부상분리조;를 포함하여 구성되는 것을 특징으로 한다.In order to achieve the above object of the present invention, the food desorption liquid treatment apparatus according to the present invention, the flotation separation tank for oil and water separation for separating the oil contained in the pretreated food desorption liquid using micro-bubbles dissolved in the pressurized water; A reaction agglomeration tank for administering a flocculant to the food desorption liquid from which oil has been removed through the flotation tank for oil and water separation, and forming a floc through rapid and slow stirring; And a flotation separation tank for solid-liquid separation separating the flocks generated in the reaction agglomeration tank by using microbubbles dissolved in the pressurized water.

또한, 본 발명에 따른 음식물 탈리액 처리장치는, 상기 고액분리용 부상분리조에서 배출되는 처리수 중 일부를 고압공기로 가압처리하여 미세기포가 용해된 가압처리수를 생성하고 이를 고액분리용 부상분리조 및 유수분리용 부상분리조로 순환시키는 가압처리수 순환장치를 더 포함하는 것을 특징으로 한다.In addition, the food desorption liquid treatment apparatus according to the present invention, by pressurizing a portion of the treated water discharged from the flotation separation tank for solid-liquid separation with high-pressure air to produce a pressurized treated water in which fine bubbles are dissolved, this separation separation for solid-liquid separation It characterized in that it further comprises a pressurized water circulating device for circulating to the tank and floating separation tank for oil and water separation.

또한, 본 발명에 따른 음식물 탈리액 처리장치는, 상기 유수분리용 부상분리조에서 분리된 유분을 저장하는 유분저장조가 더 설치되고, 상기 유분저장조에 저장된 유분을 일정한 온도로 가열하여 유분과 수분을 분리하기 위한 유분개량조가 더 설치된다.In addition, the food desorption liquid treatment apparatus according to the present invention, the oil storage tank for storing the oil separated in the flotation tank for oil-water separation is further installed, to separate the oil and water by heating the oil stored in the oil storage tank to a constant temperature Further oil refinery is installed.

또한, 상기 반응응집조에는 응집제를 투입하기 전에 알칼리 보조제를 주입하기 위한 pH 조정조가 더 포함된 것을 특징으로 한다.In addition, the reaction coagulation tank is characterized in that it further comprises a pH adjusting tank for injecting an alkali adjuvant before injecting the flocculant.

또한, 상기 고액분리용 부상분리조에는 고액분리용 부상분리조에서 분리된 고형물을 다시 고액분리하는 2차 드럼스크린이 연결된다.In addition, a secondary drum screen for solid-liquid separation of the solids separated in the solid-liquid separation float separation tank for solid-liquid separation is connected.

이와 같이, 본 발명은 유분을 분리하기 위한 유수분리용 부상분리조와, 고형물을 분리하기 위한 고액분리용 부상분리조를 분리하여 설치하고, 유분이 충분히 제거된 탈리액에 응집제를 주입함으로써 응집반응을 최대화하여 고액분리용 부상분리조에서의 고액분리가 잘 이루어지도록 하며, 고액분리용 부상분리조에서 배출되는 처리수 중 일부를 고압공기로 가압처리하여 미세기포가 용해된 가압처리수를 생성하고 이를 고액분리용 부상분리조 및 유수분리용 부상분리조로 순환 공급하여 유수분리용 부상분리조에서의 유분의 분리가 원활하게 이루어지도록 하는 것을 특징으로 한다.Thus, the present invention is installed by separating the flotation separation tank for oil-water separation and the flotation separation tank for solid-liquid separation to separate the solids, and maximizes the flocculation reaction by injecting the flocculant into the desorption liquid sufficiently removed oil Solid-liquid separation in the solid-liquid separation tank is performed well, and some of the treated water discharged from the solid-liquid separation tank is pressurized with high-pressure air to generate pressurized water in which fine bubbles are dissolved, and the solid-liquid separation is performed. It is characterized in that the separation of the oil from the flotation tank for oil and water separation by circulating supply to the flotation tank for oil separation and flotation for oil water separation.

상술한 바와 같이, 본 발명의 음식물 탈리액 처리장치에 의하면, 고액분리용 부상분리조외에 유수분리용 부상분리조를 별도로 설치하여 유수분리의 효율을 극대화함으로써 응집제의 응집반응과 고액분리의 효율을 향상시켜서 처리수질이 좋아지는 효과가 있다. As described above, according to the food desorption liquid treatment apparatus of the present invention, by installing a flotation separation tank for oil and water separation in addition to the flotation separation tank for solid-liquid separation to maximize the efficiency of the oil and water separation to improve the efficiency of flocculation flocculation reaction and solid-liquid separation The treatment water quality is improved.

본 발명은 유수분리용 부상분리조에서의 유분회수율을 높여서 고액분리의 효율을 높일 뿐만 아니라 유수분리를 위한 유분개량조의 부담을 경감시키고, 처리수 수질의 향상으로 하수종말처리장으로 배출되는 오염부하가 경감되어 하수처리장의 운영이 안정화되는 효과가 있다.The present invention not only improves the efficiency of solid-liquid separation by increasing the oil recovery rate in the flotation tank for oil and water separation, but also reduces the burden of the oil reforming tank for oil and water separation, and reduces the pollutant load discharged to the sewage treatment plant by improving the treated water quality. Thus, the operation of the sewage treatment plant is stabilized.

이하 첨부도면을 참조하여 본 발명에 따른 음식물 탈리액 처리장치에 대해서 상세히 설명한다. With reference to the accompanying drawings will be described in detail with respect to food desorption liquid treatment apparatus according to the present invention.

먼저, 도 2는 본 발명에 따른 음식물 탈리액 처리장치의 주요부분의 결합구조를 보여주는 개략적인 구성도이고, 도 3은 도 2에 도시된 유수분리용 부상분리조와 응집반응조 그리고 고액분리용 부상분리조의 결합구조를 보여주는 구성도이며, 도 4는 본 발명에 따른 음식물 탈리액 처리장치의 전체적인 구조를 보여주는 개략적인 구성도이다.First, Figure 2 is a schematic configuration showing a coupling structure of the main part of the food desorption liquid treatment apparatus according to the present invention, Figure 3 is a combination of the flotation reaction tank and flotation reaction tank and flotation separation tank for solid-liquid separation shown in Figure 2 Figure 4 is a schematic diagram showing the structure, Figure 4 is a schematic diagram showing the overall structure of the food desorption liquid treatment apparatus according to the present invention.

도시된 바와 같이, 본 발명에 따른 음식물 탈리액 처리장치는, 전처리된 음식물 탈리액에 포함되어 있는 유분을 가압처리수에 용해된 미세기포를 이용하여 분리하기 위한 유수분리용 부상분리조(10)가 구비된다. 그리고 상기 유수분리용 부상분리조(10)에서 분리된 유분은 유분저장조(50)로 보내지고, 유분저장조(50)의 유분은 유분개량조(80)에서 일정 온도로 가열되어 유분과 수분을 분리한다.As shown, the food desorption liquid treatment apparatus according to the present invention is provided with a floating separation tank 10 for oil / water separation for separating the oil contained in the pretreated food desorption liquid by using micro bubbles dissolved in the pressurized water. . And the oil separated in the oil separation tank 10 for separation of oil is sent to the oil storage tank 50, the oil of the oil storage tank 50 is heated to a constant temperature in the oil improvement tank 80 to separate the oil and water. .

상기 유수분리용 부상분리조(10)의 후단에는 유분이 제거된 음식물 탈리액에 응집제를 투입하고 교반하여 플록을 형성하기 위한 응집반응조(20)가 구비된다. 상기 응집반응조(20)에서 형성된 플록은 그 후방에 설치된 고액분리용 부상분리조(30)로 이송되어 1차로 고액분리된다. At the rear end of the flotation separation tank 10 for oil and water separation, a flocculation reaction tank 20 is formed to add flocculant to the food desorption solution from which oil is removed and to form a floc. The floc formed in the flocculation reaction tank 20 is transferred to the flotation separation tank 30 for solid-liquid separation installed at the rear thereof, and the solid-liquid separation is performed first.

그리고 상기 고액분리용 부상분리조(30)에서 분리된 슬러지는 드럼스크린(40)으로 보내져 2차로 고액분리가 이루어지고, 상기 고액분리용 부상분리조(30)에서 분리된 처리수중 일부는 처리수 배출관(34)을 통해 방류조나 하수처리장으로 보내진다.And the sludge separated from the solid-liquid separation flotation tank 30 is sent to the drum screen 40, the solid-liquid separation is made second, some of the treated water separated from the solid-liquid separation flotation separation tank 30 is treated water It is sent to the discharge tank or the sewage treatment plant through the discharge pipe 34.

이때, 상기 고액분리용 부상분리조(30)에서 분리된 처리수 중 일부는 고압공기로 가압처리되어 미세기포가 용해된 가압처리수 형태로 고액분리용 부상분리조(30)와 유수분리용 부상분리조(10)로 순환 공급되고, 상기 가압처리수는 유수분리용 부상분리조(10)와 고액분리용 부상분리조(30)에 미세기포를 공급한다.At this time, some of the treated water separated from the solid-liquid separation flotation separation tank 30 is pressurized by high-pressure air to form a solid-liquid separation separation tank 30 and flotation separation for oil-water separation in the form of pressurized water in which fine bubbles are dissolved. It is circulated and supplied to the tank 10, and the pressurized water supplies fine bubbles to the flotation separation tank 10 for oil and water separation and the flotation separation tank 30 for solid-liquid separation.

도 3을 참조하면, 상기 고액분리용 부상분리조(30)의 하단에는 고액분리 처리수 순환배출관(62)이 설치되고, 상기 고액분리 처리수 순환배출관(62)에는 처리수내에 고압의 공기를 주입하기 위한 가압펌프(61)가 설치된다. 그리고 가압펌프(61)와 고액분리용 부상분리조(30) 사이에는 제1 가압처리수 순환관(64)이 설치되고, 상기 가압펌프(61)와 유수분리용 부상분리조(10) 사이에는 제2 가압처리수 순환관(63)이 설치된다.Referring to Figure 3, the solid-liquid separation treatment water circulation discharge pipe 62 is installed at the lower end of the solid-liquid separation flotation tank 30, the solid-liquid separation treatment water circulation discharge pipe 62 is a high-pressure air in the treated water A pressure pump 61 for injecting is installed. The first pressurized water circulation pipe 64 is installed between the pressure pump 61 and the floating separation tank 30 for solid-liquid separation, and between the pressure pump 61 and the floating separation tank 10 for oil-water separation. 2 pressurized water circulation pipe (63) is installed.

따라서 상기 제2 가압처리수 순환관(64)을 통해 유수분리용 부상분리조(10)의 하부로 순환되는 가압처리수는 유수분리용 부상분리조(10)의 탈리액의 농도를 낮추고, 유분 및 고형물(SS) 분리가 용이하도록 미세기포를 발생시킨다. Therefore, the pressurized water circulated to the lower portion of the oil separation separator 10 for separation of oil and oil through the second pressurized water circulation pipe 64 lowers the concentration of the desorption liquid of the oil separation separator 10 for oil and oil separation, and oil and solids ( SS) Generates microbubbles to facilitate separation.

이하, 본 발명에 따른 음식물 탈리액의 처리공정과 함께 구체적인 구성에 대해서 설명하기로 한다.. Hereinafter, a specific configuration will be described together with a process for treating food desorption liquid according to the present invention.

일반적으로, 음식물폐기물 자원화시설의 음식물 탈리액은 공정 중 다량의 용수가 함유되어 유입되어 일반적인 음식물 탈리액과 비교할 때 매우 양호한 편이다. 따라서 1차 드럼스크린, 침사조 거치면서 비교적 크기가 큰 조대협잡물, 비중이 무거운 침전물이 제거되어 SS 30,000~50,000 수준의 탈리액이 발생한다. In general, the food desorption solution of the food waste recycling facility is very good compared to the general food desorption solution due to the inflow of a large amount of water during the process. Therefore, SS 30,000 ~ 50,000 desorption solution is generated by removing large coarse coarse matter and heavy specific sediment through primary drum screen, sedimentation tank.

그러나 전처리된 탈리액 중에는 아직도 많은 양의 유분이 남아 있다. 이러한 유분은 미생물 처리시 미생물과 공기의 접촉을 방해하여 분해효율을 떨어뜨리며, 응집반응 시 응집효율을 떨어뜨리는 등의 문제를 일으키기 때문에 폐수처리를 위해 우선적으로 제거되어야 한다.However, a large amount of oil still remains in the pretreated stripping solution. These oils have to be removed first for wastewater treatment because they cause problems such as obstructing contact between microorganisms and air during microbial treatment, and causing problems such as degradation of coagulation efficiency.

이를 위해서, 본 발명에 따른 음식물 탈리액 처리장치는, 전처리된 음식물 탈리액이 탈리액 주입관(12)을 통해 유수분리용 부상분리조(10)의 하부로 유입된다. 그리고 고액분리용 부상분리조(30)에서 배출되는 처리수 일부가 고압공기로 가압처리되어 미세기포가 용해된 가압처리수 형태로 유수분리용 부상분리조(10) 하부로 유입된다. 따라서 상기 미세기포가 용해된 가압처리수는 유수분리용 부상분리조(10)의 탈리액의 고농도를 희석시키고, 미세기포를 발생시킨다. 즉, 고액분리용 부상분리조(30)에서 배출되는 처리수는 고형물(SS)이 적기 때문에 그 처리수의 일부를 미세기포가 용해된 가압처리수 형태로 유수분리용 부상분리조(10)의 하부로 공급시켜 SS 30,000~50,000으로 유입되는 음식물 탈리액을 SS 20,000~30,000 수준으로 낮출 수 있게 되고, 유수분리를 용이하게 할 수 있다.To this end, in the food desorption liquid treatment apparatus according to the present invention, the pretreated food desorption liquid is introduced into the lower portion of the flotation separation tank 10 for oil / water separation through the desorption liquid injection tube 12. A portion of the treated water discharged from the solid-liquid separation floatation tank 30 is pressurized with high-pressure air to flow into the lower portion of the flotation separation tank 10 for oil-water separation in the form of pressurized water in which fine bubbles are dissolved. Therefore, the pressurized water in which the microbubbles are dissolved dilutes the high concentration of the desorption liquid of the flotation tank 10 for oil / water separation and generates microbubbles. That is, since the treated water discharged from the solid-liquid separation flotation separation tank 30 has little solids (SS), a portion of the treated water is in the form of pressurized treatment water in which microbubbles are dissolved, and the lower portion of the flotation separation tank for oil-water separation. It is possible to lower the food desorption liquid flowing into the SS 30,000 ~ 50,000 to SS 20,000 ~ 30,000 level, and facilitate the oil and water separation.

이어, 유수분리용 부상분리조(10)의 하부에서 부상하는 미세기포는 음식물 탈리액 중에 포함된 유분을 상부로 부상시킨다. 그리고 스크래퍼(16)는 수표면으로부터 유분을 제거한다. 이때 수분층과의 혼합 없이 유분만을 제거하기 위해 유수분리용 부상분리조(10)에는 수중격막(15)을 설치하여 수표면의 유동을 최소화하고 유분분리를 효과적으로 한다. 그리고 유수분리용 부상분리조(10)에서 분리된 유분은 유분저장조(50)로 배출되고 유분이 제거된 음식물 탈리액은 응집반응조(20)로 공급된다.Subsequently, the fine bubbles floating in the lower portion of the oil separation separator 10 float the oil contained in the food desorption solution upward. The scraper 16 removes oil from the water surface. At this time, in order to remove only oil without mixing with the water layer, an underwater septum 15 is installed in the floating separation tank 10 for oil / water separation to minimize the flow of the water surface and effectively separate the oil. The oil separated in the flotation separation tank 10 for oil and water separation is discharged into the oil storage tank 50 and the food desorption liquid from which the oil is removed is supplied to the flocculation reaction tank 20.

상기 응집반응조(20)는 고농도의 유기오염부하를 제거하기 위해 응집제를 첨가한다. 상기 응집반응조(20)는 유수분리용 부상분리조(10)와 고액분리용 부상분리조(30)의 사이에 설치된다. 따라서 유분이 제거된 음식물 탈리액에 응집제를 투여함으로써 응집효율을 극대화할 수 있다.The flocculation tank 20 adds a flocculant to remove the high concentration of organic pollution load. The flocculation reaction tank 20 is installed between the flotation separation tank 10 for oil and water separation and the flotation separation tank 30 for solid-liquid separation. Therefore, it is possible to maximize the flocculation efficiency by administering a flocculant to the food desorption liquid from which oil is removed.

바람직하게 상기 응집반응조(20)는 pH 조정조(24), 급속응집조(25), 완속응집조(26)로 구성되고, 각 조에는 교반장치(23)가 구비된다. 일반적으로 음식물 탈리액은 고농도의 유기산에 의해 낮은 pH를 나타낸다. 따라서 최적의 응집효율을 위해 적정 pH로의 보정이 필요하며 이를 위해 pH 조정조(24)에는 알칼리 보조제가 주입된다. 음식물 탈리액의 처리를 위하여 pH는 7~8로 보정되며 점도가 높은 음식물 탈리액의 특성상 교반시간을 충분히 주어 알칼리 보조제의 과다사용 없이 알칼리 보조제가 충분히 혼합되도록 한다. Preferably, the coagulation reaction tank 20 is composed of a pH adjusting tank 24, a rapid coagulation tank 25, a slow coagulation tank 26, each tank is provided with a stirring device (23). In general, food desorption liquids exhibit low pH due to high concentrations of organic acids. Therefore, it is necessary to calibrate to the appropriate pH for the optimum coagulation efficiency, for this purpose, an alkali adjuvant is injected into the pH adjustment tank (24). For the treatment of food desorption solution, the pH is adjusted to 7 ~ 8 and given sufficient stirring time due to the nature of the food desorption solution with high viscosity, the alkali adjuvant is sufficiently mixed without excessive use of the alkali adjuvant.

pH가 보정되면 응집제를 투여하여 급속(25) 및 완속(26) 교반을 통해 플록의 크기를 키운다. 적정시간 동안 반응되지 못하면 약품사용량이 증대되고 알맞은 플 록이 형성되지 않아 후단 고액분리시 효율이 크게 떨어진다. 따라서 각 조는 점도가 높은 유기산 및 SS의 함량이 높은 음식 탈리액의 특성에 따라 반응시간이 15~20분이 되도록 한다.Once the pH is corrected, flocculant is administered to increase floc size through rapid (25) and slow (26) agitation. If the reaction fails for a proper time, the amount of chemical use is increased and the appropriate floc is not formed. Therefore, each bath has a reaction time of 15 to 20 minutes depending on the characteristics of the food stripper having a high organic acid and high SS content.

이어서, 상기 응집반응조(20)에서 형성된 플록들은 고액분리용 부상분리조(30)에 유입되어 고액분리가 이루어진다. 고액분리용 부상분리조(30)는 가압 부상분리조(31)를 이용하여 탈리액 중의 플록을 고액분리한다. 즉, 음식물 탈리액 중의 미세 고형물은 드럼스크린(40)에서 고액분리하기 어렵기 때문에 1차적으로 미세기포를 이용하여 제거함으로써 유기성 고형물 농도를 크게 낮출 수 있다.Subsequently, flocs formed in the flocculation reaction tank 20 flow into the flotation separation tank 30 for solid-liquid separation, thereby performing solid-liquid separation. The flotation separation tank 30 for solid-liquid separation separates the floc in the desorption liquid using the pressure flotation separation tank 31. That is, since the fine solids in the food desorption liquid are difficult to be solid-liquid separated in the drum screen 40, the organic solids concentration can be significantly lowered by first removing the fine solids.

바람직하게, 플록이 형성된 탈리액은 탈리액 주입관(32)을 통해 고액분리용 부상분리조(30)의 하부로 유입된다. 그리고 가압펌프(61)에 의해 가압된 미세기포가 용해된 가압처리수는 고액분리용 부상분리조(30)의 하부로 유입된다. 따라서 고액분리용 부상분리조(30)에서는 가압펌프(61)에서 유입되는 가압처리수에 용해된 미세기포들이 수중의 SS와 결합하여 상부에 슬러지 층을 생성시킨다. 부상된 슬러지는 부상체류시간과 부상압력을 충분히 유지되도록 설계하여 발생되는 슬러지의 함수율을 최소로 한다. 부상분리조 상부에서는 스크래퍼(36)로 슬러지 층을 제거함으로써 SS는 3,000~10,000ppm으로 떨어지며 이에 따라 BOD, COD도 큰 폭으로 떨어져 유기오염물부하가 저감된다.Preferably, the flocculant having a flocculant is introduced into the lower portion of the flotation separation tank 30 for solid-liquid separation through the stripping liquid inlet tube 32. The pressurized water in which the microbubbles pressurized by the pressure pump 61 are dissolved is introduced into the lower portion of the flotation separation tank 30 for solid-liquid separation. Therefore, in the flotation separation tank 30 for solid-liquid separation, fine bubbles dissolved in the pressurized water flowing from the pressure pump 61 are combined with SS in the water to generate a sludge layer on the top. Floated sludge is designed to maintain sufficient floating residence time and floating pressure to minimize the water content of sludge generated. By removing the sludge layer with the scraper 36 in the upper part of the floating separation tank, SS drops to 3,000 to 10,000 ppm, and accordingly, BOD and COD also drop largely, thereby reducing organic pollutant load.

그리고 상기 고액분리용 부상분리조(30)로부터 분리된 상등액은 하수연계처리하여 잔류 유기오염물을 제거하고, 스크래퍼(36)에 의해 분리된 고형물은 드럼스크린(40)를 통해 고액분리되고 탈수기를 거쳐 함수율을 저감한다. And the supernatant separated from the solid-liquid separation flotation tank 30 is sewage-linked to remove residual organic contaminants, and the solids separated by the scraper 36 is solid-liquid separated through the drum screen 40 and dehydrator Reduce the moisture content

아울러, 상기 유분저장조(50)에 저정된 유분은 유분개량조(80)에서 유분과 수분이 분리된다. 바람직하게 상기 유분개량조(80)는 점성이 높은 기름을 히터를 이용하여 가열하여 점도를 낮춘 다음 물과 기름의 비중 차이를 이용하여 유분과 수분을 분리하여 배출한다.In addition, the oil stored in the oil storage tank 50 is separated from the oil and water in the oil improvement tank (80). Preferably, the oil fractionation tank 80 lowers the viscosity by heating a highly viscous oil using a heater and then separates the oil and water by using a difference in specific gravity between water and oil.

이와 같이 본 발명은 분리가 어려운 남은 음식물의 고형분 및 유분을 체거름 및 부상분리 공정을 거쳐 효과적으로 제거함으로써 유분회수율을 극대화하고 하수처리연계시 하수처리장 운영에 미치는 영향을 최소화한다.As such, the present invention effectively removes the solids and oil of the remaining foods that are difficult to separate through the sieving and flotation separation process to maximize the oil recovery rate and minimize the influence on the operation of the sewage treatment plant during sewage treatment.

도 1은 종래 기술에 따른 음식물 탈리액 처리장치의 일 예를 개략적인 구성도이고, 1 is a schematic configuration diagram of an example of a food leaving solution treatment apparatus according to the prior art,

도 2는 본 발명에 따른 음식물 탈리액 처리장치의 주요부분의 결합구조를 보여주는 개략적인 구성도이며, Figure 2 is a schematic block diagram showing a coupling structure of the main part of the food desorption liquid treatment apparatus according to the present invention,

도 3은 도 2에 도시된 유수분리용 부상분리조와 응집반응조 그리고 고액분리용 부상분리조의 결합구조를 보여주는 구성도이고, 3 is a block diagram showing a coupling structure of the flotation reaction tank and flocculation reaction tank and flotation separation tank for solid-liquid separation shown in Figure 2,

도 4는 본 발명에 따른 음식물 탈리액 처리장치의 전체적인 구조를 보여주는 개략적인 구성도이다.Figure 4 is a schematic diagram showing the overall structure of the food leaving solution treatment apparatus according to the present invention.

****도면의 주요 부분에 대한 부호의 설명******** Description of the symbols for the main parts of the drawings ****

10 : 유수분리용 부상분리조 20 : 응집반응조10: floating separation tank for oil and water separation 20: flocculation reaction tank

30 : 고액분리용 부상분리조 40 : 드럼스크린30: floating separation tank for solid-liquid separation 40: drum screen

50 : 유분저장조 60 : 처리수 순환장치50: oil storage tank 60: treated water circulator

61 : 가압펌프 80 : 유분개량조61 pressure pump 80 oil fractionation tank

Claims (8)

삭제delete 삭제delete 삭제delete 삭제delete 전처리한 음식물 탈리액을 처리하는 음식물 탈리액 처리방법에 있어서, In the food desorption liquid treatment method for treating pretreated food desorption liquid, 상기 전처리된 음식물 탈리액에 포함되어 있는 유분을 가압처리수에 용해된 미세기포를 이용하여 분리하는 유수 부상분리단계와;Floating water separation step of separating the oil contained in the pre-treated food desorption liquid using the micro-bubbles dissolved in the pressurized water; 상기 유수 부상분리단계에서 분리된 유분을 저장하는 유분저장단계와;An oil storage step of storing the oil separated in the floating water separation step; 상기 유분저장단계에서 저장된 유분을 일정한 온도로 가열하여 유분과 수분을 분리하기 위한 유분개량단계와;An oil improvement step for separating oil and water by heating the oil stored in the oil storage step to a constant temperature; 상기 유수분리단계에서 유분이 제거된 음식물 탈리액에 알칼리 보조제를 주입하여 pH를 조정하는 pH조정단계와;A pH adjustment step of adjusting pH by injecting an alkali adjuvant into the food desorption liquid from which oil is removed in the oil and water separation step; 상기 pH조정된 음식물 탈리액에 응집제를 투여하고 급속, 완속 교반하여 플럭을 형성시키는 급속응집단계 및 완속응집단계를 포함하여 구성되는 반응응집단계와; A reaction coagulation step including a coagulation agent to the pH-adjusted food desorption solution and including a rapid coagulation step and a slow coagulation step to form a floc by rapid and slow stirring; 상기 반응응집단계에서 생성된 플럭을 가압처리수에 용해된 미세기포를 이용하여 고액을 분리하는 고액 부상분리단계와;A solid-liquid flotation separation step of separating solids from the flocs generated in the reaction agglomeration step using micro-bubbles dissolved in pressurized water; 상기 고액 부상분리단계에서 분리되는 처리수 중 일부를 가압펌프로 가압처리하여 미세기포가 용해된 가압처리수를 생성하고 이를 상기 유수 부상분리단계와 고액 부상분리단계로 순환시키는 가압처리수 순환단계를 포함하여 구성되는 것을 특징으로 하는 음식물 탈리액 처리방법A pressurized water circulating step of pressurizing a portion of the treated water separated in the solid-liquid flotation separation step to generate pressurized water in which microbubbles are dissolved and circulating it into the flowing water separation phase and the solid-liquid flotation separation step Food removal solution treatment method characterized in that it comprises a 삭제delete 삭제delete 삭제delete
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* Cited by examiner, † Cited by third party
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CN114436446A (en) * 2022-01-28 2022-05-06 北京智通博瑞科技发展有限公司 Measurable kitchen oil and water draining treatment system and method

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