KR20000054588A - Device for treatment of night soil, food waste and house sewage and a method of treating night soil, food waste and house sewage using the device - Google Patents

Device for treatment of night soil, food waste and house sewage and a method of treating night soil, food waste and house sewage using the device Download PDF

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Publication number
KR20000054588A
KR20000054588A KR1020000032344A KR20000032344A KR20000054588A KR 20000054588 A KR20000054588 A KR 20000054588A KR 1020000032344 A KR1020000032344 A KR 1020000032344A KR 20000032344 A KR20000032344 A KR 20000032344A KR 20000054588 A KR20000054588 A KR 20000054588A
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South Korea
Prior art keywords
tank
water
primary
food waste
fermentation tank
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KR1020000032344A
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Korean (ko)
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김세창
서정엽
김수동
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김세창
서정엽
김수동
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Priority to KR1020000032344A priority Critical patent/KR20000054588A/en
Publication of KR20000054588A publication Critical patent/KR20000054588A/en
Priority to CN01221365U priority patent/CN2547726Y/en
Priority to CNB011211199A priority patent/CN1171810C/en

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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/02Biological treatment
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/10Packings; Fillings; Grids
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/30Aerobic and anaerobic processes
    • EFIXED CONSTRUCTIONS
    • E03WATER SUPPLY; SEWERAGE
    • E03CDOMESTIC PLUMBING INSTALLATIONS FOR FRESH WATER OR WASTE WATER; SINKS
    • E03C1/00Domestic plumbing installations for fresh water or waste water; Sinks
    • E03C1/12Plumbing installations for waste water; Basins or fountains connected thereto; Sinks
    • E03C1/26Object-catching inserts or similar devices for waste pipes or outlets
    • E03C1/266Arrangement of disintegrating apparatus in waste pipes or outlets; Disintegrating apparatus specially adapted for installation in waste pipes or outlets
    • E03C1/2665Disintegrating apparatus specially adapted for installation in waste pipes or outlets
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/005Black water originating from toilets
    • 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
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/20Sludge processing

Abstract

PURPOSE: A disposal apparatus of excretions, kitchen sewage, and domestic wastewater is provided, which is characterized in that the disposal apparatus is applicable to disposal of excretions, kitchen sewage, and domestic wastewater. And disposal efficiency is high compared with a conventional disposal apparatus, therefore final treated water is reusable. CONSTITUTION: Excretions, kitchen sewage, or domestic wastewater flow into a primary fermentation tank(2) to be fermented under anaerobic or partially aerobic condition. Drained wastewater from the primary fermentation tank(2) flows into a second fermentation tank(4) which has hundreds of thousands of holes(17), and is fermented under aerobic condition. Remained contaminant is adsorbed in an adsorption tank(5). Wood chips of 4-20 diameter are packed in the primary fermentation tank(2) and the second fermentation tank(4) in ratio of 1-20% and 80-100% of fermentation tank volume respectively. Then, final treated water is reusable as grey water.

Description

분뇨, 음식물쓰레기 및 생활하수 처리 장치 및 이를 이용한 분뇨, 음식물쓰레기 및 생활하수 처리 방법{DEVICE FOR TREATMENT OF NIGHT SOIL, FOOD WASTE AND HOUSE SEWAGE AND A METHOD OF TREATING NIGHT SOIL, FOOD WASTE AND HOUSE SEWAGE USING THE DEVICE}DEVICE FOR TREATMENT OF NIGHT SOIL, FOOD WASTE AND HOUSE SEWAGE AND A METHOD OF TREATING NIGHT SOIL, FOOD WASTE AND HOUSE SEWAGE USING THE DEVICE }

본발명은 분뇨, 음식물쓰레기 및 생활하수 처리 장치에 관한 것으로서 보다 상세하게는 분뇨, 씽크대 하부에 부착된 분쇄기에 의해 분쇄된 음식물쓰레기 및 생활하수를 혐기성 및 일부 호기성 조건하에서의 1차 발효조 및 호기성 조건하에서의 2차 발효조를 거쳐 완전 분해시키고, 잔류 성분을 흡착조에서 흡착시켜서 분뇨, 음식물쓰레기 및 생활하수가 완전 분해되어 고형성분이 남지 않도록 처리한 후 얻어진 물을 저장탱크에 저장시키고, 사용자의 조작에 의해 저장탱크에 저장된 물이 변기 세정수 또는 생활용수로서 재활용되는, 분뇨, 음식물쓰레기 및 생활하수 처리 장치 및 이를 이용한 분뇨, 음식물쓰레기 및 생활하수 처리 방법에 관한 것이다.The present invention relates to a manure, food waste and domestic sewage treatment apparatus, and more specifically, to the food waste and living sewage pulverized by the crusher attached to the bottom of the manure, sink base under anaerobic and some aerobic conditions under primary fermentation tank and aerobic conditions Complete decomposition through the secondary fermentation tank, adsorbing the residual components in the adsorption tank to completely remove the manure, food waste and household sewage so that no solid components remain, the water obtained is stored in the storage tank, and operated by the user. The present invention relates to a manure, food waste and domestic sewage treatment apparatus in which water stored in a storage tank is recycled as toilet water or domestic water, and a method for treating manure, food waste and domestic sewage using the same.

종래의 가정용 정화조는 침전분리실 및 여과실 또는 침전분리실, 여과실 및 산화조로 구성되어 있고, 대부분 유입된 분뇨를 단순히 일정시간 체류시켜 고액 분리시킨 후 고체 성분은 모아서 1년에 1회 정도 별도로 폐기시키고, 액체 성분은 혐기성 상태에서 유기물을 제거한 후 처리수를 방류하는 시스템이다.Conventional household septic tank is composed of sedimentation separation chamber and filtration chamber or sedimentation separation chamber, filtration chamber and oxidizing tank, and most of the collected manure is simply stayed for a certain time to separate solid-liquid, and then solid components are collected once a year. The liquid component is discarded and the system removes the organics in the anaerobic state and then discharges the treated water.

이러한 기존의 정화조는 처리 효율이 낮아서 정화조에서 나온 물이 하수도 등에 그대로 흘러 들어갈 경우 환경오염을 유발시킨다는 점, 하수의 재처리 비용이 든다는 점, 모아진 고체성분을 별도로 폐기해야 하므로 2차적인 환경오염 및 비용이 유발된다는 점 등의 문제가 있었다.These conventional septic tanks have low treatment efficiency and cause environmental pollution when water from septic tanks flows into sewage, etc., costs for reprocessing sewage, and the collected solid components have to be disposed of separately. There were problems such as cost incurred.

한편, 사찰, 공원, 캠프장, 하천 부지 등의 옥외 화장실은 대부분 비수세식이라 위생상의 문제가 있고, 수세식으로 만들 경우 세척수의 확보 및 계속적인 세척수의 공급이 곤란하다는 문제점이 있었다.On the other hand, outdoor toilets such as temples, parks, campsites, river sites, etc. are mostly non-flushing, so there is a hygiene problem, and when the flushing is made, it is difficult to secure washing water and continuously supply the washing water.

또한 종래의 음식물쓰레기 처리방법으로는 건조방식과 소각방식이 있었으나In addition, the conventional food waste treatment methods were drying and incineration.

건조방식은 음식물쓰레기를 따로 수집 및 수거해야하는 번거러움이 있고 소각방식은 일부수분 제거를 위한 전처리 공정이 필요하며 소각시 발생하는 2차 대기오염이 발생한다는 문제점이 있었다.The drying method has a problem of collecting and collecting food waste separately, and the incineration method requires a pretreatment process for removing some moisture, and there is a problem that secondary air pollution occurs during incineration.

일본 공개특허공보 제 평10-72858호에는 물의 공급을 필요로 하지 않는 순환식 분뇨 처리 장치가 공지되어 있는 바, 대변기로부터 배설된 대변은 발효조에서 현탁하면서 발효시키고, 대변기 및 소변기로부터의 소변은 별도로 정화조에 회수하여 정화시킨 후, 정화조에서 정화된 소변을 세정수로서 스톡탱크에 저장하여 이를 세정수로서 대변기 및 소변기에 공급하는 장치가 개시되어 있다. 그러나, 이러한 순환식 분뇨 처리 장치는 대변과 소변을 별도로 모아서 소변만을 정화하여 세정수로 재활용하고, 대변은 1차 발효 후 고형물 상태에서 처리해야하는 번거로움이 있다.Japanese Laid-Open Patent Publication No. Hei 10-72858 discloses a circulating manure treatment device that does not require water supply, and feces excreted from the toilet are fermented while suspended in a fermenter, and urine from the toilet and urinal is separately Disclosed is an apparatus for storing urine purified in a septic tank and then purifying the purified urine in a stock tank as washing water and supplying it to the toilet and urinal as washing water. However, the circulatory manure treatment device collects feces and urine separately, purifies only the urine, and recycles the washing water, and the feces have a troublesome treatment in a solid state after the first fermentation.

본발명은 상기와 같은 문제점을 해결하기 위한 것으로서, 가정용 정화조뿐만 아니라 야외용 화장실로서도 사용가능한, 분뇨를 완전 분해하여 고형성분을 재처리할 필요가 없고 정화된 액체 성분을 세정수로서 재순환시킬 뿐만 아니라 음식물쓰레기, 생활 하수도 동시에 처리하여 재활용하는 분뇨, 음식물쓰레기 및 생활하수 처리 장치와 방법을 제공하고자 한다.The present invention is to solve the above problems, and can be used not only for household septic tanks, but also for outdoor toilets, it is not necessary to completely dissolve manure and reprocess the solid components, and to recycle the purified liquid components as washing water as well as food and beverages. To provide a device and method for manure, food waste and domestic sewage treatment, which simultaneously treat and recycle waste and domestic sewage.

제 1도는 본발명에 따른 분뇨, 음식물쓰레기 및 생활하수 처리 장치의 종단면도이다.1 is a longitudinal sectional view of the manure, food waste and domestic sewage treatment apparatus according to the present invention.

제 2도는 본발명에 따른 2차 발효조의 사시도이다.2 is a perspective view of a secondary fermenter according to the present invention.

*도면의 주요 부분에 대한 설명* Description of the main parts of the drawing

1: 변기1: toilet seat

1': 씽크대1 ': Thinkstand

2': 분쇄기2 ': grinder

1'':생활하수관1 '': Life sewer pipe

2: 1차 발효조2: primary fermenter

3: 1차 발효액 분산파이프3: primary fermentation broth dispersion pipe

4: 2차 발효조4: secondary fermenter

5: 흡착조5: adsorption tank

6: 저장 탱크6: storage tank

7: 2차 저장조7: secondary reservoir

8, 9, 10 : 모터8, 9, 10: motor

11, 12, 13, 14, 15, 16: 파이프11, 12, 13, 14, 15, 16: Pipe

17: 통기 구멍17: vent hole

본발명의 첫번째 양상은 변기(1)로부터 이송된 분뇨, 씽크대(1') 하부에 부착된 분쇄기(2')에 의해 분쇄된 음식물쓰레기 및 생활 하수관들(1'')로부터 이송된 생활하수를 수중미생물 존재하에서 기폭시켜 혐기성 및 일부 호기성 조건하에서 발효시키는 1차 발효조(2), 수십만 개의 미세 통기 구멍(17)이 측면에 존재하고, 상부는 공기와 접촉하여 1차 발효조로부터 이송된 1차 발효액을 호기성 조건하에서 발효시키는 2차 발효조(4), 2차 발효조로부터 이송된 2차 발효액 중 잔류 성분을 흡착하는 흡착조(5), 흡착조(5)로부터 이송된 물을 저장하는 저장 탱크(6), 저장 탱크(6)를 변기(1) 및 생활용수용 수도꼭지로 연결시키는 관(15, 16)을 포함하는 분뇨, 음식물쓰레기 및 생활하수 처리 장치이다.The first aspect of the present invention is to collect the manure transported from the toilet 1, the food waste crushed by the crusher 2 ′ attached to the bottom of the sink 1 ′ and the living sewage transported from the living sewers 1 ″. The primary fermentation tank (2), which is aerated in the presence of aquatic microorganisms and fermented under anaerobic and some aerobic conditions, has hundreds of thousands of fine vent holes (17) on its side and the upper fermentation broth transferred from the primary fermentation tank in contact with air. Fermentation tank (4) for fermenting under aerobic conditions, adsorption tank (5) for adsorbing residual components in the secondary fermentation broth transferred from the secondary fermentation tank, and storage tank (6) for storing water transferred from the adsorption tank (5). ), Manure, food waste and household sewage treatment apparatus including pipes (15, 16) connecting the storage tank (6) to the toilet (1) and a faucet for household water.

분쇄기(2')는 씽크대(1') 하부에 부착되어 씽크대에서 수집된 음식물 쓰레기를 잘게 분쇄하는 역할을 한다. 잘게 분쇄된 음식물 쓰레기는 분뇨 및 생활하수와 함께 파이프(11)를 통해 수압에 의해 1차 발효조(2)로 이송된다. 따라서, 본고안에 따른 장치를 사용하면 분뇨를 처리함과 동시에 음식물쓰레기 및 생활하수관으로부터의 각종 유기물 쓰레기도 처리가능하다. 생활하수관들(1'')은 욕실 하수관, 세탁실 하수관 등 가정에서 사용되는 일체의 하수관을 의미한다.The grinder 2 'is attached to the bottom of the sink 1' and serves to finely crush the food waste collected in the sink. The finely ground food waste is transferred to the primary fermentation tank 2 by hydraulic pressure through the pipe 11 together with the manure and domestic sewage. Therefore, by using the apparatus according to the present proposal, it is possible to treat manure and various organic waste from food waste and domestic sewage pipes. Living sewer pipes (1 '') means any sewer pipe used in the home, such as bathroom sewer pipe, laundry room sewer pipe.

1차 발효조(2)는 변기(1), 씽크대(1') 및 생활하수관들(1'')로부터 이송되어진 분뇨, 음식물쓰레기 및 생활하수를 폭기 장치에 의해 폭기시켜 1차 발효시키는 곳이다. 폭기를 위해서는 통상 모터(8)가 사용된다. 분뇨 속의 유기물을 분해하는 미생물로서는 분뇨 자체 및 자연 미생물이 이용된다. 혐기성 및 호기성 미생물이 서식하기 위한 서식처는 외부로부터 공급하는데, 톱밥, 왕겨, 나무 칩(조각) 등 다공막 형성이 가능한 셀룰로스 계통의 재료가 사용된다. 미생물 서식처는 바람직하게는 완전 탈수된 4 - 20 mm 직경의 나무 칩이고, 더욱 바람직하게는 세라믹 로에서 80-100℃에서 35-40시간동안 가열하여 완전 탈수시킨 삼나무 또는 참나무 칩이다. 이러한 나무칩은 미생물의 공급원인 동시에 칩 내부에 무수히 많은 공극이 존재하여 칩의 심부에서는 혐기성 미생물이 생장할 수 있고, 칩의 표면 근처에는 호기성 미생물이 생장할 수 있는 미생물 서식지를 풍부하게 공급하는 역할을 한다. 1차 발효조에 투입하는 나무칩은 1차 발효조 부피의 1-20% 가량을 충진한다. 미생물에 의한 발효를 촉진시키기 위해서는 공기 주입 조건을 적절히 유지하는 것이 중요한데, 공기 주입은 연속 주입식으로 하고 공기 주입 속도는 분당 1차 발효조 부피의 0.3-3.0%로 하는 것이 바람직하다.The primary fermentation tank 2 is a place where the manure, food waste and household sewage transferred from the toilet 1, the sink 1 'and the living sewage pipes 1' 'are aerated by the aeration device for primary fermentation. The motor 8 is usually used for aeration. Manure itself and natural microorganisms are used as microorganisms that decompose organic matter in the manure. Habitats for anaerobic and aerobic microorganisms are supplied from the outside, and cellulosic materials capable of forming porous membranes such as sawdust, rice hulls and wood chips are used. The microbial habitat is preferably 4-20 mm diameter wood chips fully dehydrated, more preferably cedar or oak chips dehydrated by heating at 80-100 ° C. for 35-40 hours in a ceramic furnace. These wood chips are both a source of microorganisms and a myriad of pores inside the chip, which allows anaerobic microorganisms to grow in the deeper parts of the chip, and provides abundant microbial habitats for aerobic microorganisms to grow near the surface of the chip. Do it. Wood chips added to the primary fermenter fill about 1-20% of the volume of the primary fermenter. In order to promote fermentation by microorganisms, it is important to properly maintain the air injection conditions. The air injection is preferably carried out continuously and the air injection rate is preferably 0.3-3.0% of the volume of the primary fermenter per minute.

2차 발효조(4)는 1차 발효조로부터 파이프(12)를 통해 모터(10)에 의해 이송된 1차 발효액을 호기성 조건하에서 발효시키는 곳이다. 2차 발효조(4)는 호기성 조건을 만들기 위해 외부 공기와 접촉할 수 있는 특수한 구조를 가지는 데, 즉 상부는 외부 공기와 접촉할 수 있도록 개방되어 있고, 측면에는 수십만 개의 미세 통기 구멍(17)이 존재하여 충분한 공기가 2차 발효조(2) 내로 공급된다. 1차 발효조(2)에서는 밀폐된 환경 하에서 혐기성 미생물이 호기성 미생물보다 우세하게 작용한 반면, 2차 발효조(2)에서는 공기와 충분히 접촉할 수 있는 환경을 제공함으로써 호기성 미생물이 혐기성 미생물보다 우세하게 작용하여 결국 분뇨가 1차 발효조(2) 및 2차 발효조(4)를 거치는 동안 혐기성 미생물 및 호기성 미생물 모두에 의해 충분히 발효됨으로써 고형 유기물의 완전 분해가 가능해진다. 1차 발효조에서와 마찬가지로 바람직하게는 미생물 공급원 및 미생물 서식지로서 완전 탈수된 4 - 20 mm 직경의 나무칩을 사용하고, 나무칩을 2차 발효조(4)에 발효조 부피의 80-100 %만큼 충진한다. 2차 발효조(4) 내에서는 별도의 기폭 없이 1차 발효조에서 공급된 발효액을 1차 발효액 분산파이프(3)에 의해 분산하고 중력에 의한 자유낙하로 나무칩 사이를 통과하며 피처리물 중의 유기물, 고형물을 완전히 분해시킨다.The secondary fermentation tank 4 is a place where the primary fermentation broth transferred by the motor 10 from the primary fermentation tank through the pipe 12 is fermented under aerobic conditions. The secondary fermenter 4 has a special structure that can be in contact with the outside air to create aerobic conditions, i.e. the top is open for contact with the outside air, with hundreds of thousands of fine vent holes 17 on the side. Present and sufficient air is supplied into the secondary fermenter 2. In the primary fermentation tank (2), anaerobic microorganisms dominate the aerobic microorganisms in an enclosed environment, while in the secondary fermentation tank (2), the aerobic microorganisms dominate the anaerobic microorganisms by providing an environment in which the air can be sufficiently contacted. Thus, the manure is sufficiently fermented by both anaerobic and aerobic microorganisms while the manure passes through the primary fermentation tank 2 and the secondary fermentation tank 4, thereby enabling complete decomposition of the solid organic matter. As in the primary fermenter, preferably 4 to 20 mm diameter wood chips completely dehydrated as microbial source and microbial habitat, and the wood chips are charged to the secondary fermenter 4 by 80-100% of the volume of the fermenter. . In the secondary fermentation tank 4, the fermentation broth supplied from the primary fermentation tank is dispersed by the primary fermentation broth dispersion pipe 3 without passing through the primary fermentation broth and passed between the wood chips by free fall due to gravity. Decompose the solid completely.

미생물 공급원 및 서식지의 역할을 하는 나무 칩은 거의 반영구적이나, 야외 화장실에 사용되는 경우 겨울에 분뇨량이 감소하여 유기물이 부족한 관계로 나무칩이 자체 분해될 수 있으므로 1년에 1회 정도 5-10%의 나무칩을 보충해준다.Wood chips, which serve as microbial sources and habitats, are almost semi-permanent, but when used in outdoor toilets, the amount of manure is reduced in winter, and wood chips can decompose themselves due to lack of organic matter. Replenish your wood chips.

2차 발효조(4)에서 생성된 물은 파이프(13)을 통해 흡착조(5)로 이송된다. 흡착조(5)에는 흡착제가 충진되어 있어서 2차 발효 후 생성된 물에 잔류한 유기 및 무기 성분을 흡착한다. 흡착제로는 활성탄이 주로 사용된다. 흡착조를 통과시킴으로써, 세정수 중의 나쁜 냄새, 색깔 등이 완전히 제거되어 세정수로서 재이용이 가능해진다.The water produced in the secondary fermentation tank 4 is transferred to the adsorption tank 5 through the pipe 13. The adsorption tank 5 is filled with an adsorbent to adsorb organic and inorganic components remaining in the water produced after the secondary fermentation. Activated carbon is mainly used as the adsorbent. By passing through the adsorption tank, bad odors, colors, etc. in the washing water are completely removed and can be reused as the washing water.

흡착조(5)를 거쳐 완전히 정화된 물은 파이프(14)를 통해 펌프(8)에 의해 저장 탱크(6)에 저장된다. 저장 탱크(6)는 파이프(15, 16)를 통해서 변기(1) 및 생활용수용 수도꼭지에 연결되어 있어서, 사용자의 조작시 저장탱크에 저장되어 있던 물이 변기 세정수 또는 생활용수로서 재활용된다.The completely purified water via the adsorption tank 5 is stored in the storage tank 6 by the pump 8 via the pipe 14. The storage tank 6 is connected to the toilet bowl 1 and the faucet for living water through the pipes 15 and 16, so that the water stored in the storage tank at the time of the user's operation is recycled as the toilet washing water or the living water.

생활용수란, 식수 외에 정원용, 세차용, 세탁기용 용수 등을 의미한다. 생활용수로서의 재활용이 여의치 않은 경우, 변기 세정수로서 재활용되는 물 이외의 잉여 용수는 하수관으로 방류시킬 수도 있다.Living water means water for gardening, washing, washing machines, etc. in addition to drinking water. If recycling as household water is not feasible, excess water other than the water recycled as toilet flushing water may be discharged to sewage pipes.

본발명의 두번째 양상은 변기(1)로부터 이송된 분뇨, 씽크대(1') 하부에 부착된 분쇄기(2')에 의해 분쇄된 음식물쓰레기 및 생활 하수관들(1'')로부터 이송된 생활하수를, 분당 1차발효조 부피의 0.3-3.0%의 속도로 공기를 연속식으로 주입하면서 1차 발효조(2)내에서 혐기성 조건하에서 1차 발효시키는 단계; 1차 발효조(2)로부터 이송된 1차 발효액을 2차 발효조(4) 내에 분산파이프(3)에 의해 분산하고 중력에 의한 자유낙하로 나무칩 사이를 통과하며 피처리물 중의 유기물, 고형물을 완전히 2차 발효시키는 단계; 2차 발효 후 생성된 물을 흡착조(5)를 통해 통과시켜 잔류물질을 흡착시키는 단계; 얻어진 물을 저장 탱크(6)에 저장하는 단계; 및 사용자의 조작시 저장 탱크에 저장된 물이 변기용 세정수 및 생활용수로 재활용되는 단계를 포함하는 분뇨, 음식물쓰레기 및 생활하수 처리 방법이다.The second aspect of the present invention is the sewage conveyed from the toilet 1, the food waste crushed by the crusher 2 'attached to the bottom of the sink 1' and the living sewage conveyed from the living sewers 1 ''. Primary fermentation under anaerobic conditions in the primary fermenter (2) while continuously injecting air at a rate of 0.3-3.0% of the volume of the primary fermentation tank per minute; The primary fermentation broth transferred from the primary fermentation tank (2) is dispersed in the secondary fermentation tank (4) by the dispersion pipe (3) and passed between the wood chips by free fall by gravity, and completely removes organic matter and solids in the object to be treated. Secondary fermentation; Passing water generated after the second fermentation through the adsorption tank 5 to adsorb the residual material; Storing the obtained water in the storage tank 6; And the manure, food waste and household sewage treatment method comprising the step of recycling the water stored in the storage tank to the toilet water and the domestic water during the operation of the user.

본발명에 따른 분뇨 처리 방법에 사용되는 1차 발효조(2), 2차 발효조(4) 및 1차 발효조(2) 및 2차 발효조(4) 내에 미생물 서식처로서 외부에서 제공하는 재료는 상기한 장치에 대해 기술된 바와 같아서 이에 대한 상세한 기재를 생략한다.Materials externally provided as a microbial habitat in the primary fermentation tank (2), the secondary fermentation tank (4) and the primary fermentation tank (2) and the secondary fermentation tank (4) used in the method of treating manure according to the present invention are described above. As described for, the detailed description thereof is omitted.

본발명에 따른 가정용 분뇨 및 생활하수 처리 장치를 실제 크기로 제작하여 가정에 설치한 뒤 6개월간 운전하여, 7일 간격으로 현탁물질, BOD 및 COD를 측정한 결과, 평균값은 아래와 같았다.Household manure and domestic sewage treatment apparatus according to the present invention was manufactured in actual size, installed in home, and operated for 6 months, and the suspended substances, BOD and COD were measured every 7 days. The average value was as follows.

원수(原水)Raw water 처리수Treated water 처리효율(%)Processing efficiency (%) 현탁물질(mg/ℓ)Suspension (mg / ℓ) 17751775 33 99.899.8 CODMn(mgO/ℓ)COD Mn (mgO / ℓ) 507507 1313 97.497.4 BOD5(mgO/ℓ)BOD 5 (mgO / ℓ) 618618 66 99.099.0

실험 결과, 본발명에 따른 분뇨, 음식물쓰레기 및 생활하수 처리 장치로 분뇨, 음식물쓰레기 및 생활하수를 처리할 경우, 원수 중의 각종 물질이 거의 완전히 분해되어 처리되므로 이를 다시 변기용 세정수 및 생활용수로 사용하여도 손색이 없음을 알 수 있다.As a result of the experiment, when manure, food waste and household sewage treatment device according to the present invention is treated with manure, food waste and household sewage, various substances in raw water are almost completely decomposed and used again as washing water for toilet and living water. It can be seen that there is no inferiority.

상기한 바와 같이 본발명에 따른 분뇨, 음식물쓰레기 및 생활하수 처리 장치는 다음과 같은 장점을 갖는다.As described above, the manure, food waste and sewage treatment apparatus according to the present invention has the following advantages.

첫째, 분뇨, 음식물쓰레기 및 생활하수 중의 고형 성분 및 액체 성분이 모두 액체 및 기체로 완전 분해되어 이것이 세정수로서 재활용되기 때문에 재처리해야할 고형성분이 없고, 따라서 매우 위생적이며 무공해이다.First, there are no solid components to be reprocessed because the solid and liquid components in the manure, food waste and domestic sewage are all completely decomposed into liquids and gases and are recycled as washing water, thus being very hygienic and pollution free.

둘째, 설치가 간편하고 짧은 시간 내에 설치할 수 있다.Second, installation is easy and can be installed in a short time.

셋째, 변기 수세를 위한 세정수를 계속적으로 공급할 필요없이 이를 재순환시켜 세정수로 사용하므로 물을 보충할 필요가 없어서 유지 비용이 적게 든다.Third, since it is recycled and used as the washing water without continuously supplying the washing water for flushing the toilet, there is no need to replenish water, thus reducing the maintenance cost.

넷째, 일반 가정뿐만 아니라, 산간지 등 세척수 공급 및 배수가 곤란한 지역에서도 본발명에 따른 장치를 수세식 화장실로서 쓸 수 있다.Fourth, the device according to the present invention can be used as a flush toilet in a region where it is difficult to supply and drain the washing water, such as mountainous land, as well as a general home.

다섯째, 발효조 내의 미생물 서식지인 나무칩을 1년에 1회 5-10% 공급하는 점외에는 반영구적으로 본 장치를 사용할 수 있다.Fifth, the device can be used semi-permanently except for supplying 5-10% of the wood chips, which are microbial habitats in the fermenter, once a year.

여섯째, 분뇨뿐만 아니라 음식물쓰레기 및 생활하수관으로부터의 생활하수를 본발명에 따른 장치를 이용하여 동시에 처리할 수 있다.Sixth, the living sewage from food waste and living sewage pipes as well as manure can be treated at the same time using the device according to the present invention.

Claims (5)

변기(1)로부터 이송된 분뇨, 씽크대(1') 하부에 부착된 분쇄기(2')에 의해 분쇄된 음식물쓰레기 및 생활 하수관들(1'')로부터 이송된 생활하수를 수중미생물 존재 하에서 기폭시켜 혐기성 및 일부 호기성 조건하에서 발효시키는 1차 발효조(2), 수십만 개의 미세 통기 구멍(17)이 측면에 존재하고, 상부는 공기와 접촉하여 1차 발효조로부터 이송된 1차 발효액을 호기성 조건하에서 발효시키는 2차 발효조(4), 2차 발효조로부터 이송된 2차 발효액 중 잔류 성분을 흡착하는 흡착조(5), 흡착조(5)로부터 이송된 물을 저장하는 저장 탱크(6), 저장 탱크(6)를 변기(1) 및 생활용수용 수도꼭지로 연결시키는 관(15, 16)을 포함하는 분뇨, 음식물쓰레기 및 생활하수 처리 장치.The manure transferred from the toilet 1, the food waste crushed by the grinder 2 'attached to the sink 1' and the living sewage transferred from the living sewers 1 '' are detonated in the presence of aquatic microorganisms. Primary fermentation tank (2) fermented under anaerobic and some aerobic conditions, hundreds of thousands of micro vent holes (17) are present on the side, and the upper part is in contact with air to ferment the primary fermentation broth transferred from the primary fermentation tank under aerobic conditions Secondary fermentation tank (4), adsorption tank (5) for adsorbing residual components in the secondary fermentation broth transferred from the secondary fermentation tank, storage tank (6) for storing water transferred from the adsorption tank (5), storage tank (6) ), Manure, food waste and household sewage treatment apparatus comprising a pipe (15, 16) connecting the toilet (1) and a faucet for household water. 제 1항에 있어서, 1차 발효조 및 2차 발효조 내에, 완전 탈수된 직경 4 - 20 mm의 나무 칩이 발효조 부피의 1-20%만큼 포함되어 있는 장치.2. The apparatus of claim 1 wherein the primary and secondary fermentors contain completely dehydrated wood chips of diameter 4-20 mm by 1-20% of the volume of the fermentor. 제 2항에 있어서, 나무 칩은 삼나무 또는 참나무 칩인 장치.The device of claim 2, wherein the wood chips are cedar or oak chips. 제 3항에 있어서, 나무 칩은 나무를 세라믹 로 내에서 80-100℃에서 35-40시간동안 가열하여 완전 탈수시킨 칩인 장치.4. The device of claim 3, wherein the wood chips are chips that have been completely dehydrated by heating wood in a ceramic furnace at 80-100 ° C. for 35-40 hours. 변기(1)로부터 이송된 분뇨, 씽크대(1') 하부에 부착된 분쇄기(2')에 의해 분쇄된 음식물쓰레기 및 생활 하수관들(1'')로부터 이송된 생활하수를, 분당 1차 발효조 부피의 0.3-3.0%의 속도로 공기를 연속식으로 주입하면서 1차 발효조(2)내에서 혐기성 조건하에서 1차 발효시키는 단계; 1차 발효조(2)로부터 이송된 1차 발효액을 2차 발효조(4) 내에 분산파이프(3)에 의해 분산하고 중력에 의한 자유낙하로 나무칩 사이를 통과하며 피처리물 중의 유기물, 고형물을 완전히 2차 발효시키는 단계; 2차 발효 후 생성된 물을 흡착조(5)를 통해 통과시켜 잔류물질을 흡착시키는 단계; 얻어진 물을 저장 탱크(6)에 저장하는 단계; 및 사용자의 조작시 저장 탱크에 저장된 물이 변기용 세정수 및 생활용수로 재활용되는 단계를 포함하는 분뇨, 음식물쓰레기 및 생활하수 처리 방법.The primary fermenter volume per minute was collected from the manure transferred from the toilet 1, the food waste crushed by the grinder 2 'attached to the bottom of the sink 1', and the living sewage transferred from the living sewers 1 ''. Primary fermentation under anaerobic conditions in the primary fermenter (2) while continuously injecting air at a rate of 0.3-3.0% of the; The primary fermentation broth transferred from the primary fermentation tank (2) is dispersed in the secondary fermentation tank (4) by the dispersion pipe (3) and passed between the wood chips by free fall by gravity, and completely removes organic matter and solids in the object to be treated. Secondary fermentation; Passing water generated after the second fermentation through the adsorption tank 5 to adsorb the residual material; Storing the obtained water in the storage tank 6; And recycling the water stored in the storage tank to the toilet water and the household water during the operation of the user.
KR1020000032344A 2000-06-13 2000-06-13 Device for treatment of night soil, food waste and house sewage and a method of treating night soil, food waste and house sewage using the device KR20000054588A (en)

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KR1020000032344A KR20000054588A (en) 2000-06-13 2000-06-13 Device for treatment of night soil, food waste and house sewage and a method of treating night soil, food waste and house sewage using the device
CN01221365U CN2547726Y (en) 2000-06-13 2001-06-08 Device for treating feces, kitchen sewage, and domestic sewage
CNB011211199A CN1171810C (en) 2000-06-13 2001-06-08 Device and method for treating feces, kitchen sewage and domestic sewage

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KR100431222B1 (en) * 2001-07-05 2004-05-12 (주) 하나환경 Sewage/waste water purging system form circulate
KR100907480B1 (en) * 2007-04-03 2009-07-13 강호철 Sewage disposal system
KR101156466B1 (en) * 2012-04-13 2012-06-18 주식회사 에코멤브레인 Cattle-circulation treating method of livestock excretions and its environmentaliy purifying method
CN105036836A (en) * 2015-06-12 2015-11-11 许道军 Farm liquid manure treatment system and method
KR101999269B1 (en) * 2018-09-28 2019-10-02 한국토지주택공사 Waste resource smart recycling integrated management system
KR102043181B1 (en) * 2018-09-28 2019-12-02 한국토지주택공사 Organic wast smart recycling system
KR20230143336A (en) 2022-04-05 2023-10-12 주식회사 삼보기술단 Pre-treatment equipment for direct inputting of domestic wastewater and excrements, and method for the same

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Publication number Priority date Publication date Assignee Title
KR100431222B1 (en) * 2001-07-05 2004-05-12 (주) 하나환경 Sewage/waste water purging system form circulate
KR100907480B1 (en) * 2007-04-03 2009-07-13 강호철 Sewage disposal system
KR101156466B1 (en) * 2012-04-13 2012-06-18 주식회사 에코멤브레인 Cattle-circulation treating method of livestock excretions and its environmentaliy purifying method
CN105036836A (en) * 2015-06-12 2015-11-11 许道军 Farm liquid manure treatment system and method
KR101999269B1 (en) * 2018-09-28 2019-10-02 한국토지주택공사 Waste resource smart recycling integrated management system
KR102043181B1 (en) * 2018-09-28 2019-12-02 한국토지주택공사 Organic wast smart recycling system
WO2020067853A1 (en) * 2018-09-28 2020-04-02 한국토지주택공사 Smart recycling integrated management system for waste resources
KR20230143336A (en) 2022-04-05 2023-10-12 주식회사 삼보기술단 Pre-treatment equipment for direct inputting of domestic wastewater and excrements, and method for the same

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CN2547726Y (en) 2003-04-30
CN1171810C (en) 2004-10-20

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