KR101054613B1 - Apparatus for waste water single reactor composed of biological and membrane process - Google Patents

Apparatus for waste water single reactor composed of biological and membrane process Download PDF

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KR101054613B1
KR101054613B1 KR20110017112A KR20110017112A KR101054613B1 KR 101054613 B1 KR101054613 B1 KR 101054613B1 KR 20110017112 A KR20110017112 A KR 20110017112A KR 20110017112 A KR20110017112 A KR 20110017112A KR 101054613 B1 KR101054613 B1 KR 101054613B1
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wastewater
tank
membrane
microorganisms
water
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임범관
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임범관
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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
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/02Reverse osmosis; Hyperfiltration ; Nanofiltration
    • B01D61/025Reverse osmosis; Hyperfiltration
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/14Ultrafiltration; Microfiltration
    • B01D61/145Ultrafiltration
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/14Ultrafiltration; Microfiltration
    • B01D61/147Microfiltration
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D65/00Accessories or auxiliary operations, in general, for separation processes or apparatus using semi-permeable membranes
    • B01D65/02Membrane cleaning or sterilisation ; Membrane regeneration
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D65/00Accessories or auxiliary operations, in general, for separation processes or apparatus using semi-permeable membranes
    • B01D65/08Prevention of membrane fouling or of concentration polarisation
    • 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
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/441Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
    • 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
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/444Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by ultrafiltration or microfiltration
    • 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
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/78Treatment of water, waste water, or sewage by oxidation with ozone
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/06Aerobic processes using submerged filters
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/78Details relating to ozone treatment devices
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/24Separation of coarse particles, e.g. by using sieves or screens
    • 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
    • Y02W10/10Biological treatment of water, waste water, or sewage

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  • Engineering & Computer Science (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Nanotechnology (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Microbiology (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

PURPOSE: An apparatus for generating recycled water based on sewage and wastewater is provided to process plenty of wastewater using simple facilities equipped in a single reacting bath. CONSTITUTION: A biological processing bath(20) extends the residence time of microorganism. A filtering bath(30) filters inorganic materials which are non-processed in the biological processing bath using a microfiltration(MF) membrane and an ultrafiltration(UF) membrane(31). An air supplying pipe aerates air to grow microorganism. A reversible washing unit(33) detaches the microorganism from the surface of the MF membrane and the UF membrane. An advanced processing part(40) advancingly processes target water using a reverse osmosis membrane.

Description

생물처리공정과 막분리공정이 결합된 단일반응조를 이용한 하폐수 재활용수 생산장치 {APPARATUS FOR WASTE WATER SINGLE REACTOR COMPOSED OF BIOLOGICAL AND MEMBRANE PROCESS}Wastewater Recycling Water Production System Using Single Reactor Combining Biotreatment Process and Membrane Separation Process {APPARATUS FOR WASTE WATER SINGLE REACTOR COMPOSED OF BIOLOGICAL AND MEMBRANE PROCESS}

본 발명은 생물처리공정과 막분리 공정이 결합된 단일반응조를 이용한 하폐수의 처리장치 및 방법에 관한 것으로, 더욱 상세하게는 하폐수 처리과정을 거친 후 방류되는 물(이하 방류수)을 여과 및 고도처리부를 이용하여 재활용 할 수 있는 장치 및 방법에 관한 것이다.The present invention relates to an apparatus and method for treating sewage water using a single reaction tank in which a biological treatment process and a membrane separation process are combined. More particularly, the present invention provides a filtration and advanced treatment unit for filtering water discharged after the wastewater treatment process (hereinafter, referred to as effluent). It relates to a device and a method that can be recycled using.

일반적인 오수, 하수 및 폐수처리 시설에서 방류되는 방류수를 재활용하기 위한 방법은 오존처리방법, 막분리방법, 활성탄처리방법, 고도산화방법 등으로 구분된다.
Methods for recycling effluent discharged from general sewage, sewage and wastewater treatment facilities are classified into ozone treatment method, membrane separation method, activated carbon treatment method and advanced oxidation method.

오존산화방법은 오존을 폐수 속에 용해시켜 폐수 속에 포함되어 있는 분자성 유기화합물을 분해시키는 방법으로서, THM(Trihalomethane) 전구물질이나 색도 또는 냄새물질 제거에 효과적이며, 또한 오존은 살균효과도 우수하여 처리수의 모든 세균을 사멸시키며, 염소 살균시 발생될 수 있는 THM 등의 염소계 유기화합물 등을 생성치 않는 장점이 있으나 오존발생기가 고가이고 오존에 의한 유기화합물 분해가 선택적이라는 단점이 있다.
The ozone oxidation method is a method of dissolving ozone in wastewater to decompose molecular organic compounds contained in wastewater. It is effective in removing THM (trihalomethane) precursors, color or odorous substances, and ozone has excellent sterilization effect. It kills all bacteria of water and does not produce chlorine-based organic compounds such as THM that can be generated during chlorine sterilization. However, ozone generators are expensive and decomposition of organic compounds by ozone is selective.

막분리방법은 반투과성 고분자 막을 이용하여 여과에 의해 오염물질을 제거시키는 방법으로서 공업용수의 탈염을 위한 RO(역삼투여과)를 중심으로 개발되어 졌으며, 선진국에서는 점차 강화되고 있는 폐수처리 기준과 상수처리 기준에 적합하게 하기 위한 방법으로서 수처리 공정으로 MF, UF, RO, NF 등의 적용가능성을 개발하고 있다. 그러나 국내에서는 막 방법이 정수처리 기술로 MF, UF, RO 와 활성탄을 조합한 가정용 정수기에 사용되고 있을 뿐, 폐수 및 정수의 대량처리를 위한 방법으로는 고가의 시설 투자비 등으로 인해 실용화가 적은 편이다.Membrane separation method is a method of removing contaminants by filtration using semi-permeable polymer membrane. It was developed around RO (reverse osmosis filtration) for desalination of industrial water.In developed countries, wastewater treatment standards and water treatment standards are gradually strengthening. Applicability of MF, UF, RO, NF, etc. to the water treatment process is being developed as a method for making it suitable for the process. However, in Korea, membrane method is used for domestic water purifier combining MF, UF, RO and activated carbon as water treatment technology, and it is not practical to use due to expensive facility investment cost for mass treatment of waste water and purified water. .

또한 여과된 슬러지는 유기물 함량이 높을 뿐만 아니라 해양투기가 금지되어 있으므로 슬러지내 유기물 처리 및 부피 감소 등과 같은 재처리가 필요한 실정이다.
In addition, the filtered sludge is not only high organic matter content, but also because the ocean dumping is prohibited, there is a need for reprocessing such as organic matter treatment and volume reduction in the sludge.

활성탄처리방법은 다공성의 활성탄으로 원수에 포함된 미량의 흡착 가능한 유기화합물을 흡착시켜 제거하는 방법으로서, 정수처리에는 오염물질이 미량이기 때문에 활성탄 처리가 가능하지만 폐수는 분자성 유기화합물과 무기화합물이 많이 포함하고 있기 때문에 처리시설의 용량이 커지고, 활성탄 교환주기가 짧다는 단점이 있어 폐수 처리에는 거의 사용치 않고 있다.
Activated carbon treatment is a porous activated carbon that removes and adsorbs trace amounts of adsorbable organic compounds in raw water. Because it contains a lot of capacity, the capacity of the treatment facility is large, and the activated carbon exchange cycle is short, so it is rarely used for wastewater treatment.

고도처리방법은 오존, 과산화수소, 자외선, 철염, 이산화티탄과 같은 화학물질을 단독으로 사용하여 산화력이 큰 OH 라디칼을 생성시키거나, 과량의 OH라디칼을 오존/높은 pH(Ozone/high pH), 오존/과산화수소(Ozone/Hydrogen Peroxide), 오존/UV(Ozone/UV), 과산화수소/UV(Hydrogen Peroxide/UV) 등의 병합 방법으로 생성시켜 폐수 속의 분자성 유기화합물을 이산화탄소와 물로 완전 분해시키는 방법이다. Advanced treatment uses ozone, hydrogen peroxide, ultraviolet rays, iron salts, and titanium dioxide alone to produce highly oxidizing OH radicals, or to remove excess OH radicals in ozone / high pH and ozone. / Ozone / Hydrogen Peroxide, Ozone / UV, Hydrogen Peroxide / UV are produced by the combined method to completely decompose molecular organic compounds in waste water into carbon dioxide and water.

그러나 단독처리 방법은 폐수 속에 포함되어 있는 분자성 유기화합물을 분해시킬 수 있는 충분한 양의 OH라디칼 생성이 어렵거나, 또는 많은 유기화합물과 선택적으로 반응하여 처리효율이 낮아지는 단점 등으로 완벽한 폐수처리를 위해서는 과량의 화학물질을 주입해야하므로, 높은 초기투자비와 운영관리비가 요구된다. 또한, 병합처리 방법은 단독처리 방법보다 소규모 처리시설에서는 처리효율이 좋으나, 대규모 용량을 처리할 경우에는 초기투자비의 상승, 높은 유지 관리비, 처리효율의 문제점 등의 이유로 일부분만 실용화되고 있다.
However, the single treatment method is difficult to produce a sufficient amount of OH radicals to decompose the molecular organic compounds contained in the wastewater, or it can react with a large number of organic compounds to reduce the treatment efficiency. In order to inject excessive chemicals, high initial investment and operation and management costs are required. In addition, the combined treatment method has better treatment efficiency in a small treatment facility than a single treatment method, but when a large capacity is processed, only a part of the combined treatment method has been put to practical use due to an increase in initial investment cost, high maintenance cost, and problems of treatment efficiency.

전술한 막분리방법을 이용한 농축수의 재처리 방법에 대한 기술을 살펴보면 등록실용신안공보 20-265754를 들 수 있는 데, 상기 문헌은 수도와 직결되어 공급된 공급수가 역삼투압 정수기의 전처리필터를 통과하고 멤브레인을 거쳐 정수될 때, 멤브레인을 통과하지 못하고 버려지는 농축수가 배출되도록 하는 드레인관과; 상기 드레인관으로부터 배출된 농축수를 저장하며, 맨홀·오버플로우밸브·급수 및 차단밸브·배수밸브로 이루어져 농축수가 급수되도록 하는 농축수 저수조와; 상기 농축수 저수조의 급수밸브에서 급수되는 농축수를 생활용수로 재활용하여 사용하도록 각 층 및 각 구획에 설치되는 공급관로로 구성되어 멤브레인을 통과하지 못하고 배출되는 농축수를 집수하여 생활용수로 재활용할 수 있을 뿐만 아니라 생활용수로 쓰일 수 있는 농축수를 재필터링하지 않고 재활용함으로써 멤브레인의 수명을 연장할 수 있는 효과가 있다.
Looking at the technique for the reprocessing of the concentrated water using the membrane separation method described above can be registered Utility Model Publication No. 20-265754, the document is supplied directly connected to the water supplied through the pre-filter of the reverse osmosis water purifier And when the water is purified through the membrane, the drain pipe to discharge the concentrated water that can not pass through the membrane; A concentrated water reservoir configured to store concentrated water discharged from the drain pipe, the concentrated water being composed of a manhole, an overflow valve, a water supply, a shutoff valve, and a drain valve; It is composed of supply pipes installed in each layer and each compartment to recycle and use the concentrated water supplied from the water supply valve of the concentrated water reservoir as living water so that the concentrated water discharged without passing through the membrane can be collected and recycled into the domestic water. In addition, there is an effect that can extend the life of the membrane by recycling the concentrated water can be used as domestic water without re-filtering.

그러나 상기 문헌은 하폐수를 효과적으로 처리하여 재활용하는 시스템이라기보다는 저장조, 밸브, 드레인 등 일반적인 시설을 적절히 재배치하여 하폐수를 여과하는 장치에 해당된다. 따라서 여과되는 정도가 미미하여 이를 직접적인 생활용수나 산업용수에 사용하기에는 한계가 있다. 이에 본 발명자들은 하폐수를 보다 효과적으로 해결하기 위하여 연구에 연구를 거듭한 결과 단일반응조와 오존산화법을 응용하여 본 발명을 완성하기에 이르렀다.However, the document is not a system for effectively treating and recycling sewage water, but rather a device for filtering waste water by rearranging a general facility such as a storage tank, a valve, and a drain properly. Therefore, the degree of filtration is insignificant and there is a limit to use it for direct living water or industrial water. Accordingly, the present inventors have conducted studies to solve the wastewater more effectively, and have completed the present invention by applying a single reactor and ozone oxidation method.

등록실용신안공보 20-265754, 공개특허공보 10-2010-113312Utility Model Registration 20-265754, Published Patent Publication 10-2010-113312

없음.none.

따라서, 본 발명은 상기와 같은 통상적인 하폐수 고도처리 및 재활용수로 이용하기 위한 장치의 문제점을 해소하기 위해서 안출된 것으로서, 대용량의 폐수까지 처리할 수 있으며, 직접적인 생활용수나 산업용수에 사용하기에 적합할 정도의 정화수준을 나타내며, 초기투자비 및 유지관리비가 저렴하면서도 효과적인 하폐수 고도처리장치를 제공하기 위한 것이다.Therefore, the present invention has been made in order to solve the problems of the conventional apparatus for use as advanced wastewater treatment and recycled water, it is possible to treat a large amount of wastewater, it is suitable for use in direct domestic or industrial water In order to provide an effective level of purification and wastewater treatment, the initial investment and maintenance costs are low.

본 발명자들은 상기의 목적을 달성하기 위하여 단일반응조와 오존처리부를 이용하여 하폐수를 처리하는 시스템 및 이를 이용한 농축수를 재활용하는 방법을 개발하게 되었다.In order to achieve the above object, the present inventors have developed a system for treating sewage water using a single reactor and an ozone treatment unit and a method for recycling concentrated water using the same.

상기한 과제를 해결하기 위하여 본 발명은
스크린조(10)를 거쳐 유입된 하폐수를 효과적으로 재활용하기 위한 하폐수 재활용수 생산장치에 있어서,
상기 하폐수 재활용수 생산장치는 단일반응조와; 고도처리부(40)로 구성되며,
상기 단일반응조는
유입된 하폐수의 유기물질, 질소를 미생물을 사용하여 분해 제거하기 위하여 미생물의 체류시간을 장기화시켜 미생물이 지수성장단계를 지나 내생단계로 운전되는 생물처리조(20)와;
상기 생물처리조에서 제거되지 않은 무기물을 MF 또는 UF막을 통해 여과시키는 위한 여과조(30)로 구성되어 있고,
상기 여과조는 MF 또는 UF막(31)을 통해 고액분리로 미생물 농도를 대량으로 유지할 수 있는 침전기능과; 콜로이드성 물질을 여과하는 여과기능과; 0.45㎛ 공극에 의해 병원성 미생물을 제거하는 소독기능을 수행하고,
상기 여과조의 하부에는 하부에 공기공급관(32) 및 역세장치(33)가 부착되어 있어, 상기 공기공급관(32)을 통해 산소가 폭기되어 미생물의 생장을 촉진시키고, 미생물이 과도할 경우 상기 역세장치(33)를 이용하여 MF 또는 UF막(31)표면에 부착된 미생물을 탈착시키도록 운전되며,
The present invention to solve the above problems
In the wastewater recycling water production apparatus for effectively recycling the wastewater introduced through the screen tank (10),
The wastewater recycling water production apparatus includes a single reactor; It is composed of an advanced processing unit 40,
The single reactor
A biological treatment tank 20 in which microorganisms are operated in an endogenous stage after exponential growth by prolonging the retention time of the microorganisms in order to decompose and remove the organic material and nitrogen of the introduced wastewater using microorganisms;
It consists of a filtration tank 30 for filtering the inorganic material not removed from the biological treatment tank through the MF or UF membrane,
The filtration tank has a precipitation function capable of maintaining a large amount of microorganism concentration by solid-liquid separation through the MF or UF membrane 31; A filtration function for filtering the colloidal substance; It performs a disinfection function to remove pathogenic microorganisms by 0.45㎛ pore,
An air supply pipe 32 and a backwashing device 33 are attached to a lower portion of the filtration tank so that oxygen is aerated through the air supply pipe 32 to promote the growth of microorganisms, and when the microorganisms are excessive, the backwashing device (33) is used to desorb microorganisms attached to the surface of the MF or UF membrane 31,

상기 고도처리부(40)는 단일반응조에서 여과된 처리수를 RO막(41)을 이용하여 고도처리하여 이를 재활용할 수 있도록 운전되는 것을 특징으로 한 하폐수 재활용수 생산장치를 과제 해결을 위한 수단으로 제공한다.
또한 본 발명은 상기한 과제를 보다 효과적으로 해결하기 위하여
The advanced treatment unit 40 is a high-treatment process using the RO membrane 41 to filter the treated water filtered in a single reactor to provide a wastewater recycled water production apparatus characterized in that it is operated as a means for solving the problem. do.
In addition, the present invention to solve the above problems more effectively

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상기 고도처리부는 RO막을 이용하여 여과시킨 농축수에 오존을 50~150ppm으로 30분~90분간 주입시켜 고도처리하는 것을 특징으로 한 하폐수 재활용수 생산장치를 제공하고,
마지막으로 본 발명에서는
스크린조(10)를 거친 하폐수를 생물처리조(20)와 여과조(30)로 구성된 단일반응조의 생물처리조(20)로 유입시키는 단계와;
생물처리조(20)에 유입된 하폐수에 포함된 유기물질을 내생단계로 존재하는 미생물을 이용하여 분해하여 제거시키는 단계와;
상기 유기물질이 제거된 하폐수를 MF 또는 UF막(31)이 부착된 여과조(30)로 이송하여 무기물 및 콜로이드성 물질을 여과시키는 단계와;
상기 여과조(30)에서 무기물 및 콜로이드성 물질이 여과된 하폐수를 RO막(41)이 부착된 고도처리부(40)로 이송하여 여과시켜 RO농축수를 생성시키는 단계와;
The advanced processing unit provides a wastewater recycled water production apparatus, characterized in that the advanced treatment by injecting ozone into the concentrated water filtered using RO membrane at 50 ~ 150ppm 30 minutes ~ 90 minutes,
Finally, in the present invention
Introducing the wastewater having passed through the screen tank (10) into the biological treatment tank (20) of a single reaction tank consisting of the biological treatment tank (20) and the filtration tank (30);
Decomposing and removing the organic materials contained in the wastewater introduced into the biological treatment tank 20 by using microorganisms present in the endogenous stage;
Filtering the inorganic material and the colloidal material by transferring the wastewater from which the organic material is removed to the filtration tank 30 to which the MF or UF membrane 31 is attached;
Transporting the sewage water from which the inorganic material and the colloidal material are filtered in the filtration tank 30 to the advanced processing unit 40 to which the RO membrane 41 is attached to generate RO concentrated water;

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상기 고도처리부(40)에서 생성된 농축수를 오존발생부(60)를 이용하여 오존을 50~150ppm으로 30분~90분간 주입시켜 고도처리하는 단계;로 구성된 것을 특징으로 한 하폐수를 재활용하는 방법을 과제 해결을 위한 수단으로 제공한다.
Injecting the concentrated water produced in the advanced processing unit 40 using ozone generator 60 for 30 minutes to 90 minutes in an ozone 50 ~ 150ppm; advanced processing; recycling the sewage water, characterized in that consisting of To provide a means for solving the problem.

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본원 발명의 하폐수 재활용수 생산장치는 생물처리, 여과 소독 등을 단일공정의 단일반응조에 구성한 간단한 설비만으로 대용량의 폐수까지 처리할 수 있으며, 직접적인 생활용수나 산업용수에 사용하기에 적합할 정도의 정화수준을 나타내며, 초기투자비 및 유지관리비가 저렴한 장점이 있다.The wastewater recycled water production apparatus of the present invention can treat large volumes of wastewater only with a simple facility consisting of biotreatment, filtration and disinfection in a single reactor in a single process, and a level of purification suitable for use in direct living water or industrial water. It has the advantage of low initial investment and maintenance costs.

도 1은 종래의 하폐수처리 상태를 나타내는 도면이다.
도 2는 본 발명의 구성을 나타내는 도면이다.
도 3은 본 발명의 구성을 통한 하폐수가 처리되는 과정을 나타내는 도면이다.
1 is a view showing a conventional wastewater treatment state.
2 is a view showing the configuration of the present invention.
3 is a view showing a process of treating wastewater through the configuration of the present invention.

이하 도면과 실시 예를 참고하여 본 발명을 더욱 상세히 설명한다. 이하 기술된 용어와 실시 예는 본 발명을 명확하게 설명하기 위하여 예시한 것에 불과할 뿐 본 발명의 권리범위가 이에 한정되어 해석되어서는 아니됨은 명백하다.
Hereinafter, the present invention will be described in more detail with reference to the accompanying drawings and embodiments. The terms and examples described below are only illustrated to clearly describe the present invention, and it is obvious that the scope of the present invention should not be construed as being limited thereto.

도 1은 종래의 하폐수처리 상태를 나타내는 도면이다. 도시된 바와 같이 하폐수를 원수탱크로 이송하여 저장한 후 스케일방지를 위하여 스케일 방지제를 투입한 후 이를 R/O 분리장치로 이송시킨다. 그런 다음 하폐수의 PH를 조절하기 위하여 알칼리제를 투입하고 오존을 발생시켜 유해물질을 제거한다. 최종적으로 제거되지 않은 유해물질이 포함된 농축수는 활성탄탑과 이온교환수지탑을 통해 제거시키도록 구성된다. 1 is a view showing a conventional wastewater treatment state. As shown, after transporting the sewage water to the raw water tank and storing it, the anti-scaling agent is added to prevent scale and then transferred to the R / O separation device. Then, to control the pH of the sewage water, an alkaline agent is added and ozone is generated to remove harmful substances. Finally, concentrated water containing harmful substances not removed is configured to be removed through activated carbon tower and ion exchange resin tower.

종래의 방법은 하폐수처리에 포함된 유기물질 특히 유기슬러리를 제거하기에는 효과적이지 못해 반드시 활성탄탑 또는 이온교환수지탑을 사용하여야 하는 번거로움이 있다.
Conventional methods are not effective in removing organic substances, especially organic slurries, which are included in sewage water treatment, so it is cumbersome to use an activated carbon tower or an ion exchange resin tower.

도 2는 본 발명의 구성을 나타내는 도면이다. 도시된 바와 같이 본 발명은 단일반응조와; 고도처리부로 구성되어 있다.
2 is a view showing the configuration of the present invention. As shown the present invention comprises a single reactor; It is composed of advanced processing unit.

본 발명의 단일반응조는 생물처리조와; 여과조로 구성되어 있는데, 상기 단일반응조내에서 생물처리 기능, 미생물 유지기능(침전기능), 여과기능, 소독기능이 이루어진다.Single reaction tank of the present invention and the biological treatment tank; It consists of a filtration tank, the biological treatment function, microorganism maintenance function (sedimentation function), filtration function, disinfection function is made in the single reaction tank.

상기 생물처리조는 유입된 하폐수의 유기물질, 질소, 슬러지 함량을 최소화시키는 기능을 담당한다. 이를 위하여 본 발명의 생물처리조는 미생물 농도를 1,000mg/L에서 10,000mg/L까지 바람직하게는 4,000mg/L에서 7,000mg/L로 더욱 바람직하게는 5,500~6,500mg/L로 유지한다. 상기와 같은 농도로 미생물을 유지시키면 미생물의 성장상태를 지수성장단계에서 내생성장단계로 유지할 수 있어 유입되는 하폐수 유기물질 및 영양물질을 제거하면서 발생되는 잉여슬러지의 발생량을 최소화할 수 있다.The biological treatment tank is responsible for minimizing the organic material, nitrogen, sludge content of the introduced wastewater. For this purpose, the biological treatment tank of the present invention maintains the microbial concentration from 1,000 mg / L to 10,000 mg / L, preferably from 4,000 mg / L to 7,000 mg / L, more preferably from 5,500 to 6,500 mg / L. Maintaining the microorganism at the above concentration can maintain the growth state of the microorganism from the exponential growth stage to the endogenous growth stage, thereby minimizing the amount of excess sludge generated while removing the influent sewage organic matter and nutrients.

상기 생물처리조에서 사용되는 미생물은 일반 하수처리장에서 사용되는 미생물과 동일한 것을 사용한다. 구체적으로 티오바실러스 데니트리피칸스(Thiobacillus denitrificans), 티오마이크로스피라 데니트리피칸스(Thiomicrospira denitrificans, Thiobacillus versutus), 티오바실러스 티아시리스(Thiobacillus thyasiris), 티오스패라 판토트로파(Thiosphaera pantotropha), 파라코커스 데니트리피칸스(Paracoccus denitrificans) 등이 사용될 수 있으나 반드시 이에 한정되는 것은 아니다.
The microorganism used in the biological treatment tank uses the same as the microorganism used in the general sewage treatment plant. Specifically, Thiobacillus denitrificans, Thiomicrospira denitrificans, Thiobacillus versutus, Thiobacillus thiasis, Thiospara pantotropha, Parasphaera pantotroph Caucasus denitrificans and the like may be used, but are not necessarily limited thereto.

상기 여과조는 미생물 농도를 대량으로 유지할 수 있는 미생물 유지기능(침전기능)과; 콜로이드성 물질을 여과하는 여과기능과; 0.45㎛ 공극에 의해 병원성 미생물을 제거하는 소독기능을 수행한다.The filtration tank is a microorganism maintenance function (precipitation function) that can maintain a large amount of microbial concentration; A filtration function for filtering the colloidal substance; Disinfection function to remove pathogenic microorganisms by 0.45㎛ pore.

상기 여과조의 하부에는 공기공급장치가 부착되어 있고, 내부에는 0.45㎛ 크기의 공극을 가진 유리섬유필터가 형성되어 있다. 상기 공기공급장치를 통해 미생물에 산소를 공급하여 생물처리에 필요한 미생물을 유지하는 기능(침전기능)를 수행한다. 폐수의 고체성분을 걸러낼 때 일정시간이 경과하면 미생물을 포함한 부유물질에 의해 막이 오염(Fouling)되는 현상이 나타나는 데 상기 여과조 하부에 부착된 공기공급관을 통해 산소를 공급함으로써 막표면을 계속하여 세척할 수 있는 것이다. 그 결과 생물처리조 내의 미생물을 일정한 농도로 유지시킬 수 있다.An air supply device is attached to the lower part of the filtration tank, and a glass fiber filter having a pore size of 0.45 μm is formed therein. By supplying oxygen to the microorganism through the air supply device performs a function (precipitation function) to maintain the microorganisms necessary for biological treatment. When a certain time elapses when filtering out the solid components of waste water, the membrane is fouled by suspended substances including microorganisms. The membrane surface is continuously washed by supplying oxygen through an air supply pipe attached to the lower part of the filtration tank. You can do it. As a result, the microorganisms in the biological treatment tank can be maintained at a constant concentration.

상기 여과조 내부에는 0.45㎛ 크기의 공극을 가진 유리섬유필터가 형성되어 있다. 따라서 0.45㎛보다 작은 크기의 미생물이 전량 반응조 남아있게 된다.따라서 반응조내 별도의 침전조를 두지 않고 미생물을 반응조내 보유시킬 수 있다.
A glass fiber filter having a pore size of 0.45 μm is formed inside the filtration tank. Therefore, the total amount of microorganisms smaller than 0.45 μm remains in the reaction tank. Therefore, the microorganisms can be retained in the reaction tank without having a separate precipitation tank in the reaction tank.

본 발명의 단일반응조는 생물처리조와 여과조가 함께 운전되면서 미생물을 다량 보유하는 특징이 있고, 유입되는 유기물에 비해 미생물량이 많기 때문에 F/M(Foods/Microbes)비가 낮아져 처리효율이 향상되는 특징이 있다.The single reaction tank of the present invention has a feature of retaining a large amount of microorganisms while the biotreatment tank and the filtration tank are operated together, and the F / M (Foods / Microbes) ratio is lowered due to the large amount of microorganisms compared to the introduced organic material. .

또한 생물처리조를 무산소조건과 호기조건으로 구분하여 질산화균과 탈질균의 성장으로 질소제거가 탁월하고, 일부 인제거 미생물(통칭 Bio-P Bacteria ; Azotobacter 등)이 서식하여 인(P) 제거가 가능한 특징이 있다.
In addition, the biotreatment tank is divided into anoxic conditions and aerobic conditions, so nitrogen removal is excellent due to the growth of nitrifying bacteria and denitrification bacteria, and some phosphorus-removing microorganisms (commonly known as Bio-P Bacteria; Azotobacter, etc.) inhabit to remove phosphorus (P). There are possible features.

상기 단일반응조에서 처리된 하폐수는 고도처리부로 이송된다. 상기 고도처리부는 역삼투(RO)막이 설치되어 있는 데, 단일반응조에서 유입된 하폐수를 다시한번 역삼투(RO)막을 통해 여과시켜 미량영양소 및 재활용수로 이용되지 않는 불순물을 처리한다. The wastewater treated in the single reactor is sent to the advanced treatment unit. The advanced treatment unit is equipped with a reverse osmosis (RO) membrane, the wastewater introduced in a single reaction tank is filtered again through a reverse osmosis (RO) membrane to treat impurities not used as micronutrients and recycled water.

또한 상기 고도처리부에는 상기 역삼투(RO)막을 통해 여과된 하폐수(농축수)를 보다 효과적으로 재활용하기 위하여 오존공급장치를 부착해서 이를 재처리한다. 구체적으로 50~150ppm의 오존을 30분~90분간 주입된다. 필요에 따라 과산화수소와 병행하여 투입할 수도 있다.
In addition, the advanced treatment unit is attached to the ozone supply device to reprocess the sewage (concentrated water) filtered through the reverse osmosis (RO) membrane more effectively. Specifically, 50 to 150 ppm of ozone is injected for 30 to 90 minutes. If necessary, it may be added in parallel with hydrogen peroxide.

도 3은 본 발명의 구성을 통한 하폐수를 재활용수로 생산하는 과정을 나타내는 도면이다. 도시된 바와 같이 스크린조를 거친 하폐수는 단일반응조내 생물처리공정으로 유입되어 유기물질 및 영양물질을 분해 제거시키게 된다.3 is a view showing a process of producing wastewater as recycled water through the configuration of the present invention. As shown, the wastewater passed through the screen tank is introduced into the biological treatment process in a single reactor to decompose and remove organic and nutrient substances.

상기 생물처리조를 거친 하폐수는 막분리공정으로 유입시켜 무기물, 콜로이드성 물질, 대장균 등을 MF 또는 UF막을 통해 여과시키게 된다. The wastewater passed through the biological treatment tank is introduced into a membrane separation process to filter inorganic materials, colloidal substances, E. coli, and the like through MF or UF membranes.

상기 여과단계를 거친 하폐수를 고도처리부에서 미세한 불순물 및 용존물질 등을 제거하여 재활용수로 생산하고The wastewater, which has undergone the filtration step, is produced as recycled water by removing fine impurities and dissolved substances from the advanced processing unit.

고도처리 과정에서 제거된 불순물 등의 농축수는 오존 공급장치에서 오존을 50~150ppm으로 30분~90분간 주입시켜 고도처리하는 단계를 거쳐 농축수를 처리한다.Concentrated water, such as impurities removed during the high-level treatment, is treated with high-pressure treatment by injecting ozone at 50 to 150 ppm for 30 minutes to 90 minutes in an ozone supply device.

상기 고도처리 과정에서는 오존을 사용한다.Ozone is used in the advanced treatment.

오존처리방식은 처리수량에 의한 제어, 용존 오존농도에 의한 제어, 배오존 농도에 의한 제어방식으로 구분된다. 처리수량에 의한 제어는 파이롯트 실험에 의해 오존주입률을 설정하고, 처리수량을 계측하여 오존주입량을 제어하는 방식으로 전오존 처리 등에 사용된다. 이는 가장 일반적으로 사용되고 있는 방식으로 응답시간이 빠르다는 장점이 있으나, 수질의 갑작스런 변화에 대한 대처능력이 떨어진다는 단점이 있다.The ozone treatment method is divided into a control method based on the amount of water treated, a control method based on the dissolved ozone concentration, and a control method based on the ozone concentration. The control by the amount of treatment is used for all ozone treatment and the like by setting the ozone injection rate by pilot experiments and measuring the amount of treatment to control the ozone injection amount. This is the most commonly used method has the advantage that the response time is fast, but has the disadvantage that the ability to cope with sudden changes in water quality is poor.

용존 오존농도에 의한 제어방식은 용존 오존농도를 미리 설정하고 접촉지 출구의 용존오존을 계측하여 오존의 주입량을 제어하는 방식으로 후오존처리에 이용되며 주로 정수장에 많이 사용된다. 수질의 변화에 민첩하게 대처할 수 있으나, 처리수량의 변동이 적은 경우에만 사용가능하고 수중의 철, 망간 등과 같은 용해물질의 농도에 의해 정밀도가 떨어진다는 단점이 있다.The control method based on dissolved ozone concentration is used for post-ozone treatment. It is used to set ozone concentration in advance and to measure the amount of ozone injected by measuring the dissolved ozone at the outlet of the contact point. Agility can cope with changes in water quality, but it can be used only when the fluctuations in the amount of treatment are small, and the disadvantages of precision decrease due to the concentration of dissolved substances such as iron and manganese in water.

배오존 농도에 의한 제어방식은 배오존 농도를 설정하고, 배출되는 배오존 농도를 계측하여 오존 주입량을 제어하는 방식으로 하수처리장 및 폐수처리 적용에 유리하고 수질의 변화에 대처할 수 있으며 낮은 주입율의 범위에서도 제어 가능 배출오존을 측정하므로 감지기가 막힐 염려가 없는 장점이 있다. The control method based on the ozone concentration controls the ozone injection amount by setting the ozone concentration and measuring the discharged ozone concentration, which is advantageous for the application of sewage treatment plants and wastewater treatment, and can cope with changes in water quality. The controllable emission ozone is also measured over the range, so there is no risk of clogging the detector.

본원발명에서는 상기 오존처리 방식 중에서 바람직하게는 배오존 농도에 의한 제어를 사용한다. 그러나 반드시 이에 한정되는 것은 아니고 당업자라면 처리용량과 폐수의 물성 등을 고려하여 용이하게 설계, 변경하여 실시할 수 있음은 물론이다.
In the present invention, among the ozone treatment methods, control by ozone concentration is preferably used. However, the present invention is not necessarily limited thereto, and a person of ordinary skill in the art can easily design and change the process in consideration of the treatment capacity and the physical properties of the wastewater.

처리하고자 하는 폐수에 대하여 오존주입을 위해 일부 혹은 필요량을 펌핑하여 인젝터를 통과시켜, 오존을 주입한다. 또한 용해장치를 이용해 주입된 오존을 전체 유량과 혼합시켜 처리함으로써 배오존 농도를 설정하고, 배출되는 배오존 농도를 계측하여 오존 주입량을 제어한다. 1~5분 정도 배출시키면 살균, 탈색이 이루어지고 10~30분 이상 주입하면 BOD, COD 제거되기 시작한다.
The wastewater to be treated is pumped through a injector by pumping some or the necessary amount for ozone injection, and ozone is injected. In addition, the ozone injected by using a dissolving device is mixed with the total flow rate to treat the ozone concentration, and the amount of ozone discharged is measured to control the ozone injection amount. If it is discharged for 1 ~ 5 minutes, sterilization and discoloration will be done. If it is injected for more than 10 ~ 30 minutes, BOD and COD will be removed.

이하 본원발명의 하폐수처리효과를 확인하기 위하여 아래와 같은 실험을 실시하였다. 접촉포기조, 침전조, 여과조만으로 구성된 단일반응조를 사용하여 하폐수를 처리한 결과(실시예 1)와 상기 단일반응조에 생물처리조가 부가시켜 하폐수를 처리한 결과(실시예 2)와 생물처리조가 부가된 단일반응조에 고도처리부를 연결시킨 처리장치를 통한 처리결과(실시예 3)와 생물처리조가 부가된 단일반응조와 전기분해장치가 결합된 것을 대상으로 하폐수를 처리한 결과(실시예 4)를 나타내었다. 구체적인 실시예는 아래와 같다.
The following experiment was carried out to confirm the sewage treatment effect of the present invention. The result of treating wastewater using a single reaction tank consisting of a contact aeration tank, a settling tank and a filtration tank only (Example 1), and a result of treating wastewater by adding a biological treatment tank to the single reaction tank (Example 2) and a single biological treatment tank added The treatment result (Example 3) through the treatment device in which the advanced treatment unit was connected to the reaction tank, and the result of treating the wastewater with a single reaction tank to which the biological treatment tank was added and the electrolysis device were shown (Example 4). Specific embodiments are as follows.

실시예 1: 단일반응조를 이용한 하폐수의 처리Example 1 Treatment of Sewage Water Using a Single Reactor

LCD 부품인 C/F, P/F 의 공정에서 발생되는 유기물질 (TOC 22mg/L, COD 20mg/L, Cond. 1492μs/cm, T-N 7.5mg/L, T-P 0.6 mg/L)이 함유된 폐수를 정화시켰다.Wastewater containing organic substances (TOC 22mg / L, COD 20mg / L, Cond. 1492μs / cm, TN 7.5mg / L, TP 0.6 mg / L) generated in the process of LCD parts C / F and P / F Purified.

이를 위하여 접촉포기조, 침전조, 여과조를 직렬로 연결하여 단일반응조를 구성한 후 전술한 폐수를 15,000m3/day의 속도로 방류하여 2시간 동안 체류시킨 후 침전조에 스케일 방지제로서 에틸렌디아민테트라아세트산(EDTA)을 200ml/hr의 속도로 투입하였다. 그 결과를 하기 표 1을 통해 나타내었다.For this purpose, the contact aeration tank, the settling tank, and the filtration tank were connected in series to form a single reaction tank, and the wastewater was discharged at a rate of 15,000 m 3 / day for 2 hours, and then ethylenediaminetetraacetic acid (EDTA) as a scale inhibitor in the settling tank. Was added at a rate of 200 ml / hr. The results are shown in Table 1 below.

[ 단일반응조를 이용한 하폐수의 처리결과][Treatment Result of Sewage Water Using Single Reactor] 유입수Influent 유출수Runoff 유량Q(m3/day)Flow rate Q (m 3 / day) 15,00015,000 15,00015,000 TOC(mg/L)TOC (mg / L) 2222 21.521.5 COD(mg/L)COD (mg / L) 2020 19.319.3 Cond.Cond. 14921492 13001300 T-N(mg/L)T-N (mg / L) 7.57.5 4.54.5 T-P(mg/L)T-P (mg / L) 0.60.6 0.50.5

실시예 2: 생물처리조가 부가된 단일반응조를 이용한 하폐수의 처리Example 2 Treatment of Sewage Water Using a Single Reaction Tank Added with a Biotreatment Tank

실시예 1과 동일한 폐수를 처리하기 위하여 생물처리조, 여과조를 직렬로 연결한 후 각각 격벽을 통해 구분하여 단일반응조를 제작하였다. In order to treat the same wastewater as in Example 1, a biological treatment tank and a filtration tank were connected in series, and then separated through partitions to produce a single reaction tank.

상기 생물처리조에는 미생물로서 티오바실러스 데니트리피칸스(Thiobacillus denitrificans)를 3.75kg/hr의 유량으로 투입하였다. 상기 생물처리조와 침전조 사이의 공기공급관을 통해 산소를 2250 l/min의 유속으로5.3시간 동안 투입하여 미생물의 농도를 측정하여 본 결과 더 이상 미생물이 생장하지 않는 내생단계에 도달했음을 확인하였다.To the biotreatment tank, Thiobacillus denitrificans was introduced as a microorganism at a flow rate of 3.75 kg / hr. Oxygen was introduced for 5.3 hours at a flow rate of 2250 l / min through the air supply pipe between the biological treatment tank and the settling tank to measure the concentration of the microorganisms.

상기 내생단계에서 스케일 방지제로서 에틸렌디아민테트라아세트산(EDTA)을 200ml/hr의 속도로 투입하였다. 그 결과를 하기 표 2를 통해 나타내었다.Ethylenediaminetetraacetic acid (EDTA) was added at a rate of 200 ml / hr as a scale inhibitor in the endogenous step. The results are shown in Table 2 below.

[ 생물처리조가 부가된 단일반응조를 이용한 하폐수의 처리결과][Results of Treatment of Sewage Wastewater Using a Single Reactor with Biotreatment] 유입수Influent 유출수Runoff 유량Q(m3/day)Flow rate Q (m 3 / day) 15,00015,000 15,00015,000 TOC(mg/L)TOC (mg / L) 2222 2020 COD(mg/L)COD (mg / L) 2020 18.518.5 Cond.Cond. 14921492 13001300 T-N(mg/L)T-N (mg / L) 7.57.5 3.33.3 T-P(mg/L)T-P (mg / L) 0.60.6 0.40.4

실시예 3: 단일반응조와 오존처리부를 결합한 하폐수처리Example 3 Wastewater Treatment Combined with Single Reactor and Ozone Treatment Unit

생물처리조, 여과조, 오존처리부를 직렬로 연결하여 실시예 2와 동일하게 실시하였다. 여과단계를 거친 하폐수를 오존처리부로 이송하여 100ppm으로 60분간 오존을 주입하였다. 그 결과를 하기 표 3를 통해 나타내었다.It carried out similarly to Example 2, connecting a biological treatment tank, a filtration tank, and an ozone treatment part in series. The wastewater passed through the filtration step was transferred to the ozone treatment unit, and ozone was injected at 100 ppm for 60 minutes. The results are shown in Table 3 below.

[ 단일반응조와 오존처리부를 결합한 하폐수의 처리결과][Treatment result of sewage water combining a single reactor and ozone treatment unit] 유입수Influent 유출수Runoff 유량Q(m3/day)Flow rate Q (m 3 / day) 15,00015,000 15,00015,000 TOC(mg/L)TOC (mg / L) 2222 14.414.4 COD(mg/L)COD (mg / L) 2020 15.515.5 Cond.Cond. 14921492 13001300 T-N(mg/L)T-N (mg / L) 7.57.5 1.51.5 T-P(mg/L)T-P (mg / L) 0.60.6 0.40.4

실시예 4: 단일반응조와 전기분해처리장치를 결합한 하폐수처리Example 4 Wastewater Treatment Combined with Single Reactor and Electrolysis Treatment System

실시예 2와 동일하게 실시하되, 여과단계를 거친 하폐수를 NaOCl를 시료로하여 2A/l x 8V의 조건으로 0.2㎖/L만큼 30분간 전기분해를 실시하였다. 그 결과를 하기 표 4를 통해 나타내었다. The same procedure as in Example 2 was carried out, and the wastewater was subjected to filtration to NaOCl as a sample and subjected to electrolysis for 30 minutes by 0.2 ml / L under conditions of 2A / l × 8V. The results are shown in Table 4 below.

[ 단일반응조와 전기분해처리장치를 결합한 하폐수 처리결과][Sewage Wastewater Treatment Result Combining Single Reactor and Electrolysis Treatment Unit] 유입수Influent 유출수Runoff 유량Q(m3/day)Flow rate Q (m 3 / day) 15,00015,000 15,00015,000 TOC(mg/L)TOC (mg / L) 2222 19.519.5 COD(mg/L)COD (mg / L) 2020 16.516.5 Cond.Cond. 14921492 13001300 T-N(mg/L)T-N (mg / L) 7.57.5 3.03.0 T-P(mg/L)T-P (mg / L) 0.60.6 0.40.4

상기 실시예와 표의 결과를 종합하면 본원발명과 같이 생물처리조가 포함된 단일반응조를 오존처리부와 결합시킨 하폐수의 처리장치가 농축수의 처리효율 및 슬러지 함량에 있어서 가장 우수한 것으로 판명되었다.특히 TOC와 T-N의 함량에 있어서 각각 34%, 80% 제거 효율을 보여주고 있는 데, 이는 오존반응조에서 발생기 산소[O]와 수산화기[OH-] 등에 의한 직접산화 및 간접산화에 의해 오염물질이 파괴된 결과로 풀이된다.
According to the results of the above examples and tables, it was found that the wastewater treatment apparatus combining the single reaction tank containing the biological treatment tank with the ozone treatment unit as in the present invention is the most excellent in the treatment efficiency and sludge content of the concentrated water. in the content of the TN for showing a 34% and 80% removal efficiency, respectively, which generator oxygen in an ozone reaction vessel [O] and hydroxyl group [OH -] to the destruction result contaminants by the direct oxidation and indirect oxidation caused by It becomes a pool.

10: 스크린조 20: 생물처리조 30: 여과조
31: MF막, UF막 32: 공기공급관 33: 역세장치
40: 고도처리부 41: RO막 50: 공기공급수단
60: 오존발생부
10: screen tank 20: biological treatment tank 30: filtration tank
31: MF membrane, UF membrane 32: air supply pipe 33: backwash device
40: high processing unit 41: RO membrane 50: air supply means
60: ozone generator

Claims (3)

스크린조(10)를 거쳐 유입된 하폐수를 효과적으로 재활용하기 위한 하폐수 재활용수 생산장치에 있어서,
상기 하폐수 재활용수 생산장치는 단일반응조와; 고도처리부(40)로 구성되며,
상기 단일반응조는
유입된 하폐수의 유기물질, 질소를 미생물을 사용하여 분해 제거하기 위하여 미생물의 체류시간을 장기화시켜 미생물이 지수성장단계를 지나 내생단계로 운전되는 생물처리조(20)와;
상기 생물처리조에서 제거되지 않은 무기물을 MF 또는 UF막을 통해 여과시키는 위한 여과조(30)로 구성되어 있고,
상기 여과조는 MF 또는 UF막(31)을 통해 고액분리로 미생물 농도를 대량으로 유지할 수 있는 침전기능과; 콜로이드성 물질을 여과하는 여과기능과; 0.45㎛ 공극에 의해 병원성 미생물을 제거하는 소독기능을 수행하고,
상기 여과조의 하부에는 하부에 공기공급관(32) 및 역세장치(33)가 부착되어 있어, 상기 공기공급관(32)을 통해 산소가 폭기되어 미생물의 생장을 촉진시키고, 미생물이 과도할 경우 상기 역세장치(33)를 이용하여 MF 또는 UF막(31)표면에 부착된 미생물을 탈착시키도록 운전되며,
상기 고도처리부(40)는 단일반응조에서 여과된 처리수를 RO막(41)을 이용하여 고도처리하여 이를 재활용할 수 있도록 운전되는 것을 특징으로 한 하폐수 재활용수 생산장치
In the wastewater recycling water production apparatus for effectively recycling the wastewater introduced through the screen tank (10),
The wastewater recycling water production apparatus includes a single reactor; It is composed of an advanced processing unit 40,
The single reactor
A biological treatment tank 20 in which microorganisms are operated in an endogenous stage after exponential growth by prolonging the retention time of the microorganisms in order to decompose and remove the organic material and nitrogen of the introduced wastewater using microorganisms;
It consists of a filtration tank 30 for filtering the inorganic material not removed from the biological treatment tank through the MF or UF membrane,
The filtration tank has a precipitation function capable of maintaining a large amount of microorganism concentration by solid-liquid separation through the MF or UF membrane 31; A filtration function for filtering the colloidal substance; It performs a disinfection function to remove pathogenic microorganisms by 0.45㎛ pore,
An air supply pipe 32 and a backwashing device 33 are attached to a lower portion of the filtration tank so that oxygen is aerated through the air supply pipe 32 to promote the growth of microorganisms, and when the microorganisms are excessive, the backwashing device (33) is used to desorb microorganisms attached to the surface of the MF or UF membrane 31,
The advanced treatment unit 40 is a wastewater recycled water production apparatus, characterized in that it is operated to recycle the treated water filtered in a single reactor using the RO membrane 41 to recycle it.
제 1항에 있어서,
상기 고도처리부(40)는 RO막(41)을 이용하여 여과시킨 농축수에 오존을 50~150ppm으로 30분~90분간 주입시켜 고도처리하는 것을 특징으로 한 하폐수 재활용수 생산장치
The method of claim 1,
The advanced treatment unit 40 is a wastewater recycled water production apparatus, characterized in that the advanced treatment by injecting ozone into the concentrated water filtered using the RO membrane 41 at 50 ~ 150ppm for 30 minutes to 90 minutes.
스크린조(10)를 거친 하폐수를 생물처리조(20)와 여과조(30)로 구성된 단일반응조의 생물처리조(20)로 유입시키는 단계와;
생물처리조(20)에 유입된 하폐수에 포함된 유기물질을 내생단계로 존재하는 미생물을 이용하여 분해하여 제거시키는 단계와;
상기 유기물질이 제거된 하폐수를 MF 또는 UF막(31)이 부착된 여과조(30)로 이송하여 무기물 및 콜로이드성 물질을 여과시키는 단계와;
상기 여과조(30)에서 무기물 및 콜로이드성 물질이 여과된 하폐수를 RO막(41)이 부착된 고도처리부(40)로 이송하여 여과시켜 RO농축수를 생성시키는 단계와;
상기 고도처리부(40)에서 생성된 농축수를 오존발생부(60)를 이용하여 오존을 50~150ppm으로 30분~90분간 주입시켜 고도처리하는 단계;로 구성된 것을 특징으로 한 하폐수를 재활용하는 방법
Introducing the wastewater having passed through the screen tank (10) into the biological treatment tank (20) of a single reaction tank consisting of the biological treatment tank (20) and the filtration tank (30);
Decomposing and removing the organic materials contained in the wastewater introduced into the biological treatment tank 20 by using microorganisms present in the endogenous stage;
Filtering the inorganic material and the colloidal material by transferring the wastewater from which the organic material is removed to the filtration tank 30 to which the MF or UF membrane 31 is attached;
Transporting the sewage water from which the inorganic material and the colloidal material are filtered in the filtration tank 30 to the advanced processing unit 40 to which the RO membrane 41 is attached to generate RO concentrated water;
Injecting the concentrated water produced in the advanced processing unit 40 using ozone generator 60 for 30 minutes to 90 minutes in an ozone 50 ~ 150ppm; advanced processing; recycling the sewage water, characterized in that consisting of
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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101565372B1 (en) 2013-05-30 2015-11-03 (주)필로스 Apparatus and method for recycle of caustic soda solvent and by-product of bio mass
KR101688800B1 (en) * 2016-05-09 2016-12-22 세종대학교산학협력단 Treatment system for reverse osmosis concentrate and method thereof

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KR20010068850A (en) * 2000-01-10 2001-07-23 임호성 The system to treat the sanitary sewage,wastewater by the membrane separator activated sludge process and the advanced oxidation process
KR100540012B1 (en) 2005-07-26 2005-12-29 (주)대성그린테크 Ds-lt system
KR100714825B1 (en) 2006-03-03 2007-05-04 신강하이텍(주) Method for treating sewage and high organic loading wastewater by anaerobic/oxic process with membrane and biological aerated filter

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KR20010068850A (en) * 2000-01-10 2001-07-23 임호성 The system to treat the sanitary sewage,wastewater by the membrane separator activated sludge process and the advanced oxidation process
KR100540012B1 (en) 2005-07-26 2005-12-29 (주)대성그린테크 Ds-lt system
KR100714825B1 (en) 2006-03-03 2007-05-04 신강하이텍(주) Method for treating sewage and high organic loading wastewater by anaerobic/oxic process with membrane and biological aerated filter

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Publication number Priority date Publication date Assignee Title
KR101565372B1 (en) 2013-05-30 2015-11-03 (주)필로스 Apparatus and method for recycle of caustic soda solvent and by-product of bio mass
KR101688800B1 (en) * 2016-05-09 2016-12-22 세종대학교산학협력단 Treatment system for reverse osmosis concentrate and method thereof

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