KR100540012B1 - Ds-lt system - Google Patents
Ds-lt system Download PDFInfo
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- KR100540012B1 KR100540012B1 KR1020050068074A KR20050068074A KR100540012B1 KR 100540012 B1 KR100540012 B1 KR 100540012B1 KR 1020050068074 A KR1020050068074 A KR 1020050068074A KR 20050068074 A KR20050068074 A KR 20050068074A KR 100540012 B1 KR100540012 B1 KR 100540012B1
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/283—Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/78—Treatment of water, waste water, or sewage by oxidation with ozone
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2201/00—Apparatus for treatment of water, waste water or sewage
- C02F2201/002—Construction details of the apparatus
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2201/00—Apparatus for treatment of water, waste water or sewage
- C02F2201/78—Details relating to ozone treatment devices
- C02F2201/782—Ozone generators
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Abstract
본 발명은 고농도 폐수처리 후 잔여 유기물질 및 질소처리를 위한 후단처리 장치 및 방법에 관한 것으로, 고농도 폐수처리 후에도 잔존하는 유기물질 및 질소를 처리하기 위해 MBR-탈질필터처리를 시스템화하거나 오존처리-A/C필터처리를 시스템화하거나 또는, MBR-탈질필터처리-오존처리를 시스템화하는 등 고농도 폐수의 성상에 따라 선택적으로 조합하여 잔존 유기물질 및 질소를 처리하는 것으로써, 상기와 같이 시스템화된 처리장치 및 방법을 사용함으로써, 수질처리기준에 맞는 수처리를 위한 전체공정 회전수 및 그에 따른 수처리시간을 단축시킬 수 있을 뿐만 아니라, 고농도 폐수처리장치 내부에, 수처리 효율을 증가시키기 위해 추가적으로 장치 설치시에는 전체 처리공정을 중단해야 하지만, 후단 공정은 기존의 처리공정에 영향을 미치지 않고 설치하여 효율적으로 유기물질 및 질소를 처리할 수 있어 그 효과면에서 뛰어나다.The present invention relates to a post-treatment apparatus and method for treating residual organic matter and nitrogen after high concentration wastewater treatment. And / or treating the remaining organic substances and nitrogen by selectively combining them according to the characteristics of the high concentration wastewater, such as systemizing the / C filter treatment or systemizing the MBR-denitrification filter treatment-ozone treatment. By using the method, not only the overall process rotation speed and the water treatment time for water treatment meeting the water treatment standards can be shortened, but also in the high concentration wastewater treatment apparatus, the whole treatment may be performed when additional equipment is installed to increase the water treatment efficiency. The process must be stopped, but the post process does not affect the existing treatment process. It is possible to install and to efficiently process the organic material and nitrogen as excellent in terms of its effectiveness.
따라서, 본 발명에 따른 폐수의 후단처리장치 및 방법은 기존공정에서 처리된 후 잔존하는 유기 물질 및 질소를 처리하여, 수질개선 및 그에 따른 안정된 처리효율을 확보하는 효과를 갖는다.Therefore, the after-treatment apparatus and method for wastewater according to the present invention have the effect of improving the water quality and securing stable treatment efficiency by treating the remaining organic substances and nitrogen after being treated in the existing process.
Description
본 발명은 고농도 폐수처리 후 잔여 유기물질 및 질소처리를 위한 후단처리 장치 및 방법에 관한 것으로, 고농도 폐수처리 후에도 잔존하는 유기물질 및 질소를 처리하기 위해 MBR-탈질필터처리를 시스템화하거나 오존처리-A/C필터처리를 시스템화하거나 또는, MBR-탈질필터처리-오존처리를 시스템화하는 등 고농도 폐수의 성상에 따라 선택적으로 조합하여 잔존 유기물질 및 질소를 처리하는 것으로써, 상기와 같이 시스템화된 처리장치 및 방법을 사용함으로써, 수질처리기준에 맞는 수처리를 위한 전체공정 회전수 및 그에 따른 수처리시간을 단축시킬 수 있을 뿐만 아니라, 고농도 폐수처리장치 내부에, 수처리 효율을 증가시키기 위해 추가적으로 장치 설치시에는 전체 처리공정을 중단해야 하지만, 후단 공정은 기존의 처리공정에 영향을 미치지 않고 설치하여 효율적으로 유기물질 및 질소를 처리할 수 있어 그 효과면에서 뛰어나다.The present invention relates to a post-treatment apparatus and method for treating residual organic matter and nitrogen after high concentration wastewater treatment, and to systemize MBR-denitrification filter treatment or ozone treatment-A to treat residual organic matter and nitrogen even after high concentration wastewater treatment. And / or treating the remaining organic substances and nitrogen by selectively combining them according to the characteristics of the high concentration wastewater, such as systemizing the / C filter treatment or systemizing the MBR-denitrification filter treatment-ozone treatment. By using the method, not only the overall process rotation speed and the water treatment time for water treatment meeting the water treatment standards can be shortened, but also in the high concentration wastewater treatment apparatus, the whole treatment may be performed when additional equipment is installed to increase the water treatment efficiency. The process must be stopped, but the post process does not affect the existing treatment process. It is possible to install and to efficiently process the organic material and nitrogen as excellent in terms of its effectiveness.
따라서, 본 발명에 따른 폐수의 후단처리장치 및 방법은 기존공정에서 처리된 후 잔존하는 유기 물질 및 질소를 처리하여, 수질개선 및 그에 따른 안정된 처리효율을 확보하는 효과를 갖는다.Therefore, the after-treatment apparatus and method for wastewater according to the present invention have the effect of improving the water quality and securing stable treatment efficiency by treating the remaining organic substances and nitrogen after being treated in the existing process.
막분리공정은 기존 공정에 비해 상변화없이 물질을 선별적으로 분리시키므로 공정이 단순하고 다른 분리공정에 비해 에너지 효율이 우수하고 막의 재질 및 형태, 여과방식에 따라 부유물질, 콜로이드, 효소, 단백질, 유기 용매, 염등을 분리할 수 있으며 혼합 기체에서 특정성분을 분리하여 농축할 수도 있다. 이러한 이점으로 식품산업의 원료분리 및 농축, 보일러 및 반도체 세척공정에 응용되는 초순수의 제조, 폐수내 유효물질회수 및 재활용기술등의 다양한 응용이 진행중이다. Membrane separation process separates materials without phase change compared to the existing process, so the process is simple and energy-efficient compared to other separation processes, and suspended materials, colloids, enzymes, proteins, Organic solvents, salts, and the like may be separated, and specific components may be separated and concentrated in a mixed gas. Due to these advantages, various applications such as raw material separation and concentration in the food industry, production of ultrapure water applied to boiler and semiconductor cleaning processes, recovery of effective materials in wastewater, and recycling technologies are in progress.
막분리공정은 전체적인 시스템구성이 타 공정에 비하여 간단하여 공정설계 및 시설확장이 편리하며 시설자체의 부피를 작게 할 수 있으므로 설치면적을 최소로 유도할 수 있다. 특히 막분리공정을 이용하여 폐수를 처리하는 경우 처리과정에서 약품사용이 적기 때문에 슬러지 발생량을 최소화 시킬 수 있으며, 분리막 공정에서 얻어진 처리수는 원수로 사용되거나 수질에 따라 직접 제조 공정에 사용될 수 있다. 또 농축된 폐수의 용량은 전체 발생 폐수량의 10% 미만으로 줄일 수 있어 무방류 폐수처리 시스템 개발에 막분리공정이 핵심기술로 자리잡고 있는 실정이다. Membrane separation process is simpler than other processes, so the process design and facility expansion are convenient, and the volume of the facility itself can be reduced, thus minimizing installation area. In particular, when the wastewater is treated using the membrane separation process, the amount of sludge generated can be minimized because the use of chemicals is small in the treatment process, and the treated water obtained in the membrane process can be used as raw water or directly in the manufacturing process depending on the water quality. In addition, the capacity of the concentrated wastewater can be reduced to less than 10% of the total generated wastewater, so the membrane separation process is the core technology for the development of a zero discharge wastewater treatment system.
이러한 분리막 공정과 필터처리방법을 이용하게 되면, 기존의 기존의 고농도 폐수처리는 유기물질 및 질소처리가 효율적으로 처리되지 못하여 전체공정을 다시 거쳐 처리해야 하므로써 회전수 및 회전수에 따른 시간 단축을 유도할 수 있어 효율적으로 처리가능할 것이다.When the membrane process and the filter treatment method are used, the existing high concentration wastewater treatment does not efficiently process organic materials and nitrogen, and needs to be processed through the whole process again, thus inducing time reduction according to the rotation speed and the rotation speed. It can be done efficiently.
상기와 같은 목적을 달성하기 위해 본 발명에서는 기존의 고농도 폐수처리 시스템에 후단처리 장치를 추가 설치하여 고농도 폐수처리 후 후단처리로 순차적으로 처리진행하여 유기물질 및 질소처리를 효율적으로 진행하므로써, 공정회전수 및 그에 따른 시간 단축을 유도할 수 있는 고농도 폐수의 후단처리 장치 및 방법을 제공하고자 한다.In order to achieve the above object, the present invention additionally installs a post-treatment device in an existing high concentration wastewater treatment system, and proceeds sequentially with a post-treatment after high concentration wastewater treatment, thereby efficiently processing organic materials and nitrogen, thereby rotating the process. It is an object of the present invention to provide a post-treatment apparatus and method for high concentration wastewater that can lead to shortening of water and time.
상기와 같은 목적을 달성하기 위해 본 발명에서는 본 발명에서는 다음과 같은 기술적 구성을 갖는다.In order to achieve the above object, the present invention has the following technical configuration.
MBR과 탈질필터처리를 거치거나, 또는 오존처리와 A/C필터를 거치거나, 또는 상기한 MBR과 탈질필터처리를 거친 후 오존처리하여 폐수의 후단처리가 이루어지며, 이에 따른 장치적 구성을 살펴보면,After the MBR and the denitrification filter treatment, or after the ozone treatment and A / C filter, or after the MBR and the denitrification filter treatment, the wastewater is subjected to post-treatment by ozone treatment. ,
폐수를 유입하는 유입관(1)과; 유입된 폐수를 일정량 유지하면서 제1펌프(21)를 사용하여 MBR조(5)로 폐수를 공급하는 균등조(2)와; 균등조(2)로부터 압송된 폐수를 에어공급기(43)로부터 공급되는 공기를 사용하여 막처리하는 MBR조(5)와; 제2펌프(40)에 의해 MBR조(5)로부터 폐수를 공급받아 내부에 설치된 필터로 탈질처리하는 탈질필터(6)와; 탈질처리된 최종처리수를 보관하는 처리수조(7) 및 처리수조(7)로부터 처리수를 외부로 방류하는 배출펌프(71)로 구성되거나,An inlet pipe 1 for introducing wastewater; An equalization tank 2 for supplying the wastewater to the MBR tank 5 using the first pump 21 while maintaining a constant amount of the introduced wastewater; An MBR tank 5 for membrane-processing the wastewater pumped from the equalization tank 2 using the air supplied from the air supply 43; A denitrification filter 6 which receives wastewater from the MBR tank 5 by the second pump 40 and performs denitrification by a filter installed therein; Or a discharge pump 71 for discharging the treated water to the outside from the treated water tank 7 for storing the denitrified final treated water, or
상기 균등조(2)와 탈질필터(6) 사이에 위치한 MBR조(5)를 빼고, MBR조(5)를 사용하는 대신에, 균등조(2)에서 제1펌프(21)를 사용하여 압송된 폐수와 오존발생기(31)로부터 유입되는 오존과의 접촉을 유도하는 오존접촉조(3)와; 오존접촉조(3)에서 이송된 폐수를 교반용송풍기(42)로부터 에어를 공급받아 오존처리하는 오존처리수조(4) 및 제2펌프(40)와 연결된, 탈질필터(6)를 대용하는 A/C여과기(6-1)가 구성되거나, 또는Remove the MBR tank 5 located between the equalization tank 2 and the denitrification filter 6, and instead of using the MBR tank 5, pressurize using the first pump 21 in the equalization tank 2. An ozone contact tank 3 for inducing contact between the wastewater and ozone flowing from the ozone generator 31; A substitutes for the denitrification filter 6, which is connected to the ozone treatment tank 4 and the second pump 40 for receiving ozone from the wastewater transferred from the ozone contact tank 3 by receiving air from the stirring blower 42. / C filter 6-1 is configured, or
전설한 탈질필터(6)와 처리수조(7) 사이에, 오존발생기(31)로부터 유입되는 오존과의 접촉을 유도하는 오존접촉조(3)와; 오존접촉조(3)에서 이송된 폐수를 교반용송풍기(42)로부터 에어를 공급받아 오존처리하는 오존처리수조(4)가 더 구비되는 것을 특징으로 한다.An ozone contact tank 3 for inducing contact with ozone flowing from the ozone generator 31 between the legendary denitrification filter 6 and the treatment water tank 7; It is characterized in that the ozone treatment tank (4) for receiving ozone from the waste water conveyed from the ozone contact tank (3) by receiving air from the stirring blower (42).
상기한 장치 구성에 따른 완전한 장치적 결합구성을 도면을 참조하여 살펴보면,Looking at the complete mechanical coupling configuration according to the above device configuration with reference to the drawings,
MBRMBR + + 탈질필터장치Denitrification filter device
도 1에 도시된 바와 같이, 고농도 폐수처리 후 잔여 유기물질 및 질소처리를 위한 후단처리 장치는 폐수를 유입하는 유입관(1)과; 유입된 폐수를 일정량 유지하면서 제1펌프(21)를 사용하여 MBR조(5)로 폐수를 공급하는 균등조(2)와; 균등조(2)로부터 압송된 폐수를 에어공급기(43)로부터 공급되는 공기를 사용하여 막처리하는 MBR조(5)와; 제2펌프(40)에 의해 MBR조(5)로부터 폐수를 공급받아 탈질처리하는 탈질필터(6)와; 탈질처리된 최종처리수를 보관하는 처리수조(7) 및 처리수조(7)로부터 처리수를 배출관(72)을 통해 외부로 방류하는 배출펌프(71)로 구성된다.As shown in FIG. 1, the aftertreatment apparatus for treating residual organic materials and nitrogen after high concentration wastewater treatment includes an inlet pipe 1 for introducing wastewater; An equalization tank 2 for supplying the wastewater to the MBR tank 5 using the first pump 21 while maintaining a constant amount of the introduced wastewater; An MBR tank 5 for membrane-processing the wastewater pumped from the equalization tank 2 using the air supplied from the air supply 43; A denitrification filter 6 for receiving wastewater from the MBR tank 5 by the second pump 40 and performing denitrification treatment; It is composed of a treatment water tank (7) for storing the denitrified final treatment water and a discharge pump (71) for discharging the treatment water from the treatment water tank (7) to the outside through the discharge pipe (72).
오존장치 + A/C필터장치Ozone unit + A / C filter unit
도 2에 도시된 바와 같이, 폐수를 유입하는 유입관(1)과; 유입된 폐수를 일정량 유지하면서 제1펌프(21)를 사용하여 오존접촉조(3)에 폐수를 압송하는 균등조(2)와; 균등조(2)로부터 압송된 후처리대상폐수와 오존발생기(31)로부터 유입되는 오존의 접촉을 유도하는 오존접촉조(3)와; 오존접촉조(3)에서 이송된 폐수를, 교반용송풍기(42)로부터 에어를 공급받아 오존처리하는 오존처리수조(4)와; 제2펌프(40)에 의해 오존처리수조(4)로부터 압송되어온 폐수를 필터처리하는 A/C여과기(6-1)와; 필터처리된 최종처리수를 보관하는 처리수조(7) 및 배출펌프(71)와 배출관(72)로 구성된다. A/C여과기(6-1) 내부에 설치되는 필터는 제올라이트(zeolite) 20 ~ 40중량%, 활성탄 60 ~ 80 혼합하여 형성된 것을 특징으로 한다.As shown in Figure 2, the inlet pipe 1 for introducing waste water; An equalization tank 2 for pumping the wastewater into the ozone contact tank 3 using the first pump 21 while maintaining a constant amount of the introduced wastewater; An ozone contact tank (3) for inducing contact between the wastewater pumped from the equalization tank (2) and ozone flowing from the ozone generator (31); An ozone treatment tank (4) for ozone treatment of the wastewater transferred from the ozone contact tank (3) by receiving air from the stirring blower (42); An A / C filter 6-1 for filtering the wastewater pumped from the ozone treatment tank 4 by the second pump 40; It consists of a treatment water tank (7) for storing the final treated water filtered, discharge pump (71) and discharge pipe (72). The filter installed inside the A / C filter 6-1 is characterized in that formed by mixing 20 to 40% by weight of zeolite, 60 to 80 activated carbon.
MBRMBR + + 탈질필터장치Denitrification filter device + 오존장치 + Ozone system
도 3에 도시된 바와 같이, 폐수를 유입하는 유입관(1)과; 유입된 폐수를 일정량 유지하면서 제1펌프(21)를 사용하여 MBR조(5)로 폐수를 공급하는 균등조(2)와; 균등조(2)로부터 압송된 폐수를 에어공급기(43)로부터 공급되는 공기를 사용하여 막처리하는 MBR조(5)와; 제2펌프(40)에 의해 MBR조(5)로부터 폐수를 공급받아 탈질처리하는 탈질필터(6)와; 오존발생기(31)로부터 유입되는 오존의 접촉을 유도하는 오존접촉조(3)와; 오존접촉조(3)에서 이송된 폐수를, 교반용송풍기(42)로부터 에어를 공급받아 오존처리하는 오존처리수조(4)와; 오존처리수조(4)로부터 제3펌프(41)를 통해 압송된 최종처리된 처리수를 보관하는 처리수조(7) 및 배출펌프(71)와 배출관(72)로 구성된다.As shown in Figure 3, the inlet pipe (1) for introducing the waste water; An equalization tank 2 for supplying the wastewater to the MBR tank 5 using the first pump 21 while maintaining a constant amount of the introduced wastewater; An MBR tank 5 for membrane-processing the wastewater pumped from the equalization tank 2 using the air supplied from the air supply 43; A denitrification filter 6 for receiving wastewater from the MBR tank 5 by the second pump 40 and performing denitrification treatment; An ozone contact tank 3 for inducing contact of ozone flowing from the ozone generator 31; An ozone treatment tank (4) for ozone treatment of the wastewater transferred from the ozone contact tank (3) by receiving air from the stirring blower (42); It consists of a treatment water tank (7) for storing the final treated water pumped from the ozone treatment water tank (4) through the third pump (41), a discharge pump (71) and a discharge pipe (72).
상기 장치적 구성에 따른 폐수의 후단처리과정을 살펴보면,Looking at the post-treatment process of wastewater according to the device configuration,
유입관(1)을 통해 고농도 폐수처리 후에 잔여하는 유기물질 및 질소를 함유한 폐수가 균등조(2)로 유입되고, 유입된 폐수를 제1펌프(21)를 사용하여 MBR조(5)로 압송하여 하부 에어공급기(43)로부터 에어를 공급하면서 막표면에 생성되는 막오염물질 제거 및 폐수내에 공기를 공급하여 폐수를 막처리하고, 막처리된 폐수는 제2펌프(40)를 사용하여 탈질필터(6)로 압송하고, 탈질필터(6)에서 최종적으로 필터처리된 처리수는 처리수조(7)로 이송하여 배출펌프(71)를 사용하여 방류처리하거나,Wastewater containing organic substances and nitrogen remaining after the high concentration wastewater treatment is introduced into the equalization tank (2) through the inflow pipe (1), and the introduced wastewater is introduced into the MBR tank (5) using the first pump (21). By removing the pollutants generated on the surface of the membrane and supplying air into the wastewater while supplying air from the lower air supplier 43, the wastewater is membrane treated, and the treated wastewater is denitrified using the second pump 40. The treated water pumped to the filter 6 and finally filtered in the denitrification filter 6 is transferred to the treated water tank 7 and discharged using the discharge pump 71, or
상기 처리장치에서 MBR조(5)를 빼고, MBR조(5)를 사용하는 대신에, 균등조(2)로 유입된 후처리대상폐수는 제1펌프(21)를 사용하여 오존접촉조(3)로 압송하고, 오존발생기(31)로부터 공급되는 오존과 균등조(2)에서 유입된 폐수를 충분히 접촉시켜 오존처리수조(4)로 이송하고, 교반용송풍기(42)로부터 공급받은 에어를 사용하여 교반하면서 오존처리하고, 오존처리된 폐수를 제2펌프(40)에 의해 A/C여과기(6-1)로 압송하여 필터처리하고, 최종적으로 필터처리한 폐수는 처리수조(7)로 이송하여 배출펌프(71)로 방류처리하거나, 또는Instead of removing the MBR tank 5 from the treatment apparatus and using the MBR tank 5, the wastewater to be treated after being introduced into the equalization tank 2 is subjected to the ozone contact tank 3 using the first pump 21. ), The ozone supplied from the ozone generator 31 and the wastewater introduced from the equalization tank 2 are sufficiently brought into contact with the ozone treatment tank 4, and the air supplied from the stirring blower 42 is used. And ozone treatment with stirring, and the ozonated wastewater is pumped to the A / C filter 6-1 by the second pump 40 and filtered. Finally, the filtered wastewater is transferred to the treatment tank 7. Discharged to the discharge pump 71, or
전술한, 탈질필터(6)에서 탈질처리된 폐수는 처리수조(7)로 바로 이송되는 것이 아니라, 오존발생기(31)로부터 공급되는 오존과 폐수를 오존접촉조(3)에서 충분한 접촉을 시켜 오존처리수조(4)로 이송하고, 오존처리수조(4)에서는 교반용송풍기(42)로부터 공급받은 에어에 의해 교반하면서 폐수를 오존처리하고, 처리된 폐수는 처리수조(7)로 이송하여 배출펌프(71)로 방류처리한다.The waste water denitrified by the denitrification filter 6 described above is not directly transferred to the treatment water tank 7, but the ozone supplied from the ozone generator 31 is sufficiently brought into contact with the waste water in the ozone contact tank 3. Transfer to the treatment tank (4), in the ozone treatment tank (4) to ozonate the waste water while stirring by the air supplied from the stirring blower (42), the treated waste water is transferred to the treatment tank (7) to discharge pump Discharge treatment to (71).
MBR조(5)에서는 침지형막모듈을 이용하여 폐수를 처리하게 되며, 이때 높은 압력에서는 용매의 투과율이 증가하나 막내부에 오염물질이 강하게 결합되어 오염을 가속화 시키므로 적당한 압력을 유지해야 하며, 분리막의 재질은 막의 친수성 및 소수성, 막표면에 코팅전하의 분포, 표면의 거칠기, 공극율(porosity)및 입경분포에 따라 용매투과율 및 배제율이 변하므로 처리상황에 맞는 고려해야 한다. 막모듈의 구조와 설계는 막표면에서의 유체의 속도에 기인하게 되며, 낮은 유속은 농도분극과 오염을 증가시키고 결과적으로 투과율이 감소하여 빈번한 세척이 필요하다. 따라서 막모듈에서의 선속도를 증가시켜 농도분극현상을 최소화하고 부유물질의 축적을 감소시키는 흐름상태를 유지시켜야 한다. 막모듈의 형태는 관형(tubular), 중공사형(hollow fiber), 나선형(spiral wound), 평판형(plate and frame)이 대표적이며 처리대상에 따른 적합한 모듈 선정은 경제적이며 효율적인 처리의 중요인자가 된다.In the MBR tank (5), the wastewater is treated using an immersion membrane module. At this time, the solvent permeability increases at high pressure, but contaminants are strongly bound inside the membrane to accelerate the contamination, and thus, the proper pressure must be maintained. The material has to be considered according to the treatment situation because the solvent permeability and exclusion rate vary according to the hydrophilicity and hydrophobicity of the membrane, the distribution of coating charge on the surface of the membrane, the surface roughness, porosity and particle size distribution. The structure and design of the membrane module is due to the velocity of the fluid at the membrane surface, and low flow rates increase concentration polarization and contamination and consequently decrease permeability, requiring frequent cleaning. Therefore, the linear velocity in the membrane module should be increased to minimize the concentration polarization phenomenon and maintain the flow state to reduce the accumulation of suspended matter. Typical types of membrane modules are tubular, hollow fiber, spiral wound, and plate and frame. The selection of a suitable module according to the treatment target is an important factor for economical and efficient processing. .
탈질필터(6)는 질산화 미생물을 이용하여 암모니아를 질산화시키고, 탈질미생물을 이용하여 질산을 질소가스로 환원하여 공기중으로 방출시키므로서 반응계의 질소를 저감하는 방법을 이용한다.The denitrification filter 6 uses a method of nitrifying ammonia using nitrifying microorganisms, reducing nitric acid to nitrogen gas using a denitrifying microorganism, and releasing it into the air, thereby reducing nitrogen in the reaction system.
상기와 같은 구성으로 고농도 폐수처리 후 잔여 유기물질 및 질소를 분리막과 필터를 이용하여 처리하므로써, 고농도 폐수를 처리함에 있어 그 처리시간 및 비용을 최단으로 절감할 수가 있다.By treating the residual organic material and nitrogen after the high concentration wastewater treatment using the separation membrane and the filter as described above, it is possible to reduce the processing time and cost in the shortest time in treating the high concentration wastewater.
이상에서 살펴본 바와 같이, 본 발명에 따른 고농도 폐수처리에 따른 후단처리 장치 및 방법은 고농도 폐수처리에 잔존하는 유기물질 및 질소를 효율적으로 처리하여 기존의 처리방법보다 효율적인 유기물질 및 질소처리효과를 가져와 안정적인 처리수질 기대 및 수질개선에 일조하게 된다.As described above, the post-stage treatment apparatus and method according to the high concentration wastewater treatment according to the present invention efficiently treat organic substances and nitrogen remaining in the high concentration wastewater treatment, resulting in more efficient treatment of organic substances and nitrogen than conventional treatment methods. It contributes to stable treatment water quality and water quality improvement.
도 1은 본 발명에 따른 제 1실시예 형태의 폐수의 후단처리 장치 개략도.BRIEF DESCRIPTION OF THE DRAWINGS Fig. 1 is a schematic diagram of an aftertreatment apparatus for wastewater of a first embodiment according to the present invention.
도 2는 본 발명에 따른 제 2실시예 형태의 폐수의 후단처리 장치 개략도.Fig. 2 is a schematic diagram of an aftertreatment apparatus for wastewater according to a second embodiment of the present invention.
도 3은 본 발명에 따른 제 3실시예 형태의 폐수의 후단처리 장치 개략도Fig. 3 is a schematic diagram of an aftertreatment apparatus for wastewater of a third embodiment embodiment according to the present invention.
* 도면의 주요부호에 대한 설명 *Explanation of the main symbols in the drawings
1 : 유입관 2 : 균등조 3 : 오존접촉조1: inflow pipe 2: equalization tank 3: ozone contact tank
4 : 오존처리수 5 : MBR조 6 : 탈질필터4: ozone treated water 5: MBR bath 6: denitrification filter
6-1: A/C여과기 7 : 처리수조 21 : 제1펌프 6-1: A / C filter 7: Treatment tank 21: First pump
31 : 오존발생기 41 : 제3펌프 42 : 교반용송풍기 31 ozone generator 41 third pump 42 stirring blower
43 : 에어공급기 44 : 제2펌프 71 : 배출펌프 43: air supply 44: second pump 71: discharge pump
72 : 배출관72: discharge pipe
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Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
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KR100992827B1 (en) * | 2009-02-04 | 2010-11-09 | 주식회사 환경시설관리공사 | Cleaning system for waste-water purifier |
KR101054613B1 (en) | 2011-02-25 | 2011-08-04 | 임범관 | Apparatus for waste water single reactor composed of biological and membrane process |
CN104649524A (en) * | 2015-03-17 | 2015-05-27 | 山西澳科特环境工程有限公司 | Livestock and poultry breeding wastewater treatment method |
KR101636300B1 (en) * | 2016-01-14 | 2016-07-07 | 주식회사 도원엔바이로 | Waste water treating system |
CN108585364A (en) * | 2018-05-14 | 2018-09-28 | 北京赛科康仑环保科技有限公司 | A kind of advanced treatment process and its system for used water difficult to degradate |
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2005
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Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
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KR100992827B1 (en) * | 2009-02-04 | 2010-11-09 | 주식회사 환경시설관리공사 | Cleaning system for waste-water purifier |
KR101054613B1 (en) | 2011-02-25 | 2011-08-04 | 임범관 | Apparatus for waste water single reactor composed of biological and membrane process |
CN104649524A (en) * | 2015-03-17 | 2015-05-27 | 山西澳科特环境工程有限公司 | Livestock and poultry breeding wastewater treatment method |
CN104649524B (en) * | 2015-03-17 | 2016-06-29 | 山西澳科特环境工程有限公司 | A kind of livestock and poultry cultivation sewage water treatment method |
KR101636300B1 (en) * | 2016-01-14 | 2016-07-07 | 주식회사 도원엔바이로 | Waste water treating system |
CN108585364A (en) * | 2018-05-14 | 2018-09-28 | 北京赛科康仑环保科技有限公司 | A kind of advanced treatment process and its system for used water difficult to degradate |
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