KR20050100582A - Recycling system and the method of wastewater - Google Patents

Recycling system and the method of wastewater Download PDF

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KR20050100582A
KR20050100582A KR1020050090475A KR20050090475A KR20050100582A KR 20050100582 A KR20050100582 A KR 20050100582A KR 1020050090475 A KR1020050090475 A KR 1020050090475A KR 20050090475 A KR20050090475 A KR 20050090475A KR 20050100582 A KR20050100582 A KR 20050100582A
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tank
filter
sludge
filtration
storage tank
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KR100718070B1 (en
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유승원
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삼영이엔테크 주식회사
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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
    • 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
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/24Treatment of water, waste water, or sewage by flotation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • C02F1/32Treatment of water, waste water, or sewage by irradiation with ultraviolet light
    • C02F1/325Irradiation devices or lamp constructions
    • 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
    • C02F1/40Devices for separating or removing fatty or oily substances or similar floating material
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/06Controlling or monitoring parameters in water treatment pH
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/20Total organic carbon [TOC]
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/04Disinfection
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/06Sludge reduction, e.g. by lysis

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

Abstract

본 발명은 브라운관 및 모니터의 세척수를 재활용하는 폐수 재활용 시스템에 관한 것으로, 더욱 상세하게는 무기응집제인 HOC 성분을 사용하여 입자응집한 후, 이를 가압부상하여 규조토 여과기, 활성탄 여과기, UV살균기, PEP 필터, 마이크로 필터로 처리함으로써, PAD, PAA 성분을 완전히 제거하여 공업용수 및 순수 원수로 재활용할 수 있을 뿐만 아니라, 무기응집제를 사용하므로 후처리 공정에 아무런 영향을 미치지 않는 폐수 재활용 시스템에 관한 것이다.The present invention relates to a wastewater recycling system for recycling the wash water of the CRT and monitor, and more particularly, after the particle agglomeration using the HOC component, which is an inorganic coagulant, by pressure flotation and diatomaceous earth filter, activated carbon filter, UV sterilizer, and PEP filter. By treating with a micro filter, PAD and PAA components can be completely removed and recycled to industrial water and pure water, and an inorganic coagulant is used.

본 발명에 따르면, 가성소다(NaOH), 염산(HCL), 응집제(HOC)를 통해 원수의 PH를 조정하고 입자를 응집시키는 화학적 처리단계; 미세기포를 생성 접촉시켜 부유물질을 부상 제거하는 가압부상단계; 규조토를 통해 폐수에 함유된 오염물질 및 슬러지를 여과하는 1차 여과단계; 활성탄을 통해 오염물질 및 슬러지를 여과하는 2차 여과단계; UV 살균기를 통해 박테리아와 TOC를 분해 제거하는 살균단계; PEP 필터의 구상 실리카 필터 메디아를 통해 부유물질을 제거하는 3차 여과단계; MICRO 필터로 잔류 미세물질을 제거하는 4차 여과단계;를 거쳐서 재활용됨을 특징으로 하는 폐수 재활용 방법과,According to the invention, the chemical treatment step of adjusting the pH of the raw water through the caustic soda (NaOH), hydrochloric acid (HCL), flocculant (HOC) and flocculate the particles; Pressurized flotation step of generating and contacting the fine bubbles to float floating material; A primary filtration step of filtering contaminants and sludge contained in the wastewater through the diatomaceous earth; A secondary filtration step of filtering contaminants and sludge through activated carbon; A sterilization step of decomposing and removing bacteria and TOC through a UV sterilizer; A third filtration step of removing suspended solids through the spherical silica filter media of the PEP filter; And a fourth filtration step of removing residual fine materials with a MICRO filter.

가성소다(NaOH), 염산(HCL)이 유입되는 pH 조정조와 응집제(HOC)가 유입되는 반응조 및 응집조로 형성된 화학처리부; 미세기포를 발생시켜 부유물질을 부상시키는 가압부상조와 상기 가압부상조에서 분리된 슬러지를 제거하는 슬러지 저장조로 형성된 가압부상부; 미세기포를 형성하고 유량을 조절하는 순환조/저류조; 여과기, 믹싱탱크, 코팅탱크를 거치면서 규조토를 통해 슬러지를 여과하는 통상의 제 1 여과부; 저류조를 통해 유량조절된 폐수를 활성탄 여과기로 여과하는 제 2 여과부; UV장치를 통해 살균처리하는 UV살균기; 미디어를 통해 순환처리하여 부유물을 제거하는 PEP 필터와 유량조절을 위한 저류조로 형성된 제 3 여과부; 유량을 조절하는 재활용수 공급탱크와 잔류 미세물질을 제거하는 MICRO 필터로 형성된 제 4 여과부;의 조합으로 형성됨을 특징으로 하는 폐수 재활용 시스템이 제공된다.A chemical treatment unit formed of a pH adjusting tank into which caustic soda (NaOH), hydrochloric acid (HCL) flows, and a reaction tank into which a flocculant (HOC) flows; A pressure injured part formed of a sludge storage tank for removing the sludge separated from the pressure injured tank to generate fine bubbles to float the floating material; A circulation tank / storage tank which forms micro bubbles and regulates flow rate; A conventional first filtration unit for filtering sludge through diatomaceous earth while passing through a filter, a mixing tank, and a coating tank; A second filtration unit for filtering the wastewater controlled through a storage tank with an activated carbon filter; UV sterilizer for sterilization through UV device; A third filtration unit formed of a PEP filter circulating through the media to remove suspended matter and a storage tank for adjusting the flow rate; Provided is a waste water recycling system, characterized in that formed by a combination of a recycled water supply tank for adjusting the flow rate and a fourth filtration unit formed of a MICRO filter for removing residual fines.

Description

폐수 재활용 시스템 및 그 방법{Recycling system and the method of wastewater}Recycling system and the method of wastewater

본 발명은 브라운관 및 모니터의 세척수를 재활용하는 폐수 재활용 시스템에 관한 것으로, 더욱 상세하게는 무기응집제인 HOC 성분을 사용하여 입자응집한 후, 이를 가압부상하여 규조토 여과기, 활성탄 여과기, UV살균기, PEP 필터, 마이크로 필터로 처리함으로써, PAD, PAA 성분을 완전히 제거하여 공업용수 및 순수 원수로 재활용할 수 있을 뿐만 아니라, 무기응집제를 사용하므로 후처리 공정에 아무런 영향을 미치지 않는 폐수 재활용 시스템에 관한 것이다.The present invention relates to a wastewater recycling system for recycling the wash water of the CRT and monitor, and more particularly, after the particle agglomeration using the HOC component, which is an inorganic coagulant, by pressure flotation and diatomaceous earth filter, activated carbon filter, UV sterilizer, and PEP filter. By treating with a micro filter, PAD and PAA components can be completely removed and recycled to industrial water and pure water, and an inorganic coagulant is used.

일반적으로 브라운관 및 모니터의 세척으로 발생되는 폐수를 재활용하기 위한 방법으로, 화학적 방법과 물리적 방법이 있는데, 화학적 방법은 화학 약품 등을 사용하여 폐수에 함유된 오염물질의 물리적 혹은 화학적 상태를 변화시켜 침전과 분해제거 될 수 있도록 하는 방법이고, 물리적 방법은 필터가 장착된 하우징 내부로 폐수를 유입시켜 폐수에 함유된 오염물질이나 슬러지를 제거하는 방법이다.In general, there are chemical and physical methods for recycling wastewater generated by the cleaning of CRTs and monitors. The chemical method uses chemicals to change the physical or chemical state of contaminants in the wastewater. The physical method is to remove the contaminants or sludge contained in the waste water by introducing the waste water into the housing equipped with the filter.

상기 화학적 방법으로 폐수를 재활용할 경우, 이온증가에 따른 전도도(CONDUCTIVITY), TDS(TOTAL DISSOLVED SOLID)의 높은 상승 및 유기응집제 성분의 잔류로 인하여 후단 여과 시스템의 수명을 단축시키는 문제가 발생하고, 물리적 방법으로 폐수를 재활용할 경우, 폐수에 들어있는 본드의 원료성분인 PAD(Polyacrylamide Diacetoneacrylamide), PAA(Protactinium) 성분이 제거되지 않을 뿐만 아니라, 유기응집제의 잔류성분으로 인하여 후처리 필터와 고가의 설비인 R/O(REVERSE OSMOSIS)의 수명이 단축되는 등의 문제가 발생하고 있다.When the waste water is recycled by the above chemical method, there is a problem of shortening the lifespan of the rear-end filtration system due to the increase of the conductivity (CONDUCTIVITY), the TDS (TOTAL DISSOLVED SOLID), and the residual of the organic coagulant component. When recycling wastewater by the method, not only the polyacrylamide diacetoneacrylamide (PAD) and protactinium (PAA) components of the bond contained in the wastewater are removed but also the residual components of the organic coagulant, which is a post treatment filter and an expensive facility. Problems such as shortening the life of R / SE (REVERSE OSMOSIS) have occurred.

따라서 본 발명에서는 본 고안인이 선출원한 특허등록 제416656호 '규조토를 이용한 폐수의 재활용 장치'를 활용하여 PAD, PAA성분을 제거하는 동시에 후처리 공정에도 전혀 영향을 미치지 않는 폐수 재활용 시스템을 제시하고자 한다.Therefore, the present invention is to propose a wastewater recycling system that removes PAD and PAA components at the same time using the patent registration No. 416656 'apparatus recycling wastewater using diatomaceous earth', which does not affect the post-treatment process at all. do.

본 발명의 목적은 종래의 이와같은 문제점을 해소하고자 한 데 있는 것으로, 화학적 처리와 물리적 여과를 병행함으로써, 무기응집제인 HOC를 통해 폐수에 함유된 PAD, PAA 성분을 제거할 수 있고, 그로 인하여 버려지는 폐수를 재활용할 뿐만 아니라, 에너지를 절약하고, 환경을 보호할 수 있는데 있다.It is an object of the present invention to solve such problems in the prior art, by combining the chemical treatment and physical filtration, it is possible to remove the PAD, PAA components contained in the waste water through the inorganic coagulant HOC, thereby discarded Not only does waste not only recycle wastewater, but it also saves energy and protects the environment.

상기 목적을 달성하기 위한 수단으로, 화학물질을 투입하여 pH와 입자응집을 수행하는 화학처리부, 물 속에 공기와 약품을 분사시켜 오염물질을 강제로 띄운 뒤 제거하는 가압부상부, 규조토를 이용하여 여과처리하는 제 1 여과부, 활성탄을 통해 여과처리하는 제 2 여과부, 자외선으로 살균하는 UV살균기, PEP 필터를 통해 부유물을 제거하는 제 3 여과부, MICRO 필터로 잔여물질을 제거하는 제 4 여과부의 조합으로 형성되는 폐수 재활용 시스템을 제공하고자 한다. As a means for achieving the above object, the chemical treatment unit to perform the pH and particle aggregation by the input of chemicals, pressurized buoyancy to remove and then remove the contaminants by spraying air and chemicals in water, filtered using diatomaceous earth A first filtration unit for treatment, a second filtration unit for filtration through activated carbon, a UV sterilizer for sterilization with ultraviolet light, a third filtration unit for removing suspended solids through a PEP filter, and a fourth filtration unit for removing residues with a MICRO filter It is an object of the present invention to provide a wastewater recycling system formed by a combination.

통상의 폐수 재활용 방법에 있어서, 가성소다(NaOH), 염산(HCL), 응집제(HOC)를 통해 원수의 PH를 조정하고 입자를 응집시키는 화학적 처리단계; 미세기포를 생성 접촉시켜 부유물질을 부상 제거하는 가압부상단계; 규조토를 통해 폐수에 함유된 오염물질 및 슬러지를 여과하는 1차 여과단계; 활성탄을 통해 오염물질 및 슬러지를 여과하는 2차 여과단계; UV 살균기를 통해 박테리아와 TOC를 분해 제거하는 살균단계; PEP 필터의 구상 실리카 필터 메디아를 통해 부유물질을 제거하는 3차 여과단계; MICRO 필터로 잔류 미세물질을 제거하는 4차 여과단계;를 거쳐서 재활용됨을 특징으로 하는 것이다.In the conventional wastewater recycling method, a chemical treatment step of adjusting the pH of the raw water through the caustic soda (NaOH), hydrochloric acid (HCL), flocculant (HOC) and aggregates the particles; Pressurized flotation step of generating and contacting the fine bubbles to float floating material; A primary filtration step of filtering contaminants and sludge contained in the wastewater through the diatomaceous earth; A secondary filtration step of filtering contaminants and sludge through activated carbon; A sterilization step of decomposing and removing bacteria and TOC through a UV sterilizer; A third filtration step of removing suspended solids through the spherical silica filter media of the PEP filter; It is characterized in that it is recycled through a fourth filtration step of removing residual fines with a MICRO filter.

통상의 폐수 재활용 시스템에 있어서, 가성소다(NaOH), 염산(HCL)이 유입되는 pH 조정조와 응집제(HOC)가 유입되는 반응조 및 응집조로 형성된 화학처리부; 미세기포를 발생시켜 부유물질을 부상시키는 가압부상조와 상기 가압부상조에서 분리된 슬러지를 제거하는 제 1,2 슬러지 저장조로 형성된 가압부상부; 미세기포를 형성하고 유량을 조절하는 순환조/저류조; 여과기, 믹싱탱크, 코팅탱크를 거치면서 규조토를 통해 슬러지를 여과하는 통상의 제 1 여과부; 저류조를 통해 유량조절된 폐수를 활성탄 여과기로 여과하는 제 2 여과부; UV장치를 통해 살균처리하는 UV살균기; 미디어를 통해 순환처리하여 부유물을 제거하는 PEP 필터와 유량조절을 위한 저류조로 형성된 제 3 여과부; 유량을 조절하는 재활용수 공급탱크와 잔류 미세물질을 제거하는 MICRO 필터로 형성된 제 4 여과부;의 조합으로 형성됨을 특징으로 하는 것이다.In a conventional wastewater recycling system, a chemical treatment unit formed of a pH adjusting tank into which caustic soda (NaOH), hydrochloric acid (HCL) flows and a reaction tank and a flocculating tank into which a coagulant (HOC) flows; A pressure injured portion formed of a first and second sludge storage tanks for generating fine bubbles to float floating substances and removing sludge separated from the pressure injured tanks; A circulation tank / storage tank which forms micro bubbles and regulates flow rate; A conventional first filtration unit for filtering sludge through diatomaceous earth while passing through a filter, a mixing tank, and a coating tank; A second filtration unit for filtering the wastewater controlled through a storage tank with an activated carbon filter; UV sterilizer for sterilization through UV device; A third filtration unit formed of a PEP filter circulating through the media to remove suspended matter and a storage tank for adjusting the flow rate; And a fourth filtration unit formed of a recycled water supply tank for adjusting the flow rate and a MICRO filter for removing residual fine materials.

이하 첨부된 도면을 참조하여 본 발 명이 속하는 기술분야에서 통상의 지식을 가진 자가 본 발명의 기술적 사상을 용이하게 실시할 수 있도록 상세하게 설명하면 다음과 같다.Hereinafter, the present invention will be described in detail with reference to the accompanying drawings so that those skilled in the art may easily implement the technical idea of the present invention.

도 1은 본 발명의 전체를 도시한 상태도, 도 2는 본 발명의 흐름을 도시한 흐름도, 도 3은 본 발명에서 재활용수의 탁도를 도시한 그래프, 도 4는 본 발명에서 재활용수의 COD를 도시한 그래프, 도 5는 본 발명에서 재활용수의 SS를 도시한 그래프로서, 1 is a state diagram showing the whole of the present invention, Figure 2 is a flow chart showing the flow of the present invention, Figure 3 is a graph showing the turbidity of recycled water in the present invention, Figure 4 is a COD of recycled water in the present invention Figure 5, Figure 5 is a graph showing the SS of the recycled water in the present invention,

먼저 화학처리부(10)는 가성소다(NaOH), 염산(HCL), 응집제(HOC)가 보관되는 약품탱크(11a)(11b)(11c)와 pH 조정부(12), 반응조(13), 응집조(14)로 형성하는데, 이때 각 약품탱크(11a)(11b)(11c) 상에는 약품정량펌프(1)를 형성하고, pH 조정조(12), 반응조(13), 응집조(14)상에는 교반기(2)를 형성한다. First, the chemical treatment unit 10 is a chemical tank (11a) (11b) (11c) and pH adjusting unit (12), a reaction tank (13), a coagulation tank in which caustic soda (NaOH), hydrochloric acid (HCL) and a flocculant (HOC) are stored. At this time, the chemical metering pump (1) is formed on each of the chemical tank (11a) (11b) (11c), the pH adjusting tank (12), the reaction tank (13), the agitator (14) on the coagulation tank (14). 2) form.

그리고 가성소다(NaOH)와 염산(HCL)이 보관된 약품탱크(11a)(11b)의 관로는 pH 조정조(12)로 유입케하고, 응집제(HOC)가 보관된 약품탱크(11c)의 관로는 반응조(13)로 유입케한다.In addition, the conduits of the chemical tanks 11a and 11b in which caustic soda (NaOH) and hydrochloric acid (HCL) are stored are introduced into the pH adjusting tank 12, and the conduits of the chemical tanks 11c in which the flocculant (HOC) is stored. Inflow to the reactor (13).

가압부상부(20)는 감속기(3)가 형성된 가압부상조(21)와 레벨 게이지(4)가 형성된 제 1 슬러지 저장조(22) 및 상기 제 1 슬러지 저장조(22)와 배관 연결된 제 2 슬러지 저장조(22')로 형성하는데, 이때 가압부상조(21)의 관로상에는 DAF 펌프(6)를 형성하여 미세기포를 생성케 하고, 제 1,2 슬러지 저장조(22)(22') 사이의 관로상에는 슬러지 이송펌프(5a)를 형성하여 슬러지 이송 기능을 수행케 한다.The pressurization part 20 includes a pressurized flotation tank 21 in which a speed reducer 3 is formed, a first sludge storage tank 22 in which a level gauge 4 is formed, and a second sludge storage tank connected to the first sludge storage tank 22. And a DAF pump 6 is formed on the pipeline of the pressure flotation tank 21 to generate microbubbles, and on the pipeline between the first and second sludge storage tanks 22 and 22 '. A sludge conveying pump 5a is formed to perform a sludge conveying function.

순환조(30)/저류조(30')에서 먼저 순환조(30)의 관로상에는 가압부상조(21)와 연결된 DAF 펌프(6)를 함께 연결하고, 저류조(30')에는 레벨게이지(4)를 형성하며, 저류조(30')의 관로 중 하나를 슬러지 저장조(22)와 연결 형성한다.In the circulation tank 30 / storage tank 30 ', the DAF pump 6 connected to the pressure inlet tank 21 is connected together on the pipe line of the circulation tank 30, and the level gauge 4 is connected to the storage tank 30'. And one of the conduits of the storage tank 30 'is connected to the sludge storage tank 22.

제 1 여과부(40)는 본 고안인이 고안한 특허등록 제416656호 '규조토를 이용한 폐수의 재활용 장치'를 활용 개선한 것으로, 필터가 구비된 다수개의 규조토 여과기(41)에 규조토와 물을 혼합하여 1차 코팅액을 형성하는 규조토 믹싱탱크(42)를 형성하고, 상기 규조토 믹싱탱크(42) 일측으로는 1차 코팅액에 물을 혼합하여 2차 코팅액을 형성하는 규조토 코팅탱크(43)를 형성하는데, 이때 각 규조토 여과기(41)와 연결된 관로상에는 여과펌프(7a)를 형성하고, 규조토 믹싱탱크(42)와 연결된 관로상에는 공급펌프(8)를 형성하며, 규조토 코팅탱크(43)와 연결된 관로상에는 코팅펌프(9)를 형성한다. 또한 규조토 믹싱탱크(42)상에는 교반기(2)와 레벨게이지(4)를 형성하고, 규조토 코팅탱크(43)상에는 레벨게이지(4)만 형성한다.The first filtration unit 40 is improved by utilizing the patent registration No. 416656 'Recycling device for wastewater using diatomaceous earth' devised by the present inventors, diatomaceous earth and water to a plurality of diatomaceous earth filter 41 equipped with a filter A diatomaceous earth mixing tank 42 is formed to mix to form a primary coating solution, and on one side of the diatomaceous earth mixing tank 42, a diatomaceous earth coating tank 43 is formed to mix water with the primary coating solution to form a secondary coating solution. In this case, the filtration pump (7a) is formed on the pipeline connected to each of the diatomaceous earth filter 41, the supply pump (8) is formed on the pipeline connected to the diatomaceous earth mixing tank 42, the pipeline connected to the diatomaceous earth coating tank 43 On the coating pump 9 is formed. In addition, the stirrer 2 and the level gauge 4 are formed on the diatomaceous earth mixing tank 42, and only the level gauge 4 is formed on the diatomaceous earth coating tank 43.

제 2 여과부(50)는 레벨게이지(4)가 형성된 저류조(51)와 다수개의 활성탄 여과기(52)(52')로 형성하는데, 이때 저류조(51)와 활성탄 여과기(52)(52')를 연결하는 관로상에는 여과펌프(7b)를 형성한다.The second filtration unit 50 is formed of a storage tank 51 in which a level gauge 4 is formed and a plurality of activated carbon filters 52, 52 ′, wherein the storage tank 51 and activated carbon filters 52, 52 ′ are formed. The filtration pump (7b) is formed on the pipe connecting the.

제 3 여과부(60)는 내부에 구상의 실리카 필터 메디아가 형성된 PEP 필터(61)와 여과펌프(7c) 및 레벨게이지(4)가 형성된 저류조(62)로 형성하는데, 이때 제 2 여과부(50)와 제 3 여과부(60) 사이에는 UV 살균기(70)를 형성하고, 제 2 여과부(50)의 활성탄 여과기(52)(52')와 제 3 여과부(60)의 저류조(62) 사이에는 역세펌프(2a)를 형성한다.The third filtration unit 60 is formed of a PEP filter 61 in which a spherical silica filter media is formed, and a storage tank 62 in which a filtration pump 7c and a level gauge 4 are formed. A UV sterilizer 70 is formed between the 50 and the third filtration unit 60, and the storage tank 62 of the activated carbon filters 52, 52 ′ of the second filtration unit 50 and the third filtration unit 60. The backwash pump 2a is formed between the two.

제 4 여과부(80)는 재활용수를 공급하는 공급탱크(81)와 MICRO 필터(82)로 형성하는데, 공급탱크(81)와 MICRO 필터(82) 사이에는 이송펌프(5b)를 형서하고, 제 3 여과부(60)의 저류조(62)와 공급탱크(81) 사이에도 이송펌프(5c)를 형성한다.The fourth filtration unit 80 is formed of a supply tank 81 and a MICRO filter 82 for supplying recycled water, and form a transfer pump 5b between the supply tank 81 and the MICRO filter 82. A transfer pump 5c is also formed between the storage tank 62 and the supply tank 81 of the third filtration unit 60.

이상과 같이 형성된 시스템을 통해 폐수를 재활용하는 과정에 대해 살펴 보면,Looking at the process of recycling wastewater through the system formed as above,

먼저 화학적 처리단계로, First, chemical treatment

집수조(A)를 거쳐 pH 조정조(12)로 폐수의 원수가 유입되면, pH 조정조(12)로 약품탱크(11a)(11b)의 가성소다(NaOH)와 염산(HCL)이 투입 교반되어 원수(PH 4~10)를 오염물질을 요구하는 PH로 형성하게 된다.When the raw water of the wastewater flows into the pH adjusting tank 12 through the water collecting tank A, caustic soda (NaOH) and hydrochloric acid (HCL) of the chemical tanks 11a and 11b are introduced into the pH adjusting tank 12 and stirred. PH 4 ~ 10) to form a PH that requires pollutants.

pH를 조정한 후에는 원수를 반응조(13)로 유입시키는데, 이때 반응조(13) 내부에는 응집제(HOC)가 투입 교반되어 원수에 미세 플록(FLOC)을 형성하게 된다.After adjusting the pH, the raw water is introduced into the reaction tank 13, where a flocculant (HOC) is introduced into the reaction tank 13 to form a fine floc (FLOC) in the raw water.

여기서 무기응집제인 HOC는 키토산 메치올(Chitosan Methyol)을 주성분으로 하는 유백색 액체로, 유기물 제거와 색도 제거 및 기타 성분의 제거 기능을 수행할 수 있고, 응집력과 흡착력이 매우 우수한 약품이다.Here, HOC, an inorganic coagulant, is a milky white liquid containing chitosan methyol as a main component, and can remove organic matter, remove color, and remove other components, and has excellent cohesion and adsorption power.

반응조(13)를 거친 원수를 다시 응집조(14)로 유입 교반되어 미세 입자의 응집력을 촉진시키게 되고, 촉진된 입자들은 부상이 쉽도록 큰 플록(FOC)으로 성장시키게 도니다.Raw water passed through the reactor (13) is introduced into the coagulation tank (14) and stirred to promote cohesion of the fine particles, and the promoted particles are grown into large flocs (FOC) for easy flotation.

가압부상단계로, In the pressure injury step,

화학적 처리를 거친 원수를 가압 부상조(21)로 유입되는데, 이때 가압부상법을 통해 DAF 펌프(6)로 물과 공기를 혼합 흡입하여 도출하면서 미세기포를 생성하고, 생성된 기포는 부유물질에 접촉 부상시켜 탁도를 99%로 제거하며, 여기서 미세기포에 접촉 부상된 부유물질은 스키머(23)로 1차 제거한다. The raw water subjected to chemical treatment is introduced into the pressure flotation tank 21. At this time, microbubbles are generated by drawing and sucking water and air with the DAF pump 6 through the pressure flotation method, and the bubbles are generated in the suspended solids. Contact floating to remove the turbidity to 99%, where the suspended matter in contact with the microbubble is first removed by the skimmer (23).

상기 제거된 부유물질이나 오염물질은 제 1 슬러지 저장조(22)를 거쳐 제 2 슬러지 저장조(22')로 이송되고, 부유물질이 1차 제거된 처리수는 순환조(30)로 유입되어 DAF펌프(6)를 통해 또 다시 물과 공기를 혼합 흡입하여 미세기포를 형성하고, 미세기포가 형성된 처리수는 다시 저류조(30')로 유입되어 여과를 위한 유량을 조절하게 된다.The removed suspended solids or contaminants are transferred to the second sludge storage tank 22 'via the first sludge storage tank 22, and the treated water from which the suspended matter is first removed is introduced into the circulation tank 30 to supply the DAF pump. (6) again to mix and suck the water and air to form a micro-bubble, the treated water is formed in the micro-bubble again flows into the storage tank (30 ') to control the flow rate for filtration.

제 1 여과부(40) 통한 1차 여과단계로, In the first filtration step through the first filtration unit 40,

1차 여과는 규조토 믹싱탱크(42) → 규조토 코팅탱크(43) → 규조토 여과기(41)를 거쳐 코팅→정수→여과의 3가지 공정을 거치는데, 먼저 규조토 믹싱탱크(42)에서는 분말상태의 규조토와 물을 1.6:6의 혼합비로 혼합하여 1차 코팅액을 만들고, 규조토 코팅탱크(43)에서는 1차 코팅액에 물을 희석하여 2차 코팅액을 만들고, 상기 2차 코팅액을 규조토 여과기(41)로 펌핑하여 규조토 여과기(41) 내부에 형성된 필터에 코팅막을 형성한다. The primary filtration is through three processes of diatomaceous earth mixing tank (42) → diatomaceous earth coating tank (43) → diatomaceous earth filter (41), coating → water purification → filtration, and first, diatomaceous earth mixing tank (42) And water are mixed at a mixing ratio of 1.6: 6 to make a primary coating solution, and in the diatomaceous earth coating tank 43, dilute water to the primary coating solution to make a secondary coating solution, and pump the secondary coating solution to the diatomaceous earth filter 41. To form a coating film on the filter formed inside the diatomaceous earth filter (41).

규조토 여과기(41) 내부에 2차 코팅액이 코팅되면, 저류조(30')의 처리수가 각 규조토 여과기(41)로 유입되어 오염물질이 제거된 후, 제 2 여과부(50)의 저류조(51)로 유입된다.When the secondary coating solution is coated inside the diatomaceous earth filter 41, the treated water of the storage tank 30 ′ flows into each diatomaceous earth filter 41 to remove contaminants, and then the storage tank 51 of the second filtration unit 50. Flows into.

그리고 이때 차압이 어느정도 발생하게 되면 자동으로 air가 유입되어 역세가 이루어 지며, 역세가 끝나면 다시 코팅공정이 이루어지며 순환하게 되는데, 이때 역세를 통해 제거된 슬러지들은 가압부상조(21)의 슬러지가 유입되는 슬러지 저장조(22)로 이동하여 제거된다.And when the differential pressure occurs to some extent, air is automatically introduced into the backwash, and when the backwash is completed, the coating process is performed again and circulated. At this time, the sludge removed through backwashing is introduced with the sludge from the pressure injured tank 21. It is moved to the sludge reservoir 22 to be removed.

제 2 여과부(50)를 통한 2차 여과단계로, In the second filtration step through the second filtration unit 50,

규조토를 통해 여과공정을 거친 처리수가 저류조(51)로 유입되면, 활성탄 여과를 위한 유량이 조절된 후, 활성탄 여과기(52)(52')로 유입되어 각종 유기물 및 COD를 흡착 제거하게 된다.When the treated water that has undergone the filtration process through the diatomaceous earth is introduced into the storage tank 51, the flow rate for activated carbon filtration is adjusted, and then the activated carbon filters 52 and 52 ′ are introduced to adsorb and remove various organic substances and COD.

그리고 활성탄 여과기(52)(52')의 배관 말단 부분에 UV살균기(70)가 형성되어져 있어, 자외선 파장을 이용하여 물속에 함유되어 있는 박테리아 및 TOC(Total Organic Carbon)를 산화 분해시켜 제거한다.The UV sterilizer 70 is formed at the pipe end portion of the activated carbon filters 52 and 52 'to oxidatively decompose bacteria and TOC (Total Organic Carbon) contained in water using ultraviolet wavelengths.

제 3 여과부(60)를 통한 3차 여과단계로, In the third filtration step through the third filtration unit 60,

상기에서 살균처리된 처리수는 저류조(62)로 유입되어 유량이 조절된 후, PEP 필터(61)를 통해 여과되는데, 이때 PEP 필터(61)의 구상 실리카 필터메디아에 의해 처리수를 연속 순환 처리하여 부유물질을 제거하고, 부유물질에 제거된 처리수는 저류조(62)로 재유입시켜 유량을 조정한다.After the sterilized treatment water is introduced into the storage tank 62 and the flow rate is controlled, the treated water is filtered through the PEP filter 61, in which the treated water is continuously circulated by the spherical silica filter media of the PEP filter 61. To remove the suspended solids, and the treated water removed in the suspended solids is reflowed into the storage tank 62 to adjust the flow rate.

제 4 여과부(80)를 통한 4차 여과단계로, In the fourth filtration step through the fourth filtration unit 80,

제 3 여과부(60)의 저류조(62)를 통해 재활용수 공급탱크(81)로 유입되어 유량을 조절한 후, 카트리지 필터인 MICRO 필터(82)를 통해 물속에 잔류되어 있는 미세물질을 제거하여 재활용수로 사용할 수 있게 된다.After entering the recycle water supply tank 81 through the storage tank 62 of the third filtration unit 60 to adjust the flow rate, and removes the fine material remaining in the water through the cartridge filter MICRO filter 82 It can be used as recycled water.

이하 재활용을 위해 기존 수질테스트를 통한 수질현황을 살펴보면, Looking at the water quality through the existing water quality test for recycling,

상기 표 1은 LG PHILIPS-DISPLAYS(주) 구미 1공장을 대상으로한 수질현황의 실험결과로, 현재 유입되는 공업용수 원수 대비 이온성분 함유량인 전도도가 단지 26% 정도 높은 수준으로 공업용수로 사용함에 전혀 문제가 없음을 확인할 수 있고, 일반적인 공장폐수의 화학처리 수질보다 우수한 상태임을 알 수 있다. Table 1 is an experimental result of the water quality of LG PHILIPS-DISPLAYS Co., Ltd. Gumi Plant 1, and uses only 26% higher conductivity as the ionic content of industrial water. It can be confirmed that there is no problem at all, and it is superior to the chemical treatment water quality of general factory wastewater.

상기 표 2는 LG 전자(주) PDP공장을 대상으로한 수질현황의 실험결과로, 폐수원수의 육안 검사로는 탁도가 낮게 보이나 실제로는 20~33NTU정도의 고탁도 였으며 응집제를 투입하여 화학반응 후 부상을 시키면 상당량의 Scum이 발생하였다. 또한 pH조정 및 응집제 투입으로 인한 2차 오염은 Na+, Cl-이온의 증가로 나타났으나, 총 이온수가 낮기 때문에 순수제조시설에서 부하 증가 요인은 없을 것으로 예상된다.Table 2 shows the results of the water quality test for LG Electronics PDP plant, which showed low turbidity by visual inspection of wastewater, but was actually 20 ~ 33 NTU in turbidity. Injuries resulted in a significant amount of scum. In addition, secondary pollution due to pH adjustment and flocculant addition increased Na + and Cl- ions, but there is no increase factor in pure water manufacturing facilities due to low total ion water.

상기 표 1은 LG PHILIPS-DISPLAYS(주) 창원 2공장을 대상으로한 수질현황의 실험결과로, 탁도, 전도도 등의 수질데이터로 보아 공업용수 및 순수의 원수로 사용하는데 지장이 없고, 다만 COD가 조금 높으나 후처리시설의 설치로서 무난히 해결할 수 있는 사항임을 알 수 있다.Table 1 above is an experimental result of the water quality of LG PHILIPS-DISPLAYS Co., Ltd. Changwon Plant 2, and it is not a problem to use it as raw water of industrial water and pure water in terms of water quality data such as turbidity and conductivity. Although it is a little high, it can be understood that it is a matter that can be easily solved by installing after-treatment facilities.

상기 표 5는 LG PHILIPS-DISPLAYS(주) 창원 2공장을 대상으로한 폐수 재활용후의 수질결과로, 각 처리과정별 탁도, COD, SS를 나타낸 것이다.Table 5 shows the water quality after wastewater recycling for LG PHILIPS-DISPLAYS Changwon Plant 2, showing turbidity, COD, and SS for each treatment process.

상기 표 5와 도 3 내지 5를 통해 탁도, COD, SS가 공정을 거침에 따라 감소되는 것을 확인할 수 있고, 전체 여과효율은 탁도가 100% 제거, COD 68%제거, SS도 99% 제거됨을 확인할 수 있다.Through Table 5 and Figures 3 to 5 it can be seen that turbidity, COD, SS is reduced as the process goes through, the overall filtration efficiency is confirmed that 100% removal of turbidity, 68% removal of COD, 99% SS also removed Can be.

이와같이 된 본 발명은 가성소다(NaOH), 염산(HCL), 응집제(HOC)를 통한 화학적 처리와 제 1~4 여과부를 통한 물리적 여과를 병행함으로써, 폐수에 함유된 PAD, PAA 성분을 응집제인 HOC가 제거할 수 있고, 이 HOC성분은 후처리 공정에도 어떠한 영향을 미치지 않아 장치의 수명을 연장시킬 수 있는 동시에 여과 청정도를 증대시킬 수 있어, 폐수의 재활용 효율을 증대시킨데 그 효과가 있다.In the present invention, the chemical treatment through caustic soda (NaOH), hydrochloric acid (HCL), flocculant (HOC) and physical filtration through the first to fourth filtration units are performed, thereby the PAC and PAA components contained in the wastewater are collected by HOC. This HOC component has no effect on the post-treatment process, which can extend the life of the apparatus and at the same time increase the filtration cleanliness, thereby increasing the recycling efficiency of the wastewater.

도 1은 본 발명의 전체를 도시한 상태도1 is a state diagram showing the whole of the present invention

도 2는 본 발명의 흐름을 도시한 흐름도2 is a flow chart illustrating the flow of the present invention.

도 3은 본 발명에서 재활용수의 탁도를 도시한 그래프Figure 3 is a graph showing the turbidity of recycled water in the present invention

도 4는 본 발명에서 재활용수의 COD를 도시한 그래프Figure 4 is a graph showing the COD of the recycled water in the present invention

도 5는 본 발명에서 재활용수의 SS를 도시한 그래프Figure 5 is a graph showing the SS of the recycled water in the present invention

< 도면의 주요부분에 대한 부호의 설명 ><Description of Symbols for Major Parts of Drawings>

10: 화학 처리부 11a,11b,11c: 약품탱크 12: pH조정조10: chemical treatment unit 11a, 11b, 11c: chemical tank 12: pH adjustment tank

13: 반응조 14 응집조 20: 가압부상부13: reactor 14 flocculation tank 20: pressurized part

21: 가압부상부 22,22': 슬러지 저장조 23: 스키머 21: Pressurized part 22,22 ': Sludge storage tank 23: Skimmer

30: 순환조 30': 저류조 40: 제 1 여과부 30: circulation tank 30 ': storage tank 40: first filtration unit

41: 규조토 여과기 42: 규조토 믹싱탱크 43: 규조토 코팅탱크41: diatomaceous earth filter 42: diatomaceous earth mixing tank 43: diatomaceous earth coating tank

50: 제 2 여과부 51: 저류조 52,52': 활성탄 여과기50: second filter 51: reservoir 52,52 ': activated carbon filter

60: 제 3 여과부 61: PEP 필터 62: 저류조60: third filtration unit 61: PEP filter 62: storage tank

70: UV 살균기 80: 제 4 여과부 81: 공급탱크70: UV sterilizer 80: fourth filtration unit 81: supply tank

82: MICRO 필터82: MICRO filter

Claims (2)

통상의 폐수 재활용 방법에 있어서, 가성소다(NaOH), 염산(HCL), 응집제(HOC)를 통해 원수의 PH를 조정하고 입자를 응집시키는 화학적 처리단계; 미세기포를 생성 접촉시켜 부유물질을 부상 제거하는 가압부상단계; 규조토를 통해 폐수에 함유된 오염물질 및 슬러지를 여과하는 1차 여과단계; 활성탄을 통해 오염물질 및 슬러지를 여과하는 2차 여과단계; UV 살균기를 통해 박테리아와 TOC를 분해 제거하는 살균단계; PEP 필터의 구상 실리카 필터 메디아를 통해 부유물질을 제거하는 3차 여과단계; MICRO 필터로 잔류 미세물질을 제거하는 4차 여과단계;를 거쳐서 재활용됨을 특징으로 하는 폐수 재활용 방법.In the conventional wastewater recycling method, a chemical treatment step of adjusting the pH of the raw water through the caustic soda (NaOH), hydrochloric acid (HCL), flocculant (HOC) and aggregates the particles; Pressurized flotation step of generating and contacting the fine bubbles to float floating material; A primary filtration step of filtering contaminants and sludge contained in the wastewater through the diatomaceous earth; A secondary filtration step of filtering contaminants and sludge through activated carbon; A sterilization step of decomposing and removing bacteria and TOC through a UV sterilizer; A third filtration step of removing suspended solids through the spherical silica filter media of the PEP filter; Waste water recycling method characterized in that recycled through a; 4th filtration step of removing residual fines with a MICRO filter. 통상의 폐수 재활용 시스템에 있어서, 가성소다(NaOH), 염산(HCL)이 유입되는 pH 조정조와 응집제(HOC)가 유입되는 반응조 및 응집조로 형성된 화학처리부; 미세기포를 발생시켜 부유물질을 부상시키는 가압부상조와 상기 가압부상조에서 분리된 슬러지를 제거하는 슬러지 저장조로 형성된 가압부상부; 미세기포를 형성하고 유량을 조절하는 순환조/저류조; 여과기, 믹싱탱크, 코팅탱크를 거치면서 규조토를 통해 슬러지를 여과하는 통상의 제 1 여과부; 저류조를 통해 유량조절된 폐수를 활성탄 여과기로 여과하는 제 2 여과부; UV장치를 통해 살균처리하는 UV살균기; 미디어를 통해 순환처리하여 부유물을 제거하는 PEP 필터와 유량조절을 위한 저류조로 형성된 제 3 여과부; 유량을 조절하는 재활용수 공급탱크와 잔류 미세물질을 제거하는 MICRO 필터로 형성된 제 4 여과부;의 조합으로 형성됨을 특징으로 하는 폐수 재활용 시스템.In a conventional wastewater recycling system, a chemical treatment unit formed of a pH adjusting tank into which caustic soda (NaOH), hydrochloric acid (HCL) flows and a reaction tank and a flocculating tank into which a coagulant (HOC) flows; A pressure injured part formed of a sludge storage tank for removing the sludge separated from the pressure injured tank to generate fine bubbles to float the floating material; A circulation tank / storage tank which forms micro bubbles and regulates flow rate; A conventional first filtration unit for filtering sludge through diatomaceous earth while passing through a filter, a mixing tank, and a coating tank; A second filtration unit for filtering the wastewater controlled through a storage tank with an activated carbon filter; UV sterilizer for sterilization through UV device; A third filtration unit formed of a PEP filter circulating through the media to remove suspended matter and a storage tank for adjusting the flow rate; And a fourth filtration unit formed of a recycled water supply tank for adjusting the flow rate and a MICRO filter for removing residual fine materials.
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KR100931987B1 (en) * 2009-09-04 2009-12-15 주식회사 무진하이테크 Water treatment apparatus for purifing waste water using micro-bubbles
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