KR100794198B1 - Suspension contact 2nd sewage disposal system - Google Patents

Suspension contact 2nd sewage disposal system Download PDF

Info

Publication number
KR100794198B1
KR100794198B1 KR20060094660A KR20060094660A KR100794198B1 KR 100794198 B1 KR100794198 B1 KR 100794198B1 KR 20060094660 A KR20060094660 A KR 20060094660A KR 20060094660 A KR20060094660 A KR 20060094660A KR 100794198 B1 KR100794198 B1 KR 100794198B1
Authority
KR
South Korea
Prior art keywords
contact
tank
primary
bath
water
Prior art date
Application number
KR20060094660A
Other languages
Korean (ko)
Inventor
이경섭
Original Assignee
이경섭
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by 이경섭 filed Critical 이경섭
Priority to KR20060094660A priority Critical patent/KR100794198B1/en
Application granted granted Critical
Publication of KR100794198B1 publication Critical patent/KR100794198B1/en

Links

Images

Classifications

    • 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
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/10Packings; Fillings; Grids
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/12Activated sludge processes
    • C02F3/20Activated sludge processes using diffusers
    • 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
    • C02F2209/42Liquid level
    • 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

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Microbiology (AREA)
  • Biological Treatment Of Waste Water (AREA)

Abstract

An apparatus for treating sewage in a two-step type is provided to improve the performance of a flux regulating bath, thereby improving the efficiency of the apparatus and stabilizing the treatment process of the sewage. A sewage treatment apparatus comprises an adulteration separating bath(20) and a flux regulating bath(30) for a first-step process, a first contact aeration bath(40) and a first precipitation bath(50) for a second-step process, and a second contact aeration bath(60), a second precipitation bath(70), and a discharge bath(90) for a third-step process. A contact agent supporting frame for buffering the change of input load is installed within each of the flux regulating bath, the first contact aeration bath, and the second contact aeration bath. Contact agent fixing nets are installed at an upper portion and a lower portion of the contact agent supporting frame. Each of the contact agent fixing nets has a plurality of contact media thereon. Further, a plurality of contact beds is inside the contact agent supporting frame.

Description

현수형 접촉산화 2차하수처리 장치{Suspension contact 2nd sewage disposal system}Suspension contact 2nd sewage disposal system

도 1은 본 발명의 전체도      1 is an overall view of the present invention

도 2는 본 발명에 적용된 집수조의 확대도      Figure 2 is an enlarged view of the sump tank applied to the present invention

도 3은 본 발명의 접촉재지지틀과 고정네트 사시도      Figure 3 is a perspective view of the contact frame and the fixing net of the present invention

도 4는 본 발명의 접촉상의 롤 상으로 제작된 상태의 사시도       Figure 4 is a perspective view of the state produced on the roll of the contact phase of the present invention

도 5는 본 발명의 접촉상이 접촉재지지틀 내부에 설치된 정면도      Figure 5 is a front view of the contact phase of the present invention installed inside the contact frame

도 6은 본 발명의 공정 블록도      6 is a process block diagram of the present invention.

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

10: 하수처리장치 20: 협잡물분리조     10: sewage treatment apparatus 20: contaminant separation tank

21: 오수유입구 22: 경계벽     21: Sewage inlet 22: Boundary wall

23: 개구부 30: 전환유량조정조    23: opening 30: switching flow adjustment tank

31: 접촉재지지틀 32: 1차접촉상     31: contact support frame 32: primary contact phase

32a: 롤 32b: 노출부    32a: roll 32b: exposed portion

32c: 비노출부 33: 고정네트     32c: non-exposed part 33: fixed net

34: 집수조 35: 1단 에어리프트     34: sump 35: single stage air lift

36: 산기공급기 37: 반송구     36: diffuser 37: return port

38: 2단에어리프트 39: 공기조절밸브     38: two-stage air lift 39: air control valve

40: 1차접촉폭기조 41: 접촉재지지틀     40: primary contact aeration tank 41: contact support frame

42 : 2차접촉상 42a: 롤    42: secondary contact 42a: roll

42b: 노출부 42c: 비노출부     42b: exposed portion 42c: non-exposed portion

43: 고정네트 44: 산기공급기    43: fixed net 44: diffuser

50: 1차침전조 51: 1차정류기    50: primary precipitator 51: primary rectifier

52: 1차월류기 53: 1차 슬러지이송관    52: primary overflow machine 53: primary sludge transfer pipe

60: 2차 접촉폭기조 61: 접촉재지지틀    60: secondary contact aeration tank 61: contact support frame

62: 3차접촉상 62a: 롤     62: tertiary contact phase 62a: roll

62b: 노출부 62c: 비노출부    62b: exposed portion 62c: non-exposed portion

63: 고정네트 64: 산기공급기     63: fixed net 64: diffuser feeder

70: 2차침전조 71: 2차정류기     70: secondary precipitator 71: secondary rectifier

72: 2차월류기 73: 2차슬러지이송관     72: secondary overflow machine 73: secondary sludge transfer pipe

80: 슬러지저장조 90: 방류조    80: sludge storage tank 90: discharge tank

91: 방출구     91: discharge port

본 발명은 하수처리 장치에 관한 것으로서, 특히 하수처리 정화 공정 내 각기 공정별 오염부하 특성에 환경성이 강한 미생물의 군락을 단계별로 구성시켜 상호 먹이원의 특성에 의한 미생물군의 형성과 다단계 공정에 의한 먹이사슬의 연계성을 형성하는 것과, 자연과학적 미생물의 요구 특성을 생활 하수처리와 근접시켜 정화 공정을 관리의 편리함과 아울러 지속성이 연계되어 깨끗한 처리수를 얻을 수 있는 현수형 접촉산화 2차 하수처리 장치에 관한 것이다.      The present invention relates to a sewage treatment apparatus, and in particular, by constructing a group of microorganisms having a high environmental impact on the pollution load characteristics of each process in the sewage treatment purification step by step, the formation of a microbial group by the characteristics of mutual food sources and the multi-step process. Suspension type contact oxidation secondary sewage treatment device that can establish clean food water by forming the food chain linkage and bringing the required characteristics of natural scientific microorganisms into the daily sewage treatment, and the convenience and management of the purification process. It is about.

일반적으로 소규모 하수처리시설에 있어 미생물의 부착 정화방식은 관리적 부재요인을 충족하기 위하여 미생물의 부착특성과 미생물의 양적 부족에서 근시안적으로 찾아 효율성에 근접시킴으로써 연구개발 특성과 미생물의 특성 그리고 관리자의 현실적 여건이 서로 상이하여 효과적인 결과 도출이 어려운 실정이었다.      In general, in small sewage treatment facilities, the microbial attachment and purification method finds near-efficiency in microbial adhesion characteristics and quantitative deficits of microorganisms to meet administrative absence factors, thereby achieving efficiency of R & D, microbial characteristics, and manager's reality. Different from each other, it was difficult to obtain effective results.

그리하여, 물리적 방법이나 그 외 다른 업종의 정수방법 기술이 접목되거나 생물학적 처리과정을 수직의 현수식 접촉재를 나열시켜 단위 길이마다 많은 미생물이 부착되도록 많은 연구와 개발을 하여 사용하여 왔다.      As a result, many researches and developments have been made to incorporate physical methods or water purification techniques of other industries, or to use biological treatments to arrange vertical suspension contact materials so that many microorganisms are attached to each unit length.

그러나, 접촉재에 미생물의 부착량을 무작정 증가시킴으로써 접촉재의 단위 길이 당 미생물의 부착밀도가 높아 생물막 비대화 요인이 되어 유입 먹이원이 증가되거나 감소할 때에 활성리듬의 변화로 탈리와 부착의 편차가 심하여 수처리의 효율성이 일정하지 못하고 유입 하수원에 따라 좌우되는 요인이 많았다. 또한, 미생물 접촉재의 단위 길이 당 배양밀도가 높아 유지관리에 많은 정성과 미생물활성의 지속을 위한 환경적 조건의 유지가 불가피하였고, 그 유지결과에 따라 수처리 효율성이 좌우되는 모순이 대두 되고 있는 실정이다, 또한, 물리적 처리공정이나 정수업계의 중공사막, 막분리, 여과 등의 기술을 병행시켜 접목시 초기 효과는 용이하나 관리적 요인 중가와 주기적 교체 보수로 사후 유지관리비용이 많이 소요되는 취 약성을 지니고 있다.However, by inadvertently increasing the amount of microorganisms attached to the contact material, the adhesion density of microorganisms per unit length of the contact material is high, which causes biofilm thickening, and when the inflow source is increased or decreased, there is a significant variation in detachment and adhesion due to the change in active rhythm. The efficiency of the system was not constant and there were many factors that depended on the inflow sewer. In addition, due to the high culture density per unit length of the microbial contact material, it was inevitable to maintain a lot of quality and environmental conditions for the maintenance of microbial activity, and the contradiction of water treatment efficiency depends on the maintenance result. In addition, the initial effect is easy when grafting by using technologies such as hollow fiber membrane, membrane separation, and filtration in the physical treatment process or water purification industry. have.

본 발명은 상기와 같은 문제점을 해결하기 위하여 안출 한 것으로서, 자연과학적 미생물 특성에 인위적인 기본 여건을 부과할 때 미생물의 활성리듬이 증가됨을 인지하여 정화공정 내 각기 공정별 중에 전환유량조정조와, 1, 2차접촉폭기조 내에 노출과 비노출부를 갖는 롤 모양의 접촉상을 설치하여 미생물의 활성리듬이 증가되는 것을 목적으로 하고 있으며, 또 다른 목적은 단위 길이 당 최대 0.5~1.0cm 두께가 형성되어 저밀도로 유지되면서 생명력과 환경 적응성이 강한 다양한 미생물 군을 유지할 수 있어 생활하수처리와 근접시킨 정화 공정으로 관리의 편리함과 효율의 지속성이 연계되어 깨끗한 처리수를 얻을 수 있는 것을 제공함에 그 목적 있는 것이다.       The present invention has been made to solve the above problems, it is recognized that the active rhythm of the microorganism is increased when imposing artificial basic conditions on the nature of microbial characteristics, the conversion flow adjustment tank during each process in the purification process, 1, The purpose is to increase the active rhythm of microorganisms by installing a roll-shaped contact phase having exposed and non-exposed portions in the secondary contact aeration tank, and another object is to maintain a low density by forming a maximum thickness of 0.5 to 1.0 cm per unit length. In addition, it is possible to maintain a variety of microorganisms with strong vitality and environmental adaptability, and to provide clean treatment water by pursuing the purification process in close proximity to domestic sewage treatment and maintaining the convenience and efficiency of efficiency.

상기 목적을 달성하기 위한 본 발명의 하수처리장치는 전환유량조정조 측부에는 수위 저하에 따른 이송량 감소요인의 해결 및 유량조절의 효율성 증대를 위한 1단 에어리프트와, 상기 1단 에어리프트 상단부가 연결된 집수조에는 후기 공정인 1 차접촉폭기조에 대한 이송 수고가 낮아 원활한 이송이 가능하도록 정량의 원수를 공기부상으로 이송할 수 있는 2단 에어리프트와, 상기 집수조 벽면에는 상기 1단 에어리프트의 이송수 과다시 전환유량조정조로 순환시킬 수 있는 반송구와, 상기 1, 2단에어리프트에는 이송량을 제어할 수 있는 공기조절밸브와 1,2차접촉폭기조 내부에 배치된 접촉재지지틀 내부에는 다수개로 형성된 2, 3차접촉상과, 상기 접촉재지지틀 상부와 하부에는 2, 3차접촉상을 상부와 하부에서 현수 되도록 지지하는 고정네트와, 상기 2, 3차접촉상 하부에는 한 개 이상의 산기공급기와, 상기 1,2,3차접촉상은 자유굴곡 롤상으로 노출부와 비노출부와, 1,2,3차접촉상은 돌기부가 없는 평면 망목상으로 편직하여 단위 길이 당 저밀도 최대 0.5 ~ 1.0cm이내 두께가 형성된 특징이 있다.In the sewage treatment apparatus of the present invention for achieving the above object, a first stage air lift and a water collecting tank connected to an upper end of the first stage air lift for solving the factors of reducing the flow rate and increasing the efficiency of the flow rate on the side of the switching flow adjustment tank. There is a two-stage air lift that can transfer a fixed amount of raw water to the air float so as to facilitate the smooth transfer, because the transport effort for the primary contact aeration tank, which is a later process, is excessive, and the water tank wall has excessive transfer water of the first stage air lift. 2, formed of a plurality of conveying ports for circulating through the switching flow adjusting tank, and air control valves for controlling the feeding amount and contacting support frames disposed inside the 1st and 2nd contact aeration tanks. And a fixing net for supporting the third and third contact images so that the second and third contact images are suspended from the upper and lower portions in the upper and lower portions of the contact support frame. At least one diffuser feeder in the lower part of the second and third contact phases, the 1,2,3rd contact phases are free bending rolls, the exposed and non-exposed parts, and the 1,2,3rd contact phases are flat meshes without projections. Knitting is characterized by a thickness of less than 0.5 ~ 1.0cm maximum density per unit length.

이하, 본 발명을 첨부된 도면을 참고로 하여 상세히 설명하면 다음과 같다.      Hereinafter, the present invention will be described in detail with reference to the accompanying drawings.

도 1은 본 발명의 전체도이고, 도 2는 본 발명에 적용된 집수조의 확대도이며, 도 3은 본 발명의 접촉재지지틀과 접촉재고정네트 사시도이고, 도 4는 본 발명의 접촉상이 롤상으로 제작된 상태의 사시도이며, 도5 본 발명의 다수개의 접촉상이 접촉재지지틀 내부에 설치된 정면도이고, 도 6은 본 발명의 전체 공정 블록도이다.1 is an overall view of the present invention, Figure 2 is an enlarged view of the sump tank applied to the present invention, Figure 3 is a perspective view of the contact frame and the contact fixing net of the present invention, Figure 4 is a roll of the contact phase of the present invention 5 is a front view of a plurality of contact phases of the present invention installed inside the contact frame, and FIG. 6 is a block diagram of the entire process of the present invention.

도시된 바와 같이 하수처리장치(10)에는 하수가 유입할 수 있는 오수유입구(21)를 갖는 협잡물분리조(20)가 선단에 배치되고, 상기 협잡물분리조(20)와 차기공정인 전환유량조정조(30) 사이의 경계벽(22) 하부에는 개구부(23)가 설치되며, 상기 전환유량조정조(30)내부에는 접촉재지지틀(31)이 배치되고, 상기 접촉재지지틀(31)내부에는 다수개가 형성된 1차접촉상(32)이 입설되며, 상기 접촉재지지틀(31) 상부와 하부에는 1차접촉상(32)을 상부와 하부에서 현수 되도록 지지하는 고정네트(33)가 고정되어 있다.      As shown in the sewage treatment apparatus 10, a contaminant separation tank 20 having a sewage inlet 21 into which sewage may flow is disposed at the tip, and a conversion flow adjustment tank which is the next step with the contaminant separation tank 20. An opening 23 is provided in the lower portion of the boundary wall 22 between the openings 30, and a contact support frame 31 is disposed inside the switching flow rate adjustment tank 30, and a plurality of contact inside support frame 31 is provided. A dog-shaped primary contact image 32 is installed, and a fixing net 33 for supporting the primary contact image 32 to be suspended from the upper and lower portions is fixed to the upper and lower portions of the contact material support frame 31. .

상기 1차접촉상(32) 측면부에는 차기공정인 집수조(34)로 이송하기 위한 1단 에어리프트(35)가 배치되고, 1차접촉상(32) 하부에는 한 개 이상의 산기공급기(36)가 배치되며, 상기 집수조(34) 벽면에는 상기 1단 에어리프트(35)의 이송수 과다시 전환유량조정조(30)로 순환되어 연속된 기능을 갖는 반송구(37)가 배치되고, 상기 집수조(34) 차기 공정인 1차 접촉폭기조(40)로 이송수를 공급하는 2단 에어리프트(38)가 배치되며, 상기 1, 2단에어리프트(35)(38)에는 이송량을 제어할 수 있는 공기조절밸브(39)가 각각 설치되어 있다.      A first stage air lift 35 is disposed at a side surface of the primary contact bed 32 for transferring to a water collecting tank 34, which is the next process, and at least one diffuser supplier 36 is disposed below the primary contact bed 32. On the wall surface of the water collecting tank (34), a conveying port (37) having a continuous function is arranged and circulated to the transfer flow rate adjusting tank (30) of the first stage air lift (35), and the water collecting tank (34) is disposed. 2) the second stage air lift 38 for supplying the feed water to the primary contact aeration tank 40, which is the next process, is disposed, and the air control capable of controlling the transfer amount is provided in the first and second stage air lifts 35 and 38. The valves 39 are provided respectively.

상기 1차 접촉폭기조(40)내부에는 접촉재지지틀(41)이 배치되고, 상기 접촉재지지틀(41)내부에는 다수개로 형성된 2차접촉상(42)이 입설되며, 상기 접촉재지지틀(41) 상부와 하부에는 2차접촉상(42)을 상부와 하부에서 현수 되도록 지지하는 고정네트(43)가 배치되고, 상기 2차접촉상(42)의 하부에는 한 개 이상의 산기공급기(44)가 배치되며, 1차 접촉폭기조(40)와 1차 침전조(50) 사이에는 이송관(a)으로 연결되어 있다.      A contact support frame 41 is disposed in the primary contact aeration tank 40, and a plurality of secondary contact images 42 are provided in the contact support frame 41. (41) At the top and the bottom of the fixing net 43 for supporting the secondary contact phase (42) to be suspended from the top and bottom is arranged, one or more diffuser feeder 44 in the lower portion of the secondary contact image (42) ) Is disposed, and is connected to the transfer pipe (a) between the primary contact aeration tank 40 and the primary precipitation tank (50).

상기 1차 침전조(50) 내부에는 유입ㆍ유출에 대한 와류를 제거하는 1차정류기(51)와 1차월류기(52)가 상호 이격 배치되며, 1차 침전조(50) 바닥면에 쌓여 있는 슬러지를 슬러지저장조(80)로 이송하는 1차슬러지이송관(53)이 배치되어 있고, 1차 침전조(50)와 2차 접촉폭기조(60) 사이에는 이송관(b)이 연결되어 있다.       Inside the primary sedimentation tank 50, the primary rectifier 51 and the primary overcurrent flower 52 for removing vortices for inflow and outflow are disposed to be spaced apart from each other, and the sludge accumulated on the bottom surface of the primary sedimentation tank 50 is disposed. The primary sludge conveying pipe (53) for transporting to the sludge storage tank (80) is arranged, and the conveying pipe (b) is connected between the primary settling tank (50) and the secondary contact aeration tank (60).

상기 2차 접촉폭기조(60) 접촉재지지틀(61)이 배치되고, 상기 접촉재지지틀(61)내부에는 다수개가 형성된 3차접촉상(62)이 입설되며, 상기 접촉재지지틀(61) 상부와 하부에는 3차접촉상(62)을 상부와 하부에서 현수 되도록 지지하는 고정네트(63)가 배치되고, 상기 3차접촉상(62)의 하부에는 한 개 이상의 산기 공급기(64)가 배치되어 있으며, 2차 접촉폭기조(60)와 2차침전조(70)와는 이송관(c)으로 연결되어 있다.      The secondary contact aeration tank 60, the contact material support frame 61 is disposed, and the third contact image 62 is formed in the contact material support frame 61, a plurality of the contact contact frame 61, The upper and lower fixing net 63 for supporting the tertiary contact phase 62 to be suspended from the upper and lower, and one or more diffuser feeder 64 is provided at the lower portion of the tertiary contact phase 62 The secondary contact aeration tank 60 and the secondary sedimentation tank 70 are connected by a transfer pipe c.

상기 2차 침전조(70) 내부에는 유입ㆍ유출에 대한 와류를 제거하는 2차정류기(71)와 2차월류기(72)가 상호 이격 배치되며, 2차 침전조(70) 바닥면에 쌓여 있는 슬러지를 슬러지저장조(80)조 이송하는 2차슬러지이송관(73)이 배치되어 있고, 2차 침전조(70) 방류조(90) 사이에는 이송관(d)이 연결되어 있다.      Inside the secondary sedimentation tank 70, the secondary rectifier 71 and the secondary moon current flower 72 for removing vortices for inflow and outflow are disposed apart from each other, and the sludge accumulated on the bottom surface of the secondary sedimentation tank 70 is disposed. Secondary sludge conveying pipes 73 for transporting the sludge storage tank 80 tank are arranged, and the transfer pipe d is connected between the secondary settling tank 70 and the discharge tank 90.

상기 방류조(90)에는 정수된 물을 배출하는 방출구(91)가 벽면에 배치되어 있다.      In the discharge tank 90, a discharge port 91 for discharging purified water is disposed on the wall surface.

상기 슬러지저장조(80)에는 농축시 발생되는 탈리수를 재처리하여 농축효과를 증대시킬 수 있는 상등수순환관(81)이 상기 협잡물분리조(20)와 연결되어 구성된 것이다.      The sludge storage tank 80 is configured to be connected to the contaminant separation tank 20 is a supernatant water circulation pipe 81 that can increase the concentration effect by reprocessing the desorption water generated during concentration.

그리고, 상기 1,2,3차접촉상(32)(42)(62)은 자유굴곡 롤(32a)(42a)(62a)상으로 노출부(32b)(42b)(62b)와 비노출부(32c)(42c)(62c)로 형성되어 있다.      The first, second and third contact images 32, 42 and 62 are exposed portions 32b, 42b and 62b and non-exposed portions on the free bending rolls 32a, 42a and 62a. 32c, 42c, and 62c.

상기와 같이 구성된 본 발명의 실시예를 살펴 볼 것 같으면 다음과 같다.     Looking at the embodiment of the present invention configured as described above are as follows.

협잡물분리조(20)에 하수를 오수 유입구(21)에 유입하면, 개구부(22)에서는 협잡물이나 부상물이 차기 공정인 전환유량조정조(30)로 유출을 방지하는 수단과, 전환유량조정조(30) 교반에 의한 협잡물분리조(20)하부에 슬러지 누적을 방지하면서 유기계 부유물이 처리공정을 서서히 유출되는 복수의 수단을 갖는 것이다.When the sewage flows into the sewage inlet 21 in the contaminant separation tank 20, the opening 22 has a means for preventing the flow of the contaminant or floating matter into the conversion flow adjustment tank 30, which is the next step, and the switching flow adjustment tank 30. In the bottom of the contaminant separation tank 20 by agitation, organic sludge has a plurality of means for gradually flowing out of the treatment process while preventing sludge accumulation.

상기 전환유량조정조(30)내부에는 50% 범위의 용적율을 갖는 1차접촉상(32)은 전환유량조정조(30)의 양적조절특성을 미생물 발생 및 전개의 전환단계로, 물리적 기능의 유량조절과 생물학적 처리기능의 상호 전환성을 갖는 복합적인 수단으로 차기 공정인 1차 접촉폭기조(40)의 전환기능이 수행됨으로 후단 공정의 예비율 확보와 부하 변화에 대응력을 한층 증대시킨다.     The primary contact bed 32 having a volume ratio of 50% in the conversion flow adjustment tank 30 has a quantitative control characteristic of the conversion flow adjustment tank 30 as a conversion step of generating and developing microorganisms, The conversion of the first contact aeration tank 40, which is the next process, is performed as a complex means having a mutual conversion of the biological treatment function, thereby securing a reserve ratio of the subsequent process and increasing the response to load changes.

또한, 전환유량조정조(30)에 설치된 1단 에어리프트(35)는 전환유량조정조(30)의 저수위에서 1단 에어리프트(35)에 의해 이송된 이송수는 집수조(34)에 이송되고 수위가 상승된 집수조(34)는 내부에 설치된 2단 에어리프트(38)의해 2차 차기공정인 1차 접촉폭기조(40)로 이송되는 것이다. 이때 집수조(34)의 1차 이송수가 과다시 반송구(37)를 통해 전환유량조정조(30)로 순환이 연속되는 것이다.     In addition, in the first stage air lift 35 installed in the switching flow adjustment tank 30, the feed water transferred by the first stage air lift 35 at the low water level of the switching flow adjustment tank 30 is transferred to the water collecting tank 34 and the water level is increased. The raised water collecting tank 34 is transferred to the primary contact aeration tank 40, which is the secondary next step, by the two-stage air lift 38 installed therein. At this time, the primary transport water of the water collecting tank 34 is circulated continuously to the switching flow rate adjusting tank 30 through the conveying port 37.

그러므로 2단 이송에 따른 이송량의 증대와 전환유량조정조(30)의 예비공간 확보율을 1.5 ~ 2.0배 이상 증대시킴으로서 편리적 요인인 비동력, 비관리 요인으로 많이 사용되는 에어리프트의 원수 이송 문제점을 해결할 수 있으며, 수위 저하에 대한 이송량 저하 요인을 근본적으로 없앰으로써 유량조정의 완충력을 한층 증대 하였다.     Therefore, by increasing the amount of feed in accordance with the two-stage transfer and increase the reserve clearance rate of the conversion flow adjustment tank 30 by 1.5 ~ 2.0 times or more to solve the problem of raw water transfer of airlift, which is often used as a non-power, non-management factors, which are convenient factors In addition, the buffering capacity of the flow adjustment is further increased by fundamentally eliminating the factor of lowering the amount of transport for the lowering of the water level.

한편, 주처리 공정의 하나인 1차 접촉폭기조(40)내부에 60% 범위로 충진된 2차 접촉상(42)과 그 하부에 산기공급기(44)에 의해 유기물에 대한 미생물의 활성범위를 중부하로 유지시킴으로써 미생물의 대수 성장단계 특성을 유지 하면서 공정 내 미생물인 혼합액 부유물질(Mixed Liquor Suspended Solids)(이하 MLSS로 약칭함)를 2000 ~ 4000mg/ℓ 범위로 낮게 부착 유지하고 생물막의 두께를 1cm 이내로 유지함으로써 2차접촉상(42)의 접촉 미생물 부착 단위 부하를 낮게 유지하였고, 섬유사 현수시 자유 원형 롤(42a)에 의해 노출부(42b)와 비노출부(42c)가 형성되어 호기계와 혐기계가 공존하며, 1차 접촉폭기조(40)의 단속 운전에 따라 그 효과가 더욱 증대되어 고도처리 기능이 부가된다. 또 미생물 대비 2차접촉상(42)의 충진밀도를 높임으로써 접촉재 단위 길이마다 미생물의 접촉부하가 낮게 지속적으로 유지되는 기능을 주어 미생물의 변화 특성을 최소화시키는 것이다.      On the other hand, the active contact of the microorganisms for the organic matter by the secondary contact bed 42 filled in the 60% range in the primary contact aeration tank 40, which is one of the main treatment process and the acid supply unit 44 at the bottom thereof, By maintaining the characteristics of the growth phase of microorganisms while maintaining low adhesion of mixed liquor suspended solids (hereinafter referred to as MLSS), which are microorganisms in the range of 2000 to 4000 mg / l, and the thickness of the biofilm within 1 cm. The microbial attachment unit load of the secondary contact phase 42 was kept low by the holding, and the exposed portion 42b and the non-exposed portion 42c were formed by the free circular roll 42a at the time of the fiber yarn suspension. The machine coexists, and the effect is further increased by the intermittent operation of the primary contact aeration tank 40, thereby adding an advanced processing function. In addition, by increasing the packing density of the secondary contact phase 42 compared to the microorganisms, the contact load of the microorganisms is continuously maintained at every unit length of the contact material, thereby minimizing the microbial change characteristics.

이후 1차 침전조(50) 경유 탈리된 슬러지를 침전 분리시킴으로써 이후 공정의 생물학적 미생물의 특성 분리와 유기물에 대한 유입부하를 낮게 유입시킴으로써 2차 호기 공정인 2차 접촉폭기조(60)의 생물학적 특성을 저부하로 유지시키는 연계공정이 1차 침전조(50)를 중심으로 분리되는 작용을 갖는다.       After sedimentation and separation of the sludge desorbed via the first settling tank (50) by separating the characteristics of biological microorganisms of the subsequent process and low inflow load to the organic material to reduce the biological characteristics of the second contact aeration tank (60), a second aerobic process. Linkage process to maintain the load has a function of separating around the primary settling tank (50).

이후 저부하 특성을 갖는 2차 접촉폭기조(60) 내부에 배치된 3차접촉상(62)은 1차 접촉폭기조(40)에 설치된 1차접촉상(42)과 같은 60% 범위가 충진되어 있어 미생물의 서식밀도가 더욱더 낮게 0.5cm 두께 범위로 스스로 유지되고 생물막의 밀도가 1차접촉폭기조(40)와 동일하게 충진 되어있어 혼합액의 부유물질(M LSS)이 500 ~ 1000mg/ℓ 이 유지되는 특성을 갖는다.       Since the tertiary contact phase 62 disposed inside the secondary contact aeration tank 60 having low load characteristics is filled with 60% of the same range as the primary contact phase 42 installed in the primary contact aeration tank 40. The microorganisms have a low density of microorganisms in the 0.5cm thickness range, and the biofilm density is filled in the same manner as the primary contact aeration tank 40, so that the suspended solids (M LSS) of the mixed solution is maintained at 500 to 1000 mg / l. Has

그러므로 유입 유기물과 정화미생물 부착에 대한 비표면적의 여유로 정화 예비성을 보유한 기능을 얻음으로써, 미생물 상호 간의 먹이사슬의 증가와 자연정화 특성을 공유시키는 안정된 공정이 연계된다.      Therefore, by gaining the function of purifying reserve with the margin of specific surface area for inflowing organic matter and purified microorganisms, it is linked with the increase of the food chain between microorganisms and stable process of sharing natural purification characteristics.

이에 따라 최종 처리수의 효율성 보존 및 유입부하 변화에 따른 방어적 기능이 단계별로 완충되어 유지 관리성과 정화 효율성이 한층 개량된 정화공법이다.       As a result, it is the purification method that improves the maintenance and purification efficiency by buffering the protection function of the final treated water and the defensive function according to the change of inflow load.

상기와 같이 공법의 총괄적 기능을 나열하면 계외로부터 유입원이 최초 유입되면 정화 여건에 의해 초기 미생물은 2차접촉상(42)의 여과 부착특성에 의해 단기간에 미생물이 활착 전개되고 유입부하가 지속되면 전단계 공정부터 생물막이 If the inflow source is first introduced from the outside of the system as described above, the initial microorganisms are swelled and developed in a short time by the filtration adhesion characteristics of the secondary contact phase 42 due to the purification conditions. Biofilm from the previous stage

2차접촉상(42)에 형성되어 2차 접촉폭기조(60)로 이어지면서, 2차 접촉폭기조(60)는 유입부하에 따라 자연적 먹이사슬 관계로 미생물의 부착밀도가 서서히 감소된다. 그리고, 유입원이 감소되고 빈부하시 미생물의 밀도 감소 및 내생성장단계가 1차접촉폭기조(40)로 이어지면서 예비율은 더욱더 증가하게 된다. 이후 유입원이 다시 증가 되면 미생물의 활성이 2차접촉폭기조(60)로 활착 전개되어 대수성장단계가 증가 되고, 정화효율성이 유지되는 공정으로 전환된다.       The secondary contact aeration tank 60 is formed on the secondary contact phase 42 and leads to the secondary contact aeration tank 60, and the secondary contact aeration tank 60 gradually reduces the adhesion density of microorganisms due to a natural food chain relationship according to the inflow load. In addition, as the inflow source is reduced and the density reduction and endogenous growth stage of the microorganism at the time of poor load are led to the primary contact aeration tank 40, the reserve ratio is further increased. Then, when the inflow source is increased again, the activity of the microorganisms actively develops into the secondary contact aeration tank 60, so that the logarithmic growth stage is increased and the purification efficiency is maintained.

상기와 같이 이어지는 미생물학적 특성은 단계별 공정과 침전성 그리고 충진 생물막의 저부하 특성을 이용한 공법의 안출이며 처리 공정내에 미생물의 특성을 자연스럽게 유도시킨 결과로서 실시 예를 보면 각 공정별 정화 처리효율은 다음의 표와 같습니다As described above, the microbiological characteristics are a step-by-step process and precipitation of the method using the sedimentation and low load characteristics of the filling biofilm. Same as the table in

table

Figure 112006070803277-pat00001
Figure 112006070803277-pat00001

상기와 같이 본 발명은 효율성 유지와 관리적 특성을 상호 연결시켜 관리적 측면을 최소화하고 효율적 특성을 최대한 할 수 있는 정화 공정은 오염원의 정화단계를 다단계로 구성하여 정화 미생물의 특성을 상호 구분함으로써 관리적 요인에 의한 정화공정의 환경 변화시 일시적인 미생물의 변화 요인을 공정구성과 단계별 특성에서 근절하는 정화공정으로 구성하였다.      As described above, in the present invention, the purification process that minimizes the management aspect and maximizes the efficient characteristics by interconnecting the maintenance and management characteristics of the management process by configuring the purification stage of the contaminant in multiple stages to distinguish the characteristics of the purified microorganisms from each other. The change factor of the microorganisms during the environmental change of the purifying process was composed of the purifying process eradicating the process composition and the characteristics of each step.

이와 같이 생물학적 특성의 근원을 개발하고 본 공법에 적용시키기 위하여 단위 공정을 3단계로 구분하여 1단계는 전처리 및 주처리 전환기능, 물리적 보조기능과 그리고 2단계는 주처리 핵심기능으로 구성하고, 3단계는 저부하 잔여물 처리 및 예비단계와 안정화 기능을 갖는 공정으로 구분함으로써 생물학적 리듬을 각기 공정단계별로 단절시켜 다단계 방어특성이 부여됨으로써 관리적 요인이 대폭 감소되었다.      Thus, in order to develop the source of biological characteristics and apply it to this process, the unit process is divided into three stages, and the first stage consists of pretreatment and main treatment conversion functions, physical auxiliary functions, and the second stage is the main treatment core functions. The stages are divided into low load residue treatment, preliminary stages, and stabilization processes, and biological rhythms are separated by process stages to give multi-stage protective characteristics.

또한, 미생물의 저밀도 부착특성을 갖는 20cm 범위의 합사면 섬유사 접촉상을 고밀도 150 ~ 220m/㎥로 충진 함으로써 단위길이마다 정화 부하 및 부착미생물의 밀도가 최소화되고 3단계 공정을 자연 상태에 접근시킬 수 있었다.      In addition, by filling a 20 cm range of haptic fiber yarn contact phase with a high density of microorganisms with a high density of 150 ~ 220m / ㎥ to minimize the density of purifying load and adherent microorganisms per unit length, and the three-step process to approach the natural state Could.

이와 같이 단계별 공정과 섬유사 접촉상 특성에 의거 생물상의 변화리듬을 최소화하는 정화공정을 안출함으로서 관리적 특성이 대폭 축소되는 접촉산화 2차 처리방식의 하수처리 공정을 얻음으로써 수처리 효율의 증대 및 처리수의 안정화를 기할 수 있었다.In this way, by pursuing a purification process that minimizes the rhythm of biologic change based on the step-by-step process and the characteristics of the fiber yarn contact phase, the sewage treatment process of the catalytic oxidation secondary treatment method is greatly reduced, thereby increasing the water treatment efficiency and treating water. Was able to stabilize.

이상에서 설명한 바와 같이 본 발명은 내부에 충진된 접촉상의 초기 여과성과 부착성을 공유시키고 미생물 비대화를 방지할 수 있는 구조인 돌기부가 없는 망목합사형으로 되어 있고, 충진밀도를 증대함으로써 미생물의 상호 솎음효과를 증대시켜 깨끗한 처리수를 얻을 수 있을 뿐만 아니라, 유량편차가 심한 소규모 하수처리시설에서 관리가 편리한 에어리프트식 원수 이송에 의한 유량조정기능을 2단 에어리프트로 되어 있어 저수위에서 유량의 이송이 원활하게 유지할 수 있어 유량조절을 완충 능력을 증대시켜 전환유량조정조의 기능을 대폭 향상시키는 효과를 도출함으로써 처리시설의 효율성 향상과 공정의 안정화를 기할 수 있는 효과를 나타내었다.       As described above, the present invention is a mesh wood type without protrusions, which is capable of sharing the initial filterability and adhesion of the contact phase filled therein and prevents microbial hypertrophy, and increases the packing density to mutually eliminate microorganisms. In addition to increasing the effect, clean water can be obtained, and the flow control function by the air lift-type raw water transfer, which is easy to manage in small sewage treatment facilities with high flow rate deviations, is provided with two-stage air lifts, so It can maintain smoothly, and the effect of improving the buffer capacity and improving the function of the conversion flow regulating tank greatly improves the efficiency of treatment facilities and stabilizes the process.

삭제delete

Claims (4)

(삭제)(delete) 하수의 유입을 받아 비유기계, 미분해성 이물질을 분리하고 유기계 고형물을 일시적 저장분해 할 수 있는 협잡물분리조(20)와,      And a sewage separation tank (20) capable of separating non-organic, non-degradable foreign matter by receiving sewage and temporarily storage and decomposition of organic solids, 물리적 기능의 유량조절과 생물학적 처리기능의 상호 전환특성을 공유하여 수질의 특성을 호기계 정화기능으로 전개될 수 있도록 하는 전환유량조정조(30)와,A conversion flow rate adjustment tank 30 for sharing the mutual conversion characteristics of the physical function flow rate control and the biological treatment function so that the characteristics of the water quality can be developed as an exhalation function; 유기물에 대한 미생물의 활성범위를 중부하로 유지시킴으로써 미생물의 대수성단계 특성을 갖도록 하는 주처리 공정인 1차접촉폭기조(40)와,Primary contact aeration tank 40, which is the main treatment process to maintain the aerobic phase characteristics of the microorganism by maintaining the active range of the microorganism to the heavy load, 탈리된 슬러지를 1차 침전분리 시키는 1차침전조(50)와,Primary settling tank (50) for firstly separating the desorbed sludge, 유기물과 정화미생물 부착에 대한 비표면적의 여유로 정화 예비성을 보유한 기능을 얻음으로 하여 미생물 상호간의 먹이사슬의 증가와 자연정화 특성을 갖는 보조처리공정인 2차접촉폭기조(60)와,Secondary contact aeration tank (60), which is an auxiliary treatment process having an increase in the food chain and natural purification characteristics between the microorganisms by obtaining a function having a preliminary preliminary function by affording a specific surface area for attachment of organic matter and purified microorganisms, 탈리된 슬러지를 2차 침전분리 시키는 2차침진조(70)와,Secondary settling tank (70) for separating the sewage sludge secondary, 상기 1,2차침전조(50)(70)에 있던 슬러지가 모아지는 슬러지저정조(80)와Sludge storage tank 80 and the sludge collected in the first and second primary settling tank (50, 70) and 상등수를 소독처리한 후 방류하는 방류조(90)와, A discharge tank 90 for discharging the supernatant after disinfection; 상기 협잡물분리조(20)와 전환유량조정조(30)의 경계벽(22)하부에는 전환유량조정조(30)의 수위변화 및 교반에 의거 유기물의 누적을 방지하는 개구부(23)와, Under the boundary wall 22 of the contaminant separation tank 20 and the switching flow adjustment tank 30, an opening 23 for preventing the accumulation of organic matter based on the change in water level and the agitation of the switching flow adjustment tank 30, 상기 전환유량조정조(30)와, 1차접촉폭기조(40)및 2차접촉폭기조(60)내부에 배치된 접촉재지지틀(31)(41)(61)과, Contact switching frames (31) (41) (61) disposed in the switching flow rate adjustment tank (30), the primary contact aeration tank (40) and the secondary contact aeration tank (60); 상기 접촉재지지틀(31)(41)(61) 상부와 하부에는 망사형의 고정네트(33)(43)(63)와, Upper and lower contact contact frames 31, 41, 61, and mesh fixing nets 33, 43, 63, 상기 접촉재지지틀(31)(41)(61)가 하부에는 한개 이상의 산기공급기(36)(44)(64)를 갖는 정화처리 장치에 있어서, In the purification processing apparatus having the contact support frame (31) (41) (61) having at least one diffuser (36) (44) (64) at the bottom, 상기 전환유량조정조(30)측부에는 수위 저하에 따른 이송량 감소요인의 해결 및 유량조절의 효율성 증대를 위한 1단 에어리프트(35)와, The switching flow rate adjustment tank 30 side has a first stage air lift 35 for solving the factor of reducing the amount of transport due to the water level and increasing the efficiency of the flow rate adjustment; 상기 1단 에어리프트(35) 상단부가 연결된 집수조(34)에는 후기 공정인 1 차접촉폭기조(40)에 대한 이송 수고가 낮아 원활한 이송이 가능하도록 정량의 원수를 공기부상으로 이송할 수 있는 2단 에어리프트(38)와, The water tank 34 connected to the upper end of the first stage air lift 35 has two stages to transfer the quantity of raw water to the air float so that the transfer effort for the first contact aeration tank 40, which is a later process, is low. Air lift 38, 상기 집수조(34) 벽면에는 상기 1단 에어리프트(35)의 이송수 과다시 전환유량조정조(30)로 순환시킬 수 있는 반송구(37)와, A conveyance port 37 which can be circulated to the switching flow rate adjusting tank 30 when the feed water of the first stage air lift 35 is excessively formed on the wall surface of the water collecting tank 34; 상기 1, 2단에어리프트(35)(38)에는 이송량을 제어할 수 있는 공기조절밸브(39)로 구성된 것을 특징으로 하는 현수형 접촉산화 2차하수처리 장치. Suspension type contact oxidation secondary sewage treatment apparatus, characterized in that the first and second stage air lift (35) (38) is composed of an air control valve (39) capable of controlling the conveying amount. 제 2항에 있어서,  The method of claim 2, 상기 접촉재지지틀(31)(41)(61)내부에는 다수개의 1, 2, 3차접촉상(32)(42)(62)으로 배치된 것을 특징으로 하는 현수형 접촉산화 2차 하수처리 장치.Suspension type contact oxidation secondary sewage treatment, characterized in that arranged in the contact support frame 31, 41, 61, a plurality of primary, secondary, tertiary contact phase (32, 42, 62). Device. 제 3항에 있어서,  The method of claim 3, wherein 상기 1,2,3차접촉상(32)(42)(62)은 자유굴곡 롤(32a)(42a)(62a)상으로 노출부(32b)(42b)62b)와 비노출부(32c)(42c)(62c)와, The 1,2,3rd contact phases 32, 42 and 62 are exposed portions 32b, 42b and 62b and non-exposed portions 32c on free bending rolls 32a, 42a and 62a. 42c) 62c, 상기 1,2,3차접촉상(32)(42)(62)은 돌기부가 없는 평면 망목상으로 편직하여 단위 길이 당 저밀도 최대 0.5 ~ 1.0cm이내 두께가 형성된 것을 특징으로 현수형 접촉산화 2차 하수처리 장치.The 1,2,3rd contact phases 32, 42 and 62 are knitted into a flat mesh without protrusions and have a low density up to 0.5 to 1.0 cm thick per unit length. Sewage treatment unit.
KR20060094660A 2006-09-28 2006-09-28 Suspension contact 2nd sewage disposal system KR100794198B1 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
KR20060094660A KR100794198B1 (en) 2006-09-28 2006-09-28 Suspension contact 2nd sewage disposal system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
KR20060094660A KR100794198B1 (en) 2006-09-28 2006-09-28 Suspension contact 2nd sewage disposal system

Publications (1)

Publication Number Publication Date
KR100794198B1 true KR100794198B1 (en) 2008-01-11

Family

ID=39217662

Family Applications (1)

Application Number Title Priority Date Filing Date
KR20060094660A KR100794198B1 (en) 2006-09-28 2006-09-28 Suspension contact 2nd sewage disposal system

Country Status (1)

Country Link
KR (1) KR100794198B1 (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100940123B1 (en) 2007-12-14 2010-02-02 이경섭 Floating catalysis sewage disposal facility system
KR101101843B1 (en) * 2011-07-04 2012-01-05 (주) 청연 Biological reactor for removing tn and tp in winter time, and controlling method thereof
KR101648798B1 (en) * 2016-05-25 2016-08-30 이경섭 Contact-type sewage treatment and sewage treatment contact-type device using the same

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20000026328A (en) * 1998-10-20 2000-05-15 이경섭 Device for purifying wastewater
KR20000067763A (en) * 1999-07-30 2000-11-25 조정래 A waste water disposal apparatus

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20000026328A (en) * 1998-10-20 2000-05-15 이경섭 Device for purifying wastewater
KR20000067763A (en) * 1999-07-30 2000-11-25 조정래 A waste water disposal apparatus

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100940123B1 (en) 2007-12-14 2010-02-02 이경섭 Floating catalysis sewage disposal facility system
KR101101843B1 (en) * 2011-07-04 2012-01-05 (주) 청연 Biological reactor for removing tn and tp in winter time, and controlling method thereof
KR101648798B1 (en) * 2016-05-25 2016-08-30 이경섭 Contact-type sewage treatment and sewage treatment contact-type device using the same

Similar Documents

Publication Publication Date Title
JP5899373B2 (en) Process comprising an ANAMOX microorganism on a biofilm carrier for removing ammonium from a wastewater stream
CN106396080B (en) A kind of biomembrane pretreatment unit suitable for polluted raw purification
CN108383320B (en) Integrated treatment method for livestock and poultry breeding wastewater
US20070102354A1 (en) System for treating wastewater and a media usable therein
CN107500479A (en) A kind for the treatment of method for rural sewage
KR100794198B1 (en) Suspension contact 2nd sewage disposal system
CN102653436A (en) Sewage reuse treatment system and process
CN110540293A (en) Sewage treatment device and method suitable for large-amplitude fluctuation of water quantity
KR0126883Y1 (en) Facilities for treating waste water on a large scale
KR20040075413A (en) Wastewater treatment system by multiple sequencing batch reactor and its operation methods
JP2005211788A (en) Organic wastewater treatment apparatus
JP4017331B2 (en) Septic tank
JP2002177979A (en) Waste water treatment equipment
KR20020083978A (en) CPA(Continuity inflow Periodic Activated-sludge System)PROCESS
RU70512U1 (en) COMPACT INSTALLATION OF BIOLOGICAL CLEANING AND DISINFECTION OF SEWAGE WATER USING MEMBRANE FILTRATION
JP2003010871A (en) Sewage treatment apparatus and its operating method
CN201686595U (en) Sewage denitrification system
KR100460942B1 (en) Process for Treating Waste Water and Device Thereof Using Septic Tank and Sequencing Batch Reactor
KR100399702B1 (en) The method and asparatus of purificating sewage through process of foaming membrane and etc poceses
KR101032068B1 (en) Sewage-wastewater treating system and method the same, using high-effciency sequencing batch reactor process
KR20020094947A (en) Continuous Circulation Advanced Treatment by Anaerobic Contact Oxidation
KR20180068977A (en) Biological treatment of organic wastewater
JP2001212593A (en) Post-treatment method for ascending current anaerobic treatment apparatus
KR100339017B1 (en) Advanced Wate Water Treatment System of Package Type
WO2023178966A1 (en) Modular multi-stage biochemical-filtering sewage treatment system

Legal Events

Date Code Title Description
A201 Request for examination
E902 Notification of reason for refusal
E90F Notification of reason for final refusal
E701 Decision to grant or registration of patent right
GRNT Written decision to grant
FPAY Annual fee payment

Payment date: 20130104

Year of fee payment: 6

FPAY Annual fee payment

Payment date: 20140103

Year of fee payment: 7

FPAY Annual fee payment

Payment date: 20150105

Year of fee payment: 8

FPAY Annual fee payment

Payment date: 20160104

Year of fee payment: 9

FPAY Annual fee payment

Payment date: 20170105

Year of fee payment: 10

FPAY Annual fee payment

Payment date: 20171205

Year of fee payment: 11

FPAY Annual fee payment

Payment date: 20181204

Year of fee payment: 12