KR102508793B1 - Upper filter replaceable filtering wetland for non-point pollution treatment - Google Patents

Upper filter replaceable filtering wetland for non-point pollution treatment Download PDF

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KR102508793B1
KR102508793B1 KR1020220022603A KR20220022603A KR102508793B1 KR 102508793 B1 KR102508793 B1 KR 102508793B1 KR 1020220022603 A KR1020220022603 A KR 1020220022603A KR 20220022603 A KR20220022603 A KR 20220022603A KR 102508793 B1 KR102508793 B1 KR 102508793B1
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filter medium
treatment tank
filter
water
water supply
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KR1020220022603A
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Korean (ko)
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김옥희
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주식회사 에코엔지니어링
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D24/00Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof
    • B01D24/48Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof integrally combined with devices for controlling the filtration
    • B01D24/4876Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof integrally combined with devices for controlling the filtration in which the filtering elements are moved between filtering operations; particular measures for removing or replacing the filtering elements
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D24/00Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof
    • B01D24/02Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof with the filter bed stationary during the filtration
    • B01D24/20Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof with the filter bed stationary during the filtration the filtering material being provided in an open container
    • B01D24/24Downward filtration, the container having distribution or collection headers or pervious conduits
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D24/00Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof
    • B01D24/38Feed or discharge devices
    • B01D24/40Feed or discharge devices for feeding
    • 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
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2221/00Applications of separation devices
    • B01D2221/12Separation devices for treating rain or storm water
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

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

Abstract

The present invention relates to a wet filtration bed configured with a preceding storage means to perform non-point pollution treatment. The filter medium in a treatment tank is divided into a coarse filter medium (91) of an upper layer and a fine-grained filter medium (92) of a lower layer, a replaceable lower inclined-type filter medium box (80) is installed in an upper layer part, and an overflow-type water supply channel (50) is formed at an upper end of a treatment tank side wall (14), thereby enabling smooth infiltration and diffusion of treated water while completely excluding a sprinkling piping above the treatment tank, and enabling easy replacement of the upper filter medium. According to the preset invention, an upper part of the treatment tank of the wet filtration bed can be configured in a completely open state, uniform and smooth diffusion of the treated water is induced within the filter medium while operating the trickling filtration bed in an appropriate wet state without water surface formation, and the upper filter medium can be easily replaced, thereby improving performance and usability of the trickling filtration bed.

Description

여재 부분 교환형 비점오염처리 습지여상{UPPER FILTER REPLACEABLE FILTERING WETLAND FOR NON-POINT POLLUTION TREATMENT}Filter medium partial exchange type non-point pollution treatment wetland filter {UPPER FILTER REPLACEABLE FILTERING WETLAND FOR NON-POINT POLLUTION TREATMENT}

본 발명은 선행 저류 수단이 구성되어 비점오염처리를 수행하는 습지여상에 관한 것으로, 처리조내 여재를 상층의 조립여재(91)와 하층의 세립여재(92)로 구분 구성하되, 상층부에 교체 가능한 하부 경사형 여재함(80)을 설치하고 처리조 측벽(14) 상단부에 월류형 급수로(50)를 형성하여, 처리조 상부의 살수용 배관을 완전히 배제하면서도 처리수의 원활한 침투확산이 가능하며, 상층 여재의 용이한 교체도 가능하도록 한 것이다.The present invention relates to a wet filter bed configured with a prior storage means to perform non-point pollution treatment, and the filter media in the treatment tank are divided into an upper coarse filter media 91 and a lower layer fine filter media 92, and the lower portion is replaceable in the upper layer. By installing the inclined filter media box 80 and forming the overflow type water supply passage 50 at the upper end of the side wall 14 of the treatment tank, smooth penetration and diffusion of the treated water is possible while completely excluding the watering pipe at the top of the treatment tank, It is also possible to easily replace the upper filter material.

습지여상 즉, 인공습지형 여상(過床)은 물리적 여과처리와 습지로서의 기능을 동시에 수행하는 시설로서, 하폐수처리, 비점오염처리, 하천수 수질개선, 생물서식지의 제공 및 친수환경의 조성 등을 목적으로 조성된다.A wetland filter bed, that is, an artificial wetland filter bed, is a facility that simultaneously functions as a physical filtration process and a wetland, and is used for wastewater treatment, non-point pollution treatment, improvement of river water quality, provision of biological habitats, and creation of a water-friendly environment. is composed of

습지여상을 통한 수처리는 도시하수, 합류식 하수의 월류수, 낙농폐수, 매립지 침출수, 병원폐수 등의 산업폐수와 우수, 유거수(流去水) 등의 비점오염원으로부터 발생한 오염 물질의 처리 등 다양한 분야에 적용되고 있으며, 특히 도시하수 처리상 강우 초기 유출수의 일시 저류가 가능한 선행 저류 수단이 구비된 형식의 습지여상은 비점오염 처리시설로서 각광받고 있다.Water treatment through wetland filtering is applied to various fields such as industrial wastewater such as urban sewage, combined sewage overflow, dairy wastewater, landfill leachate, hospital wastewater, and pollutants generated from non-point sources such as rainwater and runoff. In particular, in urban sewage treatment, a wetland filter bed equipped with a pre-retention means capable of temporarily retaining runoff in the early stage of rainfall is in the limelight as a non-point pollution treatment facility.

이러한 습지여상은 여과 시설인 여상으로서의 기본 기능을 수행할 수 있도록 처리조 상부에 살수시설이 구비되거나, 처리조에 처리수가 완전 충만되고 상부에 상시 수면이 형성되도록 운영되고 있으며, 관련 종래기술로서 특허 제2020849호 또는 공개특허 제2009-101564호 등을 들 수 있다.Such a wetland filter bed is operated so that a watering facility is provided at the top of the treatment tank to perform the basic function as a filter bed, which is a filtration facility, or the treatment tank is completely filled with treated water and a constant water surface is formed at the top. 2020849 or Laid-Open Patent Publication No. 2009-101564;

특허 제2020849호 및 공개특허 제2009-101564호를 비롯한 종래의 습지형 여상 또는 살수여상은 처리수의 여재 통과를 유도하는 동일한 기본 구조를 가지며, 따라서 처리조내 적재된 여재 전체에 대한 처리수의 광범위한 확산을 도모하기 위한 수단이 강구될 필요가 있다.Conventional wetland type filter beds or watering filter beds, including Patent No. 2020849 and Laid-Open Patent No. 2009-101564, have the same basic structure that induces the passage of treated water through the filter medium, and therefore, a wide range of treated water for the entire filter medium loaded in the treatment tank It is necessary to devise means to promote diffusion.

즉, 처리조내 여재 중 일부분에 처리수가 편중될 경우, 전체 습지여상의 처리 효율이 저하될 뿐 아니라, 여재의 빈번한 교체가 필요하므로, 오염 처리수가 처리조 내부 공간에서 원활하게 확산될 필요가 있는 것이다.That is, when the treated water is concentrated on a part of the filter media in the treatment tank, the treatment efficiency of the entire wet filter bed is lowered, and since the filter media needs to be frequently replaced, the contaminated treated water needs to be smoothly diffused in the inner space of the treatment tank. .

이에, 종래의 습지여상에서는 오염 처리수의 원활한 확산을 유도하는 수단으로서, 특허 제2020849호에서와 같이 처리조 상부에 복잡한 살수용 배관을 설치하거나, 공개특허 제2009-101564호에서와 같이 처리조 상층에 수면(水面)이 상시 형성되도록 운용되고 있는 실정이다.Accordingly, in the conventional wetland filter bed, as a means for inducing smooth diffusion of polluted water, a complicated watering pipe is installed on the top of the treatment tank as in Patent No. 2020849, or a treatment tank as in Patent Publication No. 2009-101564. It is operated so that the water surface is always formed on the upper floor.

그러나 처리조 상부의 살수용 배관은 미관은 차치하더라도 설치에 막대한 비용이 소요될 뿐 아니라 오염 처리수의 이송 과정에서 배관의 폐색이 수시로 발생되어 효용성이 부족하고 유지관리상 상당한 애로점을 유발하는 문제가 있으며, 수면이 형성되도록 처리조를 운용하는 방식의 경우 여재에 상시 완전 침수상태가 조성될 수 밖에 없으므로 유기물 산화 등에 필요한 충분한 공기 접촉이 근본적으로 불가능할 뿐 아니라 처리조 상부 공간의 활용도 극히 제한되는 문제점을 가진다.However, apart from the aesthetics, the watering pipe at the top of the treatment tank not only costs a lot to install, but also causes clogging of the pipe from time to time in the process of transporting contaminated treated water, resulting in insufficient effectiveness and causing considerable difficulties in maintenance. However, in the case of the method of operating the treatment tank to form the water surface, the filter medium is inevitably completely submerged at all times, so it is fundamentally impossible to provide sufficient air contact necessary for oxidation of organic matter, and the utilization of the upper space of the treatment tank is extremely limited. .

본 발명은 전술한 문제점을 감안하여 창안된 것으로, 비점오염처리 습지여상에 있어서, 저판(11), 전벽(12), 후벽(13) 및 측벽(14)으로 형성된 장방형의 처리조 내부에는 종방향으로 유공관(21)이 설치되며, 전벽(12)의 외측에는 유입관(41)이 연결된 저류실(40)이 형성되고, 후벽(13)의 외측에는 배출관(31)이 연결된 집수실(30)이 형성되며, 유공관(21)의 일측 단부는 후벽(13)을 관통하여 집수실(30) 내부로 연결되고, 양측 측벽(14)의 상단부에는 각각 처리조 중심측으로 돌출된 급수로(50)가 형성되되, 급수로(50)의 측벽(14) 타측단에는 월류벽(51)이 기립 형성되며, 전벽(12) 상부에는 방수구(45)가 절개 형성되어 저류실(40)과 급수로(50)가 연결되고, 다공판인 하부 판체에 대칭 경사면이 형성된 V자형 단면의 여재함(80)이 처리조 상부에 설치되고 여재함(80)에는 조립여재(91)가 적재되며, 처리조내 여재함(80) 하부 공간에는 세립여재(92)가 적재되어, 유입관(41)을 통하여 저류실(40)로 유입된 처리수가 일시 저류된 후 방수구(45)로 배출되어 급수로(50)로 유입되고, 급수로(50)의 월류벽(51)을 따라 월류되어 조립여재(91) 상부로 투입된 후, 여재함(80)의 경사면에 적재된 조립여재(91)를 경유하면서 처리수가 유하함과 동시에 다공판인 여재함(80) 하부 판체를 통과하여 세립여재(92)로 확산 침투됨을 특징으로 하는 여재 부분 교환형 비점오염처리 습지여상이다.The present invention was devised in view of the above-mentioned problems, and in the non-point pollution treatment wetland filter bed, the inside of the rectangular treatment tank formed of the bottom plate 11, the front wall 12, the rear wall 13 and the side wall 14 has a longitudinal direction. The perforated pipe 21 is installed, the storage chamber 40 connected to the inlet pipe 41 is formed on the outside of the front wall 12, and the collection chamber 30 connected to the discharge pipe 31 is formed on the outside of the rear wall 13 is formed, one end of the perforated pipe 21 passes through the rear wall 13 and is connected to the inside of the collecting chamber 30, and the upper ends of the side walls 14 on both sides have water supply channels 50 protruding toward the center of the treatment tank, respectively. At the other end of the side wall 14 of the water supply path 50, the overflow wall 51 is formed upright, and the water discharge port 45 is cut and formed on the upper part of the front wall 12 to form the storage chamber 40 and the water supply path 50 ) is connected, and a filter media box 80 having a V-shaped cross section formed with a symmetrical inclined surface is installed on the lower plate body, which is a perforated plate, is installed on the upper part of the treatment tank, and the assembled filter media 91 is loaded in the filter media box 80, and the filter media in the treatment tank (80) The fine filter medium 92 is loaded in the lower space, and the treated water flowing into the storage chamber 40 through the inlet pipe 41 is temporarily stored and then discharged through the discharge port 45 and introduced into the water supply channel 50 And, after flowing along the overflow wall 51 of the water supply line 50 and being introduced to the top of the assembled filter media 91, the treated water flows down while passing through the assembled filter media 91 loaded on the slope of the filter media box 80 At the same time, it is a filter medium partial replacement type non-point pollution treatment wetland filter characterized in that it diffuses and penetrates into the fine filter medium 92 through the lower plate body of the filter medium box 80, which is a perforated plate.

또한, 본 발명은 상기 여재함(80)의 평면상 폭은 양측 월류벽(51) 표면 사이의 거리와 일치하여 여재함(80)이 처리조 양측 급수로(50)의 월류벽(51) 사이에 결합되고, 여재함(80)의 내부에는 수직으로 돌출된 다수의 돌출봉(81)이 접합되고, 돌출봉(81)의 상단에는 결속후크(82)가 형성됨을 특징으로 하는 여재 부분 교환형 비점오염처리 습지여상이다.In addition, in the present invention, the width of the filter box 80 in plan is equal to the distance between the surfaces of the overflow walls 51 on both sides, so that the filter box 80 is between the overflow walls 51 of the water supply channels 50 on both sides of the treatment tank. coupled to, and a plurality of protrusion rods 81 protruding vertically are bonded to the inside of the filter media box 80, and a binding hook 82 is formed at the top of the protrusion rod 81, characterized in that the filter medium part exchange type It is a wetland filter for non-point pollution treatment.

본 발명을 통하여, 습지여상의 처리조 상부를 완전 개방된 상태로 구성할 수 있을 뿐 아니라, 수면 형성을 수반하지 않는 적정 습윤 상태로 습지여상을 운용하면서도 여재내 처리수의 균일하고 원활한 확산을 유도할 수 있으며, 상층부 여재에 대한 용이한 교체가 가능하여, 습지여상의 성능 및 활용도를 제고할 수 있다.Through the present invention, it is possible to configure the upper part of the treatment tank of the wet filter bed in a completely open state, and induce uniform and smooth diffusion of the treated water in the filter media while operating the wet filter bed in an appropriately moist state without the formation of a water surface And it is possible to easily replace the filter material in the upper layer, so that the performance and utilization of the wet filter bed can be improved.

특히, 습지여상 처리조 상부의 배관을 완벽하게 배제할 수 있으므로, 습지여상의 유지관리 편의성을 개선하고 미관을 확보할 수 있을 뿐 아니라, 식생 조성 또는 시설물 설치 등 습지여상 상부 공간의 자유로운 활용이 가능하다.In particular, since the pipe at the top of the wet filter treatment tank can be completely excluded, the maintenance convenience of the wet filter bed can be improved and aesthetics can be secured, as well as the free use of the space above the wet filter bed such as vegetation formation or installation of facilities. do.

또한, 개방된 처리조 상층부에 수면을 형성하지 않고도 운용이 가능하므로, 산책로 또는 공원 등으로 습지여상을 활용할 수 있으며, 상층부 여재에 대한 자유롭고 간편한 교체가 가능하므로 습지여상의 효율적인 유지관리가 가능하다.In addition, since it can be operated without forming a water surface in the upper part of the open treatment tank, the wet filter bed can be used for walking trails or parks, and the filter material in the upper layer can be freely and easily replaced, enabling efficient maintenance of the wet filter bed.

도 1은 본 발명의 사시도
도 2는 본 발명의 여재 적재 방식 설명도
도 3은 본 발명의 구조물 사시도
도 4는 본 발명의 구조물 부분절단 사시도
도 5는 본 발명의 횡단면도
도 6은 본 발명의 종단면도
도 7은 본 발명의 요부 발췌 사시도
도 8은 본 발명의 조립여재 제작 과정 설명도
1 is a perspective view of the present invention
2 is an explanatory diagram of the filter media loading method of the present invention
Figure 3 is a perspective view of the structure of the present invention
Figure 4 is a partially cut perspective view of the structure of the present invention
5 is a cross-sectional view of the present invention
6 is a longitudinal cross-sectional view of the present invention
7 is a perspective view of an excerpt of the main part of the present invention
8 is an explanatory diagram of the manufacturing process of the granulated filter medium of the present invention

본 발명의 상세한 구성 및 작동 방식을 첨부된 도면을 통하여 설명하면 다음과 같다.The detailed configuration and operation method of the present invention will be described through the accompanying drawings.

우선 도 1은 본 발명 습지여상의 외관을 도시한 것으로, 도시된 바와 같이, 본 발명은 장방형 수조인 처리조의 전후 단부에 각각 저류실(40) 및 집수실(30)이 구성된 시설로서, 도로, 택지, 교량 등 도시 피복면에서 배출되는 강우 초기 유출수 등의 비점오염을 효율적으로 처리할 수 있도록, 최초 유입되는 처리수가 저류실(40)에 일시 저류된 후 여재가 적재된 처리조로 순차 공급되어 처리되는 방식을 가진다.First, FIG. 1 shows the appearance of the wet filter bed of the present invention. As shown, the present invention is a facility configured with a storage chamber 40 and a collection chamber 30 at the front and rear ends of a treatment tank, which is a rectangular water tank, respectively, road, In order to efficiently treat non-point pollution such as rainwater and early runoff discharged from urban covering surfaces such as residential land and bridges, the first treated water is temporarily stored in the storage chamber 40 and then sequentially supplied to the treatment tank loaded with filter media for treatment. have a way of being

즉, 전술한 비점오염 처리수에 포함된 각종 표류 협잡물 또는 부유 대입경 고형물이 처리수가 저류실(40)에 선행 체류되는 과정에서 침전되어 분리된 연후, 고형물이 상당 수준 제거된 상태의 처리수가 처리조로 공급되는 구조로서, 여과상의 접촉 및 흡착을 통한 오염물 제거 기능을 일층 효율화할 수 있는 것이다.That is, after various drifting impurities or floating large particle diameter solids included in the above-mentioned non-point pollution treated water are precipitated and separated in the process of pre-retaining the treated water in the storage chamber 40, the treated water in which the solids are removed at a considerable level is treated. As a structure supplied to the tank, it is possible to further improve the efficiency of the contaminant removal function through contact and adsorption on the filter bed.

본 발명이 적용된 비점오염처리 습지여상의 시설물 세부 구조는 도 2 내지 도 6에서와 같이, 기본적으로 여재 적재 처리조로서, 이들 도면에 도시된 바와 같이, 본 발명의 처리조 상부에는 종래기술에서 필수적으로 요구되었던 복잡한 살수용 배관이 완벽하게 배제되어 있으며, 종래기술에서는 여상 운용상 처리조 적재 여재 상측에 상시 형성될 필요가 있었던 수면(水面) 역시 형성될 필요가 없다.As shown in FIGS. 2 to 6, the detailed structure of the facility of the non-point pollution treatment wetland filter bed to which the present invention is applied is basically a filter media loading treatment tank, and as shown in these drawings, the upper part of the treatment tank of the present invention is essential in the prior art. The complicated watering pipe required for this is completely excluded, and in the prior art, the water surface, which always needed to be formed on the upper side of the filter medium loaded in the treatment tank for filter bed operation, does not need to be formed.

따라서, 처리수 상측 공간에 대한 자유로운 활용이 가능할 뿐 아니라, 미관 확보 또한 용이하여, 시설물 계획 및 시공시 부지확보에 있어서 유리할 뿐 아니라, 단순히 수처리 시설로서 구축되는 것이 아니라 산책로 또는 공원 등 다양한 부가 기능을 수행할 수도 있다.Therefore, it is not only possible to freely utilize the space above the treated water, but also to secure the aesthetics, which is advantageous in securing the site during facility planning and construction. can also be done

이러한 본 발명 습지여상의 시설물 구조를 살펴보면, 도 2 내지 도 4에서와 같이, 평면상 장방형 판체인 저판(11)의 전단 및 후단에 각각 전벽(12) 및 후벽(13)이 형성되고 저판(11)의 양 측단에는 측벽(14)이 형성되어 평면상 저판(11)의 전단 및 후단간 거리가 양 측단간 거리보다 큰 장방형의 처리조가 구축되고, 도 4에서와 같이 처리조 내부의 저판(11) 상면에는 처리조의 종방향으로 유공관(21)이 설치된다.Looking at the facility structure of the wetland filter of the present invention, as shown in FIGS. Sidewalls 14 are formed at both ends of ), so that a rectangular treatment tank in which the distance between the front and rear ends of the bottom plate 11 on a plane is greater than the distance between both side ends is constructed, and as shown in FIG. 4, the bottom plate 11 inside the treatment tank ) On the upper surface, a perforated pipe 21 is installed in the longitudinal direction of the treatment tank.

또한, 도 1 내지 도 4에서와 같이, 전벽(12)의 외측에는 유입관(41)이 연결된 저류실(40)이 형성되고, 후벽(13)의 외측에는 배출관(31)이 연결된 집수실(30)이 형성되며, 도 4에서와 같이, 유공관(21)의 일측 단부는 후벽(13)을 관통하여 집수실(30) 내부로 연결된다.In addition, as shown in FIGS. 1 to 4, the storage chamber 40 to which the inlet pipe 41 is connected is formed on the outside of the front wall 12, and the collection chamber to which the discharge pipe 31 is connected to the outside of the rear wall 13 ( 30) is formed, and as shown in FIG. 4, one end of the perforated pipe 21 passes through the rear wall 13 and is connected to the inside of the collecting chamber 30.

이러한 본 발명의 처리조는 지상에 구축되어 전체 구조물이 노출되는 형식을 가질 수 있음은 물론, 처리조 상부 일부만이 지상으로 노출되고, 저판(11) 및 양 측벽(14)을 비롯한 대부분의 구조물이 지하에 매설되는 형식을 가질 수도 있다.The treatment tank of the present invention may have a type in which the entire structure is exposed by being built on the ground, and only a part of the upper part of the treatment tank is exposed to the ground, and most of the structures including the bottom plate 11 and both side walls 14 are underground. It may have a form buried in .

도 4 및 도 5에서와 같이, 양측 측벽(14)의 상단부에는 각각 처리조 중심측으로 돌출된 급수로(50)가 형성되되, 급수로(50)의 측벽(14) 타측단에는 월류벽(51)이 기립 형성되고, 월류벽(51)의 상단에는 거치형(鋸齒形) 연속 요철부가 형성된다.As shown in FIGS. 4 and 5, a water supply passage 50 protruding toward the center of the treatment tank is formed at the upper end of each side wall 14 on both sides, and an overflow wall 51 is formed at the other end of the side wall 14 of the water supply passage 50. ) is formed upright, and a stationary continuous concave-convex portion is formed at the top of the overflow wall 51.

즉, 본 발명의 급수로(50)는 오염 처리수가 공급되어 여재로 처리수를 급수하는 수로형 구조물로서, 기본적으로 L자형 단면을 가지며 측벽(14)에 L자형 단면의 급수로(50)가 접합되어 전체적으로 U자형 단면의 수로를 형성하되, 처리조 중심측의 벽체를 월류벽(51)으로 구성하여, 이 급수로(50)를 통하여 이송되던 처리수가 월류벽(51)을 따라 월류되면서 처리조에 적재된 여재의 평면상 종방향 전체 구간에 대한 광범위한 급수가 수행되는 것이다.That is, the water supply passage 50 of the present invention is a waterway-type structure in which contaminated treatment water is supplied and treated water is supplied to the filter media, and basically has an L-shaped cross section and the side wall 14 has an L-shaped cross section water supply passage 50 It is joined to form a waterway with a U-shaped cross section as a whole, but the wall at the center of the treatment tank is configured as an overflow wall 51, and the treated water transferred through the water supply channel 50 overflows along the overflow wall 51 for treatment. A wide range of water supply is performed for the entire section in the longitudinal direction of the filter media loaded in the tank.

또한, 도 4에서와 같이, 급수로(50)의 월류벽(51)은 래버린스(labyrinth) 벽체 즉, 거치형 연속 요철이 형성되어 월류 수류가 다중 분할되는 구조를 형성함으로써, 원활한 월류를 도모함과 동시에 월류벽(51) 전체 구간 중 일부 구간에 월류 수류가 편중되는 현상을 방지할 수 있도록 하였다.In addition, as shown in FIG. 4, the overflow wall 51 of the water supply channel 50 is a labyrinth wall, that is, a stationary continuous irregularity is formed to form a structure in which the overflow water flow is multi-divided, thereby promoting smooth overflow and At the same time, it is possible to prevent the overflow water flow from being biased in some sections of the entire section of the overflow wall 51.

즉, 통상의 살수여상에서 필수적으로 요구되는 배관형 살수 설비를 생략하면서도 처리조 종단상 전체 구간에 대한 광범위한 동시 급수가 가능하도록 래버린스 월류벽(51)의 처리조 종방향 전구간 구축을 실시한 것으로, 이는 후술할 조립여재(91)의 경사면 적층 구조와 동반되어 처리수의 광범위한 균질 확산 기능을 수행하게 된다.That is, the entire longitudinal section of the treatment tank of the labyrinth overflow wall 51 was constructed so that a wide range of simultaneous water supply to the entire section on the end of the treatment tank was possible while omitting the pipe-type sprinkler equipment required in the normal watering filter bed, This is accompanied by an inclined surface laminated structure of the granulated filter media 91 to be described later, and performs a wide range of homogeneous diffusion function of the treated water.

이러한 급수로(50)에 대한 처리수 공급은 도 6에서와 같이 저류실(40)에 저류된 처리수 상층수를 방출하는 방수구(45)에 의하여 수행되는데, 전벽(12) 상부에는 방수구(45)가 절개 형성되어 저류실(40)과 급수로(50)가 연결됨으로써, 동 도면에서와 같이 유입관(41)을 통하여 저류실(40)로 최초 유입된 처리수가 일시 저류되어 고형물이 침전된 후 상층수가 방수구(45)로 배출되어 급수로(50)로 공급된다.As shown in FIG. 6, the supply of treated water to the water supply line 50 is performed by a discharge port 45 for discharging the upper layer of treated water stored in the storage chamber 40. ) is incised to connect the storage chamber 40 and the water supply passage 50, so that the treated water initially introduced into the storage chamber 40 through the inlet pipe 41 is temporarily stored as shown in the figure, and solids are precipitated. After that, the upper layer water is discharged through the discharge port 45 and is supplied to the water supply line 50.

도 5 및 도 6에서와 같이, 급수로(50)의 월류벽(51)을 따라 처리조 상부로 살수된 처리수는 여재함(80)에 적재된 상태로 처리조 상부에 포설된 조립여재(91)로 우선 투입 및 침투되며, 이어서 처리조 하층부에 포설 적재된 세립여재(92)로 침투되어 오염물이 흡착 및 제거된 후, 처리조 하측 중심부의 유공관(21)으로 유입된다.As shown in FIGS. 5 and 6, the treated water sprayed to the top of the treatment tank along the overflow wall 51 of the water supply passage 50 is assembled filter media laid on the top of the treatment tank while being loaded in the filter box 80 ( 91), and then penetrates into the fine filter medium 92 laid and loaded in the lower part of the treatment tank to adsorb and remove contaminants, and then flows into the perforated pipe 21 at the lower center of the treatment tank.

본 발명에 있어서 조립여재(91) 및 세립여재(92)는 그 사전적 의미에서와 같이, 입경이 상대적으로 큰 여재와 작은 여재를 지칭하는 것으로, 세립여재(92)로는 통상의 살수여상 여재로 활용되는 토사가 적용될 수 있고, 조립여재(91)로는 본 발명에 특화된 조립질의 입상체(粒狀體)가 적용된다.In the present invention, the granular filter medium 91 and the fine filter medium 92 refer to a filter medium having a relatively large particle diameter and a filter medium having a relatively small particle diameter, as in the dictionary meaning, and the fine filter medium 92 is a conventional watering filter medium. The soil to be utilized can be applied, and as the granular filter medium 91, a granular material of coarse quality specialized in the present invention is applied.

즉, 본 발명에 있어서 조립여재(91)를 구성하는 입상체로는 입경 5mm 내지 10mm의 입상체가 적용되며, 구체적인 재질로는 자연석 파쇄물 또는 소성(燒成) 처리된 다공성 구체(球體)가 적용될 수 있다.That is, as the granular material constituting the granulated filter medium 91 in the present invention, granular material having a particle diameter of 5 mm to 10 mm is applied, and as a specific material, crushed natural stone or calcined porous spheres may be applied. .

조립여재(91)의 입경 범위에 있어서, 조립여재(91)의 입경이 5mm 미만의 세립질일 경우, 처리수의 원활한 유하가 억제되어 후술할 신속 이송 및 광범위 하방 배출 작용이 저하될 수 밖에 없으며, 조립여재(91)의 입경이 10mm를 초과할 경우 처리수가 조립여재(91)간 공극을 충분히 경유하지 않고 직하 배출되어 이 역시 후술할 광범위 하방 배출 작용을 저하시키는 요인으로 작용할 수 있다.In the particle diameter range of the granulated filter medium 91, when the particle diameter of the granulated filter medium 91 is of a fine quality of less than 5 mm, the smooth flow of the treated water is suppressed, and the rapid transfer and wide downward discharge action described later are inevitably reduced, When the particle diameter of the granulated filter media 91 exceeds 10 mm, the treated water is directly discharged without sufficiently passing through the gaps between the granulated filter media 91, and this may also act as a factor deteriorating the downward discharge action over a wide range, which will be described later.

특히, 조립여재(91)의 입경이 과소할 경우, 조립여재(91)가 여상 처리를 실제 수행하는 세립여재(92)의 기능을 수행하게 되어, 조립여재(91)에 오염물이 과도하게 흡착될 수 있으며, 이는 조립여재(91)의 가용 수명을 단축하고 조립여재(91)의 빈번한 교체를 초래할 수 있다.In particular, when the particle diameter of the granulated filter medium 91 is too small, the granulated filter medium 91 performs the function of the fine filter medium 92 that actually performs the filter bed treatment, and contaminants are excessively adsorbed on the granulated filter medium 91. This may shorten the usable life of the granulated filter medium 91 and cause frequent replacement of the granulated filter medium 91.

도 2 및 도 3에서와 같이, 조립여재(91)가 적재되는 본 발명의 여재함(80)은 그 사전적 의미에서와 같이, 여재가 적재되는 함체 내지 용기로서, 평면상 장방형 형태를 가지며, 다공판인 하부 판체에 대칭 경사면이 형성된 V자형 단면을 가진다.2 and 3, the filter medium box 80 of the present invention in which the assembled filter medium 91 is loaded is, as in its dictionary meaning, a box or container in which the filter medium is loaded, and has a rectangular shape on a plane, It has a V-shaped cross section in which symmetrical inclined surfaces are formed on the lower plate body, which is a perforated plate.

즉, 다수의 통수공이 천공된 다공판으로 하부 판체가 형성되되, 하부 판체의 중앙부가 V자형으로 절곡되어, 도 5에서와 같이 처리조 중심축을 축으로 대칭을 이루는 여재함(80)이 설치되는 것으로, 이러한 하부 경사 구조를 통하여 상층의 조립여재(91)로 최로 공급된 처리수가 조립여재(91)의 공극을 따라 신속하게 유하함과 동시에 상기 다공판을 통과하여 광범위하게 하방 배출되는 것이다.That is, the lower plate body is formed of a perforated plate in which a plurality of water passage holes are perforated, and the central portion of the lower plate body is bent in a V shape, and a filter box 80 symmetrical about the central axis of the treatment tank is installed as shown in FIG. In this way, the treated water supplied to the upper granulated filter medium 91 through the lower inclined structure quickly flows along the gap of the granulated filter medium 91 and at the same time passes through the perforated plate and is discharged downward in a wide range.

또한, 도 2 및 도 5에서와 같이, 여재함(80) 설치 구조를 통하여 처리조 상층에는 조립여재(91)가 적층되고, 그 하부인 처리조 중앙부 및 하부에는 세립여재(92)가 적층되어, 전체적으로 처리조의 단면상 2층의 다중 여재 구조가 형성된다.In addition, as shown in FIGS. 2 and 5, through the filter media box 80 installation structure, the granulated filter media 91 is stacked on the upper layer of the treatment tank, and the fine filter media 92 is stacked on the center and lower portions of the treatment tank, , as a whole, a two-layer multi-filter structure is formed on the cross-section of the treatment tank.

따라서, 도 5 및 도 6에서와 같이, 여재함(80)이 처리조 상부에 설치되고 여재함(80)에는 조립여재(91)가 적재되며, 처리조내 여재함(80) 하부 공간에는 세립여재(92)가 적재되는 본 발명 처리조에 있어서, 유입관(41)을 통하여 저류실(40)로 유입된 처리수가 일시 저류된 후 방수구(45)로 배출되어 급수로(50)로 유입되고, 급수로(50)의 월류벽(51)을 따라 월류되어 조립여재(91) 상부로 투입된 후, 여재함(80)의 경사면에 적재된 조립여재(91)를 경유하면서 처리수가 유하함과 동시에 다공판인 여재함(80) 하부 판체를 통과하여 세립여재(92)로 확산 침투되는 처리수의 경로가 형성된다.Therefore, as shown in FIGS. 5 and 6, the filter medium box 80 is installed on the upper part of the treatment tank, the assembled filter medium 91 is loaded in the filter medium box 80, and the fine filter medium is placed in the lower space of the filter medium box 80 in the treatment tank. In the treatment tank of the present invention in which 92 is loaded, the treated water flowing into the storage chamber 40 through the inlet pipe 41 is temporarily stored, then discharged through the discharge port 45 and introduced into the water supply passage 50, and the water is supplied. After the flow overflows along the overflow wall 51 of the furnace 50 and is introduced to the top of the granulated filter media 91, the treated water flows down while passing through the granulated filter media 91 loaded on the inclined surface of the filter media box 80, and at the same time, the perforated plate A path is formed for the treated water to diffuse and penetrate into the fine filter medium 92 through the lower plate body of the phosphorus filter medium box 80 .

이로써, 도 5에서와 같이, 비록 처리조 상부 측단에 국한된 처리수의 최초 공급이 이루어짐에도 불구하고, 경사면을 형성하는 조립여재(91) 적층부를 처리수가 신속하게 통과함과 동시에, 하방 배출이 동반 수행됨으로써, 처리조 횡단면상 대부분의 면적을 차지하는 세립여재(92) 적재부 전체 영역으로 처리수가 광범위하게 확산되어 침투될 수 있으므로, 전술한 종래기술의 살수용 배관 또는 상부 수면 형성 등의 조치 없이도 처리수의 원활하고 균일한 확산 및 우수한 처리효율 확보가 가능하게 된다.As a result, as shown in FIG. 5, even though the first supply of the treated water is limited to the upper side of the treatment tank, the treated water quickly passes through the laminated filter media 91 forming the inclined surface and is accompanied by downward discharge. By performing this, the treated water can be widely diffused and penetrated into the entire area of the loading part of the fine filter medium 92, which occupies most of the area on the cross section of the treatment tank, so that the treatment can be performed without measures such as the above-mentioned prior art watersprinkling pipe or formation of the upper water surface. It is possible to ensure smooth and uniform diffusion of water and excellent treatment efficiency.

이렇듯, 세립여재(92)와 광범위하게 접촉하면서 오염물이 제거된 처리수는 유공관(21)으로 유입된 후, 도 6에서와 같이 집수실(30)로 집수되어 저류되며, 집수실(30)에 저류된 정화 처리수는 배출관(31)을 통하여 외부로 최종 배출된다.In this way, the treated water from which contaminants are removed while extensively contacting the fine filter medium 92 flows into the perforated pipe 21, and then is collected and stored in the collection chamber 30 as shown in FIG. 6, and is stored in the collection chamber 30 The accumulated purified water is finally discharged to the outside through the discharge pipe 31 .

한편, 도 7은 본 발명의 여재함(80)을 발췌하여 도시한 것으로, 도시된 바와 같이, 여재함(80)의 내부에 수직으로 돌출된 다수의 돌출봉(81)을 접합하고, 돌출봉(81)의 상단에는 결속후크(82)를 형성함으로써, 도 2에서와 같이 여재가 적재된 상태에서도 크레인 등의 장비를 활용하여 여재함(80)을 신속하게 설치 및 분리할 수 있다.On the other hand, FIG. 7 shows an excerpt of the filter box 80 of the present invention. As shown, a plurality of protruding rods 81 vertically protruding inside the filter box 80 are bonded, and the protruding rod By forming the binding hook 82 at the upper end of the 81, as shown in FIG. 2, the filter media box 80 can be quickly installed and separated using equipment such as a crane even when the media is loaded.

즉, 도 3 및 도 5에서와 같이, 여재함(80)의 평면상 폭은 양측 월류벽(51) 표면 사이의 거리와 일치하도록 형성하여, 여재함(80)이 처리조의 양측 급수로(50) 월류벽(51) 사이에 결합될 수 있도록 함으로써, 별도의 고정 수단 없이도 여재함(80)이 정위치에 안정적으로 설치될 수 있도록 하고, 상기 돌출봉(81) 및 결속후크(82)를 통하여 인양장비를 결선할 수 있도록 한 것으로, 이로써 본 발명 처리조의 최초 설치시 용이한 시공이 가능함은 물론, 유지관리에 있어서도 가용 수명이 경과된 조립여재(91)를 신속하고 간편하게 교체할 수 있다.That is, as shown in FIGS. 3 and 5, the width of the filter tray 80 in plan is formed to match the distance between the surfaces of the overflow walls 51 on both sides, so that the filter tray 80 is the water supply path 50 on both sides of the treatment tank. ) By enabling it to be coupled between the overflow walls 51, the filter tray 80 can be stably installed in place without a separate fixing means, and through the protruding rod 81 and the binding hook 82 The lifting equipment can be wired, so that easy construction is possible at the time of initial installation of the treatment tank of the present invention, and the assembled filter media 91 whose usable life has elapsed can be quickly and conveniently replaced in maintenance.

특히, 도 1 및 도 2에서와 같이, 처리조에 결합되는 여재함(80)을 처리조 종방향 중심선을 분할하는 다수의 소형 단위 여재함(80)으로 구성함으로써, 조립여재(91)를 부분적으로 교체할 수도 있을 뿐 아니라, 본 발명 습지여상의 가동을 중단하지 않으면서도 조립여재(91)를 간편하게 교체할 수 있다.In particular, as shown in FIGS. 1 and 2, by configuring the filter media box 80 coupled to the treatment tank with a plurality of small unit filter media boxes 80 dividing the longitudinal center line of the treatment tank, the assembled filter media 91 is partially formed. Not only can it be replaced, but the assembled filter medium 91 can be easily replaced without interrupting the operation of the wet filter bed of the present invention.

한편, 도 8은 본 발명의 조립여재(91) 제작 과정을 도시한 것으로, 본 발명의 조립여재(91)는 전술한 바와 같이, 입경 5mm 내지 10mm의 구형 입상체로서, 조직내 다공성이 부여되어 처리수의 유하 경로 역할 뿐 아니라, 오염물의 흡착 기능도 겸비하게 된다.Meanwhile, FIG. 8 shows a manufacturing process of the granulated filter medium 91 of the present invention. As described above, the granulated filter medium 91 of the present invention is a spherical particle having a particle diameter of 5 mm to 10 mm, and has internal porosity. It not only serves as a flow path for treated water, but also has a function of adsorbing contaminants.

이러한 본 발명의 조립여재(91)에 요구되는 특성으로는 장기간 구형(球形)을 유지함과 동시에 표면의 평탄성도 유지하여, 처리수 접촉 면적을 확보하면서도 공극간 원활한 처리수 유통을 보장하고, 외부로 노출되는 구조상 요구되는 고도의 강도를 확보하는 것이라 할 수 있는데, 이들 특성은 화산석 등 종래의 천연 다공성 입상체는 물론, 발포 성형되는 종래의 인공 다공성 입상체에서는 발현하기 어려운 특성이라 할 수 있다.The characteristics required for the granulated filter medium 91 of the present invention include maintaining a spherical shape for a long time and maintaining flatness of the surface, ensuring a smooth flow of treated water between pores while securing a contact area for treated water, and It can be said to secure a high degree of strength required for the exposed structure, and these characteristics are difficult to express in conventional artificial porous granular materials that are foam-molded as well as conventional natural porous granular materials such as volcanic stone.

이에, 본 발명에서는 점토를 구형으로 성형하여 소성(燒成) 처리하되, 미세 목분(木粉)을 사전 혼입하고, 소성 과정에서 목분의 연소 및 소실을 유도함으로써, 조직 다공성이 양호하면서도 강도가 우수하고, 표면 평탄성이 장기간 유지되는 구형 입상체를 제작하였다.Therefore, in the present invention, the clay is molded into a sphere and fired, but fine wood powder is pre-mixed, and wood powder is burned and lost during the firing process, so that the tissue porosity is good and the strength is excellent. and produced spherical granular bodies with surface flatness maintained for a long period of time.

이러한 본 발명 조립여재(91)의 제작 과정은 도 8에서와 같이, 점토, 목분 및 물을 혼합하여 페이스트를 형성하는 단계로 개시되는데, 이때 목분은 100메쉬 이하의 미세 분말상의 목분을 적용하며, 목분과 점토는 건조 분말상태에서 충분히 사전 혼합한 후 물을 투입하는 방식으로 가공하는 것이 목분과 점토의 균질혼합에 있어서 유리하다.As shown in FIG. 8, the manufacturing process of the granulated filter medium 91 of the present invention begins with the step of forming a paste by mixing clay, wood flour and water. It is advantageous in homogeneous mixing of wood flour and clay to process wood flour and clay in a manner in which water is added after sufficiently pre-mixing in a dry powder state.

목분과 점토 및 물이 혼합된 페이스트는 몰드 등에 투입 및 압착되어 구형으로 성형된 후 건조되며, 이후 건조된 성형체를 전기로에서 1,000℃ 내외에서 6시간 소성 처리함으로써, 본 발명의 조립여재(91)가 완성된다.The paste, which is a mixture of wood flour, clay, and water, is put into a mold, compressed, formed into a sphere, and then dried. Then, the dried molded body is fired in an electric furnace at around 1,000° C. for 6 hours to obtain the granulated filter medium 91 of the present invention. It is completed.

11 : 저판
12 : 전벽
13 : 후벽
14 : 측벽
21 : 유공관
30 : 집수실
31 : 배출관
40 : 저류실
41 : 유입관
45 : 방수구
50 : 급수로
51 : 월류벽
80 : 여재함
81 : 돌출봉
82 : 결속후크
91 : 조립여재
92 : 세립여재
11: bottom plate
12: front wall
13: posterior wall
14: side wall
21: perforated pipe
30: collection room
31: discharge pipe
40: storage room
41: inlet pipe
45: water outlet
50: water supply
51: overflow wall
80: Yeojaeham
81: protruding bar
82: binding hook
91: assembly filter
92: fine filter medium

Claims (2)

비점오염처리 습지여상에 있어서,
저판(11), 전벽(12), 후벽(13) 및 측벽(14)으로 형성된 장방형의 처리조 내부에는 종방향으로 유공관(21)이 설치되며;
전벽(12)의 외측에는 유입관(41)이 연결된 저류실(40)이 형성되고, 후벽(13)의 외측에는 배출관(31)이 연결된 집수실(30)이 형성되며;
유공관(21)의 일측 단부는 후벽(13)을 관통하여 집수실(30) 내부로 연결되고;
양측 측벽(14)의 상단부에는 각각 처리조 중심측으로 돌출된 L자형 단면의 급수로(50)가 형성되되, 급수로(50)의 측벽(14) 타측단에는 월류벽(51)이 기립 형성되어, 급수로(50)로 이송되던 처리수가 월류벽(51)을 따라 월류되면서 처리조의 평면상 종방향 전체 구간에 대한 급수가 수행되며;
전벽(12) 상부에는 방수구(45)가 절개 형성되어 저류실(40)과 급수로(50)가 연결되고;
다공판인 하부 판체에 대칭 경사면이 형성된 V자형 단면의 여재함(80)이 처리조 상부에 설치되고 여재함(80)에는 입경 5mm 내지 10mm의 입상체인 조립여재(91)가 적재되며, 처리조내 여재함(80) 하부 공간에는 조립여재(91)에 비하여 입경이 작은 세립여재(92)가 적재되어, 유입관(41)을 통하여 저류실(40)로 유입된 처리수가 일시 저류된 후 방수구(45)로 배출되어 급수로(50)로 유입되고, 급수로(50)의 월류벽(51)을 따라 월류되어 조립여재(91) 상부로 투입된 후, 여재함(80)의 경사면에 적재된 조립여재(91)를 경유하면서 처리수가 유하함과 동시에 다공판인 여재함(80) 하부 판체를 통과하여 세립여재(92)로 확산 침투됨을 특징으로 하는 여재 부분 교환형 비점오염처리 습지여상.
In the non-point pollution treatment wetland filter,
A perforated pipe 21 is installed in the longitudinal direction inside the rectangular treatment tank formed by the bottom plate 11, the front wall 12, the rear wall 13 and the side wall 14;
The storage chamber 40 connected to the inlet pipe 41 is formed outside the front wall 12, and the collection chamber 30 connected to the discharge pipe 31 is formed outside the rear wall 13;
One end of the perforated pipe 21 passes through the rear wall 13 and is connected to the inside of the collecting chamber 30;
An L-shaped cross section protruding toward the center of the treatment tank is formed at the upper end of the side walls 14 on both sides, and an overflow wall 51 is formed upright at the other end of the side wall 14 of the water supply passage 50. , while the treated water transferred to the water supply passage 50 overflows along the overflow wall 51, water is supplied to the entire section in the vertical direction on the plane of the treatment tank;
The water discharge port 45 is cut in the upper part of the front wall 12 to connect the storage chamber 40 and the water supply passage 50;
A filter tray 80 having a V-shaped cross section formed on a lower plate, which is a perforated plate, with a symmetrical inclined surface is installed on the top of the treatment tank, and assembled filter media 91, which is granular particles having a particle size of 5 mm to 10 mm, are loaded in the filter box 80, and inside the treatment tank In the lower space of the filter medium box 80, a fine filter medium 92 having a smaller particle size than the assembled filter medium 91 is loaded, and the treated water flowing into the storage chamber 40 through the inlet pipe 41 is temporarily stored, and then the discharge port ( 45), flows into the water supply channel 50, overflows along the overflow wall 51 of the water supply channel 50, is introduced into the upper part of the assembled filter media 91, and then loaded on the inclined surface of the filter media box 80. A filter medium partially exchangeable non-point pollution treatment wetland filter, characterized in that the treated water flows through the filter medium 91 and at the same time passes through the lower plate of the filter medium box 80, which is a perforated plate, and diffuses and penetrates into the fine filter medium 92.
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Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002336615A (en) * 2001-05-14 2002-11-26 Kiyo Kuroda Filtration equipment
KR20120140333A (en) * 2011-06-21 2012-12-31 주식회사 유비이엔씨 Infiltration trench
KR102348747B1 (en) * 2021-10-07 2022-01-07 주식회사 빌트이엔씨 Initial rain-water treatment equipment of downward filtration mode

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002336615A (en) * 2001-05-14 2002-11-26 Kiyo Kuroda Filtration equipment
KR20120140333A (en) * 2011-06-21 2012-12-31 주식회사 유비이엔씨 Infiltration trench
KR102348747B1 (en) * 2021-10-07 2022-01-07 주식회사 빌트이엔씨 Initial rain-water treatment equipment of downward filtration mode

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