KR102561960B1 - Weir watering type trickling filter - Google Patents

Weir watering type trickling filter Download PDF

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KR102561960B1
KR102561960B1 KR1020220022600A KR20220022600A KR102561960B1 KR 102561960 B1 KR102561960 B1 KR 102561960B1 KR 1020220022600 A KR1020220022600 A KR 1020220022600A KR 20220022600 A KR20220022600 A KR 20220022600A KR 102561960 B1 KR102561960 B1 KR 102561960B1
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filter medium
water
treatment tank
filter
wall
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KR1020220022600A
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Korean (ko)
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김옥희
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주식회사 에코엔지니어링
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Priority to KR1020230004631A priority patent/KR20230125726A/en
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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
    • B01D24/38Feed or discharge devices
    • B01D24/40Feed or discharge devices for feeding
    • 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
    • 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
    • C02F3/04Aerobic processes using trickle filters
    • 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)
  • Biodiversity & Conservation Biology (AREA)
  • Microbiology (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Biological Treatment Of Waste Water (AREA)

Abstract

본 발명은 처리 대상 오, 폐수가 입상체(粒狀體)인 여재(濾材)를 통과하면서 오염물이 흡착 및 산화되어 정화 처리되는 살수여과상(撒水濾過床)에 관한 것으로, 처리조내 여재를 상층의 조립여재(91)와 하층의 세립여재(92)로 구분 구성하되, 처리조 측벽(14) 상단부에 월류형 급수로(50)를 형성하여, 처리조 상부의 살수용 배관을 완전히 배제하면서도 처리수의 원활한 침투확산이 가능하도록 한 것이다.
본 발명을 통하여, 살수여과상의 처리조 상부를 완전 개방된 상태로 구성할 수 있을 뿐 아니라, 수면 형성을 수반하지 않는 적정 습윤 상태로 살수여과상을 운용하면서도 여재내 처리수의 균일하고 원활한 확산을 유도할 수 있어, 살수여과상의 성능 및 활용도를 제고할 수 있다.
The present invention relates to a watersprinkling filter bed in which pollutants are adsorbed and oxidized while passing through a granular filter medium, in which wastewater to be treated is purified. It is composed of a granular filter medium 91 and a fine filter medium 92 of the lower layer, but an overflow type water supply path 50 is formed at the upper end of the side wall 14 of the treatment tank, while completely excluding the watering pipe at the top of the treatment tank. This is to ensure smooth penetration and diffusion of water.
Through the present invention, it is possible to configure the upper part of the treatment tank on the watering filter in a completely open state, and to operate the watering filtering bed in an appropriately wet state without water surface formation, while uniformly and smoothly spreading the treated water in the filter media. It can be induced, so the performance and utilization of the trickling filter bed can be improved.

Description

월류 급수형 살수여과상{WEIR WATERING TYPE TRICKLING FILTER}Overwater watering type trickling filter {WEIR WATERING TYPE TRICKLING FILTER}

본 발명은 처리 대상 오, 폐수가 입상체(粒狀體)인 여재(濾材)를 통과하면서 오염물이 흡착 및 산화되어 정화 처리되는 살수여과상(撒水濾過床)에 관한 것으로, 처리조내 여재를 상층의 조립여재(91)와 하층의 세립여재(92)로 구분 구성하되, 처리조 측벽(14) 상단부에 월류형 급수로(50)를 형성하여, 처리조 상부의 살수용 배관을 완전히 배제하면서도 처리수의 원활한 침투확산이 가능하도록 한 것이다.The present invention relates to a watersprinkling filter bed in which pollutants are adsorbed and oxidized while passing through a granular filter medium, in which wastewater to be treated is purified. It is composed of a granular filter medium 91 and a fine filter medium 92 of the lower layer, but an overflow type water supply path 50 is formed at the upper end of the side wall 14 of the treatment tank, while completely excluding the watering pipe at the top of the treatment tank. This is to ensure smooth penetration and diffusion of water.

살수여과상은 대표적인 생물화학적 처리 시설로서 하수의 정화 처리는 물론, 공업 시설 또는 축산업 시설 등 각종 공해 배출 시설에서 배출되는 오, 폐수의 정화 처리 시설로서 활용되고 있다.As a representative biochemical treatment facility, the trickling filtration bed is used as a sewage purification treatment facility as well as a purification treatment facility for sewage and wastewater discharged from various pollutant discharge facilities such as industrial facilities or livestock farming facilities.

살수여과상은 그 사전적 의미에서와 같이, 수조에 적재된 여재층을 처리수가 통과하면서 오염물이 여재에 흡착되어 여과됨과 동시에 여재 표면에 부착된 미생물에 의하여 처리수내 유기물이 분해됨으로써 정화 처리되는 것으로, 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.As in its dictionary meaning, the water trickling filter phase is purified by decomposing organic matter in the treated water by microorganisms attached to the surface of the filter medium while the treated water passes through the filter medium layer loaded in the tank, and the contaminants are adsorbed and filtered on the filter medium. A watering facility is provided at the top of the treatment tank, or the treatment tank is completely filled with treated water and is operated so that the water surface is formed at all times.

특허 제2020849호 및 공개특허 제2009-101564호를 비롯한 종래의 살수여과상은 처리수의 여재 통과를 유도하는 동일한 기본 구조를 가지며, 따라서 처리조내 적재된 여재 전체에 대한 처리수의 광범위한 확산을 도모하기 위한 수단이 강구될 필요가 있다.Conventional trickling filtration beds, including Patent No. 2020849 and Patent Publication No. 2009-101564, have the same basic structure that induces the passage of treated water through the filter media, and therefore, to promote wide diffusion of the treated water to the entire filter media loaded in the treatment tank. Means for this need to be devised.

즉, 처리조내 여재 중 일부분에 처리수가 편중될 경우, 전체 살수여과상의 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 trickling filtration 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 살수여과상에서는 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, as a means for inducing smooth diffusion of polluted treated water in a conventional watering filter bed, 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, 살수여과상에 있어서, 저판(11), 전벽(12), 후벽(13) 및 측벽(14)으로 형성된 장방형의 처리조 내부에는 종방향으로 유공관(21)이 설치되며, 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, 처리조 내부에는 상층의 조립여재(91) 및 하층의 세립여재(92)가 포설 적층되되, 조립여재(91)와 세립여재(92) 사이에는 V자형 단면의 경계면이 형성되어, 유입관(41)을 통하여 공급된 처리수가 급수로(50)의 월류벽(51)을 따라 월류되어 조립여재(91) 상부로 투입된 후, 하부 경계면에 경사가 형성된 조립여재(91)를 경유하면서 처리수가 유하함과 동시에 하방 배출되어 세립여재(92)로 확산 침투됨을 특징으로 하는 월류 급수형 살수여과상이다.The present invention was devised in view of the above-mentioned problems, and in the water trickling filtration bed, a perforated pipe 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 21 is installed, and a collection chamber 30 to which the discharge pipe 31 is connected is formed outside the rear wall 13, and one end of the perforated pipe 21 penetrates the rear wall 13 to enter the collection chamber 30. , and at the upper ends of both side walls 14, water supply passages 50 protruding toward the center of the treatment tank are formed, and an overflow wall 51 is formed upright at the other end of the side wall 14 of the water supply passage 50, , Inside the treatment tank, the upper granulated filter medium 91 and the lower layer fine-grained filter medium 92 are laid and stacked, and a V-shaped cross-sectional boundary is formed between the granulated filter medium 91 and the fine-grained filter medium 92, so that the inlet pipe ( After the treated water supplied through 41) overflows along the overflow wall 51 of the water supply channel 50 and is injected into the upper part of the granulated filter medium 91, the treated water flows down while passing through the granulated filter medium 91 formed with a slope on the lower boundary surface. At the same time, it is discharged downward and spreads and penetrates into the fine filter medium (92).

또한, 본 발명은 상기 급수로(50)의 하부에는 처리조 중심측으로 돌출된 집수로(60)가 형성되되, 집수로(60)의 측벽(14) 타측단에는 집수벽(61)이 기립 형성되며, 후벽(13)을 관통하는 토출관(67)이 설치되어 집수로(60)와 집수실(30)이 연결되어, 유공관(21)으로 가압 주입된 세정수가 세립여재(92) 및 조립여재(91)를 경유한 후 집수벽(61)을 월류하여 집수로(60)로 유입되고 토출관(67)을 통하여 집수실(30)로 회수됨을 특징으로 하는 월류 급수형 살수여과상이다.In addition, in the present invention, a water collecting path 60 protruding toward the center of the treatment tank is formed at the lower portion of the water supply path 50, and a water collecting wall 61 is formed standing at the other end of the side wall 14 of the water collecting path 60. A discharge pipe 67 penetrating the rear wall 13 is installed to connect the water collection channel 60 and the water collection chamber 30, and the washing water pressurized and injected through the perforated pipe 21 passes through the fine filter media 92 and the assembled filter media. After passing through (91), the water overflows the water collection wall (61), flows into the water collection channel (60), and is returned to the water collection room (30) through the discharge pipe (67).

본 발명을 통하여, 살수여과상의 처리조 상부를 완전 개방된 상태로 구성할 수 있을 뿐 아니라, 수면 형성을 수반하지 않는 적정 습윤 상태로 살수여과상을 운용하면서도 여재내 처리수의 균일하고 원활한 확산을 유도할 수 있어, 살수여과상의 성능 및 활용도를 제고할 수 있다.Through the present invention, it is possible to configure the upper part of the treatment tank on the watering filter in a completely open state, and to operate the watering filtering bed in an appropriately wet state without water surface formation, while uniformly and smoothly spreading the treated water in the filter media. It can be induced, and the performance and utilization of the trickling filter bed can be improved.

특히, 살수여과상 처리조 상부의 배관을 완벽하게 배제할 수 있으므로, 살수여과상의 유지관리 편의성을 개선하고 미관을 확보할 수 있을 뿐 아니라, 식생 조성 또는 시설물 설치 등 살수여과상 상부 공간의 자유로운 활용이 가능하다.In particular, since the piping at the top of the treatment tank can be completely excluded, the maintenance convenience of the trickling filtration bed can be improved and aesthetics can be secured, as well as the free use of the upper space of the trickling filtration bed such as vegetation formation or installation of facilities. this is possible

또한, 개방된 처리조 상층부에 수면을 형성하지 않고도 운용이 가능하므로, 산책로 또는 공원 등으로 살수여과상을 활용할 수 있다.In addition, since it can be operated without forming a water surface in the upper part of the open treatment tank, the sprinkling filtration bed can be used for walking trails or parks.

도 1은 본 발명의 사시도
도 2는 본 발명의 여재 적층 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 역세 방식 설명도
도 8은 본 발명의 조립여재 제작 과정 설명도
1 is a perspective view of the present invention
Figure 2 is an explanatory diagram of the filter media layering 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 an explanatory diagram of the backwashing method of the present invention
Figure 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 살수여과상의 외관을 도시한 것으로, 도시된 바와 같이, 본 발명은 장방형 수조인 처리조의 후단부에 집수실(30)이 구성된 시설로서, 여재를 경유하여 정화 처리된 처리수가 집수실(30)에 집수된 후 외부로 배출된다.First, FIG. 1 shows the appearance of the water trickling filtration bed of the present invention. As shown, the present invention is a facility in which a water collection chamber 30 is configured at the rear end of a treatment tank, which is a rectangular water tank, and the treated water purified through the filter medium Water is collected in the collection room 30 and then discharged to the outside.

본 발명이 적용된 살수여과상의 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 trickling 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 essentially required in the prior art. Complex watering pipes are completely excluded, and in the prior art, the water surface, which always needed to be formed on the upper side of the filter media 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 살수여과상의 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 water trickling 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, 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 in FIGS. 1 to 4, a collection chamber 30 to which the discharge pipe 31 is connected is formed outside the rear wall 13, and as shown in FIG. 4, one end of the perforated pipe 21 is the rear wall 13 ) and is connected to the inside of the collection 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 vertical direction on the plane 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 1 내지 도 6에서와 같이, 유입관(41)과 급수로(50)가 연결되어, 유입관(41)에서 배출되는 오염 처리수가 급수로(50)로 유입됨으로써 이루어진다.As shown in FIGS. 1 to 6 , in the supply of treated water to the water supply line 50, the inlet pipe 41 and the water supply line 50 are connected, and the contaminated treated water discharged from the inlet pipe 41 is supplied to the water supply ( 50).

도 5 및 도 6에서와 같이, 급수로(50)의 월류벽(51)을 따라 처리조 상부로 살수된 처리수는 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 first injected and penetrated into the granulated filter media 91 installed on the top of the treatment tank, and then After penetrating into the fine filter medium 92 laid and loaded in the lower part of the treatment tank, contaminants are adsorbed and removed, and then introduced into the perforated pipe 21 at the center of the lower part 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 may 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 5에서와 같이, 조립여재(91)는 단순히 세립여재(92) 상층부에 수평 적층 포설되는 것이 아니라, 조립여재(91)층의 단면이 상면은 평활하되 하부는 V자형을 이루는 구성을 가지는 것으로, 이로써 조립여재(91)층에서의 신속한 처리수 유하 및 원활한 광범위 하방 유출이 수행될 수 있다.As shown in FIGS. 2 and 5, the granulated filter medium 91 is not simply horizontally stacked and laid on the upper layer of the fine-grain filter medium 92, but the cross section of the granulated filter medium 91 layer has a smooth upper surface and a V-shaped lower part. As a result, rapid flow of treated water and smooth downward discharge over a wide range can be performed in the layer of the granulated filter medium 91.

즉, 처리조 내부에는 상층의 조립여재(91) 및 하층의 세립여재(92)가 포설 적층되되, 조립여재(91)와 세립여재(92) 사이에는 V자형 단면의 경계면이 형성되어, 처리수가 급수로(50)의 월류벽(51)을 따라 월류되어 조립여재(91) 상부로 투입된 후, 하부 경계면에 경사가 형성된 조립여재(91)를 경유하면서 처리수가 유하함과 동시에 하방 배출되어 세립여재(92)로 확산 침투되는 것이다.That is, the upper granulated filter medium 91 and the lower fine-grain filter medium 92 are laid and stacked inside the treatment tank, and a V-shaped cross-sectional boundary is formed between the granulated filter medium 91 and the fine-grain filter medium 92, so that the treated water After the flow overflows along the overflow wall 51 of the water supply channel 50 and is introduced to the top of the granulated filter medium 91, the treated water flows down and is discharged downward while passing through the granulated filter medium 91 formed with a slope on the lower boundary surface. (92) to diffuse penetration.

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 발명에 있어서 여재에 대한 역세(逆洗)가 수행되는 상황을 예시한 것으로, 이로써 여재를 교체하지 않고도 여재간 공극에 흡착 내지 잔류되어 여재의 여과 성능을 잠식하는 오염물을 효과적으로 제거하고, 여과상의 성능을 복원할 수 있게 된다.Meanwhile, FIG. 7 illustrates a situation in which backwashing of the filter media is performed in the present invention, whereby contaminants adsorbed or remaining in the pores between the filter media and eroding the filtration performance of the filter media are effectively removed without replacing the filter media. removed, and the performance of the filter bed can be restored.

도 4 내지 도 7에서와 같이, 급수로(50)의 하부에는 처리조 중심측으로 돌출된 집수로(60)가 형성되되, 집수로(60)의 측벽(14) 타측단에는 집수벽(61)이 기립 형성되어, 역세시 주입되는 세정수의 집수 및 회수를 수행하게 되는데, 도 7에서와 같이, 조립여재(91)의 상단면은 집수벽(61)의 상단과 일치하도록 형성하는 것이 역세 수행에 있어서 유리하다.As shown in FIGS. 4 to 7, a water collecting path 60 protruding toward the center of the treatment tank is formed at the lower portion of the water supply path 50, and a water collecting wall 61 is formed at the other end of the side wall 14 of the water collecting path 60. This standing formation is performed to collect and collect the washing water injected during backwashing. As shown in FIG. 7, forming the upper surface of the assembled filter medium 91 to coincide with the upper end of the water collecting wall 61 performs backwashing. advantageous in

또한, 도 4에서와 같이, 후벽(13)을 관통하는 토출관(67)이 설치되어 집수로(60)와 집수실(30)이 연결되는데, 이로써 유공관(21)으로 가압 주입된 세정수가 세립여재(92) 및 조립여재(91)를 경유한 후 집수벽(61)을 월류하여 집수로(60)로 유입되고 토출관(67)을 통하여 집수실(30)로 회수될 수 있다.In addition, as shown in FIG. 4, a discharge pipe 67 penetrating the rear wall 13 is installed to connect the water collection channel 60 and the water collection chamber 30, whereby the washing water pressurized and injected into the perforated pipe 21 becomes fine. After passing through the filter media 92 and the assembled filter media 91, it overflows the water collecting wall 61, flows into the water collecting channel 60, and can be returned to the collecting chamber 30 through the discharge pipe 67.

이러한 본 발명의 처리조에 있어서, 역세 작업은 우선, 유입관(41) 및 집수실(30)의 배출관(31)을 모두 폐쇄하여 처리조의 가동을 중지한 후, 집수실(30) 내부의 유공관(21) 말단에 내압 호스를 연결하여 외부에서 세정수를 주입하고, 여재를 세정한 세정수가 토출관(67)을 통하여 집수실(30)로 토출됨에 따라 이를 회수하여 제거하는 방식으로 수행될 수 있다.In the treatment tank of the present invention, the backwashing operation first closes both the inlet pipe 41 and the discharge pipe 31 of the collecting chamber 30 to stop the operation of the treatment tank, and then the perforated pipe inside the collecting chamber 30 ( 21) It can be performed by connecting a pressure-resistant hose to the end, injecting washing water from the outside, and recovering and removing the washing water after washing the filter media as it is discharged to the collection chamber 30 through the discharge pipe 67. .

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
41 : 유입관
50 : 급수로
51 : 월류벽
60 : 집수로
61 : 집수벽
67 : 토출관
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
41: inlet pipe
50: water supply
51: overflow wall
60: catchment
61: catchment wall
67: discharge pipe
91: assembly filter
92: fine filter media

Claims (2)

살수여과상에 있어서,
저판(11), 전벽(12), 후벽(13) 및 측벽(14)으로 형성된 장방형의 처리조 내부에는 종방향으로 유공관(21)이 설치되며;
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;
처리조 내부에는 상층의 조립여재(91) 및 하층의 세립여재(92)가 포설 적층되되, 조립여재(91)는 입경 5mm 내지 10mm의 입상체로서 점토, 목분 및 물이 혼합된 페이스트를 구형으로 성형 및 건조한 후 전기로에서 소성 처리하여 제작되고, 세립여재(92)는 조립여재(91)에 비하여 입경이 작은 토사이며, 조립여재(91)와 세립여재(92) 사이에는 V자형 단면의 경계면이 형성되어, 유입관(41)을 통하여 공급된 처리수가 급수로(50)의 월류벽(51)을 따라 월류되어 조립여재(91) 상부로 투입된 후, 하부 경계면에 경사가 형성된 조립여재(91)를 경유하면서 처리수가 유하함과 동시에 하방 배출되어 세립여재(92)로 확산 침투됨을 특징으로 하는 월류 급수형 살수여과상.
In the trickling filtration bed,
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;
On the outside of the rear wall 13, a collection chamber 30 to which the discharge pipe 31 is connected 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;
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;
Inside the treatment tank, an upper layer of granulated filter media 91 and a lower layer of fine-grained filter media 92 are laid and stacked, and the granulated filter media 91 is a granular material with a particle size of 5 mm to 10 mm, and a paste of clay, wood flour and water is mixed in a spherical shape. It is produced by firing in an electric furnace after molding and drying, and the fine-grain filter medium 92 is soil with a smaller particle diameter than the coarse-grained filter medium 91, and the interface of the V-shaped cross section between the granulated filter medium 91 and the fine-grained filter medium 92 is formed. Formed, the treated water supplied through the inlet pipe 41 overflows along the overflow wall 51 of the water supply channel 50 and is injected into the upper part of the granulated filter medium 91, and then the granulated filter medium 91 with a slope formed on the lower boundary surface An overflow water type sprinkler filter bed, characterized in that the treated water flows down and is discharged downward at the same time as it passes through, and diffuses and penetrates into the fine filter medium (92).
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Citations (4)

* 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
KR102062232B1 (en) * 2019-03-21 2020-01-03 주식회사 미래환경연구원 Pressurized aeration type trickling filter for water treatment
KR102348747B1 (en) * 2021-10-07 2022-01-07 주식회사 빌트이엔씨 Initial rain-water treatment equipment of downward filtration mode

Patent Citations (4)

* 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
KR102062232B1 (en) * 2019-03-21 2020-01-03 주식회사 미래환경연구원 Pressurized aeration type trickling filter for water treatment
KR102348747B1 (en) * 2021-10-07 2022-01-07 주식회사 빌트이엔씨 Initial rain-water treatment equipment of downward filtration mode

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