KR100700129B1 - Waste Water Treatment System - Google Patents

Waste Water Treatment System Download PDF

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Publication number
KR100700129B1
KR100700129B1 KR1020060133220A KR20060133220A KR100700129B1 KR 100700129 B1 KR100700129 B1 KR 100700129B1 KR 1020060133220 A KR1020060133220 A KR 1020060133220A KR 20060133220 A KR20060133220 A KR 20060133220A KR 100700129 B1 KR100700129 B1 KR 100700129B1
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South Korea
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tank
layer
screen
crushing
sewage treatment
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KR1020060133220A
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Korean (ko)
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김봉길
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김봉길
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    • 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
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/40Devices for separating or removing fatty or oily substances or similar floating material
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/12Activated sludge processes
    • C02F3/1205Particular type of activated sludge processes
    • C02F3/1215Combinations of activated sludge treatment with precipitation, flocculation, coagulation and separation of phosphates
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/005Black water originating from toilets
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/24Separation of coarse particles, e.g. by using sieves or screens
    • 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)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Analytical Chemistry (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Microbiology (AREA)
  • Biological Treatment Of Waste Water (AREA)

Abstract

A waste water treatment system is provided to mount an adulteration crushing unit in flow rate control tanks for improving water treatment efficiency and use a dual stage filtering unit formed of sand and gravels, thereby lowering BOD(Biochemical Oxygen Demand) of finally treated water to 7ppm and SS(Suspended Substances) thereof to 7ppm or less. A waste water treatment system includes an adulteration crushing unit(200) having a slant adulteration crushing screen mounted to a wall(22) defining first and second flow rate control tanks(20,30) from each other, and a nozzle mounted at a lower part of the adulteration crushing screen for spraying air along a wall surface of the adulteration crushing screen, so that adulterations of waste water passing through the adulteration crushing screen is crushed. A filtering unit(100) is mounted at an end of the system and filters the treated water via dual layers of a gravel layer and a sand layer, wherein the gravels and sand are reused after cleaning without loss.

Description

오수 처리 장치{Waste Water Treatment System}Wastewater Treatment System {Waste Water Treatment System}

도 1은 본 발명에 따른 오수처리장치를 나타내는 단면도1 is a cross-sectional view showing a sewage treatment apparatus according to the present invention

도 2는 도 1의 협잡물 파쇄장치를 나타내는 도면FIG. 2 is a view showing a contaminant crushing device of FIG.

도 3은 여과장치를 나타내는 도면3 shows a filtration device.

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

10 : 스크린조 20, 30 : 유량조정조10: screen tank 20, 30: flow rate adjustment tank

40 : 유량계량조 50,60,70 : 폭기조40: flow meter tank 50, 60, 70: aeration tank

80 : 침전조 100 : 여과장치80: settling tank 100: filtration apparatus

110 : 유입층 120 : 자갈층110: inflow layer 120: gravel layer

130 : 모래층 140 ; 배출층130: sand layer 140; Discharge layer

142 : 통공 144 : 오버플로우관142: through hole 144: overflow pipe

146 : 배출구 148 : 덮개146: outlet 148: cover

200 : 협잡물 파쇄 장치 210 : 협잡물 파쇄 스크린200: contaminant crushing device 210: contaminant crushing screen

220 : 분사노즐220: injection nozzle

본 발명은 오수 처리 장치에 관한 것으로, 보다 상세하게는 유량조정조에 공기를 사용한 협잡물 파쇄장치를 구비하고 처리가 완료된 처리수를 모래와 자갈의 2단 여과장치를 사용하여 여과시켜 배출함으로써, 최종처리수의 BOD가 7ppm, SS가 7ppm 이하가 되도록 처리효율을 향상시키는 오수 처리 장치에 관한 것이다.The present invention relates to a sewage treatment device, and more specifically, to a flow rate adjusting tank, which includes a waste crushing device using air, and the treated water is filtered and discharged by using a two-stage filtration device of sand and gravel for final treatment. The present invention relates to a sewage treatment apparatus for improving the treatment efficiency so that the BOD of the water is 7 ppm and the SS is 7 ppm or less.

최근 강이나 호수에는 부영양화가 일어나고, 바다에서는 적조현상이 일어나서 물을 오염시키고 수자원을 파괴하고 있는데, 상기 부영양화 및 적조현상이 일어나는 주요 인자는 유기물질과 질소와 인으로써, 가정 및 생산현장에서 발생 되는 오/폐수가 주요인이다.In recent years, eutrophication occurs in rivers and lakes, and red tide occurs in the oceans, polluting water and destroying water resources. The main factors in which eutrophication and red tide occur are organic substances, nitrogen, and phosphorus, which are generated at home and production sites. Wastewater / wastewater is a major factor.

특히 오수는 사람의 일상생활과 관련하여 수세식 화장실, 목욕탕, 주방 등에서 배출되는 액체성 또는 고체성 오물이 섞여 있는 물을 일컬으며, 이 오수를 배출하고자 하는 사람은 법률이 정하는 방류수질 기준 이하로 정화한 후 방류하여야 한다.In particular, sewage refers to water containing liquid or solid wastes discharged from flush toilets, baths and kitchens in relation to the daily life of a person. After discharge, it must be discharged.

이와 같이 오수를 정화하여 배출하기 위한 오수처리장치의 개략적인 구성을 살펴본다.In this way it looks at the schematic configuration of the sewage treatment apparatus for purifying and discharged sewage.

상기한 종래의 오수처리장치는 통상 오수 비중이 큰 협잡물을 걸러주는 스크린조와, 상기한 스크린조를 통과한 오수의 유입에 따른 유량변동을 완화시키고 일정량의 오수를 폭기조로 이송시키는 유량조정 및 계량조, 유량조정 및 계량조를 통과한 일정량의 오수를 폭기처리하여 산화작용과 호기성 세균에 의한 소화작용을 촉진시켜, 탄산가스, 황화수소, 메탄가스 등을 제거하는 폭기조와, 상기한 폭기조를 통과한 처리수에서 협잡물 즉 오니를 침전시켜 깨끗한 상등수를 얻어 배출하는 침 전조를 포함하여 구성된다.The conventional sewage treatment apparatus has a screen tank for filtering contaminants having a large specific gravity of sewage, and a flow rate adjusting and metering tank for mitigating flow fluctuations caused by the inflow of sewage through the screen tank and transferring a certain amount of sewage to the aeration tank. , Aeration of a certain amount of sewage through the flow rate adjustment and the metering tank to promote oxidation and digestion by aerobic bacteria, and to remove carbon dioxide, hydrogen sulfide, methane gas, etc. It consists of a sedimentation tank that precipitates contaminants, or sludge, from the water to obtain clean supernatant.

그러나, 상기한 오수처리장치에서 유량 조정조는 통상 오수가 고여있기 때문에 용존산소량의 저하로 인하여 혐기성 부패가 발생하여, 악취가 발생 되고 최종 처리수의 품질저하를 유발시키는 문제점이 있었다.However, in the sewage treatment apparatus, the flow rate adjusting tank usually has sewage, so that anaerobic decay occurs due to a decrease in the amount of dissolved oxygen, which causes odor and deteriorates the quality of the final treated water.

또한, 침전조에 침전된 오니의 량이 지나치게 많거나 청소를 자주 하지 않을 경우에는 침전조에서 충분히 오니가 침전되지 않아서 그대로 배출되는 문제점이 발생되었다.In addition, when the amount of sludge precipitated in the settling tank is too large or not cleaned frequently, the sludge is not sufficiently precipitated in the settling tank, which causes a problem of being discharged as it is.

상기한 문제점을 해결하기 위한 본 발명의 목적은 유량조정조에 공기를 사용한 협잡물 파쇄장치를 구비하여 협잡물 파쇄로 인한 처리수 품질향상과 공기공급으로 인한 용존산소량 증가로 혐기성부패가 발생되지 않도록 하고, 처리가 완료된 처리수를 모래와 자갈의 2단 여과장치를 사용하여 여과시켜 배출하되, 여과재의 청소가 용이하도록 함과 아울러 여과재의 유출이 발생되지 않도록 함으로써, 최종처리수의 생물학적 산소요구량(BOD)가 7ppm, 물속의 불용성 부유 물질(SS)가 7ppm 이하가 되도록 처리효율을 향상시키는 오수 처리 장치를 제공하는 데 있다.An object of the present invention for solving the above problems is to provide a contaminant crushing device using air in the flow rate adjustment tank to prevent the anaerobic decay occurs by improving the quality of the treated water due to the crushed contaminants and the amount of dissolved oxygen caused by the air supply The treated water is filtered and discharged using a two-stage filtration device of sand and gravel, which facilitates the cleaning of the filter medium and prevents the outflow of the filter medium, thereby reducing the biological oxygen demand (BOD) of the final treated water. The present invention provides a sewage treatment apparatus that improves treatment efficiency so that 7 ppm and insoluble suspended matter (SS) in water is 7 ppm or less.

상기한 목적을 달성하기 위한 본 발명의 특징은 스크린조와, 유량조정 및 계량조, 폭기조, 침전조를 포함하여 구성되는 오수처리장치에 있어서, 상기한 유량조정조 내부에 협잡물 파쇄 스크린을 경사지게 설치하고, 상기한 협잡물 파쇄 스크린의 하부에는 협잡물 파쇄 스크린 벽면을 따라 공기를 분사하는 분사노즐을 설치하 여 스크린을 통과한 오수의 협잡물이 파쇄되도록 한 오수 처리 장치에 있다.A feature of the present invention for achieving the above object is a sewage treatment apparatus comprising a screen tank, a flow adjustment and metering tank, aeration tank, sedimentation tank, the sludge crushing screen is installed inclined inside the flow adjustment tank, At the bottom of one contaminant crushing screen is a sewage treatment apparatus in which a spray nozzle for injecting air along the wall of the contaminant crushing screen is installed to crush the contaminants of filthy water passing through the screen.

그리고, 상기한 오수처리장치의 종단에는 통형으로 형성되어 하부로부터 상부로 각각 통공이 천공된 격벽에 의하여 공간이 구획되는 유입층, 자갈층, 모래층, 배출층을 형성하고, 유입층에는 하부에 유입구를 형성하고 역세노즐을 상부를 향해서 설치하며, 배출층에는 측면 하단에 다수의 통공이 천공되고 상부면에 오버 플로우관이 하부를 향하도록 설치되며 측면에 배출구가 형성된 덮개를 측면이 벽면과 이격되도록 설치하여, 하부 유입층에 형성된 유입구를 통해서 유입된 처리수가 자갈층과 모래층을 통과하면서 여과된 후 상부 배출층에 형성된 배출구를 통해서 배출되도록 하고, 역세관을 통한 청소시에는 역세공기에 의하여 오버플로우된 상등액과 모래가 오버플로우관을 통해서 배출된 후 모래 등은 통공을 통해서 다시 투입되거나 청소과정에서 수거되어 재투입되도록 하여 여과재(모래)의 유실이 발생되지 않도록 한 여과장치를 구비하는 데 있다.In addition, the end of the sewage treatment apparatus is formed in a tubular shape to form an inlet layer, a gravel layer, a sand layer, an outlet layer partitioned by a partition wall through which holes are perforated from the bottom to the top, and an inlet at the bottom of the inlet layer. And the back washing nozzle is installed to the upper side, and a plurality of through holes are drilled at the lower side of the discharge layer, and an overflow pipe is installed at the upper side to the lower side, and a cover having a discharge port formed at the side is spaced apart from the wall surface. Thus, the treated water introduced through the inlet formed in the lower inlet layer is filtered while passing through the gravel layer and the sand layer and discharged through the outlet formed in the upper discharge layer, and the supernatant overflowed by the backwasher during the cleaning through the backwashing tube. And sand is discharged through the overflow pipe and sand is put back through the air hole or cleaned. To A so that the input material is collected to be provided with a filtering device to prevent the loss of the filter material (sand) is not generated.

이상과 같은 특징을 갖는 본 발명의 실시예를 하기에서 첨부된 도면을 참조하여 보다 상세하게 살펴본다.An embodiment of the present invention having the above characteristics will be described in more detail with reference to the accompanying drawings.

도 1은 본 발명에 따른 오수처리장치를 나타내는 단면도이고, 도 2는 도 1의 협잡물 파쇄장치를 나타내는 도면이며, 도 3은 여과장치를 나타내는 도면이다.1 is a cross-sectional view showing a sewage treatment apparatus according to the present invention, FIG. 2 is a view showing a contaminant crushing device of Figure 1, Figure 3 is a view showing a filtration device.

본 발명에 따른 오수처리장치는 크게, 스크린조(10)와, 유량조정조(20)(30) 및 유량계량조(40), 폭기조(50)(60)(70), 침전조(80) 및 여과장치(100)를 포함하여 구성된다.The sewage treatment apparatus according to the present invention is largely divided into the screen tank 10, the flow adjustment tank 20, 30 and the flow metering tank 40, the aeration tank 50, 60, 70, sedimentation tank 80 and filtration It comprises a device 100.

상기한 구성에서 스크린조(10)는 30mm 조 스크린(12)과 10mm 세 스크린(14)이 직렬로 설치되어 유입된 오수에서 협잡물이 2차로 걸러진다.In the above-described configuration, the screen tank 10 has a 30 mm bath screen 12 and a 10 mm three screen 14 installed in series to filter out impurities from the introduced sewage.

그리고, 유량조정조(20)(30)는 1차와 2차로 구분되며, 2차 유량조정조(30)의 저면에는 산소를 공급하는 (32)이 설치되어 항상 공기를 소량 공급하여 오수의 혐기성화를 방지하고 수질을 균등하게 유기지키며, 1차 유량조정조(20)의 내부에 도 2에 나타내는 협잡물 파쇄장치(200)가 더 설치되어 오수 중의 협잡물을 파쇄하면서 오수를 순환시켜 용존산소량을 증가시키는데, 이러한 협잡물 파쇄장치(200)는 하부가 1/2차 유량조정조(20)(30)를 구분하는 벽면(22)에 부착설치되고 상부는 벽면(22)과 이격되게 경사지게 설치되며 전체 면에 걸쳐서 다수의 수평 통공(212)이 천공된 협잡물 파쇄 스크린(210)과 상기한 협잡물 파쇄스크린(210)의 하부에 설치되어 공기를 협잡물 파쇄 스크린(210) 벽면을 따라 분사하는 분사노즐(220)을 포함하여 구성된다.In addition, the flow regulating tanks 20 and 30 are divided into primary and secondary, and the lower surface of the secondary flow adjusting tank 30 is provided with 32 for supplying oxygen to always supply a small amount of air to anaerobic sewage of sewage. It prevents and maintains the water quality evenly, and is further provided in the inside of the primary flow control tank 20, the debris crusher 200 shown in Figure 2 to circulate the sewage while crushing the contaminants in the sewage to increase the amount of dissolved oxygen, The contaminant crushing device 200 is attached to the wall surface 22 separating the lower half-flow control tank 20, 30, the upper portion is inclined to be spaced apart from the wall surface 22, and a plurality of The horizontal through hole 212 is installed in the lower part of the contaminant crushing screen 210 and the above-mentioned contaminant crushing screen 210 is configured to include a spray nozzle 220 for spraying air along the wall of the contaminant crushing screen 210 do.

그리고, 상기한 2차 유량조정조(30)의 상부에는 유량계량조(40)가 설치되어 오수가 일정한 량씩 폭기조(50)로 투입되도록 하고, 폭기조(50)(60)(70)의 내부에는 미생물접촉여재(52)(62)(72)가 설치되고 하부에는 폭기용 산기관(54)(64)(74)이 설치되어 유입된 오수를 미생물접촉여재(52)(62)(72)와 접촉시켜 오수 중의 유기물을 분해 흡착 산화시켜 오수를 정화시키는데 폭기조(50)(60)(70)는 3실로 구분되어 침전조(80)의 전방에 설치되는 제 1/2폭기조(50)(60)와 침전조(80)의 후방에 설치되는 재폭기조(70)로 구성된다.In addition, a flow metering tank 40 is installed at the upper portion of the secondary flow adjusting tank 30 so that filthy water is introduced into the aeration tank 50 by a predetermined amount, and microorganisms are formed in the aeration tanks 50, 60, 70. Contact media (52) (62) (72) is installed and aeration pipes (54) (64) (74) are installed at the bottom to contact the microorganism contact media (52) (62) (72). The aeration tanks 50, 60, and 70 are divided into three chambers, and the first half aeration tanks 50, 60 and the sedimentation tank are installed in front of the sedimentation tank 80. It consists of the reaeration tank 70 provided in the back of 80.

침전조(80)는 하부가 오목하게 형성되고 제 1유량조정조(20)와 연결되는 침 전 오니 이송관(80)이 설치되며 상부에는 월류웨어(84)가 설치되어 하부의 침전 오니는 제 1유량조정조(20)로 반송되고 상부의 월류웨어(84)에 의하여 부유물은 배출되지 않고 처리수만 배출된다.The sedimentation tank 80 is formed with a concave lower portion and a sedimentation sludge transfer pipe 80 connected to the first flow rate adjustment tank 20. It is conveyed to the adjustment tank 20, and only the processed water is discharged | emitted without the float by the upper overflowware 84.

그리고, 상기한 침전조(80)의 후단에는 산기관(74)과 미생물접촉여재(72)가 설치된 재폭기조(70)가 구비되고, 재폭기조(70)의 후단에는 여과장치(100)가 구비된다.And, the rear end of the settling tank 80 is provided with a re-aeration tank 70 provided with the diffuser 74 and the microorganism contact medium 72, the rear end of the re-aeration tank 70 is provided with a filtration device 100. .

상기 여과장치(100)는, 도 3에 나타내는 바와 같이 통형으로 형성되어 하부로부터 상부로 각각 통공(112)(122)(132)이 천공된 격벽(114)(124)(134)에 의하여 공간이 구획되는 유입층(110), 자갈층(120), 모래층(130), 배출층(140)을 형성한다.As shown in FIG. 3, the filtration device 100 is formed in a tubular shape and spaced by partition walls 114, 124, 134 through which holes 112, 122, 132 are perforated from bottom to top, respectively. The partitioned inlet layer 110, the gravel layer 120, the sand layer 130, and the discharge layer 140 are formed.

상기한 유입층(110)에는 하부에 유입구(116)를 형성하고 역세노즐(118)을 상부를 향해서 설치하며, 측면에 통공(119)이 천공된다.The inlet layer 110 has an inlet 116 formed at a lower portion thereof, a reverse nozzle 118 is installed upward, and a through hole 119 is drilled at a side surface thereof.

자갈층(120)과 모래층(130)에는 각각 자갈(126)과 모래(136)를 투입한다.Gravel 126 and sand 136 is added to the gravel layer 120 and sand layer 130, respectively.

그리고, 배출층(140)은 측면 하단에 다수의 통공(142)이 천공되고 상부면에 오버 플로우관(144)이 하부를 향하도록 설치되며 측면에 배출구(146)가 형성된 덮개(148)를 측면이 벽면(150)과 이격되도록 설치한다.And, the discharge layer 140 is installed so that a plurality of through-holes 142 in the lower side of the side and the overflow pipe 144 on the upper side toward the lower side and the cover 148 formed with the outlet 146 on the side It is installed to be spaced apart from the wall surface (150).

이에 따라 하부 유입층(110)에 형성된 유입구(116)를 통해서 유입된 처리수가 자갈층(120)과 모래층(130)을 통과하면서 여과된 후 상부 배출층(140)에 형성된 배출구(146)를 통해서 배출되도록 하고, 역세노즐(118)을 통한 청소시에는 역세공기에 의하여 오버플로우된 상등액과 모래 등이 오버플로우관(144)을 통해서 배출된 후 통공(142)을 통해서 다시 투입되거나 청소과정에서 모래는 수거하여 여과장치에 재투입할 수 있도록 하여 여과재(모래)의 유실이 발생되지 않도록 한다.Accordingly, the treated water introduced through the inlet 116 formed in the lower inlet layer 110 is filtered while passing through the gravel layer 120 and the sand layer 130 and then discharged through the outlet 146 formed in the upper outlet layer 140. In the case of cleaning through the backwash nozzle 118, the supernatant and sand overflowed by the backwashing air are discharged through the overflow pipe 144 and then introduced again through the through-hole 142 or sand in the cleaning process. The collection and return to the filtration system should be such that no loss of filter media (sand) occurs.

한편, 상기한 유입구(116)에는 이탈된 모래를 이송하는 이송관(160)이 더 설치된다.On the other hand, the inlet 116 is further provided with a transport pipe 160 for transporting the separated sand.

이상과 같이 구성된 본 발명에 의하면 BOD 농도 250ppm 이상, SS농도 200ppm이상이며 1일 유입 BOD 5.0kg/day, SS 4kg/day인 유입수를 BOD 및 SS 농도 7ppm이하로 처리하여 배출한다.According to the present invention configured as described above BOD concentration of 250ppm or more, SS concentration of 200ppm or more and inflow BOD 5.0kg / day, SS 4kg / day influent water discharged by treating the BOD and SS concentration of 7ppm or less.

이때, 각 조별 필요 공기량을 살펴보면, 우선 1차 유량 조정조(20)는 60ℓ/min, 2차 유량 조정조(30)는 40ℓ/min, 폭기조(50)(60)(70)는 200ℓ/min, 침전조(80)는 40ℓ/min이 요구된다.At this time, looking at the amount of air required for each group, firstly the primary flow rate adjustment tank 20 60 L / min, the secondary flow rate adjustment tank 30 40 L / min, aeration tanks 50, 60, 70 200 L / min, sedimentation tank 80 requires 40 l / min.

상기한 바와 같이 구성된 본 발명에 의하면 폭기조에서 현수미생물 접촉방법으로 오수를 처리하고, 유량을 조정하여, 배출수의 BOD 및 SS 농도가 7ppm이하로 처리되므로 오수저화 효율이 매우 우수한 효과가 있다.According to the present invention configured as described above, by treating the sewage by the suspension microorganism contact method in the aeration tank, by adjusting the flow rate, the BOD and SS concentration of the discharged water is treated to 7ppm or less, the sewage reduction efficiency is very excellent.

또한, 유량조정조에서 협잡물 파쇄장치에 의하여 협잡물을 파쇄시키면서 오수를 순환시키므로 혐기성부패가 발생되지 않고, 처리효율이 향상되는 효과가 있다.In addition, the wastewater is circulated while crushing the contaminants by the contaminant crushing device in the flow rate adjusting tank, so that anaerobic decay does not occur and the treatment efficiency is improved.

아울러, 상기한 여과장치에서는 자갈과 모래의 이중여과를 통해서 최종처리수의 협잡물을 제거하므로 정화효율이 향상되고, 자갈과 모래를 청소할때 역세노즐 을 통하여 역세공기를 불어주면 자갈과 모래가 뒤섞이면서 협잡물이 상부로 배출되고, 오버플로우관을 통해서 배출된 모래는 청소과정에서 수거하여 재사용할 수 있어서 여과재의 사용효율이 향상되고 정화효율이 향상되는 효과가 있다.In addition, the filtration device removes contaminants of the final treated water through the double filtration of gravel and sand to improve the purification efficiency, and when the gravel and sand is blown through the backwash nozzle when the gravel and sand is cleaned, the gravel and sand are mixed. The contaminants are discharged to the top, and the sand discharged through the overflow pipe can be collected and reused in the cleaning process, thereby improving the use efficiency of the filter medium and improving the purification efficiency.

Claims (3)

스크린조와, 유량조정조 및 유량계량조, 폭기조, 침전조를 포함하여 구성되는 오수처리장치에 있어서, In the sewage treatment apparatus comprising a screen tank, a flow control tank, a flow metering tank, aeration tank, sedimentation tank, 상기한 유량조정조 내부에 협잡물 파쇄 스크린을 경사지게 설치하고, 상기한 협잡물 파쇄 스크린의 하부에는 협잡물 파쇄 스크린 벽면을 따라 공기를 분사하는 분사노즐을 설치한 것을 특징으로 하는 오수 처리 장치.Sewage treatment device is installed inclined to the inside of the flow rate adjustment tank, and the spray nozzle for injecting air along the wall of the crushed crushed screen to the lower part of the crushed crushed screen. 스크린조와, 유량조정조 및 유량계량조, 폭기조, 침전조를 포함하여 구성되는 오수처리장치에 있어서,In the sewage treatment apparatus comprising a screen tank, a flow control tank, a flow metering tank, aeration tank, sedimentation tank, 상기한 오수처리장치의 종단에는 통형으로 형성되어 하부로부터 상부로 각각 통공이 천공된 격벽에 의하여 공간이 구획되는 유입층, 자갈층, 모래층, 배출층을 형성하고, 유입층에는 하부에 유입구를 형성하고 역세노즐을 상부를 향해서 설치하며, 배출층에는 측면 하단에 다수의 통공이 천공되고 상부면에 오버 플로우관이 하부를 향하도록 설치되며 측면에 배출구가 형성된 덮개를 측면이 벽면과 이격되도록 설치한 여과장치를 설치것을 특징으로 하는 오수 처리 장치.The end of the sewage treatment apparatus is formed in a tubular shape to form an inlet layer, a gravel layer, a sand layer, an outlet layer in which the space is partitioned by a partition wall through which holes are perforated from bottom to top, and an inlet is formed at the bottom of the inlet layer. The back washing nozzle is installed toward the upper side, and the discharge layer is installed so that a plurality of holes are drilled at the lower side of the side, and an overflow pipe is installed at the upper side toward the lower side, and a cover formed with an outlet at the side is spaced apart from the wall surface. Sewage treatment apparatus, characterized in that to install the device. 스크린조와, Screen, 내부에 협잡물 파쇄 스크린을 경사지게 설치하고, 상기한 협잡물 파쇄 스크린의 하부에는 협잡물 파쇄 스크린 벽면을 따라 공기를 분사하는 분사노즐을 설치 한 유량조정조,A flow regulating tank having a sludge crushing screen installed obliquely therein, and a spray nozzle for injecting air along the wall of the crushing crushing screen at the lower part of the crushing crushing screen; 유량조정조와 연결된 유량계량조,Flow metering tank connected to the flow adjusting tank, 폭기조,Aeration Tank, 침전조,Sedimentation Tank, 오수처리과정의 종단에 설치되고, 통형으로 형성되어 하부로부터 상부로 각각 통공이 천공된 격벽에 의하여 공간이 구획되는 유입층, 자갈층, 모래층, 배출층을 형성하고, 유입층에는 하부에 유입구를 형성하고 역세노즐을 상부를 향해서 설치하며, 배출층에는 측면 하단에 다수의 통공이 천공되고 상부면에 오버 플로우관이 하부를 향하도록 설치되며 측면에 배출구가 형성된 덮개를 측면이 벽면과 이격되도록 설치한 여과장치를 포함하여 구성되는 것을 특징으로 하는 오수 처리 장치.It is installed at the end of the sewage treatment process, and is formed in a tubular shape to form an inflow layer, a gravel layer, a sand layer, and an outlet layer partitioned by a partition wall having perforated holes from the bottom to the top, and an inlet at the bottom of the inflow layer. The back washing nozzle is installed to the upper side, and a plurality of through holes are drilled at the lower side of the discharge layer, and the overflow pipe is installed at the lower side of the upper side, and the cover having the outlet is formed at the side so that the side is separated from the wall surface. Sewage treatment apparatus comprising a filtration device.
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KR200197669Y1 (en) 1999-03-30 2000-09-15 일신산업주식회사 Waste water purifying system including secondary aeration chamber

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR200197669Y1 (en) 1999-03-30 2000-09-15 일신산업주식회사 Waste water purifying system including secondary aeration chamber

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