KR20020016604A - Process for high density waste water treatment - Google Patents
Process for high density waste water treatment Download PDFInfo
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- KR20020016604A KR20020016604A KR1020010052615A KR20010052615A KR20020016604A KR 20020016604 A KR20020016604 A KR 20020016604A KR 1020010052615 A KR1020010052615 A KR 1020010052615A KR 20010052615 A KR20010052615 A KR 20010052615A KR 20020016604 A KR20020016604 A KR 20020016604A
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- tank
- water
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- sludge
- separated
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- 238000000034 method Methods 0.000 title claims abstract description 13
- 238000004065 wastewater treatment Methods 0.000 title claims abstract description 5
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 58
- 239000010802 sludge Substances 0.000 claims abstract description 36
- 238000004062 sedimentation Methods 0.000 claims abstract description 22
- 238000000926 separation method Methods 0.000 claims abstract description 20
- 230000018044 dehydration Effects 0.000 claims abstract description 16
- 238000006297 dehydration reaction Methods 0.000 claims abstract description 16
- 238000007667 floating Methods 0.000 claims abstract description 14
- 238000005188 flotation Methods 0.000 claims abstract description 14
- 239000000701 coagulant Substances 0.000 claims abstract description 13
- 239000007787 solid Substances 0.000 claims abstract description 10
- 238000005345 coagulation Methods 0.000 claims abstract description 9
- 230000015271 coagulation Effects 0.000 claims abstract description 9
- 238000005352 clarification Methods 0.000 claims description 18
- 238000005054 agglomeration Methods 0.000 claims description 8
- 230000002776 aggregation Effects 0.000 claims description 8
- 239000004744 fabric Substances 0.000 claims description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical group [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 abstract description 22
- 229910000831 Steel Inorganic materials 0.000 abstract description 12
- 239000010959 steel Substances 0.000 abstract description 12
- 229910052742 iron Inorganic materials 0.000 abstract description 11
- 238000005189 flocculation Methods 0.000 abstract description 7
- 230000016615 flocculation Effects 0.000 abstract description 7
- 238000003756 stirring Methods 0.000 abstract description 7
- 238000007664 blowing Methods 0.000 abstract description 2
- 208000005156 Dehydration Diseases 0.000 description 12
- 238000002347 injection Methods 0.000 description 5
- 239000007924 injection Substances 0.000 description 5
- 239000006260 foam Substances 0.000 description 4
- 238000001035 drying Methods 0.000 description 3
- 238000001556 precipitation Methods 0.000 description 3
- 239000002351 wastewater Substances 0.000 description 3
- 238000006243 chemical reaction Methods 0.000 description 2
- 238000007599 discharging Methods 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 238000000746 purification Methods 0.000 description 2
- 239000002253 acid Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 238000006386 neutralization reaction Methods 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/24—Treatment of water, waste water, or sewage by flotation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F7/00—Aeration of stretches of water
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2201/00—Apparatus for treatment of water, waste water or sewage
- C02F2201/002—Construction details of the apparatus
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- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Physical Water Treatments (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
본 발명은 폐수처리 방법에 관한 것으로서, 장치는 응집 ·침전 ·자연탈수탱크, 가압부상탱크, 초미세기포발생장치와 건조기를 주 장치로 하여 구성되며, 응집 ·침전 · 자연탈수탱크는 외측이 철탱크(4)이며, 내측에는 강철망통(3), 다시 강철망통 내측에 탈수용 휠터빽(2)이 삽입 ·장착되고, 이 탈수용휠터빽 내측에 응집장치(6)가 설치되어 원수 유입파이프(10)와 연결되어 구성되는 탱크·가 서로 연결되며, 이렇게 구성된 탱크 상부에 부설되는 유입파이프에는 응집제 주입구(15)가 부설되고, 파이프의 내측에 송풍파이프(Q)가 내장되어 원수가 유입되면 교반과 응집이 신속히 이루어져서 탱크내로 확산되면 부유물질은 풀록을 형성하면서 수중의 부유물질은 분리되어 침전하게되고 분리되는 처리수는 즉시 휠터빽 밖으로 유출되어 부상분리탱크(10)로 유입되어 미처리 된 미세 부유물질은 부상분리처리 된 후, 청징수는 방류되거나, 다음 처리공정으로 이송된다.탱크는 교대로 응집수의 유입이 되고, 교대로 휴지시간(沐止時間)을 가지면서 탱크 내에 침전된 슬러찌를 휴지시간에 자연탈수시킨 후, 건조기로 이송시켜 완전 건조시켜 외부로 배출시킴으로서, 별도의 탈수시설을 생략시킬 수 있는 고농도 슬러찌 페수처리장치와 방법을 제공하게 된다.The present invention relates to a wastewater treatment method, the apparatus is composed of a coagulation, sedimentation, natural dehydration tank, pressurized flotation tank, ultra-miniature bubble generator and a dryer as a main device, the coagulation, sedimentation, natural dehydration tank is iron on the outside It is a tank (4), the inner side of the steel mesh (3), the dewatering filter mill (2) is inserted and mounted again inside the steel mesh, and the flocculation device (6) is installed inside the dewatering filter mill inside the raw water inflow pipe Tank constructed in connection with (10) Are connected to each other, the inlet pipe is installed in the upper tank is configured with a coagulant inlet 15 is installed, the blowing pipe (Q) is built in the inside of the pipe when the raw water flows into the stirring and flocculation is made quickly and diffused into the tank The suspended solids form a full lock, and the suspended solids in the water are separated and settled. The treated water immediately flows out of the filter mill and flows into the floating separation tank 10, and the untreated fine suspended solids are floated and separated. The collection is discharged or transferred to the next treatment. The tanks alternately inflow of condensed water and alternately have a rest time, and the sludge settled in the tank is naturally dehydrated at rest time, transferred to a dryer, completely dried and discharged to the outside. The present invention provides a high-density sludge wastewater treatment apparatus and method that can omit the dehydration facility.
Description
본 발명은 폐수정화처리 장치와 방법에 관한 것으로서, 더 상세하게는 한 장치내에서 응집, 침전, 자연탈수를 진행하고, 처리된 청징수를 부상분리탱크로 이송시켜 미 처리된 미세 부유물질을 제거시키며, 자연탈수된 슬러찌를 건조기로 이송시켜 건조시킨 후, 배출하는 고농도 슬러찌폐수 처리방법에 관한 것이다.The present invention relates to a wastewater purification treatment apparatus and method, and more particularly, to agglomeration, sedimentation, and natural dehydration in one apparatus, and to transfer treated clarified water to a flotation tank to remove untreated fine suspended solids. The present invention relates to a method for treating sludge wastewater of high concentration which is discharged after transporting natural dehydrated sludge to a dryer.
종래의 기술로서 부유물질을 제거하는데 널리 사용되고 있는 침전법을 도 3에서 살펴보면, 원수를 중화탱크(3-1)에 유입시켜 중화처리 한 다음, 반응탱크(3-2), 응집탱크(3-3)를 거치는데, 이때 각 탱크에는 지정된 응집제가 주입되어 교반이 이루어진 후, 침전탱크(3-4)로 유입되며, 침전탱크에 유입된 유입수중의 부유물질은 플록을 형성하여 서서히 하강 ·침전함으로서 청징수는 분리되고, 분리된 청징수는 방류탱크(3-5)에 유입되어 방류되거나, 또는 다음 처리공정인 생물처리탱크(3-6)로 이송되어 처리된 후, 방류탱크(3-7)로 이송되어 방류된다. 한편 침전탱크 하부층에 침전한 슬러찌는 슬러찌 저장탱크(3-8)로 이송시켜 응집 과정을 거쳐서 탈수장치(3-10)에서 강제 탈수처리를 하게된다.Referring to FIG. 3, a precipitation method widely used to remove suspended solids as a conventional technology is neutralized by introducing raw water into a neutralization tank 3-1, followed by a reaction tank 3-2 and an agglomeration tank 3. 3) In this case, the designated flocculant is injected into each tank, followed by stirring, and then flows into the settling tank (3-4), and the suspended solids in the inflow water flowing into the settling tank form a floc and gradually descend and settle. The clarification water is separated, and the separated clarification water flows into the discharge tank 3-5 and is discharged, or is transferred to the biological treatment tank 3-6, which is the next treatment process, and then treated. 7) is discharged and discharged. On the other hand, the sludge settled in the lower layer of the sedimentation tank is transferred to the sludge storage tank (3-8) to undergo a forced dehydration treatment in the dehydration device (3-10) through the coagulation process.
그런데, 응집탱크에서(3-3)에서 침전탱크(3-4)에 유입된 응집수는 풀록을 형성하여 침전하게 되는데, 이 침전속도가 대단히 느림으로 유입수는 침전탱크 내에서 장시간 체류하게 되고, 그 체류시간만큼 침전탱크는 거대하게 된다. 또한 침전한 슬러찌를 저장탱크로 이송시킬 때, 상당량의 청징수가 슬러찌와 함께 유출되어슬러찌의 함수율을 높이면서 슬러찌 양도 증가시켜 탈수처리시설을 방대하게 하는 문제점을 가지고 있다.However, in the flocculation tank (3-3), the condensed water introduced into the settling tank (3-4) is precipitated by forming a pull-lock, and the inflow water stays in the settling tank for a long time due to the very slow settling speed. The sedimentation tank becomes huge by the residence time. In addition, when the precipitated sludge is transferred to the storage tank, a considerable amount of clarification water flows out together with the sludge, thereby increasing the amount of sludge while increasing the moisture content of the sludge, thereby making the dewatering treatment facility vast.
상술한 바와 같이, 종래의 기술인 침전법에 있어서는 부유물질을 침전시키는데 장시간의 체류시간이 필요하며, 또 그 체류시간만큼 침전탱크는 거대해지고, 슬리찌 배출시에 청징수가 슬러찌와 함께 유출되어 슬러찌 양을 증가시켜 탈수처리시설을 방대하게 하는 문제점을 가지고 있다.As described above, in the conventional sedimentation method, a long residence time is required for sedimentation of suspended solids, and the sedimentation tank is enlarged by the residence time, and the clarification water flows out with the Increasing the amount of sludge has a problem of making the dewatering treatment plant vast.
본 발명은 상기의 문제점을 해결하기 위하여, 복수로 연결되어 교대로 작동되는 응집 ·침전 ·자연탈수탱크, 부상분리탱크, 초미세기포발생장치와 건조기를 주 장치로 구성하여, 원수를 유입파이프로 통해 이송시키는 과정에서 응집제 주입 및 교반을 시키면서 탱크 내로 유입시켜 응집 ·침전이 진행되면서 분리 ·유출되는 청징수를 부상분리탱크로 유입시켜 침전과정에서 미 처리된 미세 부유물질을 부상분리 제거시키는 한편, 침전된 슬러찌는 같은 탱크 내에서 자연탈수가 진행되게 하고, 자연탈수 된 슬러찌를 건조장치로 이송시켜 건조시키는 고농도 슬러찌폐수 처리방법을 제공하는데 있다.In order to solve the above problems, the present invention comprises a cohesion, sedimentation, natural dehydration tank, floating separation tank, ultra-miniature bubble generator, and a dryer as a main device, which is connected to a plurality of alternatingly operated, raw water as an inflow pipe. In the process of transfer through the flocculant injection and stirring while flowing into the tank while the flocculation and sedimentation proceeds, the clarified water is separated into the flotation tank by flotation to remove the fine suspended solids floating in the precipitation process, The precipitated sludge allows natural dehydration to proceed in the same tank, and provides a high concentration of sludge wastewater treatment method for transporting the dried dehydrated sludge to a drying apparatus for drying.
도 1은 본 고안의 장치 배치도1 is a device layout of the present invention
도 2는 응집 ·침전 ·자연탈수장치도Figure 2 is a coagulation, sedimentation, natural dehydration device
도 3은 종래의 침전법 폐수정화장치도3 is a conventional sedimentation method wastewater purification apparatus
<도면의 중요부분에 대한 설명><Description of Important Parts of Drawing>
자연탈수침전탱크 G. 기포발생장치 Natural Dewatering Precipitation Tank G. Bubble Generator
B. 기포토출밸브 P. 응집제 주입파이프B. Gig port valve P. Coagulant injection pipe
Q. 송풍 파이프 C. 기포토출실Q. Blowing pipe C. Gifoto room
D ·E. 부상분리실 H. 다공철판D.E. Floating Separation Room H. Perforated Steel Sheet
F. 청징수실 O. 슬러지 유출로F. Clarification Room O. Sludge Outflow
S. 건조기 N. 완충실S. Dryer N. Buffer
Se. 센서 12·13. 전자 밸브Se. Sensor 12 · 13. Solenoid valve
10. 유입파이프 3. 탈수용 휠터빽10. Inflow pipe 3. Dewatering filter mill
2. 강철 망 1. 철 탱크2. steel mesh 1. iron tank
6. 급속교반장치 8. 개폐장치6. Quick stirring device 8. Switchgear
9. 이송파이프 102. 부상분리탱크9. Transfer pipe 102. Floating separation tank
본 특허는 응집 ·침전 ·자연탈수탱크(), 가압부상탱크(102), 초미세기포 발생장치(G)와 건조기(S)를 주 장치로 하여 구성된다.This patent covers coagulation, sedimentation, and natural dehydration tanks ( ), The pressurized floatation tank 102, the ultra-miniature gun generator G, and the dryer S are constituted as main apparatuses.
응집 ·침전 ·자연탈수탱크는 하부에서 내경이 조금 작아지고 관통된 4각 또는 원통형의 탱크로서, 외측은 철탱크(1)이고, 이 철탱크 내측에 철탱크와 같은형으로 내경이 조금 작게된 강철망통(2)이 삽입 ·고정됨으로서 철탱크와 강철망통 사이에 공간이 확보되며, 이 강철망통(2) 내측에 강철망통과 같은 형, 같은 크기의 탈수용 휠터빽(3)이 삽입 ·장착되고, 다시 휠터빽(3) 내부에는 급속 응집장치(6)가 내장되며, 이 응집장치에는 산기장치(D)가 부착된 압축공기 공급파이프(Q)가 내장되고 하부에는 완충실(F)이 부설되어 유입파이프(10)에 연결되고, 탱크 하부에 슬러찌를 배출시킬 때 개폐하는 개폐장치(8)가 장착되며, 이 개폐장치의 연결파이프(9a)는 연결구(J)에 의해서 연결파이프(9b)와 배출파이프(9)로 연결되어 탱크는 이루어지고, 이렇게 구성된 탱크2개가 서로 연결되며, 탱크 상부에는 외부로부터 응집제 주입구(14)와 내부에 산기파이프(15)를 내장한 유입파이프(10)가탱크로 분기하여 부설되고, 이 분기된 파이프에 전자 밸브(12) · (13)가 부설되며, 각 탱크 상부에 수위 감지센서(Se)가 부설되어 탱크내의 수위를 감지하여 탱크는 교대로 작동시키며, 개폐장치(8)하부에는 개폐장치를 개방했을 때 배출되는 슬러찌를 이송시키는 컨베어(101)가 부설되어 슬러찌 저장탱크(103)에 연결되고, 이 저장탱크하부에 건조기(S)가 설치되며, 응집 ·침전 ·자연탈수탱크에서 청징수 이송을 위한 파이프(9)가 부상분리탱크(102)의 기포토출실(C)로 연결되고, 부상분리탱크는 기포토출실(C), 부상분리실(D·E), 청징수실(F)로 내부가 구획되며, 기포토출실(C)에는 기포토출밸브(B)가 부설되어 파이프로서 초미세기포발생장치(G)와 서로 연결되고, 응집제 주입 파이프(P)가 기포토출밸브(S)에 근접 부설되어 장치는 구성된다.Agglomeration, sedimentation, and natural dehydration tanks are four-hole or cylindrical tanks with a smaller inner diameter at the lower part and penetrated. The outer side is an iron tank (1). The steel mesh tube (2) is inserted and fixed to secure a space between the iron tank and the steel mesh tube. Inside the steel mesh tube (2), the same type and dewatering filter mill (3) of the same size as the steel mesh tube is inserted and installed. In addition, a quick agglomeration device (6) is built into the filter back (3), and a compressed air supply pipe (Q) with an air diffuser (D) is built in the agglomeration device, and a buffer chamber (F) is provided in the lower part. It is installed and connected to the inlet pipe 10, the opening and closing device 8 for opening and closing when discharging the sludge in the lower tank is mounted, the connecting pipe (9a) of the opening and closing device is connected to the connecting pipe (9b) by the connector (J) ) And the discharge pipe (9) is made of a tank, the tank configured in this way The two are connected to each other, the inlet pipe 10 having the coagulant inlet 14 from the outside and the diffuser pipe 15 therein from the outside Branched and installed in the tank, the solenoid valves 12, 13 are laid in the branched pipe, and a water level sensor Se is placed at the top of each tank to sense the water level in the tank. Are alternately operated, the lower portion of the switchgear 8 is provided with a conveyor 101 for transporting the sludge discharged when the switchgear is opened and connected to the sludge storage tank 103, the dryer (below) S) is installed, the pipe (9) for clarification water transfer from the flocculation, sedimentation, and natural dehydration tank is connected to the photo port chamber (C) of the flotation separation tank 102, the flotation tank is the photo port chamber (C). ), The floating separation chamber (D · E), and the clarification water chamber (F) are partitioned inside, and the photo port ejection valve (B) is installed in the gas outlet chamber (C), and the ultra-fine foam generator (G) Connected with each other, the coagulant injection pipe (P) is placed in close proximity to the gas outlet valve (S) to configure the device.
이하 본 발명의 바람직한 실시 예를 첨부한 도면에 의거하여 설명하면 다음과 같다.BEST MODE Hereinafter, preferred embodiments of the present invention will be described with reference to the accompanying drawings.
도 1은 본 발명을 단면으로 도시한 것으로서,는 행으로 서로 연결되어 구성된 응집 ·침전 ·탈수탱크이며 도 2로서 상세히 설명되며, 102는 부상분리탱크, (G)는 초미세기포발생장치, (S)는 건조장치 이다.1 is a cross-sectional view of the present invention, Is a coagulation, sedimentation, and dehydration tank which is connected to each other in a row and is described in detail as shown in FIG. 2, 102 is a floating separation tank, (G) is an ultra-small force generating device, and (S) is a drying device.
도 2는 응집 ·침전 ·탈수장치를 상세히 도시한 것으로서, 같은 형, 같은 크기의 탱크가 행으로 세로 연결되어 구성되었으며, 교대로 원수의 유입과 휴지시간을 가지면서 침전된 슬러찌를 자연탈수 시키게된다.Figure 2 shows the coagulation, sedimentation, dehydration device in detail, the same type, the same size tank It consists of vertically connected rows, and alternately dehydrates the sludge that has settled with the inflow and rest of raw water.
(1)은 원형의 철탱크로서, 상부는 내경이 크고 하부에서 내경이 작으며 내측에 강철망통(2)을 고정시키는 고정대(5)가 필요한 개수로 부설되어 있으며, 내경이 작아진 하부 외측면에 배출 파이프(9)가 부착되고, (2)는 강철망통으로서 철탱크 내측에 삽입되어 고정대(5)에 의해서 고정되어 철탱크와의 사이에 유출수의 이송이 가능한 공간이 확보되며, (3)은 탈수용 휠터빽으로서 강철망통(2) 내측에 밀착하여 삽입 ·장착되어 철탱크(1) 상부의 둘레에 부설된 고리(4)에 고정되고, 하부에는 자유로이 개폐할 수 있는 조임 끈이 부착되어 원수를 유입시킬 때는 이 끈으로 하부를 폐쇄하고 슬러찌를 토출시킬 때는 풀어서 개방한다.(1) is a circular iron tank, the upper part is the inner diameter is large, the inner diameter at the bottom is small, the inner side is laid in the required number of fixing bars (5) for fixing the steel mesh (2), the lower outer surface with a smaller inner diameter A discharge pipe 9 is attached thereto, and (2) is inserted into the iron tank inside the steel tank and is fixed by the holder 5 to secure a space for transferring the effluent water between the iron tank and (3) Is a dewatering filter mill, which is inserted and mounted in close contact with the inner side of the steel barrel (2), and is fixed to the hook (4) attached to the circumference of the upper portion of the iron tank (1). Close the lower part with this string when inflowing raw water, and release it when discharging the sludge.
(6)은 급속 응집장치로서, 내부에 산기장치(D)가 부설된 압축공기 공급파이프(9)가 내장되고 하부에는 완충실(F)이 부착되어 상부에서 유입파이프(10)에 연결되며, (10)은 유입파이프로서, 외부로부터 응집제 주입구(14)와 내부에 주입된 응집제와 원수를 혼합하는 압축공기 산기파이프(15)가 내장되어있다.(6) is a rapid agglomeration device, a compressed air supply pipe (9) with an air diffuser (D) is built therein and a buffer chamber (F) is attached to the lower portion is connected to the inlet pipe (10) from the top, Numeral 10 denotes an inlet pipe, in which a coagulant inlet 14 from the outside, and a compressed air diffuser pipe 15 for mixing coagulant and raw water injected therein are incorporated.
(8)은 개폐장치로서 철탱크(1)의 내경이 작아진 하부 관통부에 밀착·장착되어 원수 유입 시에는 폐쇄되고 슬러찌 토출시에 개방되는데, 내부에 약간의 공간을 가지며 철탱크와 밀착되는 내측 위 부분은 다공철판(多孔鐵板 · H)으로 되어 폐쇄했을 때 탈수용 휠터빽(3)의 하중을 떠받치면서 유출수의 통로가 되며, (7)은 잠금장치로서 개폐장치(8) 개방시에 해제하여 개폐장치를 하향직각(K)으로 개방시키고, (J)는 연결구로서 연결파이프(9a) ·(9b)를 서로 연결과 해제를 자유로이 할 수 있어 되개페장치 개방시에 해제되며, (9)는 청징수 이송파이프로서 응집 · 침전 · 탈수탱크와 부상분리탱크(102)에 서로 연결되어 청징수를 부상분리탱크의 기포토출실(C)로 이송한다.(8) is a switchgear, it is attached to the lower through-hole in which the inner diameter of the iron tank (1) is small, it is closed when the raw water inflow, and is opened when the sludge is discharged, has a little space inside and close to the iron tank The inner upper part is made of perforated steel plate (H), and when closed, it is a passage for the outflow water holding the load of the dewatering filter mill (3), and (7) is the locking device to open and close the opening and closing device (8). Releases the opening and closing device at a right angle (K), and (J) is a connector, and the connection pipes 9a and 9b can be freely connected and released from each other. (9) is a clarification water conveying pipe connected to the flocculation, sedimentation and dewatering tank and the flotation separation tank 102, and transfers the clarification water to the gas separation chamber (C) of the flotation separation tank.
도 1의 (102)는 부상분리탱크로서, 기포토출실(C), 부상분리실(D·E), 청징수실(F), 스캄(scum) 회수통로(O)로 구획되고, 응집 · 침전 · 탈수탱크()와 기포토출실(C)은 이송파이프(9)를 통해 서로 연결되어 있고, 기포토출실(C)에는 기포토출밸브(B)가 부설되어 파이프로서 기포발생장치(G)와 서로 연결되어 있으며, 응집제 주입을 위한 주입파이프(P)가 기포토출밸브에 근접 부설되어 있다.1, reference numeral 102 denotes a flotation separation tank, which is divided into a gipoport exit chamber (C), a flotation separation chamber (D · E), a clarification water storage chamber (F), and a scum recovery passageway (O). Sedimentation and Dewatering Tanks ) And the gas outlet chamber (C) are connected to each other through the transfer pipe (9), and the gas outlet chamber (B) is installed in the gas outlet chamber (C) is connected to the bubble generating device (G) as a pipe. The injection pipe P for injecting coagulant is placed in close proximity to the gas outlet valve.
도 1의 (G)는 초미세기포발생장치로로서, 파이프로 부상분리탱크 기포토출실(C)에 부설된 토출밸브(B)에 연결되어 초미세기포를 생성시켜 압송한다.Figure 1 (G) is a micro-foam generating device, is connected to the discharge valve (B) attached to the floating separation tank photo outlet chamber (C) by a pipe to generate and transport the ultra-mini-foam.
도 1의 (103)은 슬러찌 저장탱크로서, 컨베어(101)로 부터 탈수된 슬러찌를 받아 저장하면서 건조기에 공급하며, (S)는 건조기로서 슬러찌 저장탱크(103)에서 탈수된 슬러찌를 공급받아 건조시켜 배출한다.1, 103 is a sludge storage tank, and receives the dehydrated sludge from the conveyor 101 and supplies it to the dryer while storing the sludge, (S) supplies the dehydrated sludge from the sludge storage tank 103 as a dryer. Take it out and dry it.
다음, 상기와 같이 구성된 실시 예의 작동에 대하여 설명한다.Next, the operation of the embodiment configured as described above will be described.
먼저탱크 작동을 위해, 원수를 유입파이프(10)로 유입시키면 응집제주입구(14)에서 응집제가 주입되고 산기파이프(15)에서 토출되는 압축공기에 의한 교반으로 응집제와 원수는 혼합 ·반응되어 급속 응집장치(6)로 이송되면 산기장치(D)에서 발산되는 공기압의 소용돌이에 의해서 급속한 교반 ·응집이 진행되어 완충실(F)을 거쳐 자연스럽게 탱크 내로 밀려나가 확산되는데, 이 때부터 부유물질은 플록을 형성하면서 청징수는 분리되고, 분리되는 청징수는 플록의 침전과는 상관없이 수압에 밀려 탈수용 휠터빽(3)밖으로 유출되어 철탱크(1)와 강철 망(2) 사이의 공간을 통해서 하부로 흘러내려 개폐장치(8)의 연결파이프(9a) ·(9b)와 배출파이프(9)를 통해서 부상분리탱크의 기포토출실(C)로 유입되면, 응집제 주입파이프(P)를 통해서 응집제가 주입되고, 초미세기포발생장치(G)에서 생성된 고압의 초미세기포가 기포토출밸브(B)로부터 토출 ·발산되어 초미세기포는 토출실에 확산되는데, 이 확산작용에 의해서 교반과 응집이 이루어저서 수중에 부유하는 미세 부유물질은 풀록으로 형성되면서 초미세기포에 흡착 ·부착하여 수면으로 강제부상하여 부상분리실(C ·D)로 자연 이송되면서 청징수는 하부로, 슬러찌는 수면으로 분리되어 회수통로(O)를 따라 배출되며, 하부로 분리된 청징수는 청징수실(F)로 이송되어 방류수질 기준에 따라 외부로 방류되거나, 또는 다음 처리공정인 생물처리탱크(104)로 이송된다.first In order to operate the tank, when the raw water is introduced into the inlet pipe 10, the coagulant is injected from the coagulant inlet 14 and the coagulant and the raw water are mixed and reacted by stirring with compressed air discharged from the acid pipe 15, thereby rapidly reacting the device. When it is transferred to (6), rapid stirring and coagulation proceeds by the vortex of air released from the air diffuser (D), and it is pushed into the tank naturally through the buffer chamber (F), and from this time, the floating material forms flocs. While the clarification water is separated, the clarification water is separated by the hydraulic pressure and flows out of the dewatering filter mill (3) regardless of floc sedimentation and moves downward through the space between the iron tank (1) and the steel mesh (2). When it flows down and flows into the gasoline exit chamber C of the floating separation tank through the connecting pipes 9a and 9b of the switchgear 8 and the discharge pipe 9, the coagulant is injected through the coagulant injection pipe P. Super ultra-century gun The high-pressure micro-foamed bubbles generated by the generator G are discharged and dissipated from the gas discharge valve B, and the ultra-mini-foams are diffused into the discharge chamber. As the suspended solids are formed into full-lock, they are adsorbed and adhered to the ultra-fine cloth and forced to float to the surface, and are naturally transported to the floating separation chamber (C · D), while the clarification water is separated into the bottom and the sludge is separated into the water surface. According to the discharge, the clarified water separated into the lower part is transferred to the clarification water room (F) and discharged to the outside according to the discharge water quality standard, or is transferred to the biological treatment tank 104 which is the next treatment process.
한편, 플록은 하강하여 휠터빽 하부에 침전하게 되며, 시간이 경과함에 따라 하부에는 침전한 슬러찌가 점점 차 오르게 되어 그 만큼 수위도 높아지는데, 미리 설정된 수위에서 수위 감지센서(Se)가 이를 감지하여탱크의 전자밸브(12)를 폐쇄시켜 원수의 유입을 정지시킴과 동시에탱크의 전자 밸브(13)를 개방시켜 B탱크에 원수를 유입시킴으로서탱크는 휴지상태로 들어간다.On the other hand, the floc descends and settles under the filter mill, and as time passes, the settled sludge gradually rises and the water level rises as well, and the water level sensor Se detects it at a predetermined level. So Closing the solenoid valve 12 of the tank stops the inflow of raw water By opening the solenoid valve 13 of the tank to inject the raw water into the tank B The tank enters a rest state.
휴지상태(休止狀態)로 들어간탱크에서는 남은 청징수는 유출되고, 침전된 슬러찌도 자연탈수가 진행되어 휠터빽(3)의 하부에 자리하게 되며, 이 슬러찌는 연결구(J)를 풀어서 연결파이프(9a) ·(9b)의 연결을 해제시킨 다음, 잠금장치(7)를 풀어 개폐장치(8)를 개방하면, 휠터빽(3) 하부의 끈이 풀리면서 슬러찌는 밑으로 배출되고, 쓸러찌를 배출시킨 후, 다시 끈으로 휠터빽을 폐쇄하고, 개폐장치를 원래대로 폐쇄하면탱크는 대기상태로 돌아가게 된다.Go into a dormant state The remaining clarified water flows out from the tank, and the precipitated sludge is spontaneously dehydrated to be located in the lower part of the filter mill (3). The sludge loosens the connector (J) to connect the connecting pipe (9a) and (9b). Release the locking device (7) and open the opening and closing device (8), the string under the filter back (3) is released and the sludge is discharged underneath. And close the switch The tank will return to standby.
그리고, 일정한 시간이 경과하여,탱크에서도탱크에서와 같이 원수의 수위가 차 오르면, 이를 수위 감지센서가 감지하여탱크의 전자밸브(13)를 폐쇄하여 원수의 유입을 정지시키고, 다시탱크의 전자밸브(12)를 개방시킴으로서, A탱크에 원수의 유입이 시작된다. 이상의 작동이 연속 반복됨으로서 반응 ·응집 ·침전 ·자연탈수는 연속적으로 같은 탱크 내에서 이루어지게 되며, 일정량의 처리수는 계속 부상분리탱크(102)의 기포토출실(C)로 유입된다.And a certain time has elapsed, In the tank As in tanks, when the water level rises, the water level sensor detects it. Close the solenoid valve 13 of the tank to stop the inflow of raw water, and again By opening the solenoid valve 12 of a tank, the inflow of raw water into tank A starts. As the above operation is repeated continuously, the reaction, flocculation, sedimentation, and natural dehydration are continuously performed in the same tank, and a predetermined amount of the treated water continues to flow into the gas separation chamber C of the flotation separation tank 102.
또 한편, 각 탱크에서 배출되는 슬러찌는 이송 컨베어(101)의 작동에 의해서 슬러찌 공급탱크(103)에 이송되고, 이 공급탱크에서 공급조절장치(S-6)에 의해서 정해진 양이 건조기(S)의 입구측(S-2)에 투입되고, 투입된 슬러찌는 컨베어(S-5)를 타고 터널을 통과하는 사이에 건조는 이루어져서 출구측(S-3)에서 배출된다.On the other hand, the sludge discharged from each tank is transferred to the sludge supply tank 103 by the operation of the conveying conveyor 101, the amount determined by the supply regulator (S-6) in this supply tank is a dryer (S) Injected to the inlet side (S-2) of the), the injected sludge is made to dry while passing through the tunnel on the conveyor (S-5) is discharged from the outlet side (S-3).
본 발명은 원수가 유입되는 과정에서 순차 응집제의 주입 ·교반 ·응집이진행되고, 이렇게 응집된 응집수는 탱크 내로 확산되면서 플록이 형성됨과 동시에 청징수는 분리되어 휠터빽 밖으로 유출되어 부상분리탱크로 유입되어 미 처리되어 수중에 부유하는 물질을 다시 부상분리처리 함으로서 처리효율을 높이며, 또 탱크 내에서 자연탈수 시킨 후 건조기로 이송시켜 건조시킴으로서, 시설의 소형화에 따른 시설비 및 처리경비를 매우 절감을 할 수 있다.The present invention is injecting, stirring, and agglomeration of the flocculant in the course of raw water inflow, and the flocculated flocculant is diffused into the tank while floc is formed and the clarification water is separated and flows out of the filter back to the flotation separation tank. By increasing the efficiency of treatment by flotation and separation of the floating material in the water, which is not processed and floating in the water, it can be drastically reduced in facility and processing cost according to the miniaturization of the facility. Can be.
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| CN109081414A (en) * | 2018-10-09 | 2018-12-25 | 河北航天环境工程有限公司 | The high-efficiency clarifier of Mixing Technology is forced based on air swirl |
| CN112551860A (en) * | 2020-12-22 | 2021-03-26 | 四川省生态环境科学研究院 | Sludge concentration treatment device and method |
| CN112850984A (en) * | 2020-12-31 | 2021-05-28 | 江西挺进环保科技有限公司 | Electric field-based wastewater comprehensive treatment method |
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| CN116693019A (en) * | 2023-06-27 | 2023-09-05 | 湖南蓝旗格气体有限公司 | A waste water processor for purifying acetylene gas |
| CN117103477A (en) * | 2023-10-24 | 2023-11-24 | 福建海丝石业有限公司 | Environment-friendly stone processing equipment and method |
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| CN117263348B (en) * | 2023-11-21 | 2024-02-06 | 河北地质大学 | Copper-containing heavy metal wastewater treatment device |
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