CN2272439Y - Aerobic phase separation type fluidizing reactor - Google Patents

Aerobic phase separation type fluidizing reactor Download PDF

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Publication number
CN2272439Y
CN2272439Y CN95212040U CN95212040U CN2272439Y CN 2272439 Y CN2272439 Y CN 2272439Y CN 95212040 U CN95212040 U CN 95212040U CN 95212040 U CN95212040 U CN 95212040U CN 2272439 Y CN2272439 Y CN 2272439Y
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China
Prior art keywords
aerobic phase
fluidized reactor
reactor
aerobic
separator
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Expired - Fee Related
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CN95212040U
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Chinese (zh)
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李旭源
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Wang Kaijun
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Individual
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Priority to CN95212040U priority Critical patent/CN2272439Y/en
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    • 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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  • Biological Treatment Of Waste Water (AREA)

Abstract

The utility model discloses an aerobic phase separation type fluidizing reactor which is composed of a water distributing pipe, a gas distributing perforated pipe, a filtering layer, a rising deflector, a solid-liquid separator, a gas phase separator and carrier granules. The reactor has the obvious advantage of a high biologic content, easy separation of the carrier granules and impact load resistance, and therefore, the utility model is especially suitable for treating high concentrated organic wastewater.

Description

Aerobic phase seperated fluidized reactor
The utility model relates to the biological fluidized bed of field of waste water treatment, and biological fluidized bed is a kind of wastewater treatment equipment that grows up nineteen seventies, and it is made up of the reactor that tiny carrier granule is housed.Because the carrier granule apposition growth has a large amount of microorganisms, microorganism concn can reach 5~10 times of conventional activated sludge process, thereby has occupation of land less, efficient height, the advantage of reduced investment.But biological fluidized bed in actual use, because device contains a large amount of microorganisms and the carrier fluidised form is restive, thereby it is inhomogeneous oxygen supply to have occurred, and the shortcoming that carrier is easy to run off has influenced the stability of disposing waste water by biological fluidized bed.
The purpose of this utility model is at the existing shortcoming of above-mentioned organism fluidization bed apparatus, provides a kind of water distribution, gas distribution even, and oxygen-transfer efficiency height and carrier fluid stable are difficult for the aerobic phase seperated fluidized reactor that runs off.
The purpose of this utility model is to realize like this, the utility model is shown in figure (1), and it is by water distributor (1), gas distribution perforated pipe (2), filtering layer (3), rising director (4), admittedly annotate separator (5), gas phase separator (6) is formed, this device is divided into upwelling district (9), katabatic drainage district (10), gas phase separation district (11), settling section (12).The distribute water and air system arranges that by shown in the figure (2) gas distribution perforated pipe (2) is on water distributor (1) top.Waste water is introduced from bottom of device by water distributor (1).Air is introduced by gas distribution perforated pipe (2), perforated pipe (2) through evenly arranging discharges, and waste water passes filtering layer (3) and upwards flows under the drive of air, waste water contacts with carrier granule (7) thorough mixing in rising director (4), and organic pollutant obtains degraded.Top at reactor, because open area progressively amplifies, upflow velocity slows down, mixed solution refluxes (in a direction indicated by the arrow) with the slit that rising director (4) forms through slit and the solid-liquid separator (5) that gas phase separator (6) and solid-liquid separator (5) form, and air is overflowed from mixed solution in gas phase separation district (11).In settling section (12), because carrier granule is heavy fast greater than upflow velocity event carrier granule and liquid separation, supernatant liquor upwards flows into water leg (8) and discharges.Carrier granule is back to bottom of device through rising director (4) and the slit that the device outer wall forms, and comes back to upwelling district (9) under the drive of mixed solution, thereby forms reciprocation cycle.For making gas distribution, water distribution even, carrier granule forms stable circulation, and solid, liquid, gas three can in time separate mutually, and the utility model should guarantee adding man-hour: 1. filtering layer (3) is made up of grating stone, and the grating particle diameter is 58mm to 5mm.2. the long-pending ratio of the overflow section in upwelling district (9) and katabatic drainage district (10) is 2: 1 to 2.5: 1.3. the long-pending ratio scope of the overflow section of rising director (4), solid-liquid separator (5) and gas phase separator (6) is between 1: 1.5: 2.3 to 1: 1.8: 2.5.4. carrier granule (7) diameter is 0.1 millimeter to 0.5 millimeter a haydite.
The settling section hydraulic load is by " water supply and drainage design manual " second pond standard design.
The utility model in use its biomass can reach 20~40g/L, the settling velocity of carrier granule can reach 10m/h, thereby this device has biological content height, and carrier granule is easily separated, the obvious advantage of withstand shock load is specially adapted to handle high concentration organic sewage.

Claims (4)

1, a kind of aerobic phase seperated fluidized reactor, it is characterized in that water distributor (1) being set in aerobic phase seperated fluidized reactor bottom, gas distribution perforated pipe (2) and filtering layer (3), the middle part is provided with rising thrust-augmenting nozzle (4), and top is provided with solid-liquid separator (5) and gas phase separator (6).
2, by the aerobic phase seperated fluidized reactor of claim (1) regulation, it is characterized in that filtering layer is made up of equally distributed grating stone, the grating particle diameter is 58mm to 5mm.
By the aerobic phase seperated fluidized reactor of claim (1) regulation, it is characterized in that 3, the long-pending ratio scope of the overflow section in upwelling district (9) and katabatic drainage district (10) is 2: 1 to 2.5: 1.
4, by the aerobic phase seperated fluidized reactor of claim (1) regulation, the long-pending ratio scope of overflow section of it is characterized in that rising director (4) and solid-liquid separator (5) and gas phase separator (6) is between 1: 1.5: 2.3 to 1: 1.8: 2.5.
CN95212040U 1995-05-30 1995-05-30 Aerobic phase separation type fluidizing reactor Expired - Fee Related CN2272439Y (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN95212040U CN2272439Y (en) 1995-05-30 1995-05-30 Aerobic phase separation type fluidizing reactor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN95212040U CN2272439Y (en) 1995-05-30 1995-05-30 Aerobic phase separation type fluidizing reactor

Publications (1)

Publication Number Publication Date
CN2272439Y true CN2272439Y (en) 1998-01-14

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Family Applications (1)

Application Number Title Priority Date Filing Date
CN95212040U Expired - Fee Related CN2272439Y (en) 1995-05-30 1995-05-30 Aerobic phase separation type fluidizing reactor

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Country Link
CN (1) CN2272439Y (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100393396C (en) * 2003-10-06 2008-06-11 月岛机械株式会社 Filtration unit, installation method for a filtration unit and filtration apparatus
CN100548900C (en) * 2007-04-10 2009-10-14 江苏一环集团有限公司 Tubular organism fluidization reactor
CN101955257A (en) * 2009-07-20 2011-01-26 生态洁环保科技股份有限公司 Biological integrated treatment device of domestic sewage
CN103265118B (en) * 2009-07-20 2014-04-23 生态洁环保科技股份有限公司 Integrated biological treatment apparatus of domestic sewages used in residential areas
CN106865746A (en) * 2017-03-29 2017-06-20 天津西敦津洋环保科技有限公司 A kind of sewage disposal system including filler
CN110864280A (en) * 2018-08-28 2020-03-06 国家能源投资集团有限责任公司 Reactor and apparatus for burning carbonaceous solid fuel and method for burning carbonaceous solid fuel
CN114506965A (en) * 2020-11-17 2022-05-17 湖南盛世丰花生物科技有限公司 Three-phase biological fluidized bed for treating high-concentration organic wastewater

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100393396C (en) * 2003-10-06 2008-06-11 月岛机械株式会社 Filtration unit, installation method for a filtration unit and filtration apparatus
CN100548900C (en) * 2007-04-10 2009-10-14 江苏一环集团有限公司 Tubular organism fluidization reactor
CN101955257A (en) * 2009-07-20 2011-01-26 生态洁环保科技股份有限公司 Biological integrated treatment device of domestic sewage
CN101955257B (en) * 2009-07-20 2013-06-26 生态洁环保科技股份有限公司 Biological integrated treatment device of domestic sewage
CN103265118B (en) * 2009-07-20 2014-04-23 生态洁环保科技股份有限公司 Integrated biological treatment apparatus of domestic sewages used in residential areas
CN106865746A (en) * 2017-03-29 2017-06-20 天津西敦津洋环保科技有限公司 A kind of sewage disposal system including filler
CN106865746B (en) * 2017-03-29 2024-03-26 天津西敦津洋环保科技有限公司 Sewage treatment system comprising filler
CN110864280A (en) * 2018-08-28 2020-03-06 国家能源投资集团有限责任公司 Reactor and apparatus for burning carbonaceous solid fuel and method for burning carbonaceous solid fuel
CN114506965A (en) * 2020-11-17 2022-05-17 湖南盛世丰花生物科技有限公司 Three-phase biological fluidized bed for treating high-concentration organic wastewater
CN114506965B (en) * 2020-11-17 2023-12-19 湖南盛世丰花生物科技股份有限公司 Three-phase biological fluidized bed for treating high-concentration organic wastewater

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Addressee: Li Xuyuan

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Free format text: CORRECT: DESIGNER; FROM: LI XUYUAN TO: WANG KAIJUN; LI XUYUAN

CP03 Change of name, title or address

Address after: 100036 Beijing city Haidian District Dinghui East Building 17, No. 506 Li Xuyuan Wang Kaijun

Designer after: Wang Kaijun

Patentee after: Wang Kaijun

Designer after: Li Xuyuan

Address before: Beijing city Xicheng District Baiwanzhuang Street No. 22 Beijing construction engineering limited liability company.

Designer before: Li Xuyuan

Patentee before: Li Xuyuan

C19 Lapse of patent right due to non-payment of the annual fee
CF01 Termination of patent right due to non-payment of annual fee