CN2773061Y - Biological-membrane waste water treater - Google Patents

Biological-membrane waste water treater Download PDF

Info

Publication number
CN2773061Y
CN2773061Y CNU2005200809262U CN200520080926U CN2773061Y CN 2773061 Y CN2773061 Y CN 2773061Y CN U2005200809262 U CNU2005200809262 U CN U2005200809262U CN 200520080926 U CN200520080926 U CN 200520080926U CN 2773061 Y CN2773061 Y CN 2773061Y
Authority
CN
China
Prior art keywords
biological
waste water
membrane
aerobic
bod
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
CNU2005200809262U
Other languages
Chinese (zh)
Inventor
张成禄
张洪昌
刘贤伟
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Shandong University
Original Assignee
Shandong University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Shandong University filed Critical Shandong University
Priority to CNU2005200809262U priority Critical patent/CN2773061Y/en
Application granted granted Critical
Publication of CN2773061Y publication Critical patent/CN2773061Y/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Images

Classifications

    • 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

Landscapes

  • Biological Treatment Of Waste Water (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

A new-type biological-membrane waste water treating device belongs to the technical field of environmental science and engineering. The utility model comprises an upper part, a middle part and a lower part, wherein the upper part, the middle part and the lower part respectively form the shape of a cylindrical tower, the upper part is provided with an aerobic biological-membrane reactor, the middle part is provided with an aerobic biological filtering tank, the lower part is provided with an amphoteric amaerobic zone, the upper part and the middle part are added with fillers and provided with perforated pipes or shower heads, the lower part is provided with an aging resistant plastic rope knot with toughness and the fillers are of granulating slag. The utility model has good treating capacity for waste water with high BOD, and furthermore, the height of an amaerobic segment can be adjusted according to the size of BOD of waste water so as to realize the optimum utilization of the device and to remove the BOD to the maximum extent. The device uses granulating slag as the fillers, wherein the granulating slag is waste for a steel plant; thereby, the utilization of waste is realized. Due to the adoption of the biological-membrane process, the amount of sludge of the biological-membrane process is larger than that of the activated sludge process; thereby, sludge treatment devices and the expenses of the sludge treatment devices are decreased and the treatment expenses are decreased.

Description

A kind of novel membrane-biological membrane sewage treatment equipment
(1) technical field
The utility model relates to a kind of novel amphimicrobian expanded bed, aerobic filter tank, the integrated sewage treatment equipment of aerobic biologic membrane, belongs to the Environmental Science and Engineering field.
(2) background technology
Traditional sewage treatment equipment mostly is simple aerobic or simple anaerobism greatly, aerobic process such as activated sludge process, and biological filter or bio-disc system etc., to high BOD loading waste water, treatment effect can not be satisfactory; Anaerobism method such as digester, anaerobic mud bed, various anaerobe embrane methods etc., though anaerobic process has stronger processing power to high BOD waste water, the BOD of its water outlet is still higher, independent anaerobism method is difficult to reach the requirement of qualified discharge.
(3) summary of the invention
Many shortcomings at present Processes and apparatus existence, the utility model purpose provides a kind of with amphimicrobian expanded bed, aerobic biofilter and biomembrance process coupling, and with triplicity in same equipment, realized that the anaerobic treatment, aerobic treatment of waste water and biomembrance process handle the novel membrane-biological membrane sewage treatment equipment that carries out in same reactor.
This novel membrane-biological membrane sewage treatment equipment comprises the upper, middle and lower part, the upper, middle and lower part is constituted cylinder turriform formula, wherein, top is divided into aerobic biofilm reactor, the middle part is divided into aerobic biofilter, and the bottom is the amphimicrobian district, adds filler in last, middle part, and be furnished with perforated pipe or shower nozzle, be provided with toughness and aging-resistant plastics knot in the lower section.
Described filler is a grain slag.
The utility model is entered waste water by reactor lower part, amphimicrobian expanded bed through the bottom, filler wherein adopts the grain slag of steel mill, it is a kind of industrial waste, again upwards through aerobic biofilter, in the aerobic biofilter, used filler also is a grain slag, water enters aerobic biofilm reactor behind aerobic filter tank, in conversion unit, realize organic degraded and removal, by the top water outlet, and with a part of effluent recycling, not only realize organic degraded, and realized the removal of N (nitrogen) in the water.
The whole flow process of the utility model purification of waste water is as follows: waste water enters conversion unit by the water-in of bottom, its flow velocity should reach and make filler be in swelling state, so just make the waste water filtrate of can flowing through more equably, avoided short flow phenomenon, and make filtrate be difficult for stopping up, give full play to the function of filtrate.In the amphimicrobian expanded bed, organism in the waste water is realized preliminary degraded, and macromole changes small molecules into, is attended by portion gas, as the generation of sulfurous gas etc.On the current direction, through gas distribution system, oxygenation in the water.Arrive aerobic filter bed, here, it is big that the cross section of reactor becomes, and the flow velocity of water reduces, and filler can not expand.The aerobic biologic membrane that organism adheres on filter bed further decomposes, and with the gas partial oxidations frowzy such as sulfurous gas that anaerobic stages produces, has reduced the secondary pollution of anaerobic treatment, and the N in the water (nitrogen) is nitre attitude N (nitrogen) by partial oxidation.After waste water was handled through this two step, the BOD in the water reduced greatly, can't support the large number of biological growth, therefore, establishes an aerobic biofilm reactor that biomass is less relatively on top.Waste water enters aerobic biofilm reactor, and residual organic substances is further decomposed, and with reducing gas oxidations such as remaining sulfurous gas, the secondary pollution that anaerobic stages is produced drops to minimum.Water is overflowed by top after this three step handles, and collects through water leg, and with a part of effluent recycling to water-in, then the nitre attitude N in the water outlet can be reduced to nitrogen by the nitrate reduction bacterium in amphimicrobian stage, thereby escapes into atmosphere, realizes the removal of N (nitrogen) in the water.Like this, organism in the water and N (nitrogen) have obtained effective degraded and removal, realize standard wastewater discharge.
Use the utlity model has following advantage:
1. because anaerobism combines with aerobic, and this equipment is to high BOD waste water good treatment ability again, and, can be according to the size of waste water BOD, the height of adjusting anaerobism section is realized the optimum utilization of this equipment, at utmost removes BOD.
2. the filler that this equipment adopted is a grain slag, is the waste material of steel mill, has realized utilization of waste material.
3. grain slag surface in waste water is weakly alkaline, is easier to bio-film colonization, and treatment effect is good,
4. waste water is handled through amphimicrobian earlier, after aerobic treatment again with effluent recycling, has realized the removal of N (nitrogen) in the water.
5. because the part effluent recycling, the more difficult obstruction of filtrate.
6. because this equipment with three reactor vertical displays, is constructed in unified equipment, reduced floor space, and a part can be built in undergroundly,, also can utilize in winter, and can reduce the part power consumption than being easier to insulation on the ground.
7. owing to adopt biomembrance process, its sludge quantity is wanted specific activity mud method much less, has reduced that mud is got treatment unit and expense, and processing costs reduces.
Description of drawings
Accompanying drawing is the utility model structural representation.
Wherein, 1, the amphimicrobian expanded bed, 2, aerobic biofilter, 3, aerobic biofilm reactor, 4, grain slag, 5, water-in, 6, inlet mouth, 7, overflow the mouth of a river, 8, gas distribution system, 9, the effluent recycling pipe, 10, contact filtrate.
Embodiment
Embodiment: structure as shown in drawings, comprise the upper, middle and lower part, the upper, middle and lower part is constituted cylinder turriform formula, wherein, top is divided into aerobic biofilm reactor 3, and the middle part is divided into aerobic biofilter 2, the bottom is an amphimicrobian expanded bed 1, add grain slag 4 in last, middle part, and be furnished with perforated pipe or shower nozzle, be provided with toughness and aging-resistant plastics knot in the lower section.Working process: waste water enters amphimicrobian expanded bed 1 by the water-in 5 of bottom, and wherein flow velocity is bigger, makes filler 4 be in swelling state, make the waste water filtrate of can flowing through more equably, avoid short flow phenomenon, and made filtrate be difficult for stopping up, given full play to the function of filtrate.In the amphimicrobian expanded bed, organism in the waste water is realized preliminary degraded, and macromole changes small molecules into, is attended by portion gas, as the generation of sulfurous gas etc.Between amphimicrobian expanded bed 1 and the aerobic filter bed 2 gas distribution system is arranged, inlet mouth 6 bubbling airs are arranged, through gas distribution system 8 oxygenation in water.On the current direction, arrive aerobic filter bed 2, here, it is big that the cross section of reactor becomes, and the flow velocity of water reduces, and filler 4 can not expand.The aerobic biologic membrane that organism adheres on filter bed further decomposes, and with the gas partial oxidations frowzy such as sulfurous gas that anaerobic stages produces, has reduced the secondary pollution of anaerobic treatment, and the N in the water (nitrogen) is nitre attitude N (nitrogen) by partial oxidation.After waste water was handled through this two step, the BOD in the water reduced greatly, can't support the large number of biological growth, therefore, establishes an aerobic biofilm reactor 3 that biomass is less relatively on top.Waste water enters aerobic biofilm reactor 3, and the microorganism that residual organic substances is touched on the filtrate 10 is further decomposed, and with reducing gas oxidations such as remaining sulfurous gas, the secondary pollution that anaerobic stages is produced drops to minimum.Water is after this three step handles, overflowing the mouth of a river 7 by top flows out, collect through water leg, and a part of water outlet is back to water-in through return line 9, then the nitre attitude N in the water outlet can be reduced to nitrogen by the nitrate reduction bacterium in amphimicrobian stage, thereby escape into atmosphere, realize the removal of N (nitrogen) in the water.Like this, organism in the water and N (nitrogen) have obtained effective degraded and removal, realize standard wastewater discharge.

Claims (2)

1, a kind of novel membrane-biological membrane sewage treatment equipment, comprise the upper, middle and lower part, it is characterized in that, constitute cylinder turriform formula by the upper, middle and lower part, top is divided into aerobic biofilm reactor, and the middle part is divided into aerobic biofilter, the bottom is the amphimicrobian expanded bed, add filler in last, middle part, and be furnished with perforated pipe or shower nozzle, be provided with toughness and aging-resistant plastics knot on top.
2, a kind of novel membrane-biological membrane sewage treatment equipment according to claim 1 is characterized in that described filler is a grain slag.
CNU2005200809262U 2005-03-18 2005-03-18 Biological-membrane waste water treater Expired - Fee Related CN2773061Y (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CNU2005200809262U CN2773061Y (en) 2005-03-18 2005-03-18 Biological-membrane waste water treater

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CNU2005200809262U CN2773061Y (en) 2005-03-18 2005-03-18 Biological-membrane waste water treater

Publications (1)

Publication Number Publication Date
CN2773061Y true CN2773061Y (en) 2006-04-19

Family

ID=36708318

Family Applications (1)

Application Number Title Priority Date Filing Date
CNU2005200809262U Expired - Fee Related CN2773061Y (en) 2005-03-18 2005-03-18 Biological-membrane waste water treater

Country Status (1)

Country Link
CN (1) CN2773061Y (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100473616C (en) * 2007-03-28 2009-04-01 南京大学 Overlay sewage biochemical reactor
CN101885555B (en) * 2009-05-12 2012-04-25 江西金达莱环保研发中心有限公司 Method for treating fermentative pharmaceutical wastewater
CN112939632A (en) * 2021-01-19 2021-06-11 宁夏润安微肥科技有限公司 Calcium ammonium nitrate production system

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100473616C (en) * 2007-03-28 2009-04-01 南京大学 Overlay sewage biochemical reactor
CN101885555B (en) * 2009-05-12 2012-04-25 江西金达莱环保研发中心有限公司 Method for treating fermentative pharmaceutical wastewater
CN112939632A (en) * 2021-01-19 2021-06-11 宁夏润安微肥科技有限公司 Calcium ammonium nitrate production system
CN112939632B (en) * 2021-01-19 2022-12-02 宁夏润安微肥科技有限公司 Calcium ammonium nitrate production system

Similar Documents

Publication Publication Date Title
CN100402448C (en) Paper-making effluent purifying treatment process
CN101560039B (en) Landfill leachate wastewater treatment system and process thereof
CN102432104B (en) High-efficiency low-power multi-layer horizontal flow biomembrane sewage treatment method and equipment
CN113044971A (en) Method and system for strengthening aerobic granular sludge culture
CN202643504U (en) Organic solvent desorbed waste water and oil paint waste water treatment device
CN2773061Y (en) Biological-membrane waste water treater
CN201751397U (en) Sewage treatment device of ozone and aeration biological filter pool
CN101386446B (en) Air-lift baffling internal circulation bioreactor and use method thereof
CN103641268A (en) Two-stage bioreactor device and technology for treating garbage leachate
CN210505965U (en) Nylon 6 waste water high-efficiency treatment device
CN202543002U (en) Sewage treatment system
CN111559837A (en) Landfill leachate biochemical treatment system and process
CN204625305U (en) Sewage disposal microorganism reactor
CN203582653U (en) Livestock/fowl culture wastewater treatment system
CN216808509U (en) Movable advanced sewage treatment system based on microorganism embedding construction method
CN203269735U (en) Equipment for treating rubbish leachate by utilizing two-stage bioreactors
CN205473253U (en) Pharmacy sewage treatment plant
CN114436472A (en) Movable advanced sewage treatment system based on embedded microorganism construction method
CN1278955C (en) Composite bacterial enzyme stepped sewage purification device
CN103395951B (en) System capable of utilizing acid to neutralize slags and dehydrated aluminum sludge to treat nitrogenous wastewater and method thereof
CN100340500C (en) Middle water reuse process with compound bacteria and membrane bioreactor and apparatus therefor
CN202063802U (en) Device for processing ethylene glycol sewage
CN111825208A (en) Multistage aerobic sewage treatment combined process
CN205676225U (en) A kind of anaerobism processing percolate is held concurrently oxygen up-flow reactor
CN213652210U (en) Sewage treatment device for village and town sewage treatment

Legal Events

Date Code Title Description
C14 Grant of patent or utility model
GR01 Patent grant
C17 Cessation of patent right
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20060419