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CN105502663B - A kind of multifunctional bio denitrification reactor - Google Patents

A kind of multifunctional bio denitrification reactor Download PDF

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Publication number
CN105502663B
CN105502663B CN201610088953.7A CN201610088953A CN105502663B CN 105502663 B CN105502663 B CN 105502663B CN 201610088953 A CN201610088953 A CN 201610088953A CN 105502663 B CN105502663 B CN 105502663B
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zone
aerobic
anaerobic
reactor
waste water
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CN105502663A (en
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吴九九
熊继海
桂双林
魏源送
麦兆环
江成
夏嵩
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ENERGY RESEARCH INSTITUTE OF JIANGXI ACADEMY OF SCIENCES
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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
    • C02F3/30Aerobic and anaerobic processes
    • C02F3/301Aerobic and anaerobic treatment in the same reactor
    • 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
    • C02F3/30Aerobic and anaerobic processes
    • C02F3/302Nitrification and denitrification treatment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia

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  • 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)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

A kind of multifunctional bio denitrification reactor, the reactor include rectangle opening pond body(1), aerobic zone and anaerobic zone(13).The reactor is by dividing plate(8)Rectangle opening pond body is divided into Liang Ge areas, i.e. aerobic zone and anaerobic zone;Twoth area pass through the first effluent trough(9)And communicating pipe(12)It is interconnected;Aerobic zone is by the swash plate with a vertical certain angle(5)It is separated into aeration zone(4)And aerobic area(7);Anaerobic zone is by water-locator(14)And circulating pump(15)Form.When handling ammonia nitrogen waste water, ammonia nitrogen waste water is introduced into aerobic zone and carries out aerobic reaction reactor of the present invention, then voluntarily flows into anaerobic reaction area and carry out anaerobic reaction, and then outflow reactor, whole process are because of gesture under the promotion of ascending current, without power.Nitric efficiency beneficial to the growth of microorganism, is improved in aerobic zone and anaerobic zone zoning design by the present invention;With seldom more dissolved oxygens of aeration power consumption, reach energy-conservation purpose.

Description

A kind of multifunctional bio denitrification reactor
Technical field
The present invention relates to a kind of multifunctional bio denitrification reactor, belongs to technical field of sewage.
Background technology
With the development of society, the mankind gradually step up to environmental requirement, and it is stricter to the discharge standard of sewage, administer useless The technology of water is evolving.Ammonia nitrogen is one of main component of water pollution, is ammonia nitrogen in waste water processing using bio-denitrification technology The important method of technology, the biological denitrification process mainly used at present have:Complete nitrification and denitrification, short-cut nitrification and denitrification and portion Divide the techniques such as nitrosation Anammox, nitrifying process is more, it is necessary to aerobic environment, denitrification and anaerobism based on aerobic microbiological Ammoxidation process is more than based on anaerobe, it is desirable that anaerobic environment.At present using more technology be A/O, SBR, MBR, UASB etc., in actual use, aerobic microbiological and anaerobe all survive these technologies in same environment, Aerobic environment, or anaerobic environment, for microorganism, environment is in-and-out unstable, directly influences microorganism Growth and treatment effeciency, this is us is badly in need of the technical problem that solves on biological denitrificaion processing ammonia nitrogen waste water.
The content of the invention
The object of the present invention is to handle the problem of anxious to be resolved in ammonia nitrogen waste water according to existing biological denitrificaion, the present invention carries Go out a kind of multifunctional bio denitrification reactor and operating method.
The technical scheme is that a kind of multifunctional bio denitrification reactor of the present invention includes rectangle opening pond body, it is good Oxygen area and anaerobic zone;Rectangle opening pond body is divided into Liang Ge areas by the biological denitrification reactor by dividing plate, i.e., aerobic zone and detests Oxygen area;Twoth area are interconnected by the first effluent trough and communicating pipe;Aerobic zone is separated into aeration zone and aerobic area by swash plate;Anaerobism Area is made up of water-locator and circulating pump;By water inlet pipe and outlet pipe and external connection;Aeration zone is provided with aerator, aerator by Outside adds air and is aerated in aeration zone.
The reactor is used to handle ammonia nitrogen in high ammonia-nitrogen wastewater, and achievable short-cut nitrification-denitrification and partial nitrification- Anaerobic ammonia oxidation process.
The aerobic zone is nitrosation reaction area, by be aerated it is aerobic by ammonia oxidation bacteria by ammonium oxidation into nitrite nitrogen;Institute It is mainly anti-nitrosation reaction area or Anammox reaction zone to state anaerobic zone.Anti-nitration reaction area is mainly the environment in anaerobism Under, by anti-nitrite bacteria, nitrite nitrogen is reduced into nitrogen.Anammox reaction zone is mainly the environment in anaerobism Under, by anaerobic ammonia oxidizing bacteria, ammoniacal nitrogen and nitrite nitrogen are reacted, generate nitrogen.
The tilt angle alpha 1 of the dividing plate and horizontal plane is 20 °~50 °.
The tilt angle alpha 2 of the swash plate and vertical plane is 20 °~55 °;The distance between the top of swash plate and chamber wall L1 Between 20mm~500mm, swash plate top is consistent with water surface elevation.
10mm to 100mm gap is kept between the swash plate and the dividing plate, is easy to the backflow of waste water and sludge.
The level height of first effluent trough is necessarily more than the level height of outlet pipe.
One end of the communicating pipe connects the first effluent trough, and the other end is in anaerobic zone bottom.
The short-cut nitrification-denitrification process conditions are that aeration zone dissolved oxygen DO controls the model in 0.5mg/l~2mg/l In enclosing, aerobic area dissolved oxygen DO is controlled in the range of 0.5mg/l or so, and pH is controlled between 6.5~7.5, it is ensured that in waste water Ammonia nitrogen be mainly converted into based on nitrite nitrogen, in anaerobic zone while circulation stirring, add a certain amount of organic carbon source, will BOD:TN is controlled 2:1, the upflow velocity of anaerobic zone outlet is controlled within 0.5m/h.
The partial nitrification-anaerobic ammonia oxidation process condition is that aeration zone DO is controlled in 0.5mg/L~1.5mg/L, will Aerobic area DO Kong ≤0.3mg/L, aerobic zone pH control carry out nitrosation in 6.5~8 scopes, the ammonia for there was only part with guarantee Reaction forms nitrite nitrogen, will control NH3-N:NO2-N≧1;The upflow velocity of anaerobic zone outlet is controlled within 0.4m/h.
Multifunctional bio denitrification reactor operation principle of the present invention:High ammonia-nitrogen wastewater enters multifunctional bio by water inlet pipe 2 Denitrification reactor aerobic zone, in the effect of the aeration of aerator 3, waste water travels up to reactor head with bubble lifting, Because swash plate 5 is slant setting, the up-small and down-big space structure in aeration zone, to making gas and water constantly be extruded at top, produce Air lift effect has been given birth to, carbonated drink is broken through the water surface, the upper end of swash plate 5 has been climbed over and pours in aerobic area, due to being gushed on aeration process carbonated drink, exposing Negative pressure is formed on the bottom in gas area.In aerobic area, after the water of aeration zone climbs over swash plate 5, advection is formed, in advection again by baffle plate 6 stop forces water to be flowed down along swash plate 5, under suction function of most of water by aeration zone bottom, is flowed back around the bottom of swash plate 5 To aeration zone, aeration cycle is realized;Least a portion of water is under waterpower impetus, around baffle plate 6, then carries out slow upward advection To the first effluent trough 9, the water of the first effluent trough 9 flows into communicating pipe 12 in the presence of water-head, now by Aerobic Process for Treatment Waste water enters anaerobic zone;And the aerobic sludge of aerobic zone settles under gravity, along the oblique flow of dividing plate 8 to aeration zone, lead to Aeration is crossed to be circulated.Waste water flows into anaerobic reaction area bottom by communicating pipe 12, is mixed with highdensity anaerobic sludge, then Water-locator 14 is pumped into by circulating pump 15 and carries out mass transfer stirring, anaerobic organism is reacted more abundant, reacted waste water is slow Flow up, flow out bioreactor into the second effluent trough 10, then by outlet pipe 11;And anaerobic sludge is by Action of Gravity Field, Anaerobic reaction area is back to, so as to ensure that anaerobic sludge portion is lost in, reactor sludge quantity is on the increase, and disposal ability constantly increases By force.
The invention has the advantages that a kind of multifunctional bio denitrification reactor of the present invention is when handling ammonia nitrogen waste water, it is good Oxygen area and the multidomain treat-ment of anaerobic zone so that aerobic bacteria and anaerobic bacteria have its adaptable living environment.Ammonia nitrogen waste water is introduced into Aerobic zone carries out aerobic reaction, then voluntarily flows into anaerobic reaction area and carry out anaerobic reaction, is then flowed down in the promotion of ascending current Go out reactor, whole process is because of gesture, without power.Waste water stirs in aeration zone with sludge mixing mass transfer, is only made by aeration With and fruit.The up-small and down-big structure space in aeration zone does not only have good circulation stirring function, and because air water top by Extruding, it is easier to the transfer of oxygen so that more dissolved oxygen DO are obtained with seldom aeration power consumption, reach the saving energy, Reduce the purpose of operating cost.
Brief description of the drawings
Fig. 1 is multifunctional bio denitrification reactor structural representation of the present invention;
In figure, 1 is reactor pond body;2 be water inlet pipe;3 be aerator;4 be aeration zone;5 be swash plate;6 be baffle plate;7 are Aerobic area;8 be dividing plate;9 be the first effluent trough;10 be the second effluent trough;11 be outlet pipe;12 be communicating pipe;13 be anaerobic zone; 14 be water-locator;15 be circulating pump.
Embodiment
The embodiment of the present invention is as shown in Figure 1.
A kind of multifunctional bio denitrification reactor of the present embodiment includes rectangle opening pond body 1, aerobic zone and anaerobic zone 13;Institute State biological denitrification reactor and rectangle opening pond body 1 is divided into Liang Ge areas, i.e. aerobic zone and anaerobic zone 13 by dividing plate 8;Twoth area lead to Cross the first effluent trough 9 and communicating pipe 12 is interconnected;Aerobic zone is separated into aeration zone 4 and aerobic area 7 by swash plate 5;Anaerobic zone 13 It is made up of water-locator 14 and circulating pump 15;By water inlet pipe 2 and outlet pipe 11 and communicating pipe 12 and external connection;Aeration zone 4 is set Aerator 3, aerator 3 add air by outside and are aerated in aeration zone.
The operating method of the present embodiment reactor is as follows:
(1) short-cut nitrification-denitrification technique
With short-cut nitrification-denitrification denitrification process, it is anti-that high ammonia-nitrogen wastewater enters biological denitrificaion in a manner of continuum micromeehanics After answering device, nitrosation reaction is first carried out, this process needs flow control, the control of dissolved oxygen and the pH control intake System, by inflow control in certain scope, ensure that the nitrosation time is not excessive, dissolved oxygen DO controls in aeration zone are existed In the range of 0.5mg/l~2mg/l, aerobic area dissolved oxygen DO is controlled in the range of 0.5mg/l or so, pH controls 6.5~ Between 7.5, it is ensured that the ammonia nitrogen in waste water is mainly converted into based on nitrite nitrogen;
Waste water enters anaerobic reaction area after completing nitrosation in aerobic zone, carries out reducing instead in the presence of denitrifying bacteria Should, nitrite nitrogen is reduced into nitrogen;During this, because the growth of anti-nitrite bacteria needs carbon as its nutriment, In anaerobic zone while circulation stirring, a certain amount of organic carbon source is added, by BOD:TN is controlled 2:1;High ammonia-nitrogen wastewater passes through Short-cut nitrification-denitrification denitrification process, its ammonia nitrogen removal frank is more than 85%.
The upflow velocity that flow of inlet water is exported with anaerobic zone determines, Kong ≤0.5m/h;
(2) partial nitrification-anaerobic ammonia oxidation process
High ammonia-nitrogen wastewater, into multifunctional bio denitrification reactor, is introduced into aerobic zone progress in a manner of continuum micromeehanics Partial nitrification reacts.Because the ammonia in waste water can only partly carry out nitrosation reaction, and nitration reaction can not be carried out, therefore The dissolved oxygen DO of aerobic zone concentration must be controlled first, by aeration zone DO controls in 0.5mg/L~1.5mg/L, by aerobic area DO Kong ≤0.3mg/L, by controlling aeration quantity, shorten the reaction time, to reduce cycle-index of the waste water in aeration zone, together When aerobic zone pH controls in 6.5~8 scopes, form nitrite nitrogen to ensure to only have the ammonia of part to carry out nitrosation reaction, will control NH3-N processed:NO2-N≧1;
Due to slow-growing, multiplication cycle length, Anammox biological flora is easy to the anaerobic ammonia oxidizing bacteria of anaerobic zone Dry by other bacteriums scratches destruction, and therefore, the partial nitrification waste water into anaerobic zone contains other bacterium, it is necessary to reduce as far as possible The suspension of group flows into anaerobic zone, and the aerobic area of the aerobic zone of multifunctional bio denitrification reactor employs flat flow precipitinogen Reason design, possess the function of retention suspension, when the waste water of partial nitrification is flowing to the first effluent trough simultaneously, also entering to act charitably The precipitation Interception process of the suspensions such as oxygen animalcule;In aerobic zone, by hydraulic load control within 0.4m3/m2h, enter The waste water of anaerobic zone carries out water distribution circulation stirring in the presence of circulating pump and water-locator, so that mass transfer effect is more preferably, it is ensured that detest Anaerobic ammonium oxidation bacterium preferably carries out nitrification denitrification reaction;High ammonia-nitrogen wastewater passes through partial nitrification-anaerobic ammonia oxidation process, its ammonia Nitrogen removal efficiency is more than 80%.
The upflow velocity that flow of inlet water is exported with anaerobic zone determines, within upflow velocity Kong ≤0.4m/h.

Claims (2)

  1. A kind of 1. multifunctional bio denitrification reactor, it is characterised in that the reactor includes rectangle opening pond body, aerobic zone and Anaerobic zone;Rectangle opening pond body is divided into Liang Ge areas by the reactor by the dividing plate with the horizontal certain angle, i.e., aerobic Area and anaerobic zone;Twoth area are interconnected by the first effluent trough and communicating pipe;Aerobic zone is by with a vertical certain angle Swash plate is separated into aeration zone and aerobic area;Anaerobic zone is made up of water-locator and circulating pump;Water inlet pipe and outlet pipe and communicating pipe with External connection;Aeration zone is provided with aerator, and aerator adds air by outside and is aerated in aeration zone;The reactor is used In handling ammonia nitrogen in high ammonia-nitrogen wastewater, short-cut nitrification-denitrification and partial nitrification-anaerobic ammonia oxidation process can be achieved;
    The angle of inclination (α 1) of the dividing plate (8) and horizontal plane is 20 °~50 °;
    The angle of inclination (α 2) of the swash plate (5) and vertical plane is 20 °~55 °;The distance between the top of swash plate and chamber wall For L1 between 20mm~500mm, swash plate top is consistent with water surface elevation;
    10mm to 100mm gap is kept between the swash plate and the dividing plate, is easy to the backflow of waste water and sludge;
    The level height of first effluent trough is more than the level height of outlet pipe;
    One end of the communicating pipe connects the first effluent trough, and the other end is in anaerobic zone bottom.
  2. A kind of 2. multifunctional bio denitrification reactor according to claim 1, it is characterised in that the operation side of the reactor Method includes:
    (1) short-cut nitrification-denitrification technique
    With short-cut nitrification-denitrification denitrification process, high ammonia-nitrogen wastewater enters biological denitrification reactor in a manner of continuum micromeehanics Afterwards, nitrosation reaction is first carried out, this process needs flow control, the control of dissolved oxygen and the pH control intake, will Inflow is controlled in certain scope, ensures that the nitrosation time is not excessive, by aeration zone dissolved oxygen DO controls 0.5mg/l~ In the range of 2mg/l, aerobic area dissolved oxygen DO is controlled in the range of 0.5mg/l or so, and pH is controlled between 6.5~7.5, really The ammonia nitrogen protected in waste water is mainly converted into based on nitrite nitrogen;
    Waste water enters anaerobic reaction area after completing nitrosation in aerobic zone, and reduction reaction is carried out in the presence of denitrifying bacteria, Nitrite nitrogen is reduced into nitrogen;During this, because the growth of anti-nitrite bacteria needs carbon detesting as its nutriment While oxygen area circulation stirring, a certain amount of organic carbon source is added, by BOD:TN is controlled 2:1;
    The upflow velocity that flow of inlet water is exported with anaerobic zone determines, Kong ≤0.5m/h;
    (2) partial nitrification-anaerobic ammonia oxidation process
    High ammonia-nitrogen wastewater, into multifunctional bio denitrification reactor, is introduced into aerobic zone and carries out part in a manner of continuum micromeehanics Nitrosation reaction;Because the ammonia in waste water can only partly carry out nitrosation reaction, and nitration reaction can not be carried out, therefore first The dissolved oxygen DO of aerobic zone concentration must be controlled, aeration zone DO is controlled in 0.5mg/L~1.5mg/L, aerobic area DO is controlled ≤0.3mg/L processed, by controlling aeration quantity, shorten the reaction time, to reduce cycle-index of the waste water in aeration zone, and meanwhile it is good PH controls in oxygen area form nitrite nitrogen, control NH3- in 6.5~8 scopes, the ammonia progress nitrosation reaction for there was only part with guarantee N:NO2-N≧1;
    Due to slow-growing, multiplication cycle length, Anammox biological flora is highly susceptible to the anaerobic ammonia oxidizing bacteria of anaerobic zone The dry of other bacteriums scratches destruction, and therefore, the partial nitrification waste water into anaerobic zone contains other floras, it is necessary to reduce as far as possible Suspension flows into anaerobic zone, and the aerobic area of the aerobic zone of multifunctional bio denitrification reactor employs flat flow precipitation principle and set Meter, possess the function of retention suspension, when the waste water of partial nitrification is flowing to the first effluent trough simultaneously, also carry out it is aerobic micro- The precipitation Interception process of bioseston;In aerobic zone, hydraulic load is controlled in 0.4m3/m2Within h, into anaerobic zone Waste water carries out water distribution circulation stirring in the presence of circulating pump and water-locator, so that mass transfer effect is more preferably, it is ensured that Anammox Bacterium preferably carries out nitrification denitrification reaction;
    The upflow velocity that flow of inlet water is exported with anaerobic zone determines, within upflow velocity Kong ≤0.4m/h.
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108793398A (en) * 2018-06-08 2018-11-13 北京工业大学 The method and apparatus for coupling Anammox advanced nitrogen as the short-cut denitrification of carbon source using sludge fermentation mixture

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CN108298690B (en) * 2018-05-04 2023-07-21 中国海洋大学 Integral partial nitrosation-anaerobic ammoxidation sloping plate reinforced bioreactor
CN110713256A (en) * 2019-10-14 2020-01-21 上海理工大学 Biological pipe culvert reaction unit
CN113562841A (en) * 2021-06-10 2021-10-29 科盛环保科技股份有限公司 Efficient short-cut nitrification urban sewage deep denitrification device and method
CN113860494B (en) * 2021-08-24 2023-07-18 江苏海洋大学 Integrated wastewater denitrification process based on synchronous nitrification and denitrification
CN114538617B (en) * 2022-03-17 2024-01-23 湘潭大学 Full-automatic treatment device for deep denitrification of sewage/wastewater
CN115385448B (en) * 2022-06-30 2023-11-21 光大环境科技(中国)有限公司 Device and method for treating high ammonia nitrogen wastewater through integrated anaerobic ammonia oxidation

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100217358B1 (en) * 1994-07-15 1999-10-01 김윤 Process for the biological removal of nitrogen and phosphorus
CN102424475A (en) * 2011-10-27 2012-04-25 邹振生 Septic tank with duplex biochemical functions
CN102452768A (en) * 2010-10-27 2012-05-16 中国科学院城市环境研究所 Denitrifying phosphorus removal-anammox-shortcut nitrification integrated baffled reaction equipment
CN103819001A (en) * 2014-02-28 2014-05-28 天津机科环保科技有限公司 Anaerobic ammonia oxidation device used after shortcut nitrification of high-ammonia-nitrogen wastewater
CN205398225U (en) * 2016-02-18 2016-07-27 江西省科学院能源研究所 Multi -functional biological denitrification reactor

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100217358B1 (en) * 1994-07-15 1999-10-01 김윤 Process for the biological removal of nitrogen and phosphorus
CN102452768A (en) * 2010-10-27 2012-05-16 中国科学院城市环境研究所 Denitrifying phosphorus removal-anammox-shortcut nitrification integrated baffled reaction equipment
CN102424475A (en) * 2011-10-27 2012-04-25 邹振生 Septic tank with duplex biochemical functions
CN103819001A (en) * 2014-02-28 2014-05-28 天津机科环保科技有限公司 Anaerobic ammonia oxidation device used after shortcut nitrification of high-ammonia-nitrogen wastewater
CN205398225U (en) * 2016-02-18 2016-07-27 江西省科学院能源研究所 Multi -functional biological denitrification reactor

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108793398A (en) * 2018-06-08 2018-11-13 北京工业大学 The method and apparatus for coupling Anammox advanced nitrogen as the short-cut denitrification of carbon source using sludge fermentation mixture
CN108793398B (en) * 2018-06-08 2021-06-25 北京工业大学 Method and device for deep denitrification by coupling short-cut denitrification with anaerobic ammonia oxidation by taking sludge fermentation mixture as carbon source

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