CN109502927A - A kind of integrated A 2O bioreactor - Google Patents

A kind of integrated A 2O bioreactor Download PDF

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Publication number
CN109502927A
CN109502927A CN201910008017.4A CN201910008017A CN109502927A CN 109502927 A CN109502927 A CN 109502927A CN 201910008017 A CN201910008017 A CN 201910008017A CN 109502927 A CN109502927 A CN 109502927A
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pond
anoxic
sedimentation basin
anaerobic
integrated
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张广学
潘海燕
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Europe (shanghai) Environmental Protection Technology Co Ltd
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Europe (shanghai) Environmental Protection Technology Co Ltd
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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
    • 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
    • C02F2001/007Processes including a sedimentation step

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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

The present invention provides a kind of integrated A 2O bioreactor, the direction along drainage flow successively includes anaerobic pond, anoxic selection pond, anoxic pond, aerobic tank and sedimentation basin;The anaerobic pond is provided with wastewater inlet, and the top of the sedimentation basin is provided with supernatant outlet.The setting in anoxic selection pond can reduce oxygen and anoxic pond be added in carbon source and raw water the not guilty consumption for carrying carbon source, so that reducing additional carbon adds cost, meanwhile, the purification of removing and water quality to nitrogen phosphorus has facilitation.Sewage is after anaerobic pond, anoxic selection pond and anoxic pond, realize effective denitrogenation dephosphorizing, ammonia nitrogen and organic matter in the sewage available fully degraded in aerobic tank, simultaneously, phosphorus in sewage can obtain further effectively removing in aerobic tank, and sewage passes through in sedimentation basin to be separated by solid-liquid separation, the supernatant outlet discharge that sewage supernatant after treatment is arranged from sedimentation basin top, it is more excellent to obtain preferably Nitrogen/Phosphorus Removal, effluent quality.

Description

A kind of integrated A 2O bioreactor
Technical field
The present invention relates to technical field of sewage more particularly to a kind of integrated A 2O bioreactors.
Background technique
A2O technique is also known as AAO technique, is the abbreviation (anaerobism-of English Anaerobic-Anoxic-Oxic first letter Anaerobic-aerobic method), it is a kind of common sewage treatment process, can be used for secondary sewage processing or three-level sewage treatment, Yi Jizhong Water reuse has good Nitrogen/Phosphorus Removal.
However, existing A2O technique mostly uses Reinforced Concrete Structure design form, sedimentation basin mostly with biochemistry pool separate design, is deposited Relatively large in construction investment, construction period is relatively long, and returns of investment recycling is slow, the realistic problems such as rate of return on investment is low, and Existing Reinforced Concrete Structure can also generate a large amount of building wastes in transformation process, pollute environment.Meanwhile existing A2O technique pair Carbon source consumption is larger, and for denitrogenation dephosphorizing efficiency up for improving, effluent quality is poor.
Summary of the invention
In view of this, the technical problem to be solved in the present invention is that a kind of integrated A 2O bioreactor is provided, using this Kind bioreactor sewage treatment, can obtain preferably Nitrogen/Phosphorus Removal, effluent quality is more excellent.
The present invention provides a kind of integrated A 2O bioreactor, the direction along drainage flow successively include anaerobic pond, Anoxic selects pond, anoxic pond, aerobic tank and sedimentation basin;The anaerobic pond is provided with wastewater inlet, and the top of the sedimentation basin is set It is equipped with supernatant outlet.
It preferably, further include anaerobic selection pond;
The outlet of sewer in the anaerobic selection pond is connected with the anaerobic pond.
Preferably, it is provided with aerobic mixed liquor stripping reflux device in the aerobic tank, is used for aerobic tank outlet of sewer The part of contaminated water at place is back to aerobic tank entrance.
Preferably, further include nitrification liquid stripping reflux device, the phegma import of the nitrification liquid stripping reflux device with The phegma outlet of the aerobic tank is connected, and phegma outlet and the anoxic of the nitrification liquid stripping reflux device select pond It is connected.
Preferably, separator for mud and water is provided in the sedimentation basin.
Preferably, the separator for mud and water is inclined tube or inclined plate.
Preferably, sludge reflux air-lift device is additionally provided in the sedimentation basin, the sludge reflux air-lift device is used for Partial sludge in sedimentation basin is delivered in anaerobic selection pond.
Preferably, be provided with returned sludge slot at the top of the sedimentation basin, the import of the returned sludge slot with it is described The returned sludge outlet of sludge reflux air-lift device is connected, the reflux of the outlet and the anaerobic selection pond of the returned sludge slot Sludge import is connected.
Preferably, the pool wall and bottom of pond of the anaerobic pond, anoxic selection pond, anoxic pond, aerobic tank and sedimentation basin are HDPE film.
Preferably, the partition wall between the anaerobic pond, anoxic selection pond, anoxic pond, aerobic tank and sedimentation basin is non-concrete Partition.
The present invention provides a kind of integrated A 2O bioreactor, the direction along drainage flow successively include anaerobic pond, Anoxic selects pond, anoxic pond, aerobic tank and sedimentation basin;The anaerobic pond is provided with wastewater inlet, and the top of the sedimentation basin is set It is equipped with supernatant outlet.The setting in anoxic selection pond can use microbial degradation polluter and carry out aerobic metabolism to disappear The oxygen incorporated in anoxic selection pond is consumed, so that it is guaranteed that will not aerobic band by the muddy water mixed solution that anoxic selection pond enters anoxic pond Enter and influence the realization of respective metabolism environment, reduces an innocent person that included carbon source in carbon source and raw water is added to anoxic pond in oxygen and disappear Consumption, so that reducing additional carbon adds cost, meanwhile, the purification of removing and water quality to nitrogen phosphorus has facilitation.Sewage passes through After anaerobic pond, anoxic selection pond and anoxic pond, effective denitrogenation dephosphorizing is realized, the ammonia nitrogen and organic matter in sewage are in aerobic tank Available fully degraded, meanwhile, the phosphorus in sewage can obtain further effectively removing in aerobic tank, and sewage is in sedimentation basin The middle supernatant outlet that by being separated by solid-liquid separation, sewage supernatant after treatment is arranged from sedimentation basin top discharge, to obtain It is more excellent to obtain preferably Nitrogen/Phosphorus Removal, effluent quality.
Detailed description of the invention
Fig. 1 is the structural schematic diagram for the integrated A 2O bioreactor that one embodiment of the present of invention provides.
Specific embodiment
Below in conjunction with the embodiment of the present invention, technical solution of the present invention is clearly and completely described, it is clear that institute The embodiment of description is only a part of the embodiment of the present invention, instead of all the embodiments.Based on the embodiments of the present invention, Every other embodiment obtained by those of ordinary skill in the art without making creative efforts, belongs to this hair The range of bright protection.
The present invention provides a kind of integrated A 2O bioreactor, the direction along drainage flow successively include anaerobic pond, Anoxic selects pond, anoxic pond, aerobic tank and sedimentation basin;The anaerobic pond is provided with wastewater inlet, and the top of the sedimentation basin is set It is equipped with supernatant outlet.
Structure is that the structure for the integrated A 2O bioreactor that one embodiment of the present of invention provides is shown referring to Fig. 1, Fig. 1 It is intended to.Wherein, 1 is anaerobic selection pond, and 2 be anaerobic pond, and 3 select pond for anoxic, and 4 be anoxic pond, and 5 be aerobic tank, and 6 be precipitating Pond, 7 be aerator, and 8 be aerobic mixed liquor stripping reflux device, and 9 be nitrification liquid stripping reflux device, and 10 be mud-water separation Device, 11 be sludge reflux air-lift device, and 12 be sludge reflux slot, and 13 be advanced treatment of wastewater unit, and 14 be sludge storage pool.
Integrated A 2O bioreactor in the present invention includes anaerobic pond 2.The anaerobic pond is provided with original water inlet and dirt Water out.Sewage (i.e. raw water) to be treated enters anaerobic pond from original water inlet.PolyP bacteria in anaerobic pond is in anaerobic environment Under release phosphorus, part itrogenous organic substance carries out ammonification, meanwhile, convert degradable COD.Aerator, sewage are not provided in anaerobic pond In pollutant concentration it is higher, because decomposing pollutant consumes dissolved oxygen, so that being practically free of dissolution in water body in anaerobic pond Oxygen is suitable for the activity of anaerobe.In the embodiment of the present invention, the anaerobic pond is additionally provided with deoxidation wastewater inlet.
In an embodiment of the present invention, the integrated A 2O bioreactor further includes anaerobic selection pond 1.The anaerobism The metabolic exhaustion that the setting in selection pond can use the progress of microorganism aerobic degradation polluter falls the involvement in anaerobic selection pond Oxygen can reduce oxygen so that it is guaranteed that the muddy water mixed solution for subsequently entering anaerobic pond does not influence the realization of subsequent anaerobic pond anaerobic environment An innocent person's consumption to carbon source, reduces additional carbon and adds cost.The anaerobic selection pond is provided with outlet of sewer and returned sludge Import.The outlet of sewer in the anaerobic selection pond is connected with the anaerobic pond.The returned sludge import is for receiving from precipitating Pond conveys the returned sludge to come.Muddy water mixed solution into anaerobic selection pond needs to consume oxygen using microbe survival metabolism Characteristic realizes combined oxygen and the fully effective removing herein of free state oxygen, and the muddy water mixed solution after deoxidation is from the anaerobism The outlet of sewer discharge in pond is selected, the deoxidation wastewater inlet through anaerobic pond enters anaerobic pond.
In certain embodiments of the present invention, the design residence time in the anaerobic selection pond is no more than 1h.In the present invention Integrated A 2O bioreactor further include anoxic selection pond 3.Anoxic selection pond is provided with wastewater inlet and sewage goes out Mouthful.The wastewater inlet in anoxic selection pond is connected with the outlet of sewer of the anaerobic pond.It is flowed out from the outlet of sewer of anaerobic pond Sewage enter anoxic selection pond.
In certain embodiments of the present invention, anoxic selection pond is additionally provided with phegma import, for receiving from good Oxygen pond conveys the reflux nitrification liquid to come.The setting in anoxic selection pond can use microorganism aerobic degradation polluter into Capable metabolism and consuming incorporates oxygen (such as nitrification liquid stripping reflux incorporate oxygen) in anoxic selection pond, so that it is guaranteed that anoxic is selected Selecting pond and entering the muddy water mixed solution of anoxic pond does not influence the realization of subsequent anoxic pond anaerobic environment, reduces oxygen and disappears to an innocent person of carbon source Consumption reduces additional carbon and adds cost, realizes effective removing of combined oxygen and free state oxygen.Nitrification liquid stripping reflux because compared with Low energy consumption can realize the large scale reflux higher than tradition machinery pump, can promote the promotion of traditional A2O nitric efficiency.
In certain embodiments of the present invention, the design residence time in anoxic selection pond is no more than 1h.
Integrated A 2O bioreactor in the present invention further includes anoxic pond 4.The anoxic pond be provided with wastewater inlet and Outlet of sewer.The wastewater inlet of the anoxic pond is connected with the outlet of sewer in anoxic selection pond.Pond is selected from the anoxic Outlet of sewer discharge sewage the anoxic pond carry out denitrification denitrogenation, realize effective removing of nitrogen.Anoxic pond is in nothing It is suitable for the growth and breeding of denitrifying bacterium, to improve the removal efficiency of nitrogen in the case where oxygen or hypoxemia and sufficient carbon source.
In certain embodiments of the present invention, the anoxic pond is additionally provided with original water inlet.Sewage to be treated is (i.e. former Water) for a part into anaerobic pond, another part enters anoxic pond.Sewage (i.e. raw water) to be treated carries out in the anoxic pond Denitrification denitrogenation realizes effective removing of nitrogen.
Integrated A 2O bioreactor in the present invention further includes aerobic tank 5.The aerobic tank be provided with wastewater inlet and Outlet of sewer.The wastewater inlet of the aerobic tank is connected with the outlet of sewer of the anoxic pond.Go out from the sewage of the anoxic pond The sewage of mouth discharge enters aerobic tank.In an embodiment of the present invention, it is provided with aerator 7 in the aerobic tank, for giving Aerobic tank is efficiently oxygenated.More suitable environment is provided for the growth and breeding of aerobic microbiological, to be effectively treated in sewage Polluter.The present invention has no special limitation to the installation site of the aerator, using known to those skilled in the art Installation site.In certain embodiments of the present invention, the aerator is aerobic air blower.
In an embodiment of the present invention, aerobic mixed liquor stripping reflux device 8 is provided in the aerobic tank, for that will get well The part of contaminated water of oxygen Chi Wushuichukouchu is back to aerobic tank entrance, to dilute the dirt of high concentration at aerobic tank wastewater inlet Water.In the embodiment of the present invention, the aerobic mixed liquor stripping reflux device is mixed using the muddy water that air is realized as power source The air-lift device that liquid is promoted is closed, the present invention has no special limitation to this, can be commercially available gas device, such as PTB-65- D25 type air-lift device (Ou Ji (Shanghai) Environmental Protection Technology Co., Ltd).The present invention is to the aerobic mixed liquor stripping reflux device Installation site have no special limitation, can be by first part's sewage backflow at aerobic tank outlet of sewer to aerobic tank import Place.The effect of the aerobic mixed liquor stripping reflux device is thoroughly mixed and waterpower plug-flow provides side for aerobic tank realization It helps, to realize that the aerobic tank of traditional A2O is changed into the fluidised form being thoroughly mixed with plug-flow phase perfect combination by pulling flow type, reaches true Complete low upshift operation in positive meaning, the effective superiority environment for ensureing that the low matrix growth metabolism of nitrifier is required, improves System impact resistance promotes nitration reaction thoroughly to carry out, and improves denitrogenation removal efficiency.In certain embodiments of the present invention, The stripping reflux of aerobic mixed liquor is than under normal conditions not less than 20 times of water inlet in the aerobic tank.Ammonia nitrogen in sewage and have Machine object available fully degraded in aerobic tank, meanwhile, the phosphorus in sewage can obtain further effectively de- in aerobic tank It removes.
In certain embodiments of the present invention, the aerobic tank is additionally provided with phegma outlet.
In an embodiment of the present invention, the integrated A 2O bioreactor further includes nitrification liquid stripping reflux device 9. The nitrification liquid stripping reflux device 9 is used to for the second part sewage (i.e. reflux nitrification liquid) in 5 exit of aerobic tank being back to Anoxic selects pond 3.The nitrification liquid stripping reflux device is provided with phegma import and phegma outlet.The nitrification liquid air lift The phegma import of reflux unit is connected with the outlet of the phegma of the aerobic tank, the reflux of the nitrification liquid stripping reflux device Liquid outlet is connected with anoxic selection pond.In certain embodiments of the present invention, time of the nitrification liquid stripping reflux device Flow liquid outlet is connected with the phegma import in anoxic selection pond.Peace of the present invention to the nitrification liquid stripping reflux device 9 Holding position has no special limitation, can be back to the second part sewage (i.e. reflux nitrification liquid) in 5 exit of aerobic tank scarce Oxygen selects pond 3.In certain embodiments of the present invention, the nitrification liquid stripping reflux device is real by power source of air Existing air promotes the air-lift device of nitrification liquid, and the present invention has no special limitation to this, can be commercially available gas device, such as PTB-65-X25 type air-lift device (Ou Ji (Shanghai) Environmental Protection Technology Co., Ltd).In an embodiment of the present invention, the nitrification Liquid stripping reflux than being between 150~500% under normal conditions.
Integrated A 2O bioreactor in the present invention further includes sedimentation basin 6.It is discharged from the outlet of sewer of the aerobic tank Sewage enter sedimentation basin.In an embodiment of the present invention, it is provided with separator for mud and water 10 in the sedimentation basin, for that will enter Sewage in sedimentation basin is separated by solid-liquid separation.In an embodiment of the present invention, the top of the sedimentation basin is provided with supernatant and goes out Mouthful.In certain embodiments of the present invention, the separator for mud and water is inclined tube or inclined plate.The present invention is to the inclined tube and inclined plate Material has no special limitation, can be Propylene polymerization material, glass steel or stainless steel.In certain embodiments of the present invention, The separator for mud and water is provided with wastewater inlet, outlet of sewer and sludge outlet.The wastewater inlet of the separator for mud and water and institute The outlet of sewer for stating aerobic tank is connected.The sludge being discharged from the sludge outlet of the separator for mud and water can be temporarily stored into sedimentation basin bottom Portion.The sewage being discharged from the outlet of sewer of separator for mud and water is discharged via the outlet of sewer of sedimentation basin, and water quality is more excellent.The present invention couple The installation site of the separator for mud and water has no special limitation, can be realized into the sewage of sedimentation basin separation of solid and liquid i.e. It can.
In an embodiment of the present invention, sludge reflux air-lift device 11 is additionally provided in the sedimentation basin, the sludge returns Stream air-lift device 11 is for the partial sludge in sedimentation basin 6 to be delivered in anaerobic selection pond.In an embodiment of the present invention, institute It states sedimentation basin and is provided with returned sludge outlet.In certain embodiments, the sludge reflux air-lift device is provided with returned sludge Import and returned sludge outlet.The returned sludge import of the sludge reflux air-lift device and the returned sludge of the sedimentation basin go out Mouth is connected, and the returned sludge outlet of the sludge reflux air-lift device is connected with the returned sludge import in the anaerobic selection pond. In certain embodiments of the present invention, the sludge reflux air-lift device is that sludge air may be implemented by power source of air to mention The air-lift device risen, the present invention have no special limitation to this, can be commercially available gas device, such as PTB-65-L25 type gas Mention device (Ou Ji (Shanghai) Environmental Protection Technology Co., Ltd).In an embodiment of the present invention, sludge air lift reflux ratio usual situation It is 150~350%.
In certain embodiments of the present invention, returned sludge slot 12 is provided at the top of the sedimentation basin, the reflux is dirty The returned sludge outlet of the import of mud groove and the sludge reflux air-lift device is connected, the outlet of the returned sludge slot with it is described The returned sludge import in anaerobic selection pond is connected.
In an embodiment of the present invention, the sedimentation basin is additionally provided with excess sludge outlet.
In an embodiment of the present invention, the integrated A 2O bioreactor further includes advanced treatment of wastewater unit 13.Institute It states advanced treatment of wastewater to be connected with the outlet of sewer of the sedimentation basin, the sewage being discharged from sedimentation basin can be in advanced treatment of wastewater Unit carries out further advanced treating.The present invention has no special limit to the structure and equipment of the advanced treatment of wastewater unit System can according to need and increase corresponding advanced treatment of wastewater equipment.
In certain embodiments of the present invention, the integrated A 2O bioreactor further includes sludge storage pool 14.The dirt Mud reservoir is connected with the outlet of the excess sludge of the sedimentation basin, for remaining sludge in settlement on storage pond.
In an embodiment of the present invention, the anaerobic selection pond, anaerobic pond, anoxic select pond, anoxic pond, aerobic tank and sink The pool wall and bottom of pond in shallow lake pond are HDPE film.The present invention replaces the Reinforced Concrete Structure of the prior art using HDPE film, has very high Corrosion-resistant, resistance to oxidation characteristic, it is adaptable to different influent qualities.Especially its low, short construction period of investment and it was transformed Too many secondary pollution will not be caused in journey to environment.
In an embodiment of the present invention, the anaerobic selection pond, anaerobic pond, anoxic select pond, anoxic pond, aerobic tank and sink Partition wall between the pond of shallow lake is non-concrete partition.In certain embodiments, the shape of the non-concrete partition is corrugated or bee Nest shape, the non-concrete partition are lightweight PP plate, glass epoxy or stainless steel plate.The present invention is replaced existing using non-concrete partition Reinforced Concrete Structure in technology, can be effectively reduced cost of investment.
The present invention, as separator for mud and water, can effectively improve the surface loading of traditional sedimentation basin extremely using inclined tube or inclined plate 1.5~3.0m3/(m2It * h), while can be effectively 5~12g/L by the sludge concentration control in aerobic tank.
The water quality being discharged from the outlet of sewer of sedimentation basin is more excellent, and Nitrogen/Phosphorus Removal is more excellent.
Using a kind of integrated A 2O bioreactor sewage treatment provided by the invention, preferably denitrogenation can be obtained and removed Phosphorus effect, effluent quality are more excellent.
The present invention provides a kind of integrated A 2O bioreactor, the direction along drainage flow successively include anaerobic pond, Anoxic selects pond, anoxic pond, aerobic tank and sedimentation basin;The anaerobic pond is provided with wastewater inlet, and the top of the sedimentation basin is set It is equipped with supernatant outlet.The setting in anoxic selection pond can use microbial degradation polluter and carry out aerobic metabolism to disappear The oxygen incorporated in anoxic selection pond is consumed, so that it is guaranteed that will not aerobic band by the muddy water mixed solution that anoxic selection pond enters anoxic pond Enter and influence the realization of respective metabolism environment, reduces an innocent person that included carbon source in carbon source and raw water is added to anoxic pond in oxygen and disappear Consumption, so that reducing additional carbon adds cost, meanwhile, the purification of removing and water quality to nitrogen phosphorus has facilitation.Sewage passes through After anaerobic pond, anoxic selection pond and anoxic pond, effective denitrogenation dephosphorizing is realized, the ammonia nitrogen and organic matter in sewage are in aerobic tank Available fully degraded, meanwhile, the phosphorus in sewage can obtain further effectively removing in aerobic tank, and sewage is in sedimentation basin The middle supernatant outlet that by being separated by solid-liquid separation, sewage supernatant after treatment is arranged from sedimentation basin top discharge, to obtain It is more excellent to obtain preferably Nitrogen/Phosphorus Removal, effluent quality.
In order to further illustrate the present invention, anti-to a kind of integrated A 2O biology provided by the invention with reference to embodiments It answers device to be described in detail, but limiting the scope of the present invention cannot be understood as.
Embodiment 1
Integrated A 2O bioreactor shown in FIG. 1 is used for the sewage treatment in the Jiyuan village Jiu Hezhuan.Dirt before processing Water COD value is 228mg/L, ammonia-nitrogen content 69.6mg/L, total phosphorus content 3.5mg/L, total nitrogen content 72.6mg/L, solid Suspended matter is 66mg/L.
According to HJ 828-2017 " the measurement dichromate titration of water chemical oxygen demand " standard, the COD of effluent quality is detected Value;According to HJ 535-2009 " the measurement Berthelot spectrophotometry of Water quality ammonia nitrogen " standard, the ammonia nitrogen of effluent quality is detected Value;According to GB 11893-1989 " the measurement ammonium aluminate spectrophotometry of water quality total phosphorus " standard, the total phosphorus of effluent quality is detected Value;According to HJ 636-2012 " the measurement alkaline chitinase of water quality total nitrogen clears up ultraviolet spectrophotometry " standard, detection water outlet Total values of nitrogen might of water quality;According to GB 11901-1989 " the measurement gravimetric method of water quality suspended matter " standard, the total phosphorus of effluent quality is detected Value.
After processing, the COD value for the water body being discharged from the outlet of sewer of sedimentation basin is 35mg/L, and ammonia-nitrogen content is 0.383mg/L, total phosphorus content 0.084mg/L, total nitrogen content 2.66mg/L, solid suspension 7mg/L.As can be seen that The Nitrogen/Phosphorus Removal of integrated A 2O bioreactor provided by the invention is more excellent, and effluent quality is more excellent.
The foregoing description of the disclosed embodiments enables those skilled in the art to implement or use the present invention. Various modifications to these embodiments will be readily apparent to those skilled in the art, as defined herein General Principle can be realized in other embodiments without departing from the spirit or scope of the present invention.Therefore, of the invention It is not intended to be limited to the embodiments shown herein, and is to fit to and the principles and novel features disclosed herein phase one The widest scope of cause.

Claims (10)

1. a kind of integrated A 2O bioreactor, the direction along drainage flow successively includes anaerobic pond, anoxic selection pond, lacks Oxygen pond, aerobic tank and sedimentation basin;The anaerobic pond is provided with wastewater inlet, and the top of the sedimentation basin is provided with supernatant and goes out Mouthful.
2. integrated A 2O bioreactor according to claim 1, which is characterized in that further include anaerobic selection pond;
The outlet of sewer in the anaerobic selection pond is connected with the anaerobic pond.
3. integrated A 2O bioreactor according to claim 1, which is characterized in that be provided in the aerobic tank Oxygen mixed liquor stripping reflux device, for the part of contaminated water at aerobic tank outlet of sewer to be back to aerobic tank entrance.
4. integrated A 2O bioreactor according to claim 1, which is characterized in that further include nitrification liquid stripping reflux The phegma import of device, the nitrification liquid stripping reflux device is connected with the outlet of the phegma of the aerobic tank, the nitrification The phegma outlet of liquid stripping reflux device is connected with anoxic selection pond.
5. integrated A 2O bioreactor according to claim 1, which is characterized in that be provided with mud in the sedimentation basin Separator.
6. integrated A 2O bioreactor according to claim 5, which is characterized in that the separator for mud and water is inclined tube Or inclined plate.
7. integrated A 2O bioreactor according to claim 2, which is characterized in that be additionally provided in the sedimentation basin Sludge reflux air-lift device, the sludge reflux air-lift device are used to the partial sludge in sedimentation basin being delivered to anaerobic selection pond In.
8. integrated A 2O bioreactor according to claim 2, which is characterized in that set at the top of the sedimentation basin It is equipped with returned sludge slot, the import of the returned sludge slot is connected with the outlet of the returned sludge of the sludge reflux air-lift device, The outlet of the returned sludge slot is connected with the returned sludge import in the anaerobic selection pond.
9. integrated A 2O bioreactor according to claim 1, which is characterized in that the anaerobic pond, anoxic selection Pond, anoxic pond, aerobic tank and sedimentation basin pool wall and bottom of pond be HDPE film.
10. integrated A 2O bioreactor according to claim 1, which is characterized in that the anaerobic pond, anoxic selection Partition wall between pond, anoxic pond, aerobic tank and sedimentation basin is non-concrete partition.
CN201910008017.4A 2019-01-04 2019-01-04 A kind of integrated A 2O bioreactor Pending CN109502927A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110040914A (en) * 2019-05-20 2019-07-23 北京市高速公路交通工程有限公司 A kind of sewage disposal device and treatment process for domestic sewage denitrifying-dephosphorizing
CN110127941A (en) * 2019-05-20 2019-08-16 北京市高速公路交通工程有限公司 A kind of biological and chemical method coupling denitrification dephosphorization technique and processing equipment
CN110386738A (en) * 2019-08-13 2019-10-29 青岛思普润水处理股份有限公司 A kind of long runner stripping reflux MBBR integral system and operation method

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101723510A (en) * 2008-10-30 2010-06-09 机科发展科技股份有限公司 Preliminary dexidation-anaerobism-oxygen deficit-multistage aerobic/anaerobic biological N and P removing method and device
WO2012010096A1 (en) * 2010-07-20 2012-01-26 华南理工大学 Device for synchronously removing nitrogen and phosphorus in mixed municipal sewage and fecal sewage by using a2/o-biomembrane and method thereof
CN203007095U (en) * 2013-01-05 2013-06-19 山西省交通环境保护中心站 Sewage treatment system for expressway subsidiary facilities
CN105461061A (en) * 2015-12-31 2016-04-06 华南理工大学 A<2>/O-biology synchronous nitrogen and phosphorus removal device and method for urban sewage
CN206570174U (en) * 2017-03-16 2017-10-20 北京高能时代环境技术股份有限公司 A kind of wastewater treatment equipment
CN107973405A (en) * 2017-12-05 2018-05-01 欧基(上海)环保科技有限公司 A kind of high sludge concentration multiplication type A2O carries mark transformation Sewage Biological Treatment reaction unit
CN108675575A (en) * 2018-08-03 2018-10-19 北京市市政工程设计研究总院有限公司 A kind of A2O-D2Cooperate with the technique and device of denitrogenation dephosphorizing
CN208151064U (en) * 2018-02-05 2018-11-27 许泽宇 Energy-efficient compact compound A2/O dephosphorization denitrogenation processing system
CN209493447U (en) * 2019-01-04 2019-10-15 欧基(上海)环保科技有限公司 A kind of integrated A 2O bioreactor

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101723510A (en) * 2008-10-30 2010-06-09 机科发展科技股份有限公司 Preliminary dexidation-anaerobism-oxygen deficit-multistage aerobic/anaerobic biological N and P removing method and device
WO2012010096A1 (en) * 2010-07-20 2012-01-26 华南理工大学 Device for synchronously removing nitrogen and phosphorus in mixed municipal sewage and fecal sewage by using a2/o-biomembrane and method thereof
CN203007095U (en) * 2013-01-05 2013-06-19 山西省交通环境保护中心站 Sewage treatment system for expressway subsidiary facilities
CN105461061A (en) * 2015-12-31 2016-04-06 华南理工大学 A<2>/O-biology synchronous nitrogen and phosphorus removal device and method for urban sewage
CN206570174U (en) * 2017-03-16 2017-10-20 北京高能时代环境技术股份有限公司 A kind of wastewater treatment equipment
CN107973405A (en) * 2017-12-05 2018-05-01 欧基(上海)环保科技有限公司 A kind of high sludge concentration multiplication type A2O carries mark transformation Sewage Biological Treatment reaction unit
CN208151064U (en) * 2018-02-05 2018-11-27 许泽宇 Energy-efficient compact compound A2/O dephosphorization denitrogenation processing system
CN108675575A (en) * 2018-08-03 2018-10-19 北京市市政工程设计研究总院有限公司 A kind of A2O-D2Cooperate with the technique and device of denitrogenation dephosphorizing
CN209493447U (en) * 2019-01-04 2019-10-15 欧基(上海)环保科技有限公司 A kind of integrated A 2O bioreactor

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110040914A (en) * 2019-05-20 2019-07-23 北京市高速公路交通工程有限公司 A kind of sewage disposal device and treatment process for domestic sewage denitrifying-dephosphorizing
CN110127941A (en) * 2019-05-20 2019-08-16 北京市高速公路交通工程有限公司 A kind of biological and chemical method coupling denitrification dephosphorization technique and processing equipment
CN110386738A (en) * 2019-08-13 2019-10-29 青岛思普润水处理股份有限公司 A kind of long runner stripping reflux MBBR integral system and operation method

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