CN202022791U - Aerobic biological reactor applied to sewage treatment - Google Patents
Aerobic biological reactor applied to sewage treatment Download PDFInfo
- Publication number
- CN202022791U CN202022791U CN2011201447762U CN201120144776U CN202022791U CN 202022791 U CN202022791 U CN 202022791U CN 2011201447762 U CN2011201447762 U CN 2011201447762U CN 201120144776 U CN201120144776 U CN 201120144776U CN 202022791 U CN202022791 U CN 202022791U
- Authority
- CN
- China
- Prior art keywords
- reactor
- inlet pipe
- main body
- reactor body
- pipe
- 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
Links
Images
Landscapes
- Biological Treatment Of Waste Water (AREA)
Abstract
The utility model discloses an aerobic biological reactor applied to sewage treatment. The aerobic biological reactor comprises a compressed air inlet pipe and a reactor main body, and is characterized in that: a biological carrier is arranged in the reactor main body; a perforation aeration pipe is arranged at the bottom of the reactor main body and is connected with the compressed air inlet pipe; a water inlet pipe is arranged on one side of the reactor main body; a cylindrical grid is arranged on the other side of the reactor main body; a water tank is connected to the cylindrical grid; and a water outlet pipe is arranged on one side of the water tank. The aerobic biological reactor applied to sewage treatment can effectively remove pollution factors, such as chemical oxygen demand, nitrogen, phosphorus and the like, industrial wastewater from chemical industry, petroleum refining industry, pharmacy, paper-making industry, food industry and the like or municipal wastewater, and has the advantages of simple structure, low manufacturing cost, low running cost and good high-concentration sewage treatment effect.
Description
Technical field
The utility model relates to a kind of reactor, particularly is applied to the aerobe reactor of sewage disposal.
Background technology
In recent decades, the sewage disposal technology that the worsening shortages an urgent demand of environmental pollution that expanding economy brought and water resources exploitation is suitable, country has all dropped into substantial contribution and has been used to develop this type of sewage disposal technology.The bioremediation of waste water is divided into the activated sludge process of suspension growth and the biomembrance process of apposition growth usually.The activated sludge process of suspension growth can be divided into step aeration system, tapered aeration, complete mixing active sludge method, sequencing batch active sludge (SBR), biological adsorption and oxidation method (AB method), extended aeration process, oxidation ditch etc. again.Chinese patent application numbers 200410009048.5 discloses a kind of alternative expression internal recycle easy-to-keep biological reactor, comprise that communicating aperture, each reaction tank between aerobe reaction tank, each reaction tank are provided with effluent weir and rising pipe, it is characterized in that: the quantity of described aerobe reaction tank is 4, be the 1-4 reaction tank from left to right successively, each reaction tank be shaped as long strip shape, 4 reaction tanks are arranged side by side; Be positioned at the intermediary reaction tank and only be provided with water inlet pipe, effluent weir and rising pipe, be positioned at the intermediary reaction tank and only be provided with water inlet pipe; Between each reaction tank, be provided with communicating aperture and reflux pump; The reaction tank of both sides alternately uses as the aeration tank, and middle two reaction tanks use as the aeration tank all the time.Above-mentioned technology exist a lot of aspects between the topic.Low as the treatment unit volumetric loading, floor space is big, running maintenance is complicated, technical process is long, energy consumption is high and excess sludge production is big or the like.
The utility model content
The purpose of this utility model be provide in order to solve above-mentioned the deficiencies in the prior art a kind of simple in structure, cheap for manufacturing cost, running cost is low, handle the effective aerobe reactor that is applied to sewage disposal of high-concentration sewage.
To achieve these goals, the aerobe reactor that is applied to sewage disposal that the utility model is designed, comprise compressed air inlet pipe and reactor body, it is characterized in that being provided with bio-carrier in the described reactor body, the reactor body bottom is provided with boring aeration pipe, and boring aeration pipe is connected with compressed air inlet pipe; Reactor body one side is provided with water inlet pipe, and opposite side is provided with the tubular graticule mesh; Be connected with water tank on the tubular graticule mesh, a side of water tank is provided with rising pipe.Described boring aeration pipe can be arranged on reactor body bottom uniform distribution side by side.Described bio-carrier can be suspended in the reactor body.Described reactor body can be rectangular shape.
The aerobe reactor that is applied to sewage disposal that is applied to sewage disposal that the utility model obtains, can remove the trade effluent or the pollution factors such as the chemical oxygen demand (COD) in the municipal wastewater, nitrogen and phosphorus of industries such as chemical industry, oil refining, pharmacy, papermaking, food effectively, structure of reactor is simple, cheap for manufacturing cost, running cost is low, it is effective to handle high-concentration sewage.
Description of drawings
Fig. 1 is an embodiment one-piece construction synoptic diagram.
Among the figure: water inlet pipe 1, rising pipe 2, bio-carrier 3, compressed air inlet pipe 4, boring aeration pipe 5, tubular graticule mesh 6, reactor body 7, water tank 8.
Embodiment
Below in conjunction with drawings and Examples the utility model is further specified.
Embodiment:
As shown in Figure 1, the aerobe reactor that is applied to sewage disposal that the utility model provides, comprise compressed air inlet pipe 4 and reactor body 7, it is characterized in that being provided with bio-carrier 3 in the described reactor body 7, reactor body 7 bottoms are provided with boring aeration pipe 5, and boring aeration pipe 5 is connected with compressed air inlet pipe 4; Reactor body 7 one sides are provided with water inlet pipe 1, and opposite side is provided with tubular graticule mesh 6; Be connected with water tank 8 on the tubular graticule mesh 6, a side of water tank 8 is provided with rising pipe 2.Described boring aeration pipe 5 is uniform distribution side by side in reactor body 7 bottoms.Institute's bio-carrier 3 is suspended in the reactor body 7.Described reactor body 7 is a rectangular shape.
Sewage mixes with the reactor body 7 inner bio-carriers of placing 3 from water inlet pipe 1 water inlet of reactor body 7 one sides.Pressurized air connects by compressed air inlet pipe 4 and enters the boring aeration pipe 5 that is arranged at the bottom of the case, to the sewage inflation, gives the membranaceous biological group oxygen supply on the bio-carrier 3.The tubular graticule mesh 6 of reactor body 7 opposite sides in reaction tank, makes the water after the processing be collected to water tank 8 by tubular graticule mesh 6 on bio-carrier 3 retaining, and the rising pipe 2 by water tank one side flows out then.The utility model has following characteristics and benefit with respect to prior art: be applied to (a) that microbial film mainly anchors on the filler in the aerobe reactor of sewage disposal, sludge retention time and hydraulic detention time are irrelevant, long, the microorganism very littler than rate of rise can grow on filler, thereby strengthen the denitrogenation ability growth such as nitrifier, nitrococcus generation time.Denitrification process is divided into two stages of nitrification and denitrification, is finished by nitrifier and denitrifying bacteria respectively.The aerobe reactor that is applied to sewage disposal can be realized the spatially relatively independent growth of nitrifier and denitrifying bacteria, thereby has optimized the growth conditions of two kinds of floras.The clearance that experiment showed, this reactor total nitrogen is 80%, and hydraulic detention time can reach 4-5 hour.When (b) handling high loading sewage, the stable performance under high-load condition of this reactor process, but multi-cascade or is used with traditional activated sludge process at interval with disposing of sewage.Effect stability when handling refinery and ethylene production waste water, the chemical oxygen demand (COD) 1500mg/l of water inlet, the chemical oxygen demand (COD) of treated its water outlet is reduced to 40mg/l, and pollutants removal rate reaches 97%.(c) characteristics tubular graticule mesh 6 can effectively prevent sludge blockage.In order to prevent that filler from losing with handling current, the water outlet place of this reactor aeration tank is provided with tubular graticule mesh 6, uses boring stainless steel plate material, smooth in appearance, and corrosion-resistant, the flow area is big.The common fillers flase floor of reactor aeration tank, the situation that the agglomerate suspended sludge in the reactor aeration tank often blocks the water outlet flase floor.Boring stainless steel plate tubbiness grid smooth in appearance, adsorptivity is little, and the flow area is big, and the gap is strengthened guaranteeing to hold back under the prerequisite of filler as far as possible, is difficult for being adhered to by suspended matter, and floating stuffing is not easy to stop, and is not easy to occur the sludge blockage phenomenon.Avoid the normal operation of this problems affect entire sewage treatment system.(d) reactor body 7 is rectangle, and is simple in structure.The length-depth ratio of reactor body 7 helps filler when being 0.5 left and right sides mobile fully, perhaps solves the problem at dead angle in the pond by the pump circulation of flow deflector, and gas-water ratio is dropped to about 4: 1.The special resistance of the simple structure of reactor body 7 and waterpower is little, cuts down the consumption of energy, and has further improved the economic benefit of this reactor.(e) the utility model adopts the perforated pipe aerating regulation system, and the aperture is downward, and is simple in structure, and material is obtained easily, and processing and installation are easy, and gas distribution is even, and pore is difficult for precipitated sludge blockage.
Claims (4)
1. aerobe reactor that is applied to sewage disposal, comprise compressed air inlet pipe (4) and reactor body (7), it is characterized in that being provided with in the described reactor body (7) bio-carrier (3), reactor body (7) bottom is provided with boring aeration pipe (5), and boring aeration pipe (5) is connected with compressed air inlet pipe (4); Reactor body (7) one sides are provided with water inlet pipe (1), and opposite side is provided with tubular graticule mesh (6); Be connected with water tank (8) on the tubular graticule mesh (6), a side of water tank (8) is provided with rising pipe (2).
2. the aerobe reactor that is applied to sewage disposal according to claim 1, it is characterized in that described boring aeration pipe (5) in reactor body (7) bottom uniform distribution side by side.
3. the aerobe reactor that is applied to sewage disposal according to claim 1 and 2 is characterized in that described bio-carrier (3) is suspended in the reactor body (7).
4. the aerobe reactor that is applied to sewage disposal according to claim 1 and 2 is characterized in that described reactor body (7) is a rectangular shape.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN2011201447762U CN202022791U (en) | 2011-05-09 | 2011-05-09 | Aerobic biological reactor applied to sewage treatment |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN2011201447762U CN202022791U (en) | 2011-05-09 | 2011-05-09 | Aerobic biological reactor applied to sewage treatment |
Publications (1)
Publication Number | Publication Date |
---|---|
CN202022791U true CN202022791U (en) | 2011-11-02 |
Family
ID=44847751
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN2011201447762U Expired - Fee Related CN202022791U (en) | 2011-05-09 | 2011-05-09 | Aerobic biological reactor applied to sewage treatment |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN202022791U (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106045011A (en) * | 2016-08-15 | 2016-10-26 | 江苏裕隆环保有限公司 | Improved intercepting apparatus for suspended filler |
CN110386662A (en) * | 2019-08-16 | 2019-10-29 | 青岛思普润水处理股份有限公司 | A kind of integrated combination aerating system and installation method suitable for MBBR technique |
-
2011
- 2011-05-09 CN CN2011201447762U patent/CN202022791U/en not_active Expired - Fee Related
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106045011A (en) * | 2016-08-15 | 2016-10-26 | 江苏裕隆环保有限公司 | Improved intercepting apparatus for suspended filler |
CN110386662A (en) * | 2019-08-16 | 2019-10-29 | 青岛思普润水处理股份有限公司 | A kind of integrated combination aerating system and installation method suitable for MBBR technique |
CN110386662B (en) * | 2019-08-16 | 2023-11-24 | 青岛思普润水处理股份有限公司 | Integrated combined aeration system suitable for MBBR technology and installation method |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN102659244B (en) | Integrated internal circulation type denitrification and decarburization bio-membrane reactor and operating method thereof | |
JP7149016B2 (en) | Organic nitrogen wastewater treatment system and method | |
CN108163965B (en) | Fixed bed biological film contained micro-electrolysis deep denitrification and dephosphorization cabin | |
CN102452768A (en) | Denitrifying phosphorus removal-anammox-shortcut nitrification integrated baffled reaction equipment | |
CN202625927U (en) | Integration internal circulation type denitrification decarburization biological membrane reactor | |
CN204162577U (en) | Integration enamel assembling tank body waste disposal plant | |
CN106517516B (en) | A kind of industrial wastewater proposes mark transformation biological treatment device and treatment process | |
CN102964037A (en) | Novel sewage treatment method by combined utilization of light filter material biological aerated filter and heavy filter material biological aerated filter | |
CN102674627A (en) | Method for biochemical treatment and standard discharge of sewage of coal chemical industry | |
CN201614333U (en) | Decentralized sewage treatment device | |
CN104310710B (en) | A kind of coal chemical wastewater treating technique | |
CN103232143B (en) | Ecological combined device for treating ammonia-nitrogen sewage | |
CN103265147B (en) | Nitrogen and phosphorus removal sewage treatment device | |
CN202022791U (en) | Aerobic biological reactor applied to sewage treatment | |
CN109231673B (en) | A/O combined micro-electric field-Fe/C reinforced dephosphorization device and application thereof | |
CN102101722B (en) | Novel membrane bioreactor for treating pig farm wastewater | |
CN204529596U (en) | A kind of three-dimensional electrocatalysis coupling anaerobic processing device | |
CN208562049U (en) | A kind of three-dimensional rural sewage treatment equipment | |
CN102887613A (en) | Treatment method for high-concentration industrial wastewater | |
CN203269735U (en) | Equipment for treating rubbish leachate by utilizing two-stage bioreactors | |
CN104829045A (en) | Method for treating high-concentration chemical wastewater | |
CN212269816U (en) | Aged landfill leachate non-concentrated solution treatment system | |
CN114853271A (en) | Landfill leachate wastewater treatment system and treatment method | |
CN207792983U (en) | A kind of buried AO techniques denitrification processing device | |
CN105366808A (en) | Tricyclic type synchronous carbon removal and denitrification biological reactor |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20111102 Termination date: 20150509 |
|
EXPY | Termination of patent right or utility model |