CN201284273Y - Integrated reverse anoxic / anaerobic / aerobic sewage water denitrification and dephosphorization apparatus - Google Patents
Integrated reverse anoxic / anaerobic / aerobic sewage water denitrification and dephosphorization apparatus Download PDFInfo
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- CN201284273Y CN201284273Y CNU2008201877237U CN200820187723U CN201284273Y CN 201284273 Y CN201284273 Y CN 201284273Y CN U2008201877237 U CNU2008201877237 U CN U2008201877237U CN 200820187723 U CN200820187723 U CN 200820187723U CN 201284273 Y CN201284273 Y CN 201284273Y
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Abstract
The utility model provides an integral reversed anoxic/anaerobic/aerobic dephosphorization and denitrification sewage treatment device which comprises a biochemical reaction tank and a setting tank, wherein, the biochemical reaction tank comprises an anoxic tank, an anaerobic tank and an aerobic tank; the anoxic tank, the anaerobic tank and the aerobic tank are orderly communicated and are separated; stirrers are arranged in the anoxic tank and the anaerobic tank; an aerator is arranged in the aerobic tank; a suction dredge is arranged in the setting tank; the biochemical reaction tank and the setting tank are connected into a whole body; the setting tank and the aerobic tank of the biochemical reaction tank are separated by a partition wall with the water distribution function; and a mud backflow ditch is arranged between the setting tank and the anoxic tank of the biochemical reaction tank. Because the biochemical reaction tank and the setting tank are built into the whole structure, the front water inlet end is basically in the same level as the liquid level, the power consumption of the mud backflow can be obviously reduced, and high-delivery lost of sewage treatment plants can be reduced, and the lifting cost of mud and sewage can be saved. Simultaneously, one-time civil engineering investment cost for treating equipment can be reduced, the whole structure is compact, and the ground occupation and the construction cost are reduced.
Description
Technical field
The utility model relates to a kind of biological carbon and phosphorous removal treatment unit that is used for municipal sewage treatment, belongs to technical field of sewage.
Background technology
For control body eutrophication trend increases the weight of, strict municipal sewage plant's nitrogen, phosphorus emission standard have all been formulated in countries in the world.Compare with the traditional biological denitrification dephosphorization technique, inversion by anaerobism, anaerobic environment, inversion A/A/0 (hypoxic/anaerobic/aerobic) technology has that the denitrogenation dephosphorizing ability is strong, flow process simple (only a cover mud refluxes), cost are low, the characteristics of economic operating cost, in recent years, this technology becomes the focus of municipal sewage treatment research and engineering application gradually.
But it is in service at the waste disposal plant of realizing inversion hypoxic/anaerobic/aerobic process, for realizing higher biological denitrification denitrification effect, need keep higher return sludge ratio, cause mud backflow well liquid level fall to increase, the lifting lift that this can increase sludge reflux pump has to a certain extent increased the energy consumption of mud return-flow system.
Summary of the invention
The utility model provides the little integral type of a kind of energy consumption to be inverted hypoxic/anaerobic/aerobic denitrogenation dephosphorizing waste disposal plant at the existing higher defective of returned sluge power consumption of being inverted hypoxic/anaerobic/aerobic urban sewage treating device existence in service.
The utility model adopts following technical solution:
Integral type is inverted hypoxic/anaerobic/aerobic sewage water denitrification dephosphorization apparatus, comprise biochemical reaction tank and settling tank, biochemical reaction tank comprises anoxic pond, anaerobic pond and the Aerobic Pond that is communicated with successively and separates, in anoxic pond and the anaerobic pond agitator is installed, be provided with aerating apparatus in the Aerobic Pond, suction dredger is installed in the settling tank, biochemical reaction tank and settling tank connect as one, separate by the water distribution partition wall between the Aerobic Pond of settling tank and biochemical reaction tank, be provided with the returned sluge channel between the anoxic pond of settling tank and biochemical reaction tank.
Lattice or branch gallery are divided gallery in anoxic pond and the anaerobic pond in the Aerobic Pond.
Agitator adopts underwater propeller.
Settling tank adopts vertical-flow form, also can adopt the flat flow form.
Aerating apparatus can adopt and hang the chain type aerator, also can adopt hard-wired aerator.
The biochemical reaction tank mixed solution enters settling tank and carries out solid-liquid separation after the water distribution of water distribution partition wall.Returned sluge is directly promoted by the suction dredger in the settling tank, in the returned sluge channel is back to the anoxic pond of reaction tank.
The utility model is one because biochemical reaction tank and settling tank are built jointly, water inlet front end and settling tank liquid level are basic identical, on the one hand, can significantly reduce the power consumption that mud refluxes, also significantly reduce simultaneously the elevation loss of entire sewage treatment plant, save the lifting expense of mud and sewage greatly, finally save the day-to-day operation cost; On the other hand, integrated design can reduce the civil engineering one-time investment cost of treatment facility greatly, and integral body is provided with and arranges compactly, saves and takes up an area of, and finally saves construction cost.
Description of drawings
Fig. 1 is the structural representation of the utility model embodiment 1.
Fig. 2 is the structural representation of the utility model embodiment 2.
Among the figure: 1, anoxic pond, 2, anaerobic pond, 3, Aerobic Pond, 4, settling tank, 5, underwater propeller, 6, the water distribution partition wall, 7, mud scraper, 8, aerator, 9, the returned sluge channel, 10, breather line, 11, go out water channel, 12, rising pipe, 13, the excess sludge discharge pipe, 14, water inlet pipe, 15, walk guidance tape.
Embodiment
Fig. 1 has provided the structure schematic top plan view of present embodiment, and the biochemical reaction tank of present embodiment is square, and the depth of water that is followed successively by the anoxic pond 1, anaerobic pond 2 and 3, three ponds of Aerobic Pond that are communicated with and separate from front to back can be at 4.5 meters-6 meters.But lattices or divide gallery in anoxic pond 1 and the anaerobic pond 2 have been equipped with the underwater propeller 5 of stirring action in anoxic pond 1 and the anaerobic pond 2.Be provided with aerator 8 in the Aerobic Pond 3, aerator adopts and hangs the chain type aerator or adopt hard-wired aerator, and aerator 8 is by breather line 10 bubbling airs.Also can divide gallery in the Aerobic Pond 3, realize the pulling flow type reaction conditions.Aerobic Pond 3 and settling tank 4 are separated by water distribution partition wall 6, are interconnected, and biochemical reaction tank and settling tank 4 are built jointly be connected as a single entity.Water distribution partition wall 6 has water dispensing apparatus, has the water distribution function.Settling tank 4 adopts the flat flow structure, is provided with out water channel 11 in it, and running type mud scraper 7 is installed.Between the anoxic pond 1 of biochemical reaction tank and settling tank 4, be provided with concrete returned sluge channel 9, by running type mud scraper 7 make mud by returned sluge channel 9 from flowing in the anoxic pond 1 of biochemical reaction tank front end.Sewage enters anoxic pond 1 by water inlet pipe 14, and water is after treatment discharged by rising pipe 12.Unnecessary mud is discharged by excess sludge discharge pipe 13.Settling tank 4 can adopt vertical-flow form, also can adopt the flat flow form.Integrated device of the present utility model can adopt the skeleton construction form, also can suit measures to local conditions to adopt rolled earth dam structure formation.
Fig. 2 has provided the structure schematic top plan view of present embodiment, and the biochemical reaction tank of present embodiment is rounded, is followed successively by the anoxic pond 1, anaerobic pond 2 and the Aerobic Pond 3 that are communicated with and separate from the inside to the outside, can establish the lattice of some connections in anoxic pond 1 and the anaerobic pond 2.For making things convenient for erecting equipment and maintenance, between anoxic pond 1 and anaerobic pond 2, set up away guidance tape 15.Aerobic Pond 3 and settling tank 4 are separated by the partition wall 6 of being with the water distribution function, and are interconnected in same annular pool, biochemical reaction tank and settling tank 4 are built jointly be connected as a single entity.Returned sluge channel 9 in the settling tank 4 can be communicated with anoxic pond 1 by pipeline.The structure in each pond and installed device are the same with embodiment 1.
Claims (7)
1. an integral type is inverted hypoxic/anaerobic/aerobic sewage water denitrification dephosphorization apparatus, comprise biochemical reaction tank and settling tank, biochemical reaction tank comprises anoxic pond, anaerobic pond and the Aerobic Pond that is communicated with successively and separates, in anoxic pond and the anaerobic pond agitator is installed, be provided with aerating apparatus in the Aerobic Pond, suction dredger is installed in the settling tank, it is characterized in that: biochemical reaction tank and settling tank connect as one, partition wall by band water distribution function between the Aerobic Pond of settling tank and biochemical reaction tank separates, and is provided with the returned sluge channel between the anoxic pond of settling tank and biochemical reaction tank.
2. integral type according to claim 1 is inverted hypoxic/anaerobic/aerobic sewage water denitrification dephosphorization apparatus, it is characterized in that: lattice or branch gallery in described anoxic pond and the anaerobic pond.
3. integral type according to claim 1 is inverted hypoxic/anaerobic/aerobic sewage water denitrification dephosphorization apparatus, it is characterized in that: divide gallery in the described Aerobic Pond.
4. integral type according to claim 1 is inverted hypoxic/anaerobic/aerobic sewage water denitrification dephosphorization apparatus, and it is characterized in that: described settling tank adopts vertical-flow form.
5. integral type according to claim 1 is inverted hypoxic/anaerobic/aerobic sewage water denitrification dephosphorization apparatus, it is characterized in that: described settling tank adopts the flat flow form.
6. integral type according to claim 1 is inverted hypoxic/anaerobic/aerobic sewage water denitrification dephosphorization apparatus, it is characterized in that: described aerating apparatus adopts and hangs the chain type aerator.
7. integral type according to claim 1 is inverted hypoxic/anaerobic/aerobic sewage water denitrification dephosphorization apparatus, and it is characterized in that: described aerating apparatus adopts hard-wired aerator.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
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CNU2008201877237U CN201284273Y (en) | 2008-08-18 | 2008-08-18 | Integrated reverse anoxic / anaerobic / aerobic sewage water denitrification and dephosphorization apparatus |
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CNU2008201877237U CN201284273Y (en) | 2008-08-18 | 2008-08-18 | Integrated reverse anoxic / anaerobic / aerobic sewage water denitrification and dephosphorization apparatus |
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CN201284273Y true CN201284273Y (en) | 2009-08-05 |
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CNU2008201877237U Expired - Fee Related CN201284273Y (en) | 2008-08-18 | 2008-08-18 | Integrated reverse anoxic / anaerobic / aerobic sewage water denitrification and dephosphorization apparatus |
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103693818A (en) * | 2013-12-31 | 2014-04-02 | 北京京诚科林环保科技有限公司 | Coking wastewater biochemical treatment and sedimentation tank |
CN108545897A (en) * | 2018-06-27 | 2018-09-18 | 蓝深集团股份有限公司 | A kind of integrated sewage treating apparatus |
-
2008
- 2008-08-18 CN CNU2008201877237U patent/CN201284273Y/en not_active Expired - Fee Related
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103693818A (en) * | 2013-12-31 | 2014-04-02 | 北京京诚科林环保科技有限公司 | Coking wastewater biochemical treatment and sedimentation tank |
CN103693818B (en) * | 2013-12-31 | 2014-12-10 | 北京京诚科林环保科技有限公司 | Coking wastewater biochemical treatment and sedimentation tank |
CN108545897A (en) * | 2018-06-27 | 2018-09-18 | 蓝深集团股份有限公司 | A kind of integrated sewage treating apparatus |
CN108545897B (en) * | 2018-06-27 | 2023-10-24 | 蓝深集团股份有限公司 | Integrated sewage treatment device |
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Date | Code | Title | Description |
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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: 20090805 Termination date: 20100818 |