CN100560516C - Energy-conservation combined building aeration sedimentation tank - Google Patents
Energy-conservation combined building aeration sedimentation tank Download PDFInfo
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- CN100560516C CN100560516C CNB2007100247983A CN200710024798A CN100560516C CN 100560516 C CN100560516 C CN 100560516C CN B2007100247983 A CNB2007100247983 A CN B2007100247983A CN 200710024798 A CN200710024798 A CN 200710024798A CN 100560516 C CN100560516 C CN 100560516C
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
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Abstract
Energy-conservation combined building aeration sedimentation tank, relate to water-treatment technology field, comprise rectangle aeration tank, rectangle settling tank and connecting tube, the rectangle settling tank places the rectangle aeration tank, be communicated with by the water distribution partition wall between rectangle settling tank and rectangle aeration tank, the rectangle aeration tank is by dividing plate zoning territory, but because of each zone and rectangle settling tank shared portion wall, make the floor space of entire equipment little, cost of investment is low, aeration efficient height, particularly water inlet inserts oxygen-starved area, anaerobic zone, aerobic zone, settling region formation water cycle successively, has improved denitrogenation dephosphorizing efficient.
Description
Technical field
The present invention relates to water-treatment technology field, refer in particular to a kind of energy-conservation combined building aeration sedimentation tank that the rectangle settling tank is placed the rectangle aeration tank.
Background technology
In the existing water treating equipment, aeration tank and settling tank are independent usually to be provided with, and both are by pipe connection, on the one hand, equipment is scrappy, and structure is not compact, and floor space is big, on the other hand, aeration tank and settling tank need separately be built the pond body by laying bricks or stones, lay the longer pipe road and connect, and cost of investment is big relatively.On treatment process, the general A that adopts routine
2/ O technology, there are following three shortcomings in it: 1. because anaerobic zone ranks forefront, the nitrate in the returned sluge has a negative impact to anaerobic zone; 2. because anoxic is positioned at the system middle part, denitrification is mixed at the carbon source branch and is occupy minus advantage, thereby has influenced the denitrification effect of system; 3. owing to there is internal recycle, actually in the excess sludge that the common process system is discharged have only a small part to experience complete to put phosphorus, inhale the phosphorus process, all the other then do not experience anaerobic state basically and directly enter aerobic zone by the oxygen-starved area, and this is disadvantageous to system's dephosphorization.
Summary of the invention
The present invention is just in order to overcome above-mentioned deficiency, a kind of aeration and Round Sump pond body that is deposited in one of collecting is provided, saved cost of investment, reduced floor space, and can improve aeration efficient, the main improvement is the rectangle settling tank is placed the rectangle aeration tank, and also available shared wall reduces investment.Specifically implement like this: energy-conservation combined building aeration sedimentation tank, comprise rectangle aeration tank, rectangle settling tank and connecting tube, the rectangle settling tank places the rectangle aeration tank, be communicated with by the water distribution partition wall between rectangle settling tank and rectangle aeration tank, it is characterized in that being provided with dividing plate between rectangle aeration pool wall and rectangle precipitation pool wall, described dividing plate is separated into several zones to the rectangle aeration tank.
Settling tank can be preliminary sedimentation tank or second pond or final deposition pool, and can establish one, two or more settling tank formation in parallel.
The rectangle aeration tank can be a square or rectangular, is provided with dividing plate between rectangle aeration pool wall and rectangle precipitation pool wall, and its rectangle aeration tank is separated into several zones.One or more of anaerobic pond, anoxic pond, Aerobic Pond, equalizing tank, hydrolysis acidification pool can be arranged in these zones, to satisfy the requirement of different operating modes.Because when this design can make rectangle settling tank and rectangle aeration tank shared portion wall, can reduce cost of investment to greatest extent, and the precipitation pool wall in the aeration tank, can play impact effect to current, help improving aeration efficient.
For avoiding and traditional A
2/ O technology returned sluge nitrate discharges the influence of phosphorus to anaerobic pond, the present invention adopts a kind of new carbon source distribution means, be about to anoxic pond and place the anaerobic pond front, returned sluge, water inlet and mixed-liquor return from second pond all enter the anoxic section, returned sluge and mixed solution carry out denitrification in anoxic pond, remove nitric nitrogen, enter the anaerobism section again, guaranteed the anaerobic state of anaerobic pond, the reinforced phosphor-removing effect.In the design of pond body, dividing plate is separated at least three zones with the rectangle aeration tank, is made as oxygen-starved area, anaerobic zone, aerobic zone that order water is communicated with successively, and the water of aerobic zone and settling tank is communicated with, be equipped with sewage water inlet pipe on the oxygen-starved area, the oxygen-starved area is equipped with return line respectively and between aerobic zone, settling region.
Biological treatment zone comprises oxygen-starved area, anaerobic zone and aerobic aeration district.Consider that there is higher dephosphorization denitrogenation requirement in sewage work, second pond returned sluge and aerobic aeration district nitrification liquid can flow to the anoxic section with water inlet behind the water inlet mixing zone, under the effect of submersible agitator, the muddy water thorough mixing, and anoxic section sludge concentration can exceed nearly 50% than aerobic section, have more mud reserves and long mud mud age than conventional method, denitrification can access effective assurance.Anaerobic zone can be exempted in the internal reflux nitrification liquid dissolved oxygen to the influence of anaerobic environment, under anaerobic, polyP bacteria in the active sludge discharges the phosphorus in the cellular material, exist with deliquescent phos-phate forms, by release to phosphorus, polyP bacteria can absorb from sewage times over the phosphorus that is discharged at aerobic stage, promptly so-called excess ingestion.And then enter the aerobic aeration district, thereby reach the purpose of biological phosphate-eliminating.
In actual use, take all factors into consideration the saving of the convenience and the cost of investment of design and construction, dividing plate between rectangle aeration tank and rectangle settling tank is typically designed to the extension of rectangle precipitation pool wall, perhaps dividing plate is located at the wire place of corresponding angles between rectangle aeration tank and rectangle settling tank.
The present invention is by designing the rectangle settling tank in the rectangle aeration tank, again the rectangle aeration tank is designed to several regions, but each zone and rectangle settling tank shared portion wall, make the floor space of entire equipment little, cost of investment is low, aeration efficient height, particularly water inlet inserts oxygen-starved area, anaerobic zone, aerobic zone, settling region formation water cycle successively, has improved denitrogenation dephosphorizing efficient.
Description of drawings
Fig. 1 is a structural representation of the present invention.
Fig. 2 is the structural representation of the embodiment of the invention 2.
Fig. 3 is the structural representation of the embodiment of the invention 3.
Embodiment
Claims (6)
1. energy-conservation combined building aeration sedimentation tank, comprise rectangle aeration tank, rectangle settling tank and connecting tube, the rectangle settling tank places the rectangle aeration tank, be communicated with by the water distribution partition wall between rectangle settling tank and rectangle aeration tank, it is characterized in that being provided with dividing plate between rectangle aeration pool wall and rectangle precipitation pool wall, dividing plate is the extension of rectangle precipitation pool wall, or dividing plate is positioned at the wire place of corresponding angles between rectangle aeration tank and rectangle settling tank, and described dividing plate is separated into several zones to the rectangle aeration tank.
2. energy-conservation combined building aeration sedimentation tank according to claim 1 is characterized in that settling tank is preliminary sedimentation tank or second pond or final deposition pool.
3. energy-conservation combined building aeration sedimentation tank according to claim 2 is characterized in that settling tank is one or two or a plurality of composing in parallel.
4. according to claim 1,2, one of 3 described energy-conservation combined building aeration sedimentation tanks, it is characterized in that the rectangle aeration tank is a square or rectangular.
5. energy-conservation combined building aeration sedimentation tank according to claim 1 is characterized in that several zones are one or more of anaerobic pond, anoxic pond, Aerobic Pond, equalizing tank, hydrolysis acidification pool.
6. energy-conservation combined building aeration sedimentation tank according to claim 5, it is characterized in that dividing plate is separated at least three zones with the rectangle aeration tank, be made as oxygen-starved area, anaerobic zone, aerobic zone that order water is communicated with successively, aerobic zone and settling tank water are communicated with, be equipped with sewage water inlet pipe on the oxygen-starved area, the oxygen-starved area is equipped with return line respectively and between aerobic zone, settling region.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
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CNB2007100247983A CN100560516C (en) | 2007-06-25 | 2007-06-25 | Energy-conservation combined building aeration sedimentation tank |
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CNB2007100247983A CN100560516C (en) | 2007-06-25 | 2007-06-25 | Energy-conservation combined building aeration sedimentation tank |
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CN101113058A CN101113058A (en) | 2008-01-30 |
CN100560516C true CN100560516C (en) | 2009-11-18 |
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CNB2007100247983A Active CN100560516C (en) | 2007-06-25 | 2007-06-25 | Energy-conservation combined building aeration sedimentation tank |
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Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
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CN104129842A (en) * | 2013-05-03 | 2014-11-05 | 彭志新 | Single-tank integrated biochemical treatment process for sewage |
CN108358314B (en) * | 2018-03-08 | 2023-05-05 | 中国市政工程中南设计研究总院有限公司 | Sludge near reflux bioreactor, combined facility and application thereof |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN2542657Y (en) * | 2002-04-08 | 2003-04-02 | 青岛依维优环境工程设备有限公司 | Integrated sewage treatment device |
CN2558651Y (en) * | 2002-07-01 | 2003-07-02 | 攀钢集团钢城企业总公司环保设备厂 | Integrated household sewage treating device |
CN2639296Y (en) * | 2003-02-14 | 2004-09-08 | 胡志忠 | Integral deep treater for sewage |
US20040211722A1 (en) * | 2003-04-23 | 2004-10-28 | Lacey Joe W. | Wastewater treatment unit |
CN201065363Y (en) * | 2007-06-25 | 2008-05-28 | 无锡市联创市政工程设计有限公司 | Energy-saving co-building aeration precipitating tank |
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- 2007-06-25 CN CNB2007100247983A patent/CN100560516C/en active Active
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN2542657Y (en) * | 2002-04-08 | 2003-04-02 | 青岛依维优环境工程设备有限公司 | Integrated sewage treatment device |
CN2558651Y (en) * | 2002-07-01 | 2003-07-02 | 攀钢集团钢城企业总公司环保设备厂 | Integrated household sewage treating device |
CN2639296Y (en) * | 2003-02-14 | 2004-09-08 | 胡志忠 | Integral deep treater for sewage |
US20040211722A1 (en) * | 2003-04-23 | 2004-10-28 | Lacey Joe W. | Wastewater treatment unit |
CN201065363Y (en) * | 2007-06-25 | 2008-05-28 | 无锡市联创市政工程设计有限公司 | Energy-saving co-building aeration precipitating tank |
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CN101113058A (en) | 2008-01-30 |
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