CN102249412B - Multistage anoxic and anaerobic circulation tail section anoxic activated sludge treatment process and system - Google Patents
Multistage anoxic and anaerobic circulation tail section anoxic activated sludge treatment process and system Download PDFInfo
- Publication number
- CN102249412B CN102249412B CN 201110132026 CN201110132026A CN102249412B CN 102249412 B CN102249412 B CN 102249412B CN 201110132026 CN201110132026 CN 201110132026 CN 201110132026 A CN201110132026 A CN 201110132026A CN 102249412 B CN102249412 B CN 102249412B
- Authority
- CN
- China
- Prior art keywords
- anoxic
- tank
- anaerobic
- aerobic
- pool
- 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
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Treatment Of Sludge (AREA)
Abstract
一种多级缺氧厌氧循环尾段缺氧活性污泥处理工艺及系统,将多个好氧池、多个缺氧池交替连通,每个缺氧池均连有一个厌氧池,形成多个由一个好氧池、与该好氧池连通的后一缺氧池和与后一缺氧池相连的厌氧池组成的组合,之后将污水分流同时进入各个组合的厌氧池,每一组合的好氧池流出泥水混合液进入本组合的缺氧池,而进入厌氧池的污水与从本组合的缺氧池进入厌氧池的泥水混合液混合,并在本组合的厌氧池和缺氧池之间循环,每一组合的缺氧池流出的泥水混合液进入下一组合的好氧池,最后一个组合的缺氧池流出的混合液进入二沉池。最适用于城市生活污水处理,具有节省曝气量、需要碳源少人优点,较好地解决了因碳源偏低,碳、氮、磷比例失调,难以实现高效除磷脱氮的城市污水的处理问题。
A process and system for treating anoxic activated sludge at the end of a multi-stage anoxic-anaerobic cycle, which alternately connects multiple aerobic pools and multiple anoxic pools, and each anoxic pool is connected to an anaerobic pool to form A plurality of combinations consisting of an aerobic tank, a subsequent anoxic tank connected to the aerobic tank, and an anaerobic tank connected to the latter anoxic tank, and then the sewage is diverted into the anaerobic tanks of each combination at the same time, each A combined aerobic tank flows out of the mud-water mixture into the combined anoxic tank, and the sewage entering the anaerobic tank is mixed with the mud-water mixed solution that enters the anaerobic tank from the combined anoxic tank, and is mixed in the combined anaerobic tank. The circulation between the pool and the anoxic tank, the mud-water mixture flowing out of each combination of anoxic tanks enters the next combination of aerobic tanks, and the mixed solution flowing out of the last combination of anoxic tanks enters the secondary sedimentation tank. It is most suitable for urban domestic sewage treatment. It has the advantages of saving aeration and requiring less carbon sources. It better solves the problem of urban sewage that is difficult to achieve efficient phosphorus and nitrogen removal due to low carbon sources and imbalanced ratios of carbon, nitrogen, and phosphorus. processing problem.
Description
技术领域 technical field
本发明涉及一种多级缺氧厌氧循环尾段缺氧活性污泥处理工艺及处理系统,尤其适用于低碳源城市生活污水的处理。 The invention relates to an anoxic activated sludge treatment process and a treatment system at the tail section of a multistage anoxic anaerobic cycle, which is especially suitable for the treatment of low-carbon source urban domestic sewage.
背景技术 Background technique
近年来,水环境污染和水体富营养化的问题日益严重。而氮、磷是引起水体富营养化的主要因素。随着公众环境意识的提高和国内外对氮、磷的排放的限制标准越来越严格,研究开发经济、高效的去除氮、磷的污水处理技术,尤其是废水生物除磷脱氮技术一直是水污染控制工程领域的热点。 In recent years, the problems of water environment pollution and water eutrophication have become increasingly serious. Nitrogen and phosphorus are the main factors causing water eutrophication. With the improvement of public environmental awareness and stricter restrictions on nitrogen and phosphorus discharge at home and abroad, research and development of economical and efficient sewage treatment technologies for nitrogen and phosphorus removal, especially wastewater biological phosphorus and nitrogen removal technology has always been an important issue. Hotspots in the field of water pollution control engineering.
发明内容 Contents of the invention
技术问题:本发明的目的是克服已有技术中的不足之处,提供一种工艺简单、能耗较小、成本较低的多级缺氧厌氧循环尾段缺氧活性污泥处理工艺及处理系统。 Technical problem: the purpose of the present invention is to overcome the deficiencies in the prior art, to provide a multi-stage anoxic anaerobic cycle tail section anoxic activated sludge treatment process with simple process, low energy consumption and low cost and processing system.
技术方案:本发明的多级缺氧厌氧循环尾段缺氧活性污泥处理工艺,包括好氧、缺氧和厌氧生物处理,并二沉池进行沉淀,沉淀中排出上清液,同时将部分污泥回流,处理步骤如下: Technical solution: The anoxic activated sludge treatment process at the end of the multi-stage anoxic anaerobic cycle of the present invention includes aerobic, anoxic and anaerobic biological treatment, and the secondary sedimentation tank is used for sedimentation, and the supernatant is discharged from the sedimentation, and at the same time Return part of the sludge, and the treatment steps are as follows:
a.将多个好氧池、多个缺氧池交替连通,每个缺氧池均连有一个厌氧池,形成多个由一个好氧池、与该好氧池连通的后一缺氧池和与后一缺氧池相连的厌氧池组成的组合; a. A plurality of aerobic pools and a plurality of anoxic pools are alternately connected, and each anoxic pool is connected with an anaerobic pool to form a plurality of aerobic pools, the latter anoxic pools connected with the aerobic pool, and a combination of anaerobic tanks connected to the latter anoxic tank;
b.将污水分流同时进入各个组合的厌氧池,每一组合的好氧池流出泥水混合液进入本组合的缺氧池,而进入厌氧池的污水与从本组合的缺氧池进入厌氧池的泥水混合液混合,并在本组合的厌氧池和缺氧池之间循环,每一组合的缺氧池流出的泥水混合液进入下一组合的好氧池,最后一个组合的缺氧池流出的混合液进入二沉池。 b. Separate the sewage into the anaerobic tanks of each combination at the same time, and the mud-water mixture flowing out of each combination of aerobic tanks enters the anoxic tank of the combination, and the sewage entering the anaerobic tank enters the anaerobic tank from the anoxic tank of the combination The mud-water mixture is mixed and circulated between the anaerobic tank and the anoxic tank of this combination. The mud-water mixture flowing out of each combination of anoxic tanks enters the next combination of aerobic tanks, and the last combination of anoxic tanks flows out The mixed solution enters the secondary sedimentation tank.
所述的由一个好氧池、与该好氧池连通的后一缺氧池和与后一缺氧池相连的厌氧池组成的组合的个数为2~30个;所述的厌氧池与缺氧池合建或分建;所述的缺氧池和好氧池合建或分建。 The number of the combination consisting of an aerobic pool, a subsequent anoxic pool connected to the aerobic pool, and an anaerobic pool connected to the latter anoxic pool is 2 to 30; The pool and the anoxic pool are built together or separately; the anoxic pool and the aerobic pool are built together or separately.
本发明实现多级缺氧厌氧循环尾段缺氧活性污泥工艺的处理系统,包括多个好氧池、多个缺氧池、多个厌氧池和一个二沉池,所述的多个好氧池、多个缺氧池以好氧池、缺氧池、好氧池、缺氧池的形式交替连通,每个缺氧池均连通一个厌氧池,每个厌氧池均与污水管连通,二沉池的回流管连通第一个好氧池。 The present invention realizes the treatment system of the anoxic activated sludge process at the end of multi-stage anoxic anaerobic cycle, including multiple aerobic pools, multiple anoxic pools, multiple anaerobic pools and a secondary sedimentation tank. One aerobic pool and multiple anoxic pools are alternately connected in the form of aerobic pool, anoxic pool, aerobic pool, and anoxic pool. Each anoxic pool is connected to an anaerobic pool, and each anaerobic pool is connected to an anaerobic pool. The sewage pipe is connected, and the return pipe of the secondary settling tank is connected to the first aerobic tank.
有益效果:本发结合废水生物处理方法,充分利用有限的碳源,提高了废水处理中碳源的利用率,有效地解决了废水生物除磷中碳源不足的问题,同时大幅度地提高了系统的污泥浓度。污水直接进入厌氧池,将有限的碳源优先供给聚磷菌;泥水混合液在厌氧池和缺氧池之间循环,有利于在缺氧条件下形成反硝化除磷,将反硝化脱氮和过量吸磷2个独立过程合二为一,一碳两用。通过使活性污泥交替经过厌氧、缺氧和好氧环境,使得各类微生物交替进入对本身有利的生长环境,使微生物不会因长时间处于对自身不利的生长环境受到抑制,有利于各类微生物保持高生物活性。来自二沉池的回流污泥全部进入好氧池有利于尽快恢复好氧微生物的活性。本发明具有节省曝气量、需要碳源较少等优点,可以较好地解决因碳源偏低,碳、氮、磷比例失调,而难以实现高效除磷脱氮的城市污水的处理问题。 Beneficial effects: the present invention combines the wastewater biological treatment method to make full use of limited carbon sources, improves the utilization rate of carbon sources in wastewater treatment, effectively solves the problem of insufficient carbon sources in wastewater biological phosphorus removal, and greatly improves The sludge concentration of the system. The sewage directly enters the anaerobic tank, and the limited carbon source is preferentially supplied to the phosphorus accumulating bacteria; the mud-water mixture circulates between the anaerobic tank and the anoxic tank, which is conducive to the formation of denitrification and phosphorus removal under anoxic conditions, and the denitrification and denitrification Combine two independent processes with excess phosphorus absorption into one, one carbon with two uses. By making the activated sludge pass through the anaerobic, anoxic and aerobic environments alternately, various microorganisms can alternately enter the growth environment that is beneficial to themselves, so that the microorganisms will not be inhibited by being in a growth environment that is unfavorable to themselves for a long time, which is beneficial to all kinds of microorganisms. Microorganisms maintain high biological activity. All the return sludge from the secondary settling tank enters the aerobic tank, which is conducive to recovering the activity of aerobic microorganisms as soon as possible. The invention has the advantages of saving aeration amount, requiring less carbon source, etc., and can better solve the problem of urban sewage treatment that is difficult to achieve high-efficiency phosphorus and nitrogen removal due to low carbon source and imbalanced ratio of carbon, nitrogen and phosphorus.
附图说明 Description of drawings
图1是本发明的工艺流程图。 Fig. 1 is a process flow diagram of the present invention.
具体实施方式 Detailed ways
下面结合附图对本发明的实施例做进一步的描述: Embodiments of the present invention are further described below in conjunction with accompanying drawings:
本发明的多级缺氧厌氧循环尾段缺氧活性污泥处理工艺,将多个好氧池、多个缺氧池交替连通,每个缺氧池均连有一个厌氧池,形成多个由一个好氧池、与该好氧池连通的后一缺氧池和与后一缺氧池相连的厌氧池组成的组合,该组合的个数为2~30个。将污水分流同时进入多个组合的厌氧池,每一组合的好氧池流出泥水混合液进入本组合的缺氧池,而进入厌氧池的污水与从本组合的缺氧池进入厌氧池的泥水混合液混合,厌氧池与缺氧池合建或分建,缺氧池和好氧池合建或分建。在一个组合的厌氧池和缺氧池之间循环,每一组合的缺氧池流出的泥水混合液进入下一组合的好氧池,最后一个组合的缺氧池流出的混合液进入二沉池,在二沉池中固液分离,排出上清液,回流污泥进入第一个好氧池,并定时排出剩余污泥。 The anoxic activated sludge treatment process at the tail section of the multi-stage anoxic anaerobic cycle of the present invention alternately connects a plurality of aerobic pools and a plurality of anoxic pools, and each anoxic pool is connected with an anaerobic pool to form multiple A combination consisting of an aerobic pool, a subsequent anoxic pool connected to the aerobic pool, and an anaerobic pool connected to the latter anoxic pool, the number of the combination is 2 to 30. Divide sewage into multiple combined anaerobic tanks at the same time, and the mud-water mixture from each combined aerobic tank enters the combined anoxic tank, and the sewage entering the anaerobic tank enters the anaerobic tank from the combined anoxic tank The mud-water mixture of the pool is mixed, the anaerobic pool and the anoxic pool are built together or separately, and the anoxic pool and the aerobic pool are built together or separately. Cycle between a combined anaerobic tank and anoxic tank, the mud-water mixture flowing out of each combined anoxic tank enters the next combined aerobic tank, and the mixed liquid flowing out of the last combined anoxic tank enters the secondary sedimentation tank , solid-liquid separation in the secondary settling tank, discharge the supernatant, return the sludge into the first aerobic tank, and regularly discharge the remaining sludge.
本发明的实现多级缺氧厌氧循环尾段缺氧活性污泥工艺的处理系统,主要由多个好氧池、缺氧池、多个厌氧池和一个二沉池构成,厌氧池与缺氧池可以合建也可以分建,缺氧池和好氧池可以合建也可以分建。多个好氧池和多个缺氧池以好氧池、缺氧池、好氧池、缺氧池的形式交替连通,每个缺氧池均连通一个厌氧池,每个厌氧池均与污水管连通,二沉池的回流管连通第一个好氧池。 The treatment system for realizing the anoxic activated sludge process at the tail section of the multistage anoxic anaerobic cycle of the present invention is mainly composed of multiple aerobic pools, anoxic pools, multiple anaerobic pools and a secondary sedimentation tank. It can be built together with the anoxic pool or separately, and the anoxic pool and the aerobic pool can be built together or separately. Multiple aerobic pools and multiple anoxic pools are alternately connected in the form of aerobic pools, anoxic pools, aerobic pools, and anoxic pools. Each anoxic pool is connected to an anaerobic pool. It is connected with the sewage pipe, and the return pipe of the secondary sedimentation tank is connected with the first aerobic tank.
Claims (1)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN 201110132026 CN102249412B (en) | 2011-05-20 | 2011-05-20 | Multistage anoxic and anaerobic circulation tail section anoxic activated sludge treatment process and system |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN 201110132026 CN102249412B (en) | 2011-05-20 | 2011-05-20 | Multistage anoxic and anaerobic circulation tail section anoxic activated sludge treatment process and system |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN102249412A CN102249412A (en) | 2011-11-23 |
| CN102249412B true CN102249412B (en) | 2013-02-13 |
Family
ID=44977047
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN 201110132026 Expired - Fee Related CN102249412B (en) | 2011-05-20 | 2011-05-20 | Multistage anoxic and anaerobic circulation tail section anoxic activated sludge treatment process and system |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN102249412B (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103601296B (en) * | 2013-11-15 | 2015-11-25 | 玉溪师范学院 | A kind of D-A of diphasic anaerobic anoxic alternate run 2/ O sewage-treating reactor |
| CN109851049B (en) * | 2019-04-11 | 2024-06-18 | 信开环境投资有限公司 | Sewage treatment unit and use method and application thereof |
| CN112079521B (en) * | 2020-08-27 | 2022-09-27 | 生态环境部华南环境科学研究所 | Based on A 2 Alternate rural sewage treatment device for O process |
Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US6562237B1 (en) * | 1998-12-04 | 2003-05-13 | Tox Olaopa | Biological nutrient removal using the olaopa process |
| CN1772655A (en) * | 2005-09-27 | 2006-05-17 | 中国矿业大学 | A high-efficiency nitrification process for sewage biological treatment |
| CN2801772Y (en) * | 2005-06-28 | 2006-08-02 | 中国矿业大学 | Frequent nitration denitrification device for sewage biological treatment |
| CN200946120Y (en) * | 2005-06-23 | 2007-09-12 | 中国矿业大学 | Integrated multifunctional membrane bioreactor |
-
2011
- 2011-05-20 CN CN 201110132026 patent/CN102249412B/en not_active Expired - Fee Related
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US6562237B1 (en) * | 1998-12-04 | 2003-05-13 | Tox Olaopa | Biological nutrient removal using the olaopa process |
| CN200946120Y (en) * | 2005-06-23 | 2007-09-12 | 中国矿业大学 | Integrated multifunctional membrane bioreactor |
| CN2801772Y (en) * | 2005-06-28 | 2006-08-02 | 中国矿业大学 | Frequent nitration denitrification device for sewage biological treatment |
| CN1772655A (en) * | 2005-09-27 | 2006-05-17 | 中国矿业大学 | A high-efficiency nitrification process for sewage biological treatment |
Also Published As
| Publication number | Publication date |
|---|---|
| CN102249412A (en) | 2011-11-23 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN104860482B (en) | The method of up-flow anaerobic sludge blanket+anoxic/aerobic+anaerobic ammonia oxidation reactor PROCESS FOR TREATMENT treatment of advanced stage landfill leachate advanced nitrogen | |
| CN104230107B (en) | A kind of A2/O+ MBR combined sewage water reclaiming process and device thereof | |
| CN102557343B (en) | Process and device for treating sewage through denitrification and dephosphorization by oxic-anaerobic-anoxic-oxic (OAAO) plus membrane bioreactor (MBR) process | |
| CN104512963B (en) | A kind of multistage simultaneous nitrification-denitrification biofilm system denitrogenation method of integral type and device | |
| CN102653423A (en) | Membrane bioreactor sewage treatment method and apparatus for enhancing denitrifying dephosphatation through mud-water separation and backflow | |
| CN102583743A (en) | Dual-sludge denitrification dephosphorizing and denitrifying A/A-O device and method | |
| CN204958663U (en) | Wastewater treatment process's mud adsorption separation degree of depth nitrogen and phosphorus removal system | |
| CN102674537A (en) | Reversed-order SBR (Sequencing Batch Reactor) water processing device and method for enhanced nitrogen removal | |
| CN103936231B (en) | A kind of energy-saving inversion A AO-MBR sewage water treatment method | |
| CN202688093U (en) | Improved A/O (anoxic/oxic) four-point section-water supply high-efficiency synchronous nitrogen and phosphorus removal device | |
| CN104609651B (en) | A large-scale pig farm wastewater advanced treatment system | |
| CN209989143U (en) | Denitrifying phosphorus removal coupling vibration oxygen deficiency MBR device | |
| CN106587350B (en) | Sewage treatment system and treatment method based on magnetic coagulation AAS and magnetized MABR | |
| CN202729946U (en) | Two-stage anoxic/oxic (A/O)-membrane biological reactor (MBR) nitrogen and phosphorus removal device | |
| CN205442793U (en) | A2/O-biological synchronous nitrogen and phosphorus removal device for urban sewage | |
| CN202265459U (en) | A-CASS sewage processing system | |
| CN108178294A (en) | A kind of method of the low matrix anaerobic ammonia oxidation process of synchronous tandem promoter | |
| CN201458900U (en) | Improvement of the device for denitrification and dephosphorization at depth of water inlet in stages | |
| CN106495324B (en) | High-efficient denitrification and dephosphorization multistage AO+SBR sewage disposal reaction tank and method | |
| CN102153254B (en) | Anoxic and aerobic circulating activated sludge process | |
| CN102259981B (en) | A Sequencing Batch Biological Phosphorus and Nitrogen Removal Process | |
| CN204356197U (en) | Modified form MSBR reactor | |
| CN102249412B (en) | Multistage anoxic and anaerobic circulation tail section anoxic activated sludge treatment process and system | |
| CN105130092B (en) | Treatment device and method for degradation and nitrogen removal of printing and dyeing wastewater high-concentration organic matters | |
| CN103755025B (en) | Double-membrane double-circulation sewage treatment process for enhancing denitrifying phosphorus removal |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| 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: 20130213 Termination date: 20190520 |
|
| CF01 | Termination of patent right due to non-payment of annual fee |
