CN102276062A - Multistage anaerobic and anoxic circulating final segment aerobic activated sludge process - Google Patents
Multistage anaerobic and anoxic circulating final segment aerobic activated sludge process Download PDFInfo
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Abstract
一种多级厌氧缺氧循环尾段好氧活性污泥工艺,将多个缺氧池、好氧池交替连接,每个缺氧池均连接一个厌氧池,由一个缺氧池、与该缺氧池连接的后一厌氧池和与该缺氧池相连的好氧池形成一个组合,之后将污水分流同时进入各个组合的厌氧池和二沉池,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本组合的好氧池,好氧池流出泥水混合液进入下一个组合的缺氧池,最后一个组合的好氧池流出的泥水混合液进入二沉池。最适用于城市生活污水处理,具有节省曝气量、需要碳源少的优点,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。
An aerobic activated sludge process at the end of a multi-stage anaerobic-anoxic cycle, which alternately connects a plurality of anoxic pools and aerobic pools, and each anoxic pool is connected to an anaerobic pool. The latter anaerobic pond connected to the anoxic pond forms a combination with the aerobic pond connected to the anoxic pond, and then the sewage is shunted into the anaerobic pond and the secondary sedimentation pond of each combination at the same time, and the sewage entering the anaerobic pond is combined with the secondary sedimentation pond. The mud-water mixture entering the anaerobic pool from the anoxic pool of this combination is mixed, and circulates between the anaerobic pool and the anoxic pool of this combination, and the mud-water mixture flowing out of the anoxic pool of each combination enters the aerobic pool of this combination The mud-water mixture flowing out of the aerobic tank enters the next combined anoxic tank, and the mud-water mixture flowing out of the last combined aerobic tank 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 source. It better solves the urban sewage that is difficult to achieve efficient phosphorus and nitrogen removal due to low carbon source and imbalance of carbon, nitrogen and phosphorus ratio. processing problem.
Description
技术领域 technical field
本发明涉及生物除磷脱氮工艺,尤其是一种适用于低碳源城市生活污水处理的多级厌氧缺氧循环尾段好氧活性污泥工艺。 The invention relates to a biological phosphorus and nitrogen removal process, in particular to an aerobic activated sludge process at the end of a multi-stage anaerobic-anoxic cycle suitable for low-carbon source urban domestic sewage treatment.
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,成本低的多级厌氧缺氧循环尾段好氧活性污泥工艺。 Technical problem: The purpose of this invention is to overcome the deficiencies in the prior art and provide a multi-stage aerobic activated sludge process at the end of anaerobic anoxic cycle with simple process, low energy consumption and low cost.
技术方案:本发明的多级厌氧缺氧循环尾段好氧活性污泥工艺,包括缺氧、厌氧和好氧生物处理,并进行沉淀,沉淀中排出上清液,同时将部分污泥回流,处理过程步骤如下: Technical solution: The aerobic activated sludge process at the end of the multi-stage anaerobic-anoxic cycle of the present invention includes anoxic, anaerobic and aerobic biological treatment, and sedimentation, the supernatant is discharged from the sedimentation, and part of the sludge is Backflow, the processing steps are as follows:
a.将多个缺氧池、多个好氧池交替连通,每个缺氧池均连有一个厌氧池,形成多个由一个缺氧池、与该缺氧池连通的后一厌氧池和与该缺氧池相连的好氧池组成的组合; a. A plurality of anoxic pools and a plurality of aerobic pools are alternately connected, and each anoxic pool is connected with an anaerobic pool to form a plurality of anoxic pools, the latter anaerobic pools connected with the anoxic pool and a combination of aerobic tanks connected to the anoxic tank;
b.将污水分流同时进入各个组合的厌氧池和二沉池,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本组合的好氧池,每一组合的好氧池流出泥水混合液进入下一个组合的缺氧池,最后一个组合的好氧池流出的混合液进入二沉池。 b. Separate the sewage into the anaerobic tank and the secondary sedimentation tank of each combination at the same time, the sewage entering the anaerobic tank is mixed with the mud-water mixture entering the anaerobic tank from the anoxic tank of this combination, and the anaerobic tank and the anaerobic tank of this combination are mixed. Circulation between oxygen pools, the mud-water mixture flowing out of each combination of anoxic pools enters the aerobic pool of this combination, the mud-water mixture flowing out of each combination of aerobic pools enters the next combination of anoxic pools, and the last combination is good The mixed liquor flowing out of the oxygen tank enters the secondary sedimentation tank.
所述的由一个缺氧池、与该缺氧池连通的后一厌氧池和与该缺氧池相连的好氧池组成的组合的个数为2~30个;所述的缺氧池与厌氧池合建或分建;所述的缺氧池和好氧池合建或分建。 The number of the combination consisting of an anoxic pool, an anaerobic pool connected to the anoxic pool and an aerobic pool connected to the anoxic pool is 2 to 30; the anoxic pool Built together or separately with anaerobic pool; said anoxic pool and aerobic pool are built together or separately.
有益效果:本发明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,将反硝化脱氮和吸磷2个独立过程合二为一,一碳两用。分流进入二沉池的污水与最后一个好氧池中流出的泥水混合液一起进入二沉池,在泥水分离过程中,继续完成反硝化反应,减少回流污泥及出水中的亚硝态氮和硝态氮。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 waste water biological treatment method, fully utilizes the limited carbon source, improves the utilization rate of the carbon source in the waste water treatment, effectively solves the problem of insufficient carbon source in the waste water 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 The two independent processes of absorbing phosphorus and absorbing phosphorus are combined into one, and one carbon is used for two purposes. The sewage diverted into the secondary settling tank enters the secondary settling tank together with the mud-water mixture flowing out of the last aerobic tank. During the mud-water separation process, the denitrification reaction is continued to reduce the nitrite nitrogen and nitrite nitrogen in the return sludge and effluent water. Nitrate nitrogen. 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。 Figure 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作进一步的描述: Embodiments of the present invention will be further described below in conjunction with the accompanying drawings:
本发明的多级厌氧缺氧循环尾段好氧活性污泥工艺,主要通过缺氧池、厌氧池和好氧池进行缺氧、厌氧和好氧生物处理,再经过二沉池沉淀,沉淀中排出上清液,同时将部分污泥回流,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。首先将多个缺氧池、多个好氧池交替连通,每个缺氧池均连有一个厌氧池,形成多个由一个缺氧池、与该缺氧池连通的后一厌氧池和与该缺氧池相连的好氧池组成的组合;由一个缺氧池、与该缺氧池连通的后一厌氧池和与该缺氧池相连的好氧池组成的组合的个数为2~30个。将污水分流同时进入各个组合的厌氧池和二沉池,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本组合的好氧池,每一组合的好氧池流出泥水混合液进入下一个组合的缺氧池,最后一个组合的好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缺氧池,并定时排出剩余污泥。 The aerobic activated sludge process at the end of the multi-stage anaerobic anoxic cycle of the present invention mainly performs anoxic, anaerobic and aerobic biological treatment through the anoxic tank, anaerobic tank and aerobic tank, and then settles through the secondary sedimentation tank , the supernatant is discharged during the sedimentation, and part of the sludge is refluxed at the same time. The anaerobic tank and the anoxic tank can be built together or separately, and the anoxic tank and the aerobic tank can be built together or separately. First connect multiple anoxic pools and multiple aerobic pools alternately, and each anoxic pool is connected to an anaerobic pool to form multiple anaerobic pools connected by one anoxic pool and the anoxic pool Combination with the aerobic pool connected to the anoxic pool; the number of combinations consisting of an anoxic pool, the next anaerobic pool connected to the anoxic pool, and an aerobic pool connected to the anoxic pool 2 to 30 pieces. Separate the sewage into the anaerobic tank and the secondary sedimentation tank of each combination at the same time, the sewage entering the anaerobic tank is mixed with the mud-water mixture entering the anaerobic tank from the anoxic tank of this combination, and the anaerobic tank and the anaerobic tank of this combination are mixed. Circulation between oxygen pools, the mud-water mixture flowing out of each combination of anoxic pools enters the aerobic pool of this combination, the mud-water mixture flowing out of each combination of aerobic pools enters the next combination of anoxic pools, and the last combination is good The mixed liquor flowing out of the oxygen tank enters the secondary settling tank, where the solid and liquid are separated, the supernatant is discharged, and the return sludge enters the first anoxic tank, and the remaining sludge is discharged regularly.
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Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103668835A (en) * | 2013-12-06 | 2014-03-26 | 无锡大阿福信息科技有限公司 | System for recycling waste alkaline water in weak alkali pool |
| CN104478081A (en) * | 2014-12-01 | 2015-04-01 | 中国矿业大学 | Anaerobic-anoxic/aerobic-parallel reinforced dephosphorization and denitrification technique |
| CN109851049A (en) * | 2019-04-11 | 2019-06-07 | 信开水环境投资有限公司 | Sewage treatment unit and its application method and purposes |
| CN110745948A (en) * | 2019-09-27 | 2020-02-04 | 中车环境科技有限公司 | Sectional water inlet deep dephosphorization and denitrification process |
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| CN1772655A (en) * | 2005-09-27 | 2006-05-17 | 中国矿业大学 | A high-efficiency nitrification process for sewage biological treatment |
| CN101691268A (en) * | 2009-09-17 | 2010-04-07 | 上海市政工程设计研究总院 | Biochemical reaction tank and denitrification and dephosphorization process thereof |
| CN101885559A (en) * | 2010-06-25 | 2010-11-17 | 可事托环保设备(上海)有限公司 | Multi-level biological nitrogen and phosphorus removal sewage treatment method and device |
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- 2011-05-20 CN CN 201110132025 patent/CN102276062A/en active Pending
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1772655A (en) * | 2005-09-27 | 2006-05-17 | 中国矿业大学 | A high-efficiency nitrification process for sewage biological treatment |
| CN101691268A (en) * | 2009-09-17 | 2010-04-07 | 上海市政工程设计研究总院 | Biochemical reaction tank and denitrification and dephosphorization process thereof |
| CN101885559A (en) * | 2010-06-25 | 2010-11-17 | 可事托环保设备(上海)有限公司 | Multi-level biological nitrogen and phosphorus removal sewage treatment method and device |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103668835A (en) * | 2013-12-06 | 2014-03-26 | 无锡大阿福信息科技有限公司 | System for recycling waste alkaline water in weak alkali pool |
| CN104478081A (en) * | 2014-12-01 | 2015-04-01 | 中国矿业大学 | Anaerobic-anoxic/aerobic-parallel reinforced dephosphorization and denitrification technique |
| CN109851049A (en) * | 2019-04-11 | 2019-06-07 | 信开水环境投资有限公司 | Sewage treatment unit and its application method and purposes |
| CN110745948A (en) * | 2019-09-27 | 2020-02-04 | 中车环境科技有限公司 | Sectional water inlet deep dephosphorization and denitrification process |
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Application publication date: 20111214 |
