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CN200964368Y - Membrane biological reactor - Google Patents

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Publication number
CN200964368Y
CN200964368Y CNU2006200100778U CN200620010077U CN200964368Y CN 200964368 Y CN200964368 Y CN 200964368Y CN U2006200100778 U CNU2006200100778 U CN U2006200100778U CN 200620010077 U CN200620010077 U CN 200620010077U CN 200964368 Y CN200964368 Y CN 200964368Y
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activated carbon
filter tank
biological activated
water
membrane
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刘建广
张春阳
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Shandong Jianzhu University
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Shandong Jianzhu University
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    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
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    • Y02W10/10Biological treatment of water, waste water, or sewage

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Abstract

本实用新型为一种膜生物反应器,属于水处理装置领域。其技术方案为:它包括滤池,在滤池的底部设置有进水口,在滤池内靠近底部并在进水口的上方设置有生物活性炭滤层,在生物活性炭滤层的上部设置有膜组件。该方案采用在微污染水经过膜组件之前设置有生物活性炭过滤层净化装置,其结构简单,制造成本低,净化效果好。

Figure 200620010077

The utility model relates to a membrane bioreactor, which belongs to the field of water treatment devices. The technical scheme is as follows: it includes a filter tank, a water inlet is arranged at the bottom of the filter tank, a biological activated carbon filter layer is arranged near the bottom in the filter tank and above the water inlet, and a membrane module is arranged on the upper part of the biological activated carbon filter layer . The scheme adopts a biological activated carbon filter layer purification device before the slightly polluted water passes through the membrane module, which has a simple structure, low manufacturing cost and good purification effect.

Figure 200620010077

Description

膜生物反应器membrane bioreactor

技术领域technical field

本实用新型涉及一种膜生物反应器,尤其涉及一种一体式膜生物反应器。The utility model relates to a membrane bioreactor, in particular to an integrated membrane bioreactor.

背景技术Background technique

膜生物反应器技术是一项新兴的水处理新技术,是传统生物处理工艺与膜分离技术的有机结合,已成功地应用于水处理。膜生物反应器一般由膜分离组件及生物反应器两部分组成,根据膜组件设置的位置,主要分为分置式和淹没式两种。淹没式的膜生物反应器组合工艺是将膜组件置入生物反应器内,经过膜得到滤液,悬浮物及活性污泥等物质被截留在生物反应器内,对于高氨氮、高有机物的微污染水源水或当污泥浓度过高时使膜的过滤通量降低,阻力增大,增加了能耗,运行管理不便。Membrane bioreactor technology is a new water treatment technology, which is an organic combination of traditional biological treatment process and membrane separation technology, and has been successfully applied to water treatment. Membrane bioreactors are generally composed of membrane separation modules and bioreactors. According to the location of membrane modules, they are mainly divided into two types: split type and submerged type. The submerged membrane bioreactor combination process is to put the membrane module into the bioreactor, and obtain the filtrate through the membrane, and the suspended solids and activated sludge are trapped in the bioreactor, which is suitable for micro-pollution with high ammonia nitrogen and high organic matter. When the source water or the sludge concentration is too high, the filtration flux of the membrane is reduced, the resistance is increased, the energy consumption is increased, and the operation and management are inconvenient.

发明内容Contents of the invention

本实用新型是针对现有技术所存在的缺点,而提供了一种一体式膜生物反应器的技术方案,该方案采用在微污染水经过膜组件之前设置有生物活性炭过滤层的一次净化装置,其结构简单,制造成本低,净化效果好。The utility model aims at the shortcomings of the prior art, and provides a technical solution of an integrated membrane bioreactor, which adopts a primary purification device provided with a biological activated carbon filter layer before the slightly polluted water passes through the membrane module, The structure is simple, the manufacturing cost is low, and the purification effect is good.

本实用新型是通过如下技术措施实现的:它包括滤池,在滤池的底部设置有进水口,在滤池内靠近底部并在进水口的上方设置有生物活性炭滤层,在生物活性炭滤层的上部设置有膜组件。The utility model is realized through the following technical measures: it includes a filter tank, a water inlet is arranged at the bottom of the filter tank, a biological activated carbon filter layer is arranged near the bottom in the filter tank and above the water inlet, and a biological activated carbon filter layer is arranged on the bottom of the filter tank The upper part is provided with a membrane module.

在所述的膜组件的底部,生物活性炭滤层的上部设置有曝气装置。在膜组件底部设曝气管,以对膜组件进行清洗,其曝气强度只需满足清洗的要求。这是因为不需要生物活性炭在水中流化,因此,曝气强度较低。At the bottom of the membrane module, an aeration device is arranged on the upper part of the biological activated carbon filter layer. An aeration pipe is installed at the bottom of the membrane module to clean the membrane module, and the aeration intensity only needs to meet the cleaning requirements. This is because the BAC does not need to be fluidized in the water, therefore, the aeration intensity is lower.

在生物活性炭滤层底部设置有曝气装置和反冲洗装置。这样可以在进水氨氮较高时进行曝气充氧并定期对生物活性炭滤池反冲洗,保持其清洁通畅。具体包括与生物活性炭滤层底部腔体连接的滤池曝气管和滤池反冲气管。在滤池的上部设置有净水出水口。所述的滤池底部设置的进水口与滤池进水管和滤池反冲进水管连接。An aeration device and a backwashing device are arranged at the bottom of the biological activated carbon filter layer. In this way, aeration and oxygenation can be carried out when the ammonia nitrogen in the influent is high, and the biological activated carbon filter can be backwashed regularly to keep it clean and smooth. Specifically, it includes a filter aeration pipe and a filter recoil air pipe connected to the bottom cavity of the biological activated carbon filter layer. A clean water outlet is arranged on the upper part of the filter tank. The water inlet provided at the bottom of the filter is connected with the filter water inlet pipe and the filter backwash water inlet pipe.

该实用新型可以采用如下方式设计装配,将生物活性炭滤池炭层以上的空间加高,将膜组件放在滤层上部的水中,当滤池水位与清水池水位高差较大,可利用水位差出水,降低运行费用,生物活性炭滤池采用向上流方式,池底部进水,并在池底部曝气,曝气量根据进水氨氮浓度,气∶水一般不超过0.5∶1,当有臭氧氧化工艺且采用纯氧为臭氧气源时,可不曝气。通常由于曝气量小,生物活性炭滤层仍保持固定床的状态,经生物活性炭滤层处理的水在上部通过膜组件过滤出水,在膜组件底部设曝气管,以对膜组件进行清洗,曝气强度只需满足清洗的要求。由于不需要生物活性炭在水中流化,因此,曝气强度较低。在生物活性炭滤池底部设置反冲洗装置,定期对生物活性炭滤池反冲洗。虽然对生物活性炭滤池进行曝气,由于膜组件的过滤截留作用,不存在生物活性炭的流失问题,由于对生物活性炭滤层曝气,解决了高氨氮情况下生物活性炭滤池中溶解氧不足的问题,保证了对氨氮的去除。The utility model can be designed and assembled in the following way. The space above the carbon layer of the biological activated carbon filter is increased, and the membrane module is placed in the water above the filter layer. Poor water output, lower operating costs, biological activated carbon filter adopts upward flow method, water enters the bottom of the pool, and aerates at the bottom of the pool, the aeration rate is based on the ammonia nitrogen concentration of the incoming water, and the air: water generally does not exceed 0.5: 1. When there is ozone When the oxidation process is used and pure oxygen is used as the ozone source, no aeration is required. Usually, due to the small amount of aeration, the biological activated carbon filter layer still maintains a fixed bed state, and the water treated by the biological activated carbon filter layer passes through the membrane module to filter the water in the upper part, and an aeration tube is installed at the bottom of the membrane module to clean the membrane module. The aeration intensity only needs to meet the cleaning requirements. The aeration intensity is low because there is no need for bioactivated carbon to be fluidized in water. A backwashing device is installed at the bottom of the biological activated carbon filter to backwash the biological activated carbon filter regularly. Although the biological activated carbon filter is aerated, due to the filtration and interception of the membrane module, there is no loss of biological activated carbon. Due to the aeration of the biological activated carbon filter layer, the problem of insufficient dissolved oxygen in the biological activated carbon filter under the condition of high ammonia nitrogen is solved. problem, ensuring the removal of ammonia nitrogen.

附图说明Description of drawings

图1为本实用新型具体实施方式的结构示意图。Fig. 1 is a schematic structural view of a specific embodiment of the present invention.

图中,1、膜组件,2、生物活性炭滤层,3、水泵,4、净水出水口,5、滤池进水管,6、滤池反冲进水管,7、滤池曝气管,8、滤池反冲气管,9、膜组件曝气管,10、反冲出水管,11、滤池进水口。In the figure, 1. Membrane module, 2. Bioactive carbon filter layer, 3. Water pump, 4. Clean water outlet, 5. Filter inlet pipe, 6. Filter recoil inlet pipe, 7. Filter aeration pipe, 8. Filter recoil air pipe, 9. Membrane module aeration pipe, 10. Recoil outlet pipe, 11. Filter water inlet.

具体实施方式Detailed ways

为能清楚说明本方案的技术特点,下面通过一个具体实施方式,并结合其附图,对本方案进行阐述。In order to clearly illustrate the technical features of the solution, the solution will be described below through a specific implementation mode combined with the accompanying drawings.

一种膜生物反应器,它包括滤池,在滤池的底部设置有与滤池进水管5连通的进水口11,在滤池内靠近底部并在进水口11的上方设置有生物活性炭滤层2,在生物活性炭滤层2的上部设置有膜组件1。在膜组件1的底部,生物活性炭滤层2的上部设置有曝气装置,它包括膜组件曝气管10。在生物活性炭滤层2底部设置有曝气装置和反冲洗装置,具体包括与生物活性炭滤层2底部腔体连接的滤池曝气管7和滤池反冲气管8。在滤池的上部设置有净水出水口4,出水口4处通过管路与水泵3连接。滤池底部设置的进水口与滤池进水管5和滤池反冲进水管6连接。A kind of membrane bioreactor, it comprises filter tank, is provided with the water inlet 11 that is communicated with filter tank water inlet pipe 5 at the bottom of filter tank, is near the bottom in filter tank and is provided with biological activated carbon filter layer above water inlet 11 2. A membrane module 1 is arranged on the upper part of the biological activated carbon filter layer 2 . At the bottom of the membrane module 1 , the upper part of the biological activated carbon filter layer 2 is provided with an aeration device, which includes a membrane module aeration pipe 10 . An aeration device and a backwashing device are arranged at the bottom of the bioactive carbon filter layer 2, specifically including a filter aeration pipe 7 and a filter backwash air pipe 8 connected to the bottom cavity of the bioactive carbon filter layer 2. A clean water outlet 4 is arranged on the upper part of the filter tank, and the water outlet 4 is connected with the water pump 3 through a pipeline. The water inlet provided at the bottom of the filter tank is connected with the filter tank water inlet pipe 5 and the filter tank recoil water inlet pipe 6 .

本实用新型未经描述的技术的特征可以采用现有技术,在此不再赘述。The features of the technology not described in the utility model can adopt the prior art, and will not repeat them here.

Claims (6)

1, a kind of membrane bioreactor, it comprises the filter tank, it is characterized in that, is provided with water-in in the bottom in filter tank, near bottom and be provided with the biological activated carbon filtering layer above water-in, is provided with membrane module on the top of biological activated carbon filtering layer in the filter tank.
2, membrane bioreactor according to claim 1 is characterized in that, in the bottom of described membrane module, the top of biological activated carbon filtering layer is provided with aerating apparatus.
3, membrane bioreactor according to claim 1 and 2 is characterized in that, is provided with aerating apparatus and back-purge system in biological activated carbon filtering layer bottom.
4, membrane bioreactor according to claim 3 is characterized in that, described aerating apparatus comprises filter tank aeration tube and the filter tank recoil tracheae that is connected with biological activated carbon filtering layer bottom cavity with back-purge system.
5, membrane bioreactor according to claim 1 and 2 is characterized in that, is provided with the water purification water outlet on the top in filter tank.
6, membrane bioreactor according to claim 1 is characterized in that, the water-in that bottom, described filter tank is provided with is connected with the filter tank backflushing water intake pipe with the filter tank water inlet pipe.
CNU2006200100778U 2006-09-25 2006-09-25 Membrane biological reactor Expired - Fee Related CN200964368Y (en)

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Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101434444B (en) * 2007-11-16 2011-04-06 中国石油化工股份有限公司 Membrane bioreactor and use thereof in wastewater treatment
US8329035B2 (en) 2007-12-19 2012-12-11 Saudi Arabian Oil Company Suspended media granular activated carbon membrane biological reactor system and process
US8440074B2 (en) 2009-07-08 2013-05-14 Saudi Arabian Oil Company Wastewater treatment system including irradiation of primary solids
US8551341B2 (en) 2009-06-15 2013-10-08 Saudi Arabian Oil Company Suspended media membrane biological reactor system including suspension system and multiple biological reactor zones
US8557111B2 (en) 2009-07-08 2013-10-15 Saudi Arabian Oil Company Low concentration wastewater treatment system
CN103387316A (en) * 2013-08-06 2013-11-13 常州友达环保科技有限公司 Hybrid two-stage membrane bio-reactor (MBR)
CN103387317A (en) * 2013-08-06 2013-11-13 常州友达环保科技有限公司 Integrated two-stage membrane bio-reactor (MBR)
CN115974305A (en) * 2022-12-09 2023-04-18 山东中欧膜技术研究有限公司 Integrated membrane method water treatment system and treatment method

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101434444B (en) * 2007-11-16 2011-04-06 中国石油化工股份有限公司 Membrane bioreactor and use thereof in wastewater treatment
US8329035B2 (en) 2007-12-19 2012-12-11 Saudi Arabian Oil Company Suspended media granular activated carbon membrane biological reactor system and process
US8551341B2 (en) 2009-06-15 2013-10-08 Saudi Arabian Oil Company Suspended media membrane biological reactor system including suspension system and multiple biological reactor zones
US8440074B2 (en) 2009-07-08 2013-05-14 Saudi Arabian Oil Company Wastewater treatment system including irradiation of primary solids
US8557111B2 (en) 2009-07-08 2013-10-15 Saudi Arabian Oil Company Low concentration wastewater treatment system
US8721889B2 (en) 2009-07-08 2014-05-13 Saudi Arabian Oil Company Wastewater treatment process including irradiation of primary solids
CN103387316A (en) * 2013-08-06 2013-11-13 常州友达环保科技有限公司 Hybrid two-stage membrane bio-reactor (MBR)
CN103387317A (en) * 2013-08-06 2013-11-13 常州友达环保科技有限公司 Integrated two-stage membrane bio-reactor (MBR)
CN115974305A (en) * 2022-12-09 2023-04-18 山东中欧膜技术研究有限公司 Integrated membrane method water treatment system and treatment method
CN115974305B (en) * 2022-12-09 2023-09-12 山东中欧膜技术研究有限公司 Integrated membrane method water treatment system and treatment method

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Granted publication date: 20071024

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