CN204281404U - A kind of novel film bioreactor device - Google Patents

A kind of novel film bioreactor device Download PDF

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Publication number
CN204281404U
CN204281404U CN201420684787.3U CN201420684787U CN204281404U CN 204281404 U CN204281404 U CN 204281404U CN 201420684787 U CN201420684787 U CN 201420684787U CN 204281404 U CN204281404 U CN 204281404U
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reaction tank
water
tank
mbr reaction
net
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吴文伶
张涛
王珂
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China State Construction Engineering Corp Ltd CSCEC
China Construction Baili Engineering Technology Development Co Ltd
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China State Construction Engineering Corp Ltd CSCEC
China Construction Baili Engineering Technology Development Co Ltd
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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
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

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Abstract

A kind of film bioreactor device, comprise the raw water box, MBR reaction tank and the filtered water tank that connect in turn, the top fixing horizontal cover net of MBR reaction tank, bottom be provided with can move up and down, horizontal compression net that centre has hyperfiltration membrane assembly pre-opened hole, filled polyurethane sponge filler between two nets, when horizontal compression net receives reaction tank top, filler is received to top simultaneously, avoid back flushing to the destruction of micropopulation in filler; Polyurethane sponge has vesicular structure, for microorganism growth provides carrier, can be suitable for the apposition growth of anaerobism and aerobic microbiological simultaneously, nitration denitrification effect is strengthened, and the clearance of nitrogen improves; The existence of filler effectively can reduce the concentration of active sludge in reaction tank, reduces microorganism concn in mixed solution, delays Pollution of Ultrafiltration Membrane; Main line also establishes two counter-flushing pipelines, realizes back flushing and the same pump of exiting water process, has saved equipment cost, be widely used in the process of municipal effluent and trade effluent, especially the process of high-concentration ammonia nitrogenous wastewater.

Description

一种新型的膜生物反应器装置A new type of membrane bioreactor device

技术领域 technical field

本实用新型涉及污水治理领域,特别是涉及一种新型的膜生物反应器装置。 The utility model relates to the field of sewage treatment, in particular to a novel membrane bioreactor device.

背景技术 Background technique

膜生物反应器(MBR)为膜分离技术与生物处理技术有机结合之新型态废水处理系统。是一种由膜分离单元与生物处理单元相结台的新型水处理技术,以膜组件取代二沉池在生物反应器中保持高活性污泥浓度减少污水处理设施占地,并通过保持低污泥负荷减少污泥量。主要利用沉浸于好氧生物池内的膜分离设备截留槽内的活性污泥与大分子固体物。在膜制造技术不断提升支援下,MBR处理技术将更加成熟。 Membrane bioreactor (MBR) is a new type of wastewater treatment system that organically combines membrane separation technology and biological treatment technology. It is a new type of water treatment technology that combines a membrane separation unit with a biological treatment unit. It replaces the secondary settling tank with membrane modules to maintain a high concentration of active sludge in the bioreactor to reduce the footprint of sewage treatment facilities and maintain low pollution Sludge loading reduces sludge volume. Mainly use the membrane separation equipment immersed in the aerobic biological tank to retain the activated sludge and macromolecular solids in the tank. With the continuous improvement of membrane manufacturing technology, MBR processing technology will become more mature.

作为一种高效的水处理技术,MBR 正处于发展完善阶段,其自身仍存在一定缺陷需要进一步解决。如膜污染问题始终是一个难以解决的技术问题,现有技术中采用错流技术虽然可以在一定程度上降低膜的污染,但所需技术设备复杂,能耗高,膜维护过程复杂,对设备和技术人员要求高,造价运行成本也高;此外,生化处理时间长、效率低且总氮去除率低也是目前限制MBR 工程应用的主要瓶颈。 As an efficient water treatment technology, MBR is in the stage of development and perfection, and it still has certain defects that need to be further resolved. For example, the membrane fouling problem is always a technical problem that is difficult to solve. Although the cross-flow technology in the existing technology can reduce the membrane fouling to a certain extent, the required technical equipment is complicated, the energy consumption is high, and the membrane maintenance process is complicated. High requirements for technical personnel and high construction and operation costs; in addition, long biochemical treatment time, low efficiency and low total nitrogen removal rate are currently the main bottlenecks that limit the application of MBR projects.

实用新型内容 Utility model content

本实用新型提供了一种新型的膜生物反应器装置,主要用于解决现有膜生物反应器装置污水处理时膜污染严重、采用错流技术虽然可以在一定程度上降低膜的污染但所需技术设备复杂、能耗高、膜维护过程复杂、对设备及技术人员要求高、造价运行成本也较高的问题;还解决现有膜生物反应器装置污水生化处理时间长、效率低且总氮去除率低的技术难题。 The utility model provides a new type of membrane bioreactor device, which is mainly used to solve the serious membrane pollution in the sewage treatment of the existing membrane bioreactor device. Although the cross-flow technology can reduce the membrane pollution to a certain extent, the required Complex technical equipment, high energy consumption, complex membrane maintenance process, high requirements for equipment and technical personnel, and high cost of construction and operation; it also solves the problems of long time, low efficiency and total nitrogen biochemical treatment of sewage in existing membrane bioreactor devices. The technical problem of low removal rate.

为解决上述技术问题,本实用新型采用的技术方案是: In order to solve the problems of the technologies described above, the technical solution adopted in the utility model is:

一种新型的膜生物反应器装置,包括有原水箱,MBR反应池,清水箱,连通原水箱与MBR反应池的进水管,连通MBR反应池与清水箱的连接管,以及连接在清水箱出口的出水管,所述进水管上设有进水阀门和进水泵,连接管上由MBR反应池向清水箱方向顺序设有连接管控制阀门、出水泵和电磁阀,出水管上设有出水阀门,所述MBR反应池的底部设有排泥管和与鼓风机连接的曝气管,MBR反应池内部设有超滤膜组件和反应池液位计,污水进入MBR反应池,在MBR反应池被微生物净化处理、经过超滤膜组件后进入清水箱,再从清水箱排出,其特征在于:所述MBR反应池的顶部固定有一个水平盖网,底部设有一个可上下移动的水平压缩网,水平压缩网与水平盖网之间的MBR反应池中填充聚氨酯海绵填料,水平压缩网的网面中间开有供设于水平压缩网和水平盖网之间的超滤膜组件穿过的预留孔。 A new type of membrane bioreactor device, including a raw water tank, an MBR reaction tank, a clean water tank, a water inlet pipe connecting the raw water tank and the MBR reaction tank, a connecting pipe connecting the MBR reaction tank and the clean water tank, and connecting the outlet of the clean water tank The water outlet pipe is provided with a water inlet valve and a water inlet pump on the water inlet pipe. The connecting pipe is provided with a connecting pipe control valve, an outlet water pump and a solenoid valve in sequence from the MBR reaction tank to the clean water tank, and the water outlet pipe is provided with an outlet valve. , the bottom of the MBR reaction tank is provided with a mud discharge pipe and an aeration pipe connected to the blower, and an ultrafiltration membrane module and a reaction tank level gauge are arranged inside the MBR reaction tank, and the sewage enters the MBR reaction tank, where it is Microbial purification treatment, enter the clean water tank after passing through the ultrafiltration membrane module, and then discharge from the clean water tank. It is characterized in that: the top of the MBR reaction tank is fixed with a horizontal cover net, and the bottom is provided with a horizontal compression net that can move up and down. The MBR reaction tank between the horizontal compression net and the horizontal cover net is filled with polyurethane sponge filler, and the middle of the net surface of the horizontal compression net is opened for the ultrafiltration membrane module between the horizontal compression net and the horizontal cover net to pass through. hole.

作为本实用新型的优选技术方案,所述连接管控制阀门与出水泵之间的连接管通过反冲洗管路一与清水箱连通,MBR反应池与连接管控制阀门之间的连接管通过反冲洗管路二与连接管控制阀门与电磁阀之间的连接管连通,所述反冲洗管路一上设有反冲洗控制进水阀门,反冲洗管路二上设有反冲洗控制出水阀门。 As a preferred technical solution of the present utility model, the connecting pipe between the connecting pipe control valve and the outlet pump communicates with the clean water tank through the backwash pipeline one, and the connecting pipe between the MBR reaction tank and the connecting pipe control valve passes through the backwashing pipe. The second pipeline communicates with the connecting pipe between the connecting pipe control valve and the electromagnetic valve. The first backwashing pipeline is provided with a backwashing control water inlet valve, and the backwashing pipeline 2 is provided with a backwashing control water outlet valve.

作为本实用新型的进一步优选技术方案,所述聚氨酯海绵填料的粒径范围为0.5~1.5cm,可以为球体、立方体或不规则形体。 As a further preferred technical solution of the present invention, the polyurethane sponge filler has a particle size ranging from 0.5 to 1.5 cm, and can be in the shape of a sphere, a cube or an irregular shape.

进一步优选的,所述水平压缩网和水平盖网是孔径为1~5mm的钢丝网。 Further preferably, the horizontal compression net and the horizontal cover net are steel wire nets with a hole diameter of 1-5 mm.

进一步优选的,所述原水箱内设有原水箱液位计,所述原水箱液位计设置于原水箱的底部,高于进水管。 Further preferably, a raw water tank liquid level gauge is provided in the raw water tank, and the raw water tank liquid level gauge is set at the bottom of the raw water tank, higher than the water inlet pipe.

进一步优选的,所述反应池液位计包括高度依次降低的出水液位计、进水高水位液位计和进水低水位液位计,当MBR反应池内水位低于低水位液位计时,进水泵启动开始进水,当水位达到高水位液位计时,进水泵停止进水;间歇出水,出水的时长和间隔通过电路控制,可在控制系统上手动设置。 Further preferably, the liquid level gauge of the reaction tank includes an outlet water level gauge, a water inlet high water level gauge and an inlet water low water level gauge whose heights are successively reduced. When the water level in the MBR reaction tank is lower than the low water level gauge, The water inlet pump starts to feed water, and when the water level reaches the high water level, the water inlet pump stops feeding water; intermittent water discharge, the duration and interval of water discharge are controlled by the circuit, and can be manually set on the control system.

进一步优选的,所述超滤膜组件是浸没于MBR反应池内的液体中的PVDF中空纤维膜。 Further preferably, the ultrafiltration membrane module is a PVDF hollow fiber membrane submerged in the liquid in the MBR reaction tank.

与现有技术相比,本实用新型的技术优势在于: Compared with the prior art, the technical advantages of the utility model are:

1、节约设备降低成本 1. Save equipment and reduce costs

主管路上设两个分支管路反冲洗管路一和反冲洗管路二,排水时连接管控制阀门和出水阀门开启,同时反冲洗控制进水阀门和反冲洗控制出水阀门关闭,反冲洗时,连接管控制阀门和出水阀门关闭,反冲洗控制进水阀门和反冲洗控制出水阀门开启,手动启动出水泵,清水箱内的水顺次经过清水箱、反冲洗管路一、出水泵、反冲洗管路二进入MBR反应池内进行反冲洗,反冲洗与出水过程用同一个泵,节约了设备,降低了成本; There are two branch pipelines on the main road, backwashing pipeline 1 and backwashing pipeline 2. When draining, the connecting pipe control valve and the water outlet valve are opened, and the backwashing control water inlet valve and the backwashing control water outlet valve are closed at the same time. When backwashing, The connecting pipe control valve and the water outlet valve are closed, the backwash control water inlet valve and the backwash control water outlet valve are opened, the outlet pump is manually started, and the water in the clean water tank passes through the clean water tank, backwash pipeline 1, outlet pump, and backwash in sequence The second pipeline enters the MBR reaction tank for backwashing, and the same pump is used for backwashing and water outlet process, which saves equipment and reduces costs;

2、有效保留微生物 2. Effectively retain microorganisms

MBR反应池的顶部固定水平盖网,底部设可上下移动、中间开有超滤膜组件预留孔的水平压缩网,两网之间填充聚氨酯海绵填料,水平压缩网收到反应池顶部时将填料同时收至顶部,避免反冲洗对填料中微生物群的破坏,尤其是在进行化学反冲洗时对填料中微生物的毒害; The top of the MBR reaction tank is fixed with a horizontal cover net, and the bottom is equipped with a horizontal compression net that can move up and down and has holes reserved for ultrafiltration membrane modules in the middle. The polyurethane sponge filler is filled between the two nets. When the horizontal compression net is received at the top of the reaction pool, it will The packing is collected to the top at the same time, avoiding the damage to the microorganisms in the packing by backwashing, especially the poisoning of the microorganisms in the packing during chemical backwashing;

3、提高总氮的去除率 3. Improve the removal rate of total nitrogen

向污泥混合液中投加聚氨酯海绵填料,聚氨酯海绵具有多孔结构,可以为微生物生长提供载体,在填料表面及其填料微孔内可形成微生物膜,在生物膜内部和填料微孔内部的厌氧环境中生长反硝化细菌,而在生物膜外部的好氧环境中生长有硝化细菌,因而形成了硝化-反硝化反应共存的环境,能同时适于厌氧及好氧微生物的附着生长,使硝化反硝化作用加强,氮的去除效率提高;同时,填料的存在可有效降低反应池内活性污泥的浓度,使膜生物反应器的排泥量少,较长的污泥龄有助于硝化细菌和反硝化细菌的生长,因此这种新型的膜生物反应器有助于提高总氮的去除效率; Add polyurethane sponge filler to the sludge mixture. The polyurethane sponge has a porous structure and can provide a carrier for the growth of microorganisms. A microbial film can be formed on the surface of the filler and in the micropores of the filler. Denitrifying bacteria grow in the oxygen environment, while nitrifying bacteria grow in the aerobic environment outside the biofilm, thus forming an environment where nitrification-denitrification reactions coexist, which can be suitable for the attachment and growth of anaerobic and aerobic microorganisms at the same time, so that The nitrification and denitrification effect is strengthened, and the removal efficiency of nitrogen is improved; at the same time, the presence of filler can effectively reduce the concentration of activated sludge in the reaction tank, so that the amount of sludge discharged from the membrane bioreactor is small, and the longer sludge age is conducive to nitrifying bacteria. and the growth of denitrifying bacteria, so this new membrane bioreactor helps to improve the removal efficiency of total nitrogen;

4、降低膜污染 4. Reduce membrane fouling

聚氨酯海绵填料的应用可有效降低反应池内活性污泥的浓度,减少混合液中微生物浓度,延缓超滤膜污染。 The application of polyurethane sponge filler can effectively reduce the concentration of activated sludge in the reaction tank, reduce the concentration of microorganisms in the mixed solution, and delay the fouling of the ultrafiltration membrane.

本实用新型可广泛应用于城市污水及部分工业废水的处理,尤其是高浓度氨氮废水的处理。 The utility model can be widely used in the treatment of urban sewage and some industrial wastewater, especially the treatment of high-concentration ammonia nitrogen wastewater.

附图说明 Description of drawings

图1 是本实用新型涉及的膜生物反应器装置的水处理流程图; Fig. 1 is the water treatment flowchart of the membrane bioreactor device that the utility model relates to;

图2 是本实用新型涉及的MBR反应池4的结构示意图; Fig. 2 is the structural representation of the MBR reaction pool 4 that the utility model relates to;

图3是本实用新型涉及的水平压缩网6的结构示意图; Fig. 3 is a schematic structural view of the horizontal compression network 6 involved in the utility model;

图4是本实用新型涉及的水平盖网7的结构示意图。 Fig. 4 is a schematic structural view of the horizontal cover net 7 involved in the present invention.

附图标记:1-原水箱、2-进水管、3-进水泵、4-MBR反应池、5-聚氨酯海绵填料、6-水平压缩网、7-水平盖网、8-底槽、9-曝气管、10-超滤膜组件、11-液位计、11.1-低水位液位计、11.2-高水位液位计、11.3-出水液位计、12-鼓风机、13-出水泵、14-电磁阀、15-气体流量计、16-出水流量计、17-反冲洗管路一、18-反冲洗管路二、19-出水管、20-清水箱、21-排泥管、22.1-进水阀门、22.2-压力表控制阀门、22.3-连接管控制阀门、22.4-反冲洗控制进水阀门、22.5-反冲洗控制出水阀门、22.6-出水阀门、22.7-排泥管控制阀门、23-压力表、24-原水箱液位计、25-预留孔、26-连接管。 Reference signs: 1-raw water tank, 2-water inlet pipe, 3-water inlet pump, 4-MBR reaction tank, 5-polyurethane sponge packing, 6-horizontal compression net, 7-horizontal cover net, 8-bottom tank, 9- Aeration pipe, 10-ultrafiltration membrane module, 11-liquid level gauge, 11.1-low water level gauge, 11.2-high water level gauge, 11.3-outlet level gauge, 12-blower, 13-outlet pump, 14 -Solenoid valve, 15-gas flow meter, 16-water outlet flow meter, 17-backwash pipeline 1, 18-backwash pipeline 2, 19-water outlet pipe, 20-clean water tank, 21-silt discharge pipe, 22.1- Water inlet valve, 22.2-pressure gauge control valve, 22.3-connecting pipe control valve, 22.4-backwash control water inlet valve, 22.5-backwash control water outlet valve, 22.6-water outlet valve, 22.7-mud discharge pipe control valve, 23- Pressure gauge, 24-raw water tank liquid level gauge, 25-reserved hole, 26-connecting pipe.

具体实施方式 Detailed ways

下面结合附图和实施例对本实用新型进一步说明。如图1所示,包括有原水箱1,MBR反应池4,清水箱20,连通原水箱1与MBR反应池4的进水管2,连通MBR反应池4与清水箱20的连接管26,以及连接在清水箱20出口的出水管19,所述进水管2上设有进水阀门22.1和进水泵3,连接管26上由MBR反应池4向清水箱20方向顺序设有压力表23、连接管控制阀门22.3、出水泵13和电磁阀14,出水管19上设有出水阀门22.6,压力表23由压力表控制阀门22.2控制,所述MBR反应池4的底部设有排泥管21和与鼓风机12连接的曝气管9,排泥管21设置于MBR反应池4的底部,可以定期排走部分活性污泥,控制污泥龄,排泥管21上设有排泥管控制阀门22.7;所述曝气管9置于MBR反应池4的底槽8内,以防止形成沉积的污泥层;MBR反应池4内部设有超滤膜组件10和反应池液位计11,所述超滤膜组件10是浸没于MBR反应池4内的液体中的PVDF中空纤维膜;所述出水泵13与清水箱20之间设有出水流量计16,所述鼓风机12与曝气管9之间设有气体流量计15。 Below in conjunction with accompanying drawing and embodiment the utility model is further described. As shown in Figure 1, comprise raw water tank 1, MBR reaction tank 4, clear water tank 20, the water inlet pipe 2 that communicates with raw water tank 1 and MBR reaction tank 4, the connecting pipe 26 that communicates with MBR reaction tank 4 and clear water tank 20, and Connected to the water outlet pipe 19 at the outlet of the clean water tank 20, the water inlet pipe 2 is provided with a water inlet valve 22.1 and a water inlet pump 3, and the connection pipe 26 is provided with a pressure gauge 23, a connection Pipe control valve 22.3, outlet pump 13 and solenoid valve 14, outlet pipe 19 is provided with outlet valve 22.6, pressure gauge 23 is controlled by pressure gauge control valve 22.2, and the bottom of described MBR reaction tank 4 is provided with mud discharge pipe 21 and with The aeration pipe 9 connected to the blower 12 and the sludge discharge pipe 21 are arranged at the bottom of the MBR reaction tank 4, which can regularly discharge part of the activated sludge and control the sludge age. The sludge discharge pipe 21 is provided with a sludge discharge pipe control valve 22.7; Described aeration pipe 9 is placed in the bottom tank 8 of MBR reaction tank 4, to prevent the sludge layer of formation; The filter membrane assembly 10 is a PVDF hollow fiber membrane submerged in the liquid in the MBR reaction tank 4; an outlet flow meter 16 is arranged between the outlet pump 13 and the clean water tank 20; A gas flow meter 15 is provided.

所述MBR反应池4的顶部固定有一个水平盖网7,底部设有一个可上下移动的水平压缩网6,所述水平压缩网6的网面中间开有供设于水平压缩网6和水平盖网7之间的超滤膜组件10穿过的预留孔25;所述水平压缩网6和水平盖网7的网面均为水平方向;所述水平压缩网6和水平盖网7之间的其他空间填充聚氨酯海绵填料5。所述聚氨酯海绵填料5的粒径范围为0.5~1.5cm,可以为球体、立方体或其他不规则形体。所述水平压缩网6和水平盖网7都是孔径为1~5mm的钢丝网。 The top of the MBR reaction tank 4 is fixed with a horizontal cover net 7, and the bottom is provided with a horizontal compression net 6 that can move up and down. The reserved hole 25 that the ultrafiltration membrane assembly 10 passes between the cover net 7; the mesh surfaces of the horizontal compression net 6 and the horizontal cover net 7 are all horizontal directions; the horizontal compression net 6 and the horizontal cover net 7 The other spaces between are filled with polyurethane sponge filler 5. The polyurethane sponge filler 5 has a particle size ranging from 0.5 to 1.5 cm, and can be in the form of spheres, cubes or other irregular shapes. Both the horizontal compression net 6 and the horizontal cover net 7 are steel wire nets with a hole diameter of 1-5 mm.

所述连接管控制阀门22.3与出水泵13之间的连接管26通过反冲洗管路一17与清水箱20连通,MBR反应池4与连接管控制阀门22.3之间的连接管26通过反冲洗管路二18与连接管控制阀门22.3与电磁阀14之间的连接管26连通,所述反冲洗管路一17上设有反冲洗控制进水阀门22.4,反冲洗管路二18上设有反冲洗控制出水阀门22.5。反冲洗管路包括顺次连接的清水箱20、反冲洗管路一17、出水泵13、反冲洗管路二18和MBR反应池4,反冲洗时,清水箱内的水顺次经过清水箱20、反冲洗管路一17、出水泵13、反冲洗管路二18进入MBR反应池4内进行反冲洗。 The connecting pipe 26 between the connecting pipe control valve 22.3 and the outlet pump 13 communicates with the clean water tank 20 through the backwash pipeline 17, and the connecting pipe 26 between the MBR reaction tank 4 and the connecting pipe control valve 22.3 passes through the backwashing pipe Road two 18 communicates with the connecting pipe 26 between the connecting pipe control valve 22.3 and the solenoid valve 14. The backwashing pipeline one 17 is provided with a backwashing control water inlet valve 22.4, and the backwashing pipeline two 18 is provided with a backwashing pipeline. Flushing control water outlet valve 22.5. The backwash pipeline includes clean water tank 20, backwash pipeline one 17, outlet pump 13, backwash pipeline two 18 and MBR reaction tank 4 connected in sequence. During backwash, the water in the clean water tank passes through the clean water tank in sequence 20. Backwash pipeline 1 17, outlet pump 13, and backwash pipeline 2 18 enter the MBR reaction tank 4 for backwashing.

所述原水箱1内设有原水箱液位计24,所述原水箱液位计24设置于原水箱1的底部,略高于进水管2,当原水箱1中水位低于原水箱液位计24时,进水泵3停止工作;反应池液位计11包括高度逐渐降低的出水液位计11.3、进水高水位液位计11.2和进水低水位液位计11.1,当MBR反应池4内水位低于进水低水位液位计11.1时,进水泵3开启,原水箱1中污水进入MBR反应池4内;当MBR反应池4内水位到达进水高水位液位计11.2时,进水泵3关闭,停止进水;当MBR反应池4内水位低于出水液位计11.3时,出水泵13关闭,停止出水。 The raw water tank 1 is provided with a raw water tank liquid level gauge 24, and the raw water tank liquid level gauge 24 is arranged on the bottom of the raw water tank 1, slightly higher than the water inlet pipe 2, when the water level in the raw water tank 1 is lower than the raw water tank liquid level At 24 o'clock, the water inlet pump 3 stops working; the reaction tank level gauge 11 includes a water outlet level gauge 11.3 whose height gradually decreases, an inlet high water level gauge 11.2 and an inlet low water level gauge 11.1, when the MBR reaction tank 4 When the internal water level is lower than the inlet low water level gauge 11.1, the inlet pump 3 is turned on, and the sewage in the raw water tank 1 enters the MBR reaction tank 4; when the water level in the MBR reaction tank 4 reaches the inlet high water level gauge 11.2, the inlet pump The water pump 3 is closed to stop the water intake; when the water level in the MBR reaction tank 4 is lower than the water outlet level gauge 11.3, the water outlet pump 13 is closed to stop the water outlet.

设备的曝气量由鼓风机12和气体流量计15控制,出水流量由出水泵13和出水流量计16调节,出水时间和间歇时间可在控制系统上设置。 The aeration rate of the equipment is controlled by blower 12 and gas flowmeter 15, and the outlet water flow is regulated by outlet pump 13 and outlet water flowmeter 16. The outlet time and intermittent time can be set on the control system.

下面结合附图分别就本实用新型设备在污水处理过程和反冲洗过程的使用状态进行详细说明: Below in conjunction with accompanying drawing respectively with regard to the use state of the utility model equipment in sewage treatment process and backwashing process, describe in detail:

1、污水处理过程:设备污水处理自动运行状态下,开启压力表控制阀门22.2、连接管控制阀门22.3和出水阀门22.6,同时关闭反冲洗控制进水阀门22.4和反冲洗控制出水阀门22.5,污水从原水箱1中泵入MBR反应池4内,经过分布在聚氨酯海绵填料5内及混合液中的微生物作用后得到净化,净化后的水通过超滤膜组件10后泵出,在生物处理和膜过滤的联合作用下,污水处理效率高处理时间短,参见图2,此过程中,聚氨酯海绵填料5均匀的悬浮于整个MBR反应池4内,反应器内微生物有悬浮的,也有在聚氨酯海绵填料5表面形成微生物膜或吸附在填料微孔内的,微生物多样化的存在形式有助于提高污水处理效果;微生物大部分吸附在填料的表面或微孔内,水中悬浮的微生物数量减少,有利于减缓膜污染;填料微孔内部存在厌氧空间,有利于厌氧微生物的大量繁殖,使总氮去除率高。曝气管置于底槽内,在曝气的作用下,整个反应池内活性污泥的浓度均匀,没有污泥沉淀区或曝气死角,反应系统具有较高的污水处理效率。 1. Sewage treatment process: When the sewage treatment equipment is in automatic operation state, open the pressure gauge control valve 22.2, the connecting pipe control valve 22.3 and the water outlet valve 22.6, and close the backwash control water inlet valve 22.4 and the backwash control water outlet valve 22.5 at the same time, the sewage from The raw water tank 1 is pumped into the MBR reaction pool 4, and purified by microorganisms distributed in the polyurethane sponge filler 5 and the mixed solution. The purified water passes through the ultrafiltration membrane module 10 and then pumped out. Under the combined effect of filtration, the sewage treatment efficiency is high and the treatment time is short. See Figure 2. During this process, the polyurethane sponge filler 5 is evenly suspended in the entire MBR reaction tank 4. Some microorganisms are suspended in the reactor, and some are in the polyurethane sponge filler. 5. If the microbial film is formed on the surface or adsorbed in the micropores of the filler, the diversified existence of microorganisms helps to improve the sewage treatment effect; most of the microorganisms are adsorbed on the surface of the filler or in the micropores, and the number of microorganisms suspended in the water is reduced, which is beneficial Membrane fouling is slowed down; there is anaerobic space inside the micropores of the filler, which is conducive to the large-scale reproduction of anaerobic microorganisms and makes the removal rate of total nitrogen high. The aeration tube is placed in the bottom tank. Under the action of aeration, the concentration of activated sludge in the entire reaction tank is uniform, there is no sludge sedimentation area or aeration dead angle, and the reaction system has high sewage treatment efficiency.

2、反冲洗操作:当压力表23的读数达到0.04~0.05MPa时,需要对超滤膜组件10进行反冲洗。反冲洗时,停止自动运行程序,将反冲洗的清水或添加了化学试剂的反冲洗水加入到清水箱20中,关闭连接管控制阀门22.3、出水阀门22.6,开启反冲洗控制进水阀门22.4和反冲洗控制出水阀门22.5,手动启动出水泵13,这时清水箱20内的水经过反冲洗控制进水阀门22.4、出水泵13、出水流量计16、反冲洗控制出水阀门22.5进入MBR反应池4内,实现对超滤膜组件10的反冲洗。 2. Backwashing operation: when the reading of the pressure gauge 23 reaches 0.04-0.05MPa, it is necessary to backwash the ultrafiltration membrane module 10 . When backwashing, stop the automatic operation program, add the backwashing water or the backwashing water with chemical reagents into the clean water tank 20, close the connecting pipe control valve 22.3, the water outlet valve 22.6, open the backwashing control water inlet valve 22.4 and Backwash control outlet valve 22.5, manual start water outlet pump 13, at this time the water in clean water tank 20 enters MBR reaction pool 4 through backwash control inlet valve 22.4, outlet pump 13, outlet water flow meter 16, backwash control outlet valve 22.5 Inside, the backwashing of the ultrafiltration membrane module 10 is realized.

Claims (7)

1. a novel film bioreactor device, include raw water box (1), MBR reaction tank (4), filtered water tank (20), be communicated with the water inlet pipe (2) of raw water box (1) and MBR reaction tank (4), be communicated with the pipe connecting (26) of MBR reaction tank (4) and filtered water tank (20), and be connected to the rising pipe (19) that filtered water tank (20) exports, described water inlet pipe (2) is provided with inlet valve (22.1) and intake pump (3), pipe connecting (26) is sequentially with pipe connecting by-pass valve control (22.3) by MBR reaction tank (4) to filtered water tank (20) direction, go out water pump (13) and magnetic valve (14), rising pipe (19) is provided with flowing water Valve (22.6), the bottom of described MBR reaction tank (4) be provided with shore pipe (21) and and the aeration tube (9) that is connected with gas blower (12), MBR reaction tank (4) inside is provided with hyperfiltration membrane assembly (10) and reaction tank liquidometer (11), it is characterized in that:
The top of described MBR reaction tank (4) is fixed with a horizontal cover net (7), bottom is provided with a horizontal compression net (6) moving up and down, filled polyurethane sponge filler (5) in MBR reaction tank (4) between horizontal compression net (6) and horizontal cover net (7), has the pre-opened hole (25) for being located at the hyperfiltration membrane assembly (10) between horizontal compression net (6) and horizontal cover net (7) and passing in the middle of the wire side of horizontal compression net (6).
2. novel film bioreactor device according to claim 1, it is characterized in that: described pipe connecting by-pass valve control (22.3) is communicated with filtered water tank (20) by counter-flushing pipeline one (17) with the pipe connecting (26) gone out between water pump (13), pipe connecting (26) between MBR reaction tank (4) with pipe connecting by-pass valve control (22.3) is communicated with the pipe connecting (26) between water flow meter (16) and magnetic valve (14) by counter-flushing pipeline two (18), described counter-flushing pipeline one (17) is provided with back flushing and controls inlet valve (22.4), counter-flushing pipeline two (18) is provided with back flushing and controls flowing water Valve (22.5).
3. novel film bioreactor device according to claim 1, is characterized in that: the particle size range of described polyurethane sponge filler (5) is 0.5 ~ 1.5cm, is spheroid, cubes or anomalistic object.
4. novel film bioreactor device according to claim 1, is characterized in that: the woven wire of described horizontal compression net (6) and horizontal cover net (7) to be aperture be 1 ~ 5mm.
5. novel film bioreactor device according to claim 1, is characterized in that: be provided with raw water box liquidometer (24) in described raw water box (1), and described raw water box liquidometer (24) is arranged at the bottom of raw water box (1), higher than water inlet pipe (2).
6. novel film bioreactor device according to claim 1, is characterized in that: described reaction tank liquidometer (11) comprises the water outlet liquidometer (11.3), high-water liquidometer (11.2) and the low-water level liquidometer (11.1) that reduce highly gradually.
7. novel film bioreactor device according to claim 1, is characterized in that: described hyperfiltration membrane assembly (10) is immersed in the PVDF hollow-fibre membrane in MBR reaction tank (4) interior liquid.
CN201420684787.3U 2014-11-17 2014-11-17 A kind of novel film bioreactor device Expired - Fee Related CN204281404U (en)

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Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105236568A (en) * 2015-08-07 2016-01-13 北京大学 Method for running anammox by utilizing microbial immobilization membrane bioreactor
CN106477722A (en) * 2016-12-21 2017-03-08 河海大学 A kind of combined film bioreactor and application thereof
CN109970263A (en) * 2018-03-02 2019-07-05 柏天劳有限公司 a purification device
CN110776092A (en) * 2019-11-16 2020-02-11 北京逸智联科技有限公司 An MBR membrane bioreactor
CN117247135A (en) * 2023-07-24 2023-12-19 福建海峡石墨烯产业技术研究院有限公司 Sewage treatment equipment and sewage treatment method
CN117466431A (en) * 2023-10-17 2024-01-30 天津市水利工程集团有限公司 Intelligent modularized rural domestic sewage membrane method integrated treatment device and method

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105236568A (en) * 2015-08-07 2016-01-13 北京大学 Method for running anammox by utilizing microbial immobilization membrane bioreactor
CN105236568B (en) * 2015-08-07 2017-06-16 北京大学 A kind of method that Anammox is run using microbial immobilized membrane bioreactor
CN106477722A (en) * 2016-12-21 2017-03-08 河海大学 A kind of combined film bioreactor and application thereof
CN109970263A (en) * 2018-03-02 2019-07-05 柏天劳有限公司 a purification device
CN109970263B (en) * 2018-03-02 2022-10-14 柏天劳有限公司 a purification device
CN110776092A (en) * 2019-11-16 2020-02-11 北京逸智联科技有限公司 An MBR membrane bioreactor
CN110776092B (en) * 2019-11-16 2020-10-23 威海启达机电科技有限公司 An MBR membrane bioreactor
CN117247135A (en) * 2023-07-24 2023-12-19 福建海峡石墨烯产业技术研究院有限公司 Sewage treatment equipment and sewage treatment method
CN117466431A (en) * 2023-10-17 2024-01-30 天津市水利工程集团有限公司 Intelligent modularized rural domestic sewage membrane method integrated treatment device and method

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