CN114573106A - Upflow type electric auxiliary anaerobic-aerobic coupling biomembrane reactor - Google Patents

Upflow type electric auxiliary anaerobic-aerobic coupling biomembrane reactor Download PDF

Info

Publication number
CN114573106A
CN114573106A CN202210289824.XA CN202210289824A CN114573106A CN 114573106 A CN114573106 A CN 114573106A CN 202210289824 A CN202210289824 A CN 202210289824A CN 114573106 A CN114573106 A CN 114573106A
Authority
CN
China
Prior art keywords
chamber
aerobic
air
anaerobic
support plate
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.)
Granted
Application number
CN202210289824.XA
Other languages
Chinese (zh)
Other versions
CN114573106B (en
Inventor
艾力江·努尔拉
张琼方
艾尼瓦尔·买买提
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Xinjiang University
Original Assignee
Xinjiang University
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Xinjiang University filed Critical Xinjiang University
Priority to CN202210289824.XA priority Critical patent/CN114573106B/en
Publication of CN114573106A publication Critical patent/CN114573106A/en
Application granted granted Critical
Publication of CN114573106B publication Critical patent/CN114573106B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/30Aerobic and anaerobic processes
    • C02F3/301Aerobic and anaerobic treatment in the same reactor
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2203/00Apparatus and plants for the biological treatment of water, waste water or sewage
    • C02F2203/006Apparatus and plants for the biological treatment of water, waste water or sewage details of construction, e.g. specially adapted seals, modules, connections
    • 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

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Microbiology (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Biological Treatment Of Waste Water (AREA)
  • Apparatus Associated With Microorganisms And Enzymes (AREA)

Abstract

The invention discloses an upflow type electrically-assisted anaerobic-aerobic coupled biofilm reactor, which comprises a reaction pipe, wherein the reaction pipe is sequentially provided with an anaerobic chamber, an aeration chamber and an aerobic chamber from bottom to top, the liquid outlet end of the anaerobic chamber is communicated with the liquid inlet end of the aerobic chamber through the aeration chamber, an air supply part is arranged in the aeration chamber and comprises an air supply piece and an air injection piece, the air supply piece is positioned below the air injection piece and communicated with the air injection piece, the air outlet end of the aeration chamber is communicated with the air inlet end of the aerobic chamber through the air injection piece, and the air supply piece is in transmission connection with the air injection piece through a rotating rod; and the carrier part is arranged in the aerobic chamber and comprises a carrier frame. The invention can realize the problems of membrane pollution and cavity blockage caused by filler stacking in the aerobic chamber, simultaneously improve the biodegradability of the anaerobic chamber and the aerobic chamber, improve the aeration effect of the aerobic chamber, reduce the quantity of oxygen entering the anaerobic chamber and further improve the reaction rate of the reactor.

Description

一种升流式电辅助厌氧-好氧耦合生物膜反应器An Upflow Electric-Assisted Anaerobic-Aerobic Coupled Biofilm Reactor

技术领域technical field

本发明涉及污水处理技术领域,特别是涉及一种升流式电辅助厌氧-好氧耦合生物膜反应器。The invention relates to the technical field of sewage treatment, in particular to an up-flow electric-assisted anaerobic-aerobic coupled biofilm reactor.

背景技术Background technique

近年来,个人护理产品作为一种新出现的污染物被广泛研究。然而,由于高消耗和稳定的化学结构,经常在污水处理厂、地表水和地下水中被检测到,尽管它们的浓度很低,但仍会对水环境和生态平衡产生负面影响,甚至造成饮用水的污染。传统污水处理对有机物的去除方法主要有活性污泥法和生物膜法等生物处理技术,然而制药废水中的残存药物会抑制传统生物方法中微生物的生长及活性,影响污水中有机物的去除效果。另一方面,单纯的好氧或厌氧系统无法实现有机物的完全降解,需要将好氧和厌氧生物反应器结合起来。然而,由于这些药物的化学结构稳定,它们在微生物降解中的去除效率似乎仍无法令人满意,因此有必要开发新的方法来改善废水中有机物的去除。In recent years, personal care products have been extensively studied as an emerging pollutant. However, due to high consumption and stable chemical structure, they are often detected in sewage treatment plants, surface water and groundwater, and despite their low concentrations, they can still negatively affect the water environment and ecological balance, and even cause drinking water pollution. Traditional wastewater treatment methods for the removal of organic matter mainly include biological treatment technologies such as activated sludge method and biofilm method. However, residual drugs in pharmaceutical wastewater will inhibit the growth and activity of microorganisms in traditional biological methods, and affect the removal of organic matter in wastewater. On the other hand, pure aerobic or anaerobic systems cannot achieve complete degradation of organic matter, and a combination of aerobic and anaerobic bioreactors is required. However, due to the stable chemical structure of these drugs, their removal efficiency in microbial degradation still seems unsatisfactory, so it is necessary to develop new methods to improve the removal of organics from wastewater.

生物电化学反应器(BERs)是由微生物、电极和污染物三者相互作用组成的系统,由于生物催化剂相对于现有化学催化剂具有更高的催化效率与特异性,附着在电极上的微生物能够加快电极与污染物之间的电子转移,从而加快污染物的降解。其基本原理是使电极与微生物产生协同效应,通过电刺激的手段,提高微生物对外界环境压力的抗性,以提高对具有生物毒性的难降解污染物的代谢活性,并通过加快电子的转移对功能微生物进行富集、以改善微生物群落结构,进而提高难降解污染物的去除效果。由于具有这些特点,近年来生物电化学反应器受到了全球学者的广泛关注,其运行的性能也得到了提升。其中生物电化学厌氧好氧耦合反应器(AO-UBERs)最具有实用潜力。Bioelectrochemical reactors (BERs) are systems composed of interactions between microorganisms, electrodes and pollutants. Since biocatalysts have higher catalytic efficiency and specificity than existing chemical catalysts, microorganisms attached to electrodes can Accelerates the electron transfer between the electrode and the contaminant, thereby accelerating the degradation of the contaminant. The basic principle is to make the electrode and the microorganism produce a synergistic effect, and to improve the resistance of the microorganism to the external environmental pressure by means of electrical stimulation, so as to improve the metabolic activity of the biotoxic refractory pollutants, and to accelerate the transfer of electrons. Functional microorganisms are enriched to improve the microbial community structure, thereby improving the removal effect of refractory pollutants. Due to these characteristics, bioelectrochemical reactors have received extensive attention from scholars around the world in recent years, and their operating performance has also been improved. Among them, bioelectrochemical anaerobic-aerobic coupled reactors (AO-UBERs) have the most practical potential.

然而,传统生物电化学厌氧好氧耦合系统也具有一些缺点,首先,其好氧区微生物生长较快,导致膜污染和腔体堵塞,需要频繁对好氧区进行清理,以保证系统的正常使用,其次,现有系统无法对污水中的复杂有机物进行去除,进而影响了污水处理效果。除此之外,现有技术中对好氧区的曝气效果较差,同时,由于结构问题等因素,当好氧区进行曝气处理时,氧气容易进入厌氧区内,进而导致厌氧区不能正常对废水进行处理,因此亟待一种升流式电辅助厌氧-好氧耦合生物膜反应器,以解决上述问题。However, the traditional bioelectrochemical anaerobic-aerobic coupling system also has some disadvantages. First, the microorganisms in the aerobic zone grow rapidly, which leads to membrane fouling and clogging of the cavity. Frequent cleaning of the aerobic zone is required to ensure the normal operation of the system. Second, the existing system cannot remove the complex organic matter in the sewage, which affects the effect of sewage treatment. In addition, the aeration effect of the aerobic zone in the prior art is poor. At the same time, due to structural problems and other factors, when the aerobic zone is aerated, oxygen easily enters the anaerobic zone, which in turn leads to anaerobic conditions. Therefore, an up-flow electric-assisted anaerobic-aerobic coupled biofilm reactor is urgently needed to solve the above problems.

发明内容SUMMARY OF THE INVENTION

本发明的目的是提供一种升流式电辅助厌氧-好氧耦合生物膜反应器,以解决上述现有技术存在的问题,能够实现好氧室由于填料堆叠导致的膜污染和腔体堵塞问题,同时提高厌氧室和好氧室的生物降解能力,此外,提高好氧室的曝气效果,并降低氧气进入厌氧室的数量,进而提高反应器的反应速率。The purpose of the present invention is to provide an up-flow electric-assisted anaerobic-aerobic coupled biofilm reactor to solve the above-mentioned problems in the prior art, and to realize membrane fouling and cavity blockage caused by packing stacking in the aerobic chamber At the same time, the biodegradability of the anaerobic chamber and the aerobic chamber is improved, in addition, the aeration effect of the aerobic chamber is improved, and the amount of oxygen entering the anaerobic chamber is reduced, thereby increasing the reaction rate of the reactor.

为实现上述目的,本发明提供了如下方案:本发明提供一种升流式电辅助厌氧-好氧耦合生物膜反应器,包括反应管,所述反应管由上至下依次设置有厌氧室、曝气室、好氧室,所述厌氧室出液端通过所述曝气室与所述好氧室进液端连通,In order to achieve the above object, the present invention provides the following solution: the present invention provides an up-flow electric-assisted anaerobic-aerobic coupled biofilm reactor, comprising a reaction tube, and the reaction tube is sequentially provided with an anaerobic reactor from top to bottom chamber, aeration chamber, and aerobic chamber, the liquid outlet end of the anaerobic chamber is communicated with the liquid inlet end of the aerobic chamber through the aeration chamber,

供气部,设置在曝气室内,所述供气部包括供气件和喷气件,所述供气件位于所述喷气件下方,且所述供气件与所述喷气件连通,所述曝气室出气端通过所述喷气件与所述好氧室进气端连通,所述供气件通过转杆与所述喷气件传动连接;The air supply part is arranged in the aeration chamber, the air supply part includes an air supply part and an air injection part, the air supply part is located under the air injection part, and the air supply part is communicated with the air injection part, and the air supply part is in communication with the air injection part. The air outlet end of the aeration chamber is communicated with the air inlet end of the aerobic chamber through the air blowing part, and the air supply part is drivingly connected with the air blowing part through a rotating rod;

载体部,设置在所述好氧室内,所述载体部包括载体架,所述载体架分别与所述反应管和所述转杆可拆卸连接,所述厌氧室内设置有若干载体块;The carrier part is arranged in the aerobic chamber, the carrier part includes a carrier frame, the carrier frame is detachably connected with the reaction tube and the rotating rod, and a plurality of carrier blocks are arranged in the anaerobic chamber;

供电部,设置在所述反应管外,所述供电部阳极与所述好氧室电性连接,所述供电部阴极与所述厌氧室电性连接。The power supply part is arranged outside the reaction tube, the anode of the power supply part is electrically connected to the aerobic chamber, and the cathode of the power supply part is electrically connected to the anaerobic chamber.

优选的,所述反应管内壁固接的第一支板和第二支板,所述第一支板位于所述第二支板上方,所述曝气室通过所述第一支板和所述第二支板与所述厌氧室和所述好氧室分隔,所述供气件包括与所述第二支板顶端固接的供气盒,所述供气盒内设置有旋转叶片,所述转杆穿过所述供气盒和所述旋转叶片,且所述转杆与所述供气盒转动连接,所述转杆与所述旋转叶片固接,所述供气盒侧壁连通有进氧管,所述供气盒顶端与所述喷气件连通。Preferably, the first support plate and the second support plate are fixedly connected to the inner wall of the reaction tube, the first support plate is located above the second support plate, and the aeration chamber passes through the first support plate and the second support plate. The second support plate is separated from the anaerobic chamber and the aerobic chamber, the air supply member comprises an air supply box fixedly connected with the top of the second support plate, and a rotating blade is arranged in the air supply box , the rotating rod passes through the air supply box and the rotating blade, and the rotating rod is rotatably connected with the air supply box, the rotating rod is fixedly connected with the rotating blade, and the air supply box side An oxygen inlet pipe is communicated with the wall, and the top end of the air supply box is communicated with the air jet.

优选的,所述旋转叶片侧壁上固接有若干尖端凸起,所述尖端凸起与所述进氧管出气端对应设置。Preferably, a plurality of pointed protrusions are fixed on the side wall of the rotating blade, and the pointed protrusions are arranged corresponding to the gas outlet end of the oxygen inlet pipe.

优选的,所述喷气件包括与所述第二支板顶端固接的喷筒,所述供气盒位于所述喷筒内,所述喷筒内壁固接有第一气石,所述供气盒通过连通管与所述第一气石连通,所述喷筒出气端设置有第二气石,所述第二气石贯穿所述第一支板,且所述第二气石与所述转杆固接,所述第二气石与所述第一支板转动连接。Preferably, the air blowing member includes a spray cylinder fixedly connected to the top of the second support plate, the air supply box is located in the spray cylinder, the inner wall of the spray cylinder is fixed with a first air stone, and the air supply box is located in the spray cylinder. The air box is communicated with the first air stone through a communication pipe, the air outlet end of the spray cylinder is provided with a second air stone, the second air stone penetrates through the first support plate, and the second air stone is connected to the second air stone. The rotating rod is fixedly connected, and the second air stone is rotatably connected with the first support plate.

优选的,所述第二气石孔径小于所述第一气石孔径,且所述第二气石出气口倾斜设置。Preferably, the aperture of the second air stone is smaller than the aperture of the first air stone, and the gas outlet of the second air stone is inclined.

优选的,所述喷筒为圆台型结构,且所述喷筒靠近所述第一支板的端部直径小于所述喷筒靠近所述第二支板的端部直径。Preferably, the spray cylinder is of a circular truncated structure, and the diameter of the end portion of the spray cylinder close to the first support plate is smaller than the diameter of the end portion of the spray cylinder close to the second support plate.

优选的,所述好氧室上方连通有溢流室,所述溢流室连通有溢流管,所述好氧室与所述溢流室通过第三支板分隔,所述第三支板上开设有阶梯型通槽,所述阶梯型通槽内设置与其相匹配的阶梯板,所述载体架套设在所述转杆上,且所述阶梯板与所述转杆顶端可拆卸连接。Preferably, an overflow chamber is communicated above the aerobic chamber, an overflow pipe is communicated with the overflow chamber, and the aerobic chamber and the overflow chamber are separated by a third support plate, and the third support plate There is a stepped through groove on the upper part, a matching stepped plate is arranged in the stepped through groove, the carrier frame is sleeved on the rotating rod, and the stepped plate is detachably connected with the top of the rotating rod .

优选的,所述转杆底端贯穿第二支板伸入所述厌氧室内,所述转杆与所述第二支板转动连接,所述转杆上固接有若干搅拌板,若干所述搅拌板均位于所述厌氧室内。Preferably, the bottom end of the rotating rod penetrates the second support plate and extends into the anaerobic chamber, the rotating rod is rotatably connected with the second support plate, and a plurality of stirring plates are fixed on the rotating rod. The stirring plates are all located in the anaerobic chamber.

优选的,所述供电部包括电源,所述好氧室和所述厌氧室分别通过导电板与所述电源电性连接,所述电源阳极与位于所述好氧室的导电板电性连接,所述电源阴极与位于所述厌氧室的导电板电性连接。Preferably, the power supply unit includes a power source, the aerobic chamber and the anaerobic chamber are respectively electrically connected to the power source through a conductive plate, and the power supply anode is electrically connected to the conductive plate located in the aerobic chamber. , the power supply cathode is electrically connected to the conductive plate located in the anaerobic chamber.

优选的,所述第一支板、所述第二支板、所述第三支板上分别开设有供废液流通的流通口,且所述第二支板上的流通口内固接有筛网。Preferably, the first support plate, the second support plate, and the third support plate are respectively provided with flow ports for the circulation of waste liquid, and the flow ports on the second support plate are fixed with sieves. network.

本发明公开了以下技术效果:The present invention discloses the following technical effects:

1.在好氧室内设置载体架,相对于现有的填料来说,载体架不会出现填料填料堆叠的情况,从而不会导致膜污染和腔体堵塞问题,且载体架更换方便,实用性高,此外由于载体块的存在,提高厌氧室的生物降解能力,两者配合最终提高反应器对废水的净化效果。1. The carrier frame is set in the aerobic chamber. Compared with the existing fillers, the carrier frame will not be stacked with fillers, so as not to cause membrane pollution and cavity blockage problems, and the carrier frame is easy to replace and practical. In addition, due to the existence of the carrier block, the biodegradation capacity of the anaerobic chamber is improved, and the combination of the two finally improves the purification effect of the reactor on the wastewater.

2.供气件将外部供给氧气进行初次剪切,随后经过喷气件进行再次剪切,使得气泡变小,进而提高曝气效果,同时,供气件可带动转杆转动,而转杆可带动载体架转动,使得载体架搅拌好氧室内的废水,提高废水与微生物的混合效果,从而提高好氧室的净化效果。2. The air supply part cuts the oxygen supplied from the outside for the first time, and then cuts it again through the air jet part to make the air bubbles smaller, thereby improving the aeration effect. At the same time, the air supply part can drive the rotating rod to rotate, and the rotating rod can drive The rotation of the carrier frame enables the carrier frame to stir the wastewater in the aerobic chamber to improve the mixing effect of wastewater and microorganisms, thereby improving the purification effect of the aerobic chamber.

3.通过设置喷气件,一方面使得被多次剪切的气泡较为容易的进入好氧室内,同时,使得气泡不易进入厌氧室内,从而提高好氧室和眼厌氧室微生物的生存环境。3. By setting the air jet, on the one hand, the air bubbles that have been sheared many times can easily enter the aerobic chamber, and at the same time, it is difficult for the air bubbles to enter the anaerobic chamber, thereby improving the living environment of microorganisms in the aerobic chamber and the anaerobic chamber.

附图说明Description of drawings

为了更清楚地说明本发明实施例或现有技术中的技术方案,下面将对实施例中所需要使用的附图作简单地介绍,显而易见地,下面描述中的附图仅仅是本发明的一些实施例,对于本领域普通技术人员来讲,在不付出创造性劳动性的前提下,还可以根据这些附图获得其他的附图。In order to more clearly illustrate the embodiments of the present invention or the technical solutions in the prior art, the accompanying drawings required in the embodiments will be briefly introduced below. Obviously, the drawings in the following description are only some of the present invention. In the embodiments, for those of ordinary skill in the art, other drawings can also be obtained according to these drawings without creative labor.

图1为反应器的结构示意图;Fig. 1 is the structural representation of reactor;

图2为图1中A处的局部放大图;Fig. 2 is the partial enlarged view of A place in Fig. 1;

图3为图1中B处的局部放大图;Fig. 3 is a partial enlarged view at B in Fig. 1;

图4为图1中C处的局部放大图;Fig. 4 is a partial enlarged view at C in Fig. 1;

图5为供气部的立体图;Fig. 5 is the perspective view of the gas supply part;

其中,1-反应管,2-厌氧室,3-曝气室,4-好氧室,5-转杆,6-载体架,7-第一支板,8-第二支板,9-供气盒,10-旋转叶片,11-进氧管,12-尖端凸起,13-喷筒,14-第一气石,15-第二气石,16-溢流室,17-溢流管,18-第三支板,19-阶梯板,20-搅拌板,21-电源,22-导电板,23-筛网,24-流通口,25-出液管,26-进液管,27-供气箱,28-单向阀,29-固定螺栓。Among them, 1-reaction tube, 2-anaerobic chamber, 3-aeration chamber, 4-aerobic chamber, 5-rotating rod, 6-carrier rack, 7-first support plate, 8-second support plate, 9 -Air supply box, 10-rotating vane, 11-oxygen inlet pipe, 12-tip protrusion, 13-spray barrel, 14-first airstone, 15-second airstone, 16-overflow chamber, 17-overflow Flow tube, 18-third support plate, 19-step plate, 20-stirring plate, 21-power supply, 22-conductive plate, 23-screen, 24-flow port, 25-liquid outlet pipe, 26-liquid inlet pipe , 27- air supply box, 28- one-way valve, 29- fixing bolt.

具体实施方式Detailed ways

下面将结合本发明实施例中的附图,对本发明实施例中的技术方案进行清楚、完整地描述,显然,所描述的实施例仅仅是本发明一部分实施例,而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员在没有做出创造性劳动前提下所获得的所有其他实施例,都属于本发明保护的范围。The technical solutions in the embodiments of the present invention will be clearly and completely described below with reference to the accompanying drawings in the embodiments of the present invention. Obviously, the described embodiments are only a part of the embodiments of the present invention, but not all of the embodiments. Based on the embodiments of the present invention, all other embodiments obtained by those of ordinary skill in the art without creative efforts shall fall within the protection scope of the present invention.

为使本发明的上述目的、特征和优点能够更加明显易懂,下面结合附图和具体实施方式对本发明作进一步详细的说明。In order to make the above objects, features and advantages of the present invention more clearly understood, the present invention will be described in further detail below with reference to the accompanying drawings and specific embodiments.

本发明提供一种升流式电辅助厌氧-好氧耦合生物膜反应器,包括反应管1,反应管1由上至下依次设置有厌氧室2、曝气室3、好氧室4,厌氧室2出液端通过曝气室3与好氧室4进液端连通,供气部,设置在曝气室3内,供气部包括供气件和喷气件,供气件位于喷气件下方,且供气件与喷气件连通,曝气室3出气端通过喷气件与好氧室4进气端连通,供气件通过转杆5与喷气件传动连接;载体部,设置在好氧室4内,载体部包括载体架6,载体架6分别与反应管1和转杆5可拆卸连接,厌氧室2内设置有若干载体块;供电部,设置在反应管1外,供电部阳极与好氧室4电性连接,供电部阴极与厌氧室2电性连接。The present invention provides an up-flow electric-assisted anaerobic-aerobic coupled biofilm reactor, comprising a reaction tube 1, and the reaction tube 1 is provided with an anaerobic chamber 2, an aeration chamber 3, and an aerobic chamber 4 in sequence from top to bottom , the liquid outlet end of the anaerobic chamber 2 is communicated with the liquid inlet end of the aerobic chamber 4 through the aeration chamber 3, and the air supply part is arranged in the aeration chamber 3. The air supply part includes an air supply part and an air injection part, and the air supply part is located in Below the jet part, and the air supply part is communicated with the air jet part, the air outlet end of the aeration chamber 3 is communicated with the air inlet end of the aerobic chamber 4 through the air jet part, and the air supply part is driven and connected with the air jet part through the rotating rod 5; the carrier part is arranged on the In the aerobic chamber 4, the carrier part includes a carrier frame 6, and the carrier frame 6 is detachably connected with the reaction tube 1 and the rotating rod 5 respectively, and several carrier blocks are arranged in the anaerobic chamber 2; the power supply part is arranged outside the reaction tube 1, The anode of the power supply part is electrically connected to the aerobic chamber 4 , and the cathode of the power supply part is electrically connected to the anaerobic chamber 2 .

废液由下至上依次经过厌氧室2、曝气室3、好氧室4,当对好氧室4进行曝气处理时,供气件启动,向曝气室3内提供氧气,氧气经过供气件初次剪切后进入喷气件,最终由喷气件进入好氧室4内,在供气件工作时,供气件带动转杆5旋转,转杆5带动载体架6旋转,从而对好氧室4内的废液进行缓慢搅拌,同时由于载体架6旋转,使其不易被污染。而供电部进行供电,以使得微生物富集。The waste liquid passes through the anaerobic chamber 2, the aeration chamber 3, and the aerobic chamber 4 in sequence from bottom to top. When the aerobic chamber 4 is aerated, the gas supply is started to provide oxygen into the aeration chamber 3, and the oxygen passes through the aeration chamber 4. The air supply part enters the air-jet part after the initial shearing, and finally enters the aerobic chamber 4 by the air-injection part. When the air-supply part works, the air-supply part drives the rotating rod 5 to rotate, and the rotating rod 5 drives the carrier frame 6 to rotate. The waste liquid in the oxygen chamber 4 is slowly stirred, and at the same time, due to the rotation of the carrier frame 6, it is not easily contaminated. The power supply unit supplies power to enrich the microorganisms.

上述运行过程中采用实际制药废水或者城市污水,运行方式为升流式。即污水先进入厌氧室2(水力停留时间为24h),实现有机物的初步去除。经过中部曝气室3为好氧室4维持好氧环境,有机物下一步进水好氧室4,实现有机物的深度去除,难降解有机物的降解,含氮物质的硝化反硝化作用以及除磷的作用,实现污水的深度处理。In the above operation process, actual pharmaceutical wastewater or urban sewage is used, and the operation mode is upflow. That is, the sewage first enters the anaerobic chamber 2 (the hydraulic retention time is 24h) to realize the preliminary removal of organic matter. After the middle aeration chamber 3 is the aerobic chamber 4 to maintain the aerobic environment, the organic matter enters the water aerobic chamber 4 in the next step to realize the deep removal of organic matter, degradation of refractory organic matter, nitrification and denitrification of nitrogenous substances and phosphorus removal. function to achieve advanced treatment of sewage.

本发明的一个实施例中,好氧室4连通有出液管25,从而将符合排放要求的废液排出,厌氧室2连通有进液管26,从而将废液导入厌氧室2内。In one embodiment of the present invention, the aerobic chamber 4 is connected with a liquid outlet pipe 25 so as to discharge the waste liquid that meets the discharge requirements, and the anaerobic chamber 2 is connected with a liquid inlet pipe 26 so as to introduce the waste liquid into the anaerobic chamber 2 .

本发明的一个实施例中,载体块优选但不限于为导电生物膜载体碳毡小块,其上附着阴极厌氧发酵微生物,以实现有机物的初步降解,其碳毡小块填料粒度大小优选为1cm-2cm。In an embodiment of the present invention, the carrier block is preferably, but not limited to, a small piece of conductive biofilm carrier carbon felt, on which is attached cathodic anaerobic fermentation microorganisms to achieve preliminary degradation of organic matter, and the particle size of the small piece of carbon felt filler is preferably 1cm-2cm.

本发明的一个实施例中,载体架6优选但不限于为导电生物膜载体碳刷,其上附着有阳极好氧微生物,以实现对有机物的氧化降解。In an embodiment of the present invention, the carrier frame 6 is preferably, but not limited to, a conductive biofilm carrier carbon brush, on which an aerobic microorganism is attached to achieve oxidative degradation of organic matter.

进一步优化方案,反应管1内壁固接的第一支板7和第二支板8,第一支板7位于第二支板8上方,曝气室3通过第一支板7和第二支板8与厌氧室2和好氧室4分隔,供气件包括与第二支板8顶端固接的供气盒9,供气盒9内设置有旋转叶片10,转杆5穿过供气盒9和旋转叶片10,且转杆5与供气盒9转动连接,转杆5与旋转叶片10固接,供气盒9侧壁连通有进氧管11,供气盒9顶端与喷气件连通。第一支板7和第二支板8起到分隔作用,外部氧气由进氧管11导入供气盒9内,并击打在旋转叶片10上,使得旋转叶片10转动,随后氧气通过供气盒9顶端进入喷气件内。而旋转叶片10转动,带动转杆5旋转,从而使其可以带动载体架6旋转。To further optimize the scheme, the first support plate 7 and the second support plate 8 are fixedly connected to the inner wall of the reaction tube 1, the first support plate 7 is located above the second support plate 8, and the aeration chamber 3 passes through the first support plate 7 and the second support plate 8. The plate 8 is separated from the anaerobic chamber 2 and the aerobic chamber 4. The air supply member includes an air supply box 9 fixedly connected to the top of the second support plate 8. The air supply box 9 is provided with a rotating blade 10, and the rotating rod 5 passes through the air supply box 9. The air box 9 and the rotating blade 10, and the rotating rod 5 is rotatably connected with the air supply box 9, the rotating rod 5 is fixedly connected with the rotating blade 10, the oxygen inlet pipe 11 is communicated with the side wall of the air supply box 9, and the top of the air supply box 9 is connected to the air jet. Pieces are connected. The first support plate 7 and the second support plate 8 play a role of separation. The external oxygen is introduced into the air supply box 9 through the oxygen inlet pipe 11, and hits the rotating blade 10, so that the rotating blade 10 rotates, and then the oxygen passes through the air supply. The top of the box 9 enters the air jet. The rotation of the rotating blade 10 drives the rotating rod 5 to rotate, so that it can drive the carrier frame 6 to rotate.

本发明的一个实施例中,反应管1外设置用于提供氧气的供气箱27,供气箱27通过进氧管11与供气盒9连通。In an embodiment of the present invention, an air supply box 27 for supplying oxygen is provided outside the reaction tube 1 , and the air supply box 27 communicates with the air supply box 9 through the oxygen inlet pipe 11 .

本发明的另一实施例中,供气盒9上连通有两进氧管11,两进氧管11分别穿过反应管1与供气箱27连通,一进氧管11使旋转叶片10顺时针转动,另一进氧管11使旋转叶片10逆时针转动,两进氧管11上均设置有单向阀28。将进氧管11设置两个,根据两进氧管11的位置不同,因此可以向旋转叶片10不同位置喷气,使得旋转叶片10既可以顺时针旋转又可以逆时针旋转,其目的是使得载体架6既可以顺时针旋转又可以逆时针旋转,进而提高对废水与微生物的混合效果。而单向阀28的存在,使得一进氧管11工作时,氧气不会由另一进氧管11回流。In another embodiment of the present invention, two oxygen inlet pipes 11 are connected to the gas supply box 9, and the two oxygen inlet pipes 11 respectively pass through the reaction tube 1 and communicate with the gas supply box 27. Clockwise rotation, the other oxygen inlet pipe 11 makes the rotating blade 10 rotate counterclockwise, and a one-way valve 28 is provided on both oxygen inlet pipes 11 . Two oxygen inlet pipes 11 are arranged. According to the different positions of the two oxygen inlet pipes 11, the air can be jetted to different positions of the rotating blade 10, so that the rotating blade 10 can rotate clockwise and counterclockwise. The purpose is to make the carrier frame 6 It can be rotated both clockwise and counterclockwise, thereby improving the mixing effect of wastewater and microorganisms. The existence of the one-way valve 28 ensures that when one oxygen inlet pipe 11 is working, oxygen will not flow back from the other oxygen inlet pipe 11 .

进一步优化方案,旋转叶片10侧壁上固接有若干尖端凸起12,尖端凸起12与进氧管11出气端对应设置。尖端凸起12与氧气泡初步接触,进而对氧气泡进行初步剪切,以提高对好氧室4的曝气效果。In a further optimized solution, a plurality of tip projections 12 are fixedly connected to the side wall of the rotating blade 10 , and the tip projections 12 are arranged corresponding to the gas outlet end of the oxygen inlet pipe 11 . The tip protrusion 12 is in preliminary contact with the oxygen bubbles, and then the oxygen bubbles are preliminarily sheared, so as to improve the aeration effect of the aerobic chamber 4 .

进一步优化方案,喷气件包括与第二支板8顶端固接的喷筒13,供气盒9位于喷筒13内,喷筒13内壁固接有第一气石14,供气盒9通过连通管与第一气石14连通,喷筒13出气端设置有第二气石15,第二气石15贯穿第一支板7,且第二气石15与转杆5固接,第二气石15与第一支板7转动连接。由供气盒9排出的氧气经过连通管进入第一气石14,第一气石14对氧气泡进一步剪切,从而减小氧气泡直径。而进一步减小的氧气泡经过第二气石15导入好氧室4内。To further optimize the solution, the air jet includes a spray cylinder 13 fixedly connected to the top of the second support plate 8, the air supply box 9 is located in the spray cylinder 13, the inner wall of the spray cylinder 13 is fixed with a first air stone 14, and the air supply box 9 communicates through The pipe is communicated with the first air stone 14, the air outlet end of the spray cylinder 13 is provided with a second air stone 15, the second air stone 15 penetrates the first support plate 7, and the second air stone 15 is fixedly connected with the rotating rod 5, and the second air stone 15 is connected with the rotating rod 5. The stone 15 is rotatably connected to the first support plate 7 . The oxygen discharged from the air supply box 9 enters the first air stone 14 through the communication pipe, and the first air stone 14 further shears the oxygen bubbles, thereby reducing the diameter of the oxygen bubbles. The further reduced oxygen bubbles are introduced into the aerobic chamber 4 through the second air stone 15 .

进一步优化方案,第二气石15孔径小于第一气石14孔径,且第二气石15出气口倾斜设置。为了再次减小氧气泡直径,第二气石15的孔径比第一气石14孔径小,而由于第二气石15跟随转杆5共同转动,以及第二气石15出气口倾斜设置,使得由第二气石15排出的氧气泡可以较为均匀的甩入好氧室4内,从而提高好氧室4的曝气效果。In a further optimization scheme, the aperture of the second air stone 15 is smaller than the aperture of the first air stone 14 , and the air outlet of the second air stone 15 is inclined. In order to reduce the diameter of the oxygen bubbles again, the aperture of the second air stone 15 is smaller than that of the first air stone 14. Since the second air stone 15 rotates together with the rotating rod 5 and the air outlet of the second air stone 15 is inclined, so that the The oxygen bubbles discharged from the second air stone 15 can be thrown into the aerobic chamber 4 evenly, thereby improving the aeration effect of the aerobic chamber 4 .

此外,第二气石15的倾斜角度和倾斜方向可以根据实际使用设置,可以通过更换不同型号的第二气石15,以提高曝气效果。In addition, the inclination angle and inclination direction of the second air stone 15 can be set according to actual use, and the aeration effect can be improved by replacing the second air stone 15 of different models.

进一步优化方案,喷筒13为圆台型结构,且喷筒13靠近第一支板7的端部直径小于喷筒13靠近第二支板8的端部直径。喷筒13的底端与第二支板8固定,其顶端又通过第二气石15与好氧室4连通,因此气泡不易离开喷筒13进入曝气室3内,而喷筒13圆台型结构设置,进一步可以防止氧气泡进入厌氧室2,从而提高厌氧室2的反应速率。In a further optimized solution, the spray barrel 13 has a circular truncated structure, and the diameter of the end of the spray barrel 13 near the first support plate 7 is smaller than the diameter of the end of the spray barrel 13 near the second support plate 8 . The bottom end of the spray cylinder 13 is fixed with the second support plate 8, and its top is communicated with the aerobic chamber 4 through the second air stone 15, so the air bubbles are not easy to leave the spray cylinder 13 and enter the aeration chamber 3, and the spray cylinder 13 is circular truncated. The structural arrangement can further prevent oxygen bubbles from entering the anaerobic chamber 2 , thereby increasing the reaction rate of the anaerobic chamber 2 .

进一步优化方案,好氧室4上方连通有溢流室16,溢流室16连通有溢流管17,好氧室4与溢流室16通过第三支板18分隔,第三支板18上开设有阶梯型通槽,阶梯型通槽内设置与其相匹配的阶梯板19,载体架6套设在转杆5上,且阶梯板19与转杆5顶端可拆卸连接。溢流室16的存在可以防止好氧室4溢流,而在第三支板18上设置阶梯板19,使其可以对载体架6进行固定。当需要安装载体架6时,将载体架6安装在阶梯板19底端,随后将阶梯板19放入阶梯型通槽内,通过阶梯型通槽对阶梯板19进行限位,同时,将载体架6套设在转杆5上,待阶梯板19定位完毕后,通过多根固定螺栓29分别对阶梯板19与第三支板18、阶梯板19与转杆5进行固定To further optimize the solution, an overflow chamber 16 is connected to the top of the aerobic chamber 4, an overflow pipe 17 is connected to the overflow chamber 16, and the aerobic chamber 4 and the overflow chamber 16 are separated by a third support plate 18, and the third support plate 18 is separated. A stepped through groove is provided, and a matching stepped plate 19 is arranged in the stepped through groove. The existence of the overflow chamber 16 can prevent the aerobic chamber 4 from overflowing, and a stepped plate 19 is provided on the third support plate 18 so that the carrier frame 6 can be fixed. When the carrier frame 6 needs to be installed, install the carrier frame 6 on the bottom end of the stepped plate 19, then put the stepped plate 19 into the stepped through groove, and limit the stepped plate 19 through the stepped through groove. The frame 6 is sleeved on the rotating rod 5. After the positioning of the stepped plate 19 is completed, the stepped plate 19 and the third supporting plate 18, the stepped plate 19 and the rotating rod 5 are respectively fixed by a plurality of fixing bolts 29.

进一步优化方案,转杆5底端贯穿第二支板8伸入厌氧室2内,转杆5与第二支板8转动连接,转杆5上固接有若干搅拌板20,若干搅拌板20均位于厌氧室2内。转杆5带动搅拌板20在厌氧室2内转动,使得搅拌板20搅拌厌氧室2内的废液,从而提高废液与微生物的混合效果。To further optimize the solution, the bottom end of the rotating rod 5 penetrates the second support plate 8 and extends into the anaerobic chamber 2, the rotating rod 5 is rotatably connected with the second support plate 8, and several stirring plates 20 are fixed on the rotating rod 5. 20 are located in the anaerobic chamber 2. The rotating rod 5 drives the stirring plate 20 to rotate in the anaerobic chamber 2, so that the stirring plate 20 stirs the waste liquid in the anaerobic chamber 2, thereby improving the mixing effect of the waste liquid and the microorganisms.

进一步优化方案,供电部包括电源21,好氧室4和厌氧室2分别通过导电板22与电源21电性连接,电源21阳极与位于好氧室4的导电板22电性连接,电源21阴极与位于厌氧室2的导电板22电性连接。在电源21的作用下形成闭合回路,进水从下往上,经过厌氧室2初步降解,于好氧室4进一步矿化。运行过程中有机物在厌氧室2和好氧室4被高效去除。To further optimize the scheme, the power supply part includes a power supply 21, the aerobic chamber 4 and the anaerobic chamber 2 are respectively electrically connected to the power supply 21 through the conductive plate 22, the anode of the power supply 21 is electrically connected to the conductive plate 22 located in the aerobic chamber 4, and the power supply 21 The cathode is electrically connected to the conductive plate 22 located in the anaerobic chamber 2 . A closed loop is formed under the action of the power source 21 , and the influent water is initially degraded from the bottom to the top through the anaerobic chamber 2 , and further mineralized in the aerobic chamber 4 . During operation, organic matter is efficiently removed in the anaerobic chamber 2 and the aerobic chamber 4.

本发明的一个实施例中,导电板22优选但不限于为钛片,以对厌氧室2和好氧室4进行分别供电。In one embodiment of the present invention, the conductive plate 22 is preferably, but not limited to, a titanium sheet, so as to supply power to the anaerobic chamber 2 and the aerobic chamber 4 respectively.

进一步优化方案,第一支板7、第二支板8、第三支板18上分别开设有供废液流通的流通口24,且第二支板8上的流通口24内固接有筛网23。流通口24的存在是便于废液流动,而筛网23的存在,使得厌氧室2内的载体块无法进入曝气室3内。To further optimize the solution, the first support plate 7, the second support plate 8, and the third support plate 18 are respectively provided with a circulation port 24 for the circulation of the waste liquid, and the circulation port 24 on the second support plate 8 is fixed with a sieve. Net 23. The existence of the flow port 24 is to facilitate the flow of the waste liquid, and the existence of the screen 23 prevents the carrier blocks in the anaerobic chamber 2 from entering the aeration chamber 3 .

工作过程:work process:

废液由下至上依次经过厌氧室2、曝气室3、好氧室4,当对好氧室4进行曝气处理时,电源21和供气箱27启动,外部氧气由进氧管11导入供气盒9内,并击打在旋转叶片10上,使得旋转叶片10转动,随后氧气经过第一气石14和第二气石15进入好氧室4内,在此过程中,旋转叶片10带动转杆5转动,转杆5带动载体架6和搅拌板20转动,其分别对好氧室4和厌氧室2内的废液进行搅拌,从而提高废液与为微生物的混合效果。The waste liquid passes through the anaerobic chamber 2, the aeration chamber 3, and the aerobic chamber 4 in sequence from bottom to top. When the aerobic chamber 4 is aerated, the power supply 21 and the air supply box 27 are activated, and the external oxygen is supplied by the oxygen inlet pipe 11. It is introduced into the air supply box 9, and hits the rotating blade 10, so that the rotating blade 10 rotates, and then the oxygen enters the aerobic chamber 4 through the first air stone 14 and the second air stone 15. During this process, the rotating blade 10 drives the rotating rod 5 to rotate, and the rotating rod 5 drives the carrier frame 6 and the stirring plate 20 to rotate, which respectively stirs the waste liquid in the aerobic chamber 4 and the anaerobic chamber 2, thereby improving the mixing effect of the waste liquid and the microorganisms.

在本发明的描述中,需要理解的是,术语“纵向”、“横向”、“上”、“下”、“前”、“后”、“左”、“右”、“竖直”、“水平”、“顶”、“底”、“内”、“外”等指示的方位或位置关系为基于附图所示的方位或位置关系,仅是为了便于描述本发明,而不是指示或暗示所指的装置或元件必须具有特定的方位、以特定的方位构造和操作,因此不能理解为对本发明的限制。In the description of the present invention, it should be understood that the terms "portrait", "horizontal", "upper", "lower", "front", "rear", "left", "right", "vertical", The orientation or positional relationship indicated by "horizontal", "top", "bottom", "inner", "outer", etc. is based on the orientation or positional relationship shown in the drawings, and is only for the convenience of describing the present invention, rather than indicating or It is implied that the device or element referred to must have a particular orientation, be constructed and operate in a particular orientation, and therefore should not be construed as limiting the invention.

以上所述的实施例仅是对本发明的优选方式进行描述,并非对本发明的范围进行限定,在不脱离本发明设计精神的前提下,本领域普通技术人员对本发明的技术方案做出的各种变形和改进,均应落入本发明权利要求书确定的保护范围内。The above-mentioned embodiments are only to describe the preferred modes of the present invention, but not to limit the scope of the present invention. Without departing from the design spirit of the present invention, those of ordinary skill in the art can make various modifications to the technical solutions of the present invention. Variations and improvements should fall within the protection scope determined by the claims of the present invention.

Claims (10)

1. An up-flow type electrically-assisted anaerobic-aerobic coupled biofilm reactor, which comprises a reaction tube (1), wherein the reaction tube (1) is sequentially provided with an anaerobic chamber (2), an aeration chamber (3) and an aerobic chamber (4) from bottom to top, the liquid outlet end of the anaerobic chamber (2) is communicated with the liquid inlet end of the aerobic chamber (4) through the aeration chamber (3),
the gas supply part is arranged in the aeration chamber (3) and comprises a gas supply piece and a gas spraying piece, the gas supply piece is positioned below the gas spraying piece and communicated with the gas spraying piece, the gas outlet end of the aeration chamber (3) is communicated with the gas inlet end of the aerobic chamber (4) through the gas spraying piece, and the gas supply piece is in transmission connection with the gas spraying piece through a rotating rod (5);
the carrier part is arranged in the aerobic chamber (4), the carrier part comprises a carrier frame (6), the carrier frame (6) is detachably connected with the reaction tube (1) and the rotating rod (5) respectively, and a plurality of carrier blocks are arranged in the anaerobic chamber (2);
The power supply part is arranged outside the reaction tube (1), the anode of the power supply part is electrically connected with the aerobic chamber (4), and the cathode of the power supply part is electrically connected with the anaerobic chamber (2).
2. The upflow electrically-assisted anaerobic-aerobic coupled biofilm reactor of claim 1, wherein: a first support plate (7) and a second support plate (8) which are fixedly connected with the inner wall of the reaction tube (1), the first support plate (7) is positioned above the second support plate (8), the aeration chamber (3) is separated from the anaerobic chamber (2) and the aerobic chamber (4) through the first support plate (7) and the second support plate (8), the gas supply part comprises a gas supply box (9) fixedly connected with the top end of the second support plate (8), a rotating blade (10) is arranged in the air supply box (9), the rotating rod (5) penetrates through the air supply box (9) and the rotating blade (10), the rotating rod (5) is rotationally connected with the air supply box (9), the rotating rod (5) is fixedly connected with the rotating blades (10), the side wall of the air supply box (9) is communicated with an oxygen inlet pipe (11), and the top end of the air supply box (9) is communicated with the air injection piece.
3. The upflow, electrically-assisted anaerobic-aerobic coupled biofilm reactor of claim 2, wherein: the side wall of the rotating blade (10) is fixedly connected with a plurality of tip protrusions (12), and the tip protrusions (12) are arranged corresponding to the air outlet end of the oxygen inlet pipe (11).
4. The upflow electrically-assisted anaerobic-aerobic coupled biofilm reactor of claim 2, wherein: the air injection part comprises an air injection barrel (13) fixedly connected with the top end of the second support plate (8), the air supply box (9) is located in the air injection barrel (13), a first air stone (14) is fixedly connected with the inner wall of the air injection barrel (13), the air supply box (9) is communicated with the first air stone (14) through a communicating pipe, the air outlet end of the air injection barrel (13) is provided with a second air stone (15), the second air stone (15) penetrates through the first support plate (7), the second air stone (15) is fixedly connected with the rotating rod (5), and the second air stone (15) is rotatably connected with the first support plate (7).
5. The upflow, electrically-assisted anaerobic-aerobic coupled biofilm reactor of claim 4, wherein: the aperture of the second air stone (15) is smaller than that of the first air stone (14), and the air outlet of the second air stone (15) is obliquely arranged.
6. The upflow, electrically-assisted anaerobic-aerobic coupled biofilm reactor of claim 4, wherein: the spraying cylinder (13) is of a circular truncated cone structure, and the diameter of the end part, close to the first support plate (7), of the spraying cylinder (13) is smaller than that of the end part, close to the second support plate (8), of the spraying cylinder (13).
7. The upflow electrically-assisted anaerobic-aerobic coupled biofilm reactor of claim 2, wherein: aerobic chamber (4) top intercommunication has overflow chamber (16), overflow chamber (16) intercommunication has overflow pipe (17), aerobic chamber (4) with overflow chamber (16) are separated through third extension board (18), the notch cuttype leads to the groove has been seted up on third extension board (18), the notch cuttype leads to the inslot and sets up rather than assorted notch cuttype (19), carrier frame (6) cover is established on bull stick (5), just notch cuttype (19) with the connection can be dismantled on bull stick (5) top.
8. The upflow electrically-assisted anaerobic-aerobic coupled biofilm reactor of claim 2, wherein: the bottom end of the rotating rod (5) penetrates through the second support plate (8) and extends into the anaerobic chamber (2), the rotating rod (5) is rotatably connected with the second support plate (8), a plurality of stirring plates (20) are fixedly connected to the rotating rod (5), and the plurality of stirring plates (20) are all located in the anaerobic chamber (2).
9. The upflow electrically-assisted anaerobic-aerobic coupled biofilm reactor of claim 1, wherein: the power supply portion comprises a power supply (21), the aerobic chamber (4) and the anaerobic chamber (2) are respectively connected with the power supply (21) through a conductive plate (22), the anode of the power supply (21) is electrically connected with the conductive plate (22) of the aerobic chamber (4), and the cathode of the power supply (21) is electrically connected with the conductive plate (22) of the anaerobic chamber (2).
10. The upflow electrically assisted anaerobic-aerobic coupled biofilm reactor of claim 7, wherein: the first support plate (7), the second support plate (8) and the third support plate (18) are respectively provided with a circulation port (24) for waste liquid circulation, and a screen (23) is fixedly connected in the circulation port (24) on the second support plate (8).
CN202210289824.XA 2022-03-23 2022-03-23 Up-flow type electric-assisted anaerobic-aerobic coupling biomembrane reactor Active CN114573106B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202210289824.XA CN114573106B (en) 2022-03-23 2022-03-23 Up-flow type electric-assisted anaerobic-aerobic coupling biomembrane reactor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202210289824.XA CN114573106B (en) 2022-03-23 2022-03-23 Up-flow type electric-assisted anaerobic-aerobic coupling biomembrane reactor

Publications (2)

Publication Number Publication Date
CN114573106A true CN114573106A (en) 2022-06-03
CN114573106B CN114573106B (en) 2023-07-28

Family

ID=81777521

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202210289824.XA Active CN114573106B (en) 2022-03-23 2022-03-23 Up-flow type electric-assisted anaerobic-aerobic coupling biomembrane reactor

Country Status (1)

Country Link
CN (1) CN114573106B (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115893680A (en) * 2022-11-15 2023-04-04 中化环境科技工程有限公司 Electric enhanced biological reaction device and method for treating COD (chemical oxygen demand) and TN (total nitrogen) in wastewater
CN118026417A (en) * 2024-04-11 2024-05-14 四川发展环境科学技术研究院有限公司 Urban sewage treatment device with coupling of nitrification and anaerobic ammonia oxidation

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101977853A (en) * 2008-01-28 2011-02-16 Ntnu技术转移股份有限公司 Method and device for the treatment of waste water
CN102491517A (en) * 2011-11-28 2012-06-13 山东大学 Anaerobic and aerobic sewage treatment unit and sewage treatment method
CN104229995A (en) * 2014-10-09 2014-12-24 天津工业大学 Method for degrading degradation-resistant organic wastewater by double sludge tower-type electrical bioreactor
CN110342692A (en) * 2019-08-20 2019-10-18 重庆化工职业学院 Sewage-treatment plant for environmental protection
CN111039510A (en) * 2019-12-30 2020-04-21 华北水利水电大学 A wastewater filtration device for agricultural water-saving irrigation and its filtration method
US20220073390A1 (en) * 2018-12-19 2022-03-10 Bio Proj Tecnologia Ambiental Ltda. Fixed Biofilm Anaerobic-Aerobic Combined Reactor For Treating Wastewater

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101977853A (en) * 2008-01-28 2011-02-16 Ntnu技术转移股份有限公司 Method and device for the treatment of waste water
CN102491517A (en) * 2011-11-28 2012-06-13 山东大学 Anaerobic and aerobic sewage treatment unit and sewage treatment method
CN104229995A (en) * 2014-10-09 2014-12-24 天津工业大学 Method for degrading degradation-resistant organic wastewater by double sludge tower-type electrical bioreactor
US20220073390A1 (en) * 2018-12-19 2022-03-10 Bio Proj Tecnologia Ambiental Ltda. Fixed Biofilm Anaerobic-Aerobic Combined Reactor For Treating Wastewater
CN110342692A (en) * 2019-08-20 2019-10-18 重庆化工职业学院 Sewage-treatment plant for environmental protection
CN111039510A (en) * 2019-12-30 2020-04-21 华北水利水电大学 A wastewater filtration device for agricultural water-saving irrigation and its filtration method

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
王庆国等: "《上海国际旅游度假区基础设施绿色建设关键技术研究与应用》", 化学工业出版社, pages: 264 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115893680A (en) * 2022-11-15 2023-04-04 中化环境科技工程有限公司 Electric enhanced biological reaction device and method for treating COD (chemical oxygen demand) and TN (total nitrogen) in wastewater
CN118026417A (en) * 2024-04-11 2024-05-14 四川发展环境科学技术研究院有限公司 Urban sewage treatment device with coupling of nitrification and anaerobic ammonia oxidation

Also Published As

Publication number Publication date
CN114573106B (en) 2023-07-28

Similar Documents

Publication Publication Date Title
CN212799817U (en) Moving bed biofilm reaction system
CN103435224A (en) Waste water treatment technology for livestock breeding
CN1548384A (en) Aerator and advanced waste water treatment method using the same
CN114573106B (en) Up-flow type electric-assisted anaerobic-aerobic coupling biomembrane reactor
CN114315037A (en) An inverted A2/O-GDMBR integrated village sewage treatment device and method with an applied electric field
CN110240367A (en) A sewage treatment system and method for simultaneous and efficient removal of carbon, nitrogen and phosphorus
CN217868539U (en) Sewage treatment device convenient to move
CN112479368A (en) Sewage treatment device of biofilm reactor and treatment method thereof
CN101549930B (en) System and method for processing high-concentration printing and dyeing wastewater
CN212954755U (en) Integrated sewage treatment device
CN210620379U (en) Biological aeration device for degrading organic matters in sewage
CN210438586U (en) High-efficient environment-friendly sewage treatment circulating equipment
CN219136609U (en) Ozone volcanic rock biological aerated filter
CN203048733U (en) Advanced sewage treatment device
CN203269735U (en) Equipment for treating rubbish leachate by utilizing two-stage bioreactors
CN212799980U (en) Efficient and rapid purification device for dredging tail water
CN102531159B (en) Membrane bioreactor combining plug flow and circulation of surface and micro-bubble aerations
GB2619123A (en) Integrated inverted A2/O-GDMBR based on external electric field for village sewage treatment device and method
CN210528571U (en) Biological contact oxidation process equipment using nano aeration technology
CN207973654U (en) A kind of initial stage garbage percolation liquid treating system
CN219567722U (en) Aeration device and sewage purification system
CN220201674U (en) Sequence intermittent sewage treatment device
CN217323552U (en) Integrated device for treating domestic sewage
CN110980936B (en) Biological nitrogen and phosphorus removal device for HJDLZYS and application thereof
CN221988335U (en) High-efficiency micro-nano bubble oxygenator

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant