CN108298690B - Integrated Partial Nitrosation-ANAMMOX Inclined Plate Enhanced Bioreactor - Google Patents

Integrated Partial Nitrosation-ANAMMOX Inclined Plate Enhanced Bioreactor Download PDF

Info

Publication number
CN108298690B
CN108298690B CN201810418854.XA CN201810418854A CN108298690B CN 108298690 B CN108298690 B CN 108298690B CN 201810418854 A CN201810418854 A CN 201810418854A CN 108298690 B CN108298690 B CN 108298690B
Authority
CN
China
Prior art keywords
zone
inclined plate
combined
plate
anaerobic
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.)
Active
Application number
CN201810418854.XA
Other languages
Chinese (zh)
Other versions
CN108298690A (en
Inventor
季军远
王俊丹
宋霞
洪波
宋维星
张倩
朱晓桐
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.)
Ocean University of China
Original Assignee
Ocean University of China
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 Ocean University of China filed Critical Ocean University of China
Priority to CN201810418854.XA priority Critical patent/CN108298690B/en
Publication of CN108298690A publication Critical patent/CN108298690A/en
Application granted granted Critical
Publication of CN108298690B publication Critical patent/CN108298690B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

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
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • 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)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

本发明提供了一种一体式部分亚硝化‑厌氧氨氧化斜板强化生物反应器,所述生物反应器主体结构为长方体,从左至右依次分为好氧区、过渡区、厌氧区、导流区、分离区,包括进水管、隔室双侧布水器、微孔曝气管、好氧区排泥管、过渡区与厌氧区排泥管、分离区排泥管、回流管、好氧区与过渡区排气管、厌氧区排气管、分离区排气管、出水槽、出水管、挡板、组合斜板Ⅰ、组合斜板Ⅱ、斜板。该生物反应器可实现功能区之间的自主调配、完全避免曝气对厌氧功能微生物的毒害作用、大幅提高泥水分离效果、提升反应器整体脱氮效能。有益效果如下:1)抗冲击负荷能力强,占地面积小。2)避免曝气对反应器性能影响。3)实现功能区的自主调配。4)提高反应器整体效能。

The invention provides an integrated partial nitrosation-anammox slanted plate enhanced bioreactor. The main structure of the bioreactor is a cuboid, which is divided into an aerobic zone, a transition zone, anaerobic zone, a diversion zone, and a separation zone from left to right, including water inlet pipes, compartment double-sided water distributors, microporous aeration pipes, aerobic zone mud discharge pipes, transition zone and anaerobic zone sludge discharge pipes, separation zone mud discharge pipes, return pipes, aerobic zone and transition zone exhaust pipes, anaerobic zone exhaust pipes, and separation zones. Pipe, outlet tank, outlet pipe, baffle, combined sloping plate I, combined sloping plate II, sloping plate. The bioreactor can realize autonomous allocation between functional areas, completely avoid the poisonous effect of aeration on anaerobic functional microorganisms, greatly improve the separation effect of mud and water, and improve the overall denitrification efficiency of the reactor. The beneficial effects are as follows: 1) The impact load resistance is strong, and the occupied area is small. 2) Avoid the influence of aeration on the performance of the reactor. 3) Realize the autonomous allocation of functional areas. 4) Improve the overall efficiency of the reactor.

Description

一体式部分亚硝化-厌氧氨氧化斜板强化生物反应器Integrated Partial Nitrosation-ANAMMOX Inclined Plate Enhanced Bioreactor

技术领域technical field

本发明涉及一种污水生物自养脱氮反应器,属于污水脱氮生物处理领域,尤其涉及一种一体式部分亚硝化-厌氧氨氧化斜板强化生物反应器。The invention relates to a biological autotrophic denitrification reactor for sewage, which belongs to the field of biological treatment for denitrification of sewage, in particular to an integrated partial nitrosation-anammox slant plate enhanced bioreactor.

背景技术Background technique

环境保护部2017年地表水环境质量状况指出,氨氮已成我国地表水中主要污染指标之一。近年来,生活生产过程中所排放的氨氮浓度已远超出受纳水体的自净能力,已成为我国水环境保护面临的一大难题。氨氮污染不仅会引起水体富营养化等一系列环境问题,同时也是威胁人类健康的一大隐患。The Ministry of Environmental Protection pointed out in 2017 the environmental quality of surface water that ammonia nitrogen has become one of the main pollution indicators of surface water in my country. In recent years, the concentration of ammonia nitrogen discharged in the process of life and production has far exceeded the self-purification capacity of the receiving water body, which has become a major problem in the protection of my country's water environment. Ammonia nitrogen pollution will not only cause a series of environmental problems such as eutrophication of water bodies, but also a major hidden danger that threatens human health.

传统脱氮技术处理氨氮废水时,存在运行成本较高,污泥处置困难等问题。部分亚硝化-厌氧氨氧化(PN-ANAMMOX)工艺为一种新型的全自养脱氮技术,可解决传统脱氮存在问题,该工艺运行过程中无需投加有机碳源,污泥产量低,节省25%的曝气量,可极大降低处理成本等。生物反应器是实现部分亚硝化-厌氧氨氧化工艺的核心,部分亚硝化-厌氧氨氧化生物反应器主要有分体式与一体式两种,一体式具有节省投资成本、可实现碱度内部平衡等特点而备受关注。但其存在曝气过程影响ANAMMOX功能菌活性致使反应器整体脱氮能力提升较慢,且好氧区、厌氧区无法自主分配等不足。When the traditional denitrification technology treats ammonia nitrogen wastewater, there are problems such as high operating costs and difficulties in sludge disposal. The partial nitritation-anaerobic ammonium oxidation (PN-ANAMMOX) process is a new type of fully autotrophic denitrification technology, which can solve the existing problems of traditional denitrification. During the operation of this process, no organic carbon source is needed, the sludge output is low, and the aeration rate can be saved by 25%, which can greatly reduce the treatment cost. The bioreactor is the core of the partial nitrosation-anammox process. There are two main types of partial nitrosation-anammox bioreactors: split type and integrated type. The integrated type has the characteristics of saving investment costs and realizing the internal balance of alkalinity. However, the aeration process affects the activity of ANAMMOX functional bacteria, which leads to a slow increase in the overall denitrification capacity of the reactor, and the aerobic zone and anaerobic zone cannot be independently allocated.

发明内容Contents of the invention

本发明针对目前部分亚硝化-厌氧氨氧化生物反应器存在功能区间分配、曝气对厌氧氨氧化功能菌群活性影响等问题,提出了一种可克服现有装置不足的新型部分亚硝化-厌氧氨氧化斜板强化生物反应器,可实现功能区之间的自主调配、完全避免曝气影响、大幅提高泥水分离效果、提升反应器整体脱氮效能。Aiming at the problems of functional area allocation and the effect of aeration on the activity of anammox functional flora in current partial nitrosation-anammox bioreactors, the present invention proposes a new type of partial nitrosation-anammox slant-plate enhanced bioreactor that can overcome the deficiencies of existing devices.

为解决上述技术问题,本发明采用以下技术方案予以实现:In order to solve the above-mentioned technical problems, the present invention adopts the following technical solutions to achieve:

本发明所述的一体式部分亚硝化-厌氧氨氧化斜板强化生物反应器结构为长方体,可由钢板或有机玻璃制作,可为污水脱氮处理一体化装置,也可为拼装式模块单体与其他不同的处理工艺构成复合型处理设施。一体式部分亚硝化-厌氧氨氧化生物反应器包括生物反应器主体、隔室双侧布水器、进水管、微孔曝气管、好氧区排泥管、过渡区与厌氧区排泥管、分离区排泥管、回流管、好氧区与过渡区排气管、厌氧区排气管、分离区排气管、出水槽、出水管。生物反应器主体从左至右为好氧区、过渡区、厌氧区、导流区、分离区。The integrated partial nitrosation-anammox slant-plate enhanced bioreactor of the present invention has a cuboid structure and can be made of steel plates or plexiglass. It can be an integrated device for sewage denitrification treatment, or it can be an assembled modular monomer and other different treatment processes to form a composite treatment facility. The integrated partial nitritation-anammox bioreactor includes the main body of the bioreactor, the double-sided water distributor of the compartment, the water inlet pipe, the microporous aeration pipe, the sludge discharge pipe in the aerobic zone, the sludge discharge pipe in the transition zone and the anaerobic zone, the sludge discharge tube in the separation zone, the return pipe, the exhaust pipe in the aerobic zone and the transition zone, the exhaust pipe in the anaerobic zone, the exhaust pipe in the separation zone, the water outlet tank, and the water outlet pipe. From left to right, the main body of the bioreactor is an aerobic zone, a transition zone, an anaerobic zone, a diversion zone, and a separation zone.

所述的好氧区内置有半软性纤维束填料、隔室双侧布水器。好氧区通过挡板与其右侧的过渡区分隔,但通过挡板与组合斜板Ⅰ之间的缝隙相通;通过组合斜板Ⅰ与厌氧区分隔。好氧区最左侧底部从左至右分别设有隔室双侧布水器、微孔曝气管。隔室双侧布水器与进水管相连通。好氧区顶板上设有好氧区与过渡区排气管,好氧区与挡板底部结合处布有好氧区排泥管。The aerobic zone is built with semi-soft fiber bundle packing and water distributors on both sides of the compartment. The aerobic zone is separated from the transition zone on the right side by the baffle, but it communicates with the gap between the baffle and the combined sloping plate I; it is separated from the anaerobic zone by the combined sloping plate I. The leftmost bottom of the aerobic zone is equipped with compartment double-sided water distributors and microporous aeration tubes from left to right. The water distributor on both sides of the compartment is connected with the water inlet pipe. The aerobic zone and the transition zone exhaust pipes are arranged on the roof of the aerobic zone, and the aerobic zone mud discharge pipe is arranged at the junction of the aerobic zone and the bottom of the baffle.

所述的过渡区内置有流化床填料K1。过渡区左侧通过挡板与好氧区分隔,但通过挡板与组合斜板Ⅰ之间的缝隙相通;通过组合斜板Ⅰ与厌氧区分隔,但通过组合斜板Ⅰ与组合斜板Ⅱ之间缝隙相通。A fluidized bed filler K1 is built in the transition zone. The left side of the transition zone is separated from the aerobic zone by the baffle, but communicated with the gap between the baffle and the combined inclined plate I; separated from the anaerobic zone by the combined inclined plate I, but communicated through the gap between the combined inclined plate I and the combined inclined plate II.

所述的厌氧区位于过渡区与分离区之间,通过组合斜板Ⅰ与过渡区分隔,但通过组合斜板Ⅰ与组合斜板Ⅱ底部之间缝隙相通;通过组合斜板Ⅱ分别与导流区、分离区分隔,但通过组合斜板Ⅱ与顶板之间的缝隙与导流区相通;厌氧区顶板上布有厌氧区排气管,厌氧区组合斜板Ⅰ与组合斜板Ⅱ底部之间缝隙处设有过渡区与厌氧区排泥管。The anaerobic zone is located between the transition zone and the separation zone, and is separated from the transition zone by the combined sloping plate I, but communicates through the gap between the combined sloping plate I and the bottom of the combined sloping plate II; the combined sloping plate II is separated from the diversion zone and the separation zone, but communicates with the diversion zone through the gap between the combined sloping plate II and the top plate;

所述的导流区位于厌氧区的右上侧,通过组合斜板Ⅱ与厌氧区分隔,但通过组合斜板Ⅱ与顶板之间的缝隙与厌氧区相通;通过斜板与分离区分隔,但通过斜板与组合斜板Ⅱ之间缝隙与分离区相通。The diversion zone is located on the upper right side of the anaerobic zone, separated from the anaerobic zone by the combined inclined plate II, but communicated with the anaerobic zone through the gap between the combined inclined plate II and the top plate; separated from the separation zone by the inclined plate, but communicated with the separation zone through the gap between the inclined plate and the combined inclined plate II.

所述的分离区位于生物反应器主体的最右侧,通过组合斜板Ⅱ、斜板分别与厌氧区、导流区分隔,但通过斜板与组合斜板Ⅱ之间缝隙与导流区相通;分离区顶板上设有分离区排气管,外侧设有出水槽、出水管、回流管,分离区通过出水槽狭缝与出水槽连通;分离区与组合斜板Ⅱ底部结合处布有分离区排泥管。The separation zone is located on the far right side of the main body of the bioreactor, and is separated from the anaerobic zone and the diversion zone by the combined sloping plate II and the sloping plate respectively, but communicates with the diversion zone through the gap between the sloping plate and the combined sloping plate II; a separation zone exhaust pipe is provided on the top plate of the separation zone, and a water outlet tank, a water outlet pipe, and a return pipe are arranged on the outside, and the separation zone communicates with the water outlet tank through the slit of the water outlet tank; a separation zone sludge discharge pipe is arranged at the junction of the separation zone and the bottom of the combined inclined plate II.

其中,所述生物反应器主体长(L)、宽(W)、高(H)比值为(4~6):1:(2~3),好氧区、过渡区、厌氧区、分离区体积比为3:1:2:1。Wherein, the ratio of the length (L), width (W) and height (H) of the bioreactor body is (4-6):1:(2-3), and the volume ratio of the aerobic zone, transition zone, anaerobic zone, and separation zone is 3:1:2:1.

其中,所述隔室双侧布水器长度与生物反应器主体宽度相等,双侧板与反应器主体面形成封闭隔室,双侧板均开有圆孔阵,圆孔直径(D)为(0.05~0.015)L,双侧板的宽度为0.03L。Wherein, the length of the water distributor on both sides of the compartment is equal to the width of the main body of the bioreactor, the double side plate and the main surface of the reactor form a closed compartment, and both side plates are opened with a circular hole array, the diameter (D) of the round hole is (0.05 ~ 0.015) L, and the width of the double side plate is 0.03 L.

其中,所述微孔曝气管长度为好氧区长度1/2,一端紧邻隔室双侧布水器,沿生物反应器长度方向布置,位于反应器主体高度面一侧。Wherein, the length of the microporous aeration pipe is 1/2 of the length of the aerobic zone, and one end is adjacent to the double-sided water distributor of the compartment, arranged along the length direction of the bioreactor, and located on one side of the height surface of the reactor main body.

其中,所述挡板位于反应器主体1/2L处并垂直设置,挡板高度为(1/2~2/3)H。Wherein, the baffle is located at 1/2L of the main body of the reactor and arranged vertically, and the height of the baffle is (1/2˜2/3)H.

其中,所述组合斜板Ⅰ由纵向斜板和横向斜板组成,纵向斜板与横向斜板之间夹角为150°;纵向斜板与反应器顶板接合,水平夹角为60°;横向斜板水平夹角为30°。Wherein, the combined inclined plate I is composed of a longitudinal inclined plate and a transverse inclined plate, and the angle between the longitudinal inclined plate and the transverse inclined plate is 150°; the longitudinal inclined plate is joined to the top plate of the reactor, and the horizontal angle is 60°; the horizontal angle between the transverse inclined plate is 30°.

其中,所述组合斜板Ⅱ由纵向斜板和横向斜板组成,纵向斜板与横向斜板夹角为150°;纵向斜板与反应器主体底部接合,水平夹角为60°,横向斜板水平夹角为30°;组合斜板Ⅱ与组合斜板Ⅰ之间缝隙宽度为2~10cm,组合斜板Ⅱ中横向斜板上边缘高度低于出水管高度3~15cm。Wherein, the combined inclined plate II is composed of a longitudinal inclined plate and a transverse inclined plate, and the angle between the longitudinal inclined plate and the transverse inclined plate is 150°; the longitudinal inclined plate is joined to the bottom of the reactor main body at a horizontal angle of 60°, and the horizontal inclined plate is 30°; the width of the gap between the combined inclined plate II and the combined inclined plate I is 2-10 cm, and the height of the edge of the transverse inclined plate in the combined inclined plate II is lower than the height of the outlet pipe by 3-15 cm.

其中,所述斜板与反应器主体顶板接合,水平夹角为60°;斜板与组合斜板Ⅱ之间缝隙宽度为2~10cm。Wherein, the inclined plate is joined to the top plate of the main body of the reactor, and the horizontal angle is 60°; the width of the gap between the inclined plate and the combined inclined plate II is 2-10 cm.

其中,所述出水槽狭缝高度低于出水管高度6~15cm,回流管与出水槽狭缝等高。Wherein, the height of the slit of the water outlet is 6-15 cm lower than that of the water outlet pipe, and the height of the return pipe is equal to the slit of the water outlet.

其中,所述好氧区与过渡区排气管、厌氧区排气管、分离区排气管均位于反应器主体顶板宽度的1/2处,分别位于各功能区长度的1/2处,排气管的内径均为2~10cm。Wherein, the exhaust pipes of the aerobic zone and the transition zone, the exhaust pipe of the anaerobic zone, and the exhaust pipe of the separation zone are all located at 1/2 of the width of the top plate of the reactor main body, respectively located at 1/2 of the length of each functional zone, and the inner diameters of the exhaust pipes are all 2 to 10 cm.

其中,所述的好氧区置有好氧反硝化絮体污泥,好氧区中半软性纤维束填料体积占好氧区体积的25%~45%;厌氧区置有厌氧氨氧化颗粒污泥,过渡区填充满流化填料K1,污泥种类由反应过程自动调配。Wherein, the aerobic zone is equipped with aerobic denitrification floc sludge, and the volume of the semi-soft fiber bundle filler in the aerobic zone accounts for 25% to 45% of the volume of the aerobic zone; the anaerobic zone is equipped with anammox granular sludge, and the transition zone is filled with fluidized filler K1, and the sludge type is automatically allocated by the reaction process.

反应器构型设计对部分亚硝化与厌氧氨氧化功能区间合理配置、反应死区降低、反应器内流态优化、脱氮效能提高等均至关重要。本发明利用挡板、组合斜板将生物反应器分为好氧区、过渡区、厌氧区、导流区、沉淀区,过渡区可实现半程硝化与厌氧氨氧化功能区的自主配置,并完全避免曝气过程对厌氧氨氧化功能菌活性的不利影响;通过组合斜板优化反应器的整体流态,大幅降低反应器功能死区,提高反应器有效反应体积,减少占地面积;通过斜板设置延长反应历程、反应时间;实现反应器各功能区全混流,反应器整体平推流,大幅提高脱氮去除效率;设计沉淀区斜板可增大沉淀区面积,放缓污水水平流速,更利于污泥沉淀,提高泥水分离效果;通过好氧区填充填料,可维持反应器内较高的亚硝化功能微生物量,显著提升脱氮容积负荷,提高反应器抗冲击负荷能力。The configuration design of the reactor is very important for the reasonable configuration of the functional areas of partial nitrification and anammox, the reduction of the reaction dead zone, the optimization of the flow state in the reactor, and the improvement of the nitrogen removal efficiency. The present invention divides the bioreactor into aerobic zone, transition zone, anaerobic zone, diversion zone, and sedimentation zone by using baffles and combined sloping plates. The transition zone can realize the independent configuration of the half-process nitrification and anammox functional zone, and completely avoid the adverse effect of the aeration process on the activity of anammox functional bacteria; optimize the overall flow state of the reactor by combining the sloping plate, greatly reduce the functional dead zone of the reactor, increase the effective reaction volume of the reactor, and reduce the occupied area; set the sloping plate to prolong the reaction process and reaction time; realize full mixed flow in each functional zone of the reactor, The overall push flow of the reactor can greatly improve the denitrification and removal efficiency; the design of the sloping plate in the sedimentation zone can increase the area of the sedimentation zone, slow down the horizontal flow rate of sewage, which is more conducive to sludge sedimentation, and improve the separation effect of sludge and water; filling the aerobic zone with filler can maintain a high amount of nitrification functional microorganisms in the reactor, significantly increase the denitrification volume load, and improve the reactor’s impact load resistance.

本发明的有益效果如下:The beneficial effects of the present invention are as follows:

1)抗冲击负荷能力强,占地面积小。好氧区、过渡区均置有填料,可维持较高的功能微生物量;厌氧区置有厌氧氨氧化颗粒污泥,厌氧氨氧化功能微生物浓度高。反应器可达较高的容积负荷,从而占地面积小,且高浓度功能微生物可大幅提高反应器抗冲击负荷能力。1) Strong impact load resistance and small footprint. The aerobic zone and the transition zone are equipped with fillers, which can maintain a high functional microbial biomass; the anaerobic zone is equipped with anammox granular sludge, and the concentration of anammox functional microorganisms is high. The reactor can reach a higher volume load, thereby occupying a small area, and the high concentration of functional microorganisms can greatly improve the reactor's ability to resist shock loads.

2)避免曝气对反应器性能影响。过渡区的设置可在好氧区与厌氧区之间形成缓冲空间,氧气在过渡区可被微生物有效利用,可完全消除其对后续厌氧氨氧化功能菌群的氧毒作用,从而维持反应器高效稳定运行。2) Avoid the influence of aeration on the performance of the reactor. The setting of the transition zone can form a buffer space between the aerobic zone and the anaerobic zone. Oxygen can be effectively used by microorganisms in the transition zone, which can completely eliminate its oxygen toxicity to the subsequent anammox functional flora, thereby maintaining the efficient and stable operation of the reactor.

3)实现功能区的自主调配。过渡区可在反应器实际运行中自主调整其所行使的功能,可在好氧半程硝化、厌氧氨氧化进行合理切换,可自调整好氧区、厌氧区之间配比,对运行参数的变动进行快速有效的响应,自主调节合理分配。3) Realize the independent allocation of functional areas. The transition zone can independently adjust its functions during the actual operation of the reactor. It can reasonably switch between aerobic half-process nitrification and anammox, and can self-adjust the ratio between the aerobic zone and the anaerobic zone. It can respond quickly and effectively to changes in operating parameters, and independently adjust and rationally allocate.

4)提高反应器整体效能。挡板、组合斜板合理设置,可优化反应器的流态,降低反应器功能死区,延长反应历程,增加反应时间,且反应器各功能区实现全混,而反应器整体实现平推流,大幅提高反应器脱氮性能;增大分离区表面积,从而降低污水表面流速,可提高泥水分离效果。4) Improve the overall efficiency of the reactor. Reasonable setting of baffles and combined inclined plates can optimize the flow state of the reactor, reduce the functional dead zone of the reactor, prolong the reaction process, increase the reaction time, and achieve full mixing in each functional area of the reactor, while the reactor as a whole realizes plug flow, which greatly improves the denitrification performance of the reactor; increases the surface area of the separation area, thereby reducing the surface velocity of sewage, and improving the separation effect of mud and water.

在发明内容部分中引入了一系列简化形式的概念,这将在具体实施方式部分中进一步详细说明。本发明内容部分并不意味着要试图限定出所要求保护的技术方案的关键特征和必要技术特征,更不意味着试图确定所要求保护的技术方案的保护范围。A series of concepts in simplified form are introduced in the Summary of the Invention, which will be further detailed in the Detailed Description. The summary of the present invention does not mean trying to limit the key features and essential technical features of the claimed technical solution, nor does it mean trying to determine the protection scope of the claimed technical solution.

以下结合附图,详细说明本发明的优点和特征。The advantages and features of the present invention will be described in detail below in conjunction with the accompanying drawings.

附图说明Description of drawings

下面将结合附图及实施例对本发明作进一步说明,附图中:The present invention will be further described below in conjunction with accompanying drawing and embodiment, in the accompanying drawing:

图1为一体式部分亚硝化-厌氧氨氧化斜板强化生物反应器结构示意图;Figure 1 is a structural schematic diagram of an integrated partial nitrosation-anammox inclined plate enhanced bioreactor;

图2为一体式部分亚硝化-厌氧氨氧化斜板强化生物反应器俯视图;Figure 2 is the top view of the integrated partial nitrosation-anammox inclined plate enhanced bioreactor;

其中,1、生物反应器主体;2、好氧区;3、过渡区;4、厌氧区;5、导流区;6、分离区;7、进水管;8、隔室双侧布水器;9、微孔曝气管;10、好氧区排泥管;11、过渡区与厌氧区排泥管;12、分离区排泥管;13、回流管;14、好氧区与过渡区排气管;15、厌氧区排气管;16、分离区排气管;17、出水槽;18、出水管;19、挡板;20、组合斜板Ⅰ;21、组合斜板Ⅱ;22、斜板;201、组合斜板Ⅰ纵向斜板;202、组合斜板Ⅰ横向斜板;211、组合斜板Ⅱ纵向斜板;212、组合斜板Ⅱ横向斜板。Among them, 1. Bioreactor main body; 2. Aerobic zone; 3. Transition zone; 4. Anaerobic zone; 5. Diversion zone; 6. Separation zone; 7. Inlet pipe; 6. Exhaust pipe in the separation area; 17. Outlet tank; 18. Outlet pipe; 19. Baffle plate; 20. Composite inclined plate I; 21. Combined inclined plate II; 22. Inclined plate; 201. Combined inclined plate I longitudinal inclined plate;

具体实施方式Detailed ways

为了使本发明的目的、技术方案及优点更加清楚明白,以下结合附图和实施例对本发明作进一步详细的说明。应当理解,此处所描述的实施例仅仅用以解释本发明,并不用于限定本发明。In order to make the object, technical solution and advantages of the present invention clearer, the present invention will be further described in detail below in conjunction with the accompanying drawings and embodiments. It should be understood that the embodiments described here are only used to explain the present invention, not to limit the present invention.

在下文的描述中,给出了大量具体的细节以便提供对本发明更为彻底的理解。然而,对于本领域技术人员来说显而易见的是,本发明可以无需一个或多个这些细节而得以实施。在其他的例子中,为了避免与本发明发生混淆,对于本领域公知的一些技术特征未进行描述。In the following description, numerous specific details are given in order to provide a more thorough understanding of the present invention. It will be apparent, however, to one skilled in the art that the present invention may be practiced without one or more of these details. In other examples, some technical features known in the art are not described in order to avoid confusion with the present invention.

为了彻底了解本发明,将在下列的描述中提出详细的结构。显然,本发明的施行并不限定于本领域的技术人员所熟习的特殊细节。本发明的较佳实施例详细描述如下,然而除了这些详细描述外,本发明还可以具有其他实施方式。In order to provide a thorough understanding of the present invention, the detailed structure will be set forth in the following description. It is evident that the practice of the invention is not limited to specific details familiar to those skilled in the art. Preferred embodiments of the present invention are described in detail below, however, the present invention may have other embodiments besides these detailed descriptions.

以下结合附图对本发明的实施例做详细描述。Embodiments of the present invention will be described in detail below in conjunction with the accompanying drawings.

如图1、2所示,一体式部分亚硝化-厌氧氨氧化斜板强化生物反应器结构为长方体,可由钢板或有机玻璃制作,可为污水脱氮处理一体化装置,也可为拼装式模块单体与其他不同的处理工艺构成复合型处理设施。包括生物反应器主体1、隔室双侧布水器8、进水管7、微孔曝气管9、好氧区排泥管10、过渡区与厌氧区排泥管11、分离区排泥管12、回流管13、好氧区与过渡区排气管14、厌氧区排气管15、分离区排气管16、出水槽17、出水管18。生物反应器主体从左至右为好氧区2、过渡区3、厌氧区4、导流区5、分离区6。As shown in Figures 1 and 2, the integrated partial nitrosation-anammox inclined-plate enhanced bioreactor has a cuboid structure, which can be made of steel plate or plexiglass, and can be used as an integrated device for sewage denitrification treatment, or as a composite treatment facility composed of an assembled modular monomer and other different treatment processes. Including bioreactor main body 1, compartment bilateral water distributor 8, water inlet pipe 7, microporous aeration pipe 9, aerobic zone mud discharge pipe 10, transition zone and anaerobic zone mud discharge pipe 11, separation zone mud discharge pipe 12, return pipe 13, aerobic zone and transition zone exhaust pipe 14, anaerobic zone exhaust pipe 15, separation zone exhaust pipe 16, water outlet tank 17, and water outlet pipe 18. From left to right, the main body of the bioreactor is an aerobic zone 2, a transition zone 3, an anaerobic zone 4, a diversion zone 5, and a separation zone 6.

所述的好氧区2内置有半软性纤维束填料、隔室双侧布水器8。好氧区2通过挡板19与其右侧的过渡区3分隔,并通过挡板19与组合斜板Ⅰ20之间的缝隙相通;通过组合斜板Ⅰ20与厌氧区4分隔。好氧区2最左侧底部从左至右分别设有隔室双侧布水器8、微孔曝气管9,隔室双侧布水器8与进水管7相连通。好氧区2顶板上设有好氧区与过渡区排气管14,好氧区2与挡板19底部结合处设有好氧区排泥管10。The aerobic zone 2 is built with semi-soft fiber bundle fillers and water distributors 8 on both sides of the compartment. The aerobic zone 2 is separated from the transition zone 3 on the right side by the baffle plate 19, and communicates with the gap between the baffle plate 19 and the combined sloping plate I20; it is separated from the anaerobic zone 4 by the combined sloping plate I20. The leftmost bottom of the aerobic zone 2 is provided with compartment double-sided water distributors 8 and microporous aeration pipes 9 from left to right, and the compartment double-sided water distributors 8 are connected to the water inlet pipe 7 . The top plate of the aerobic zone 2 is provided with an exhaust pipe 14 for the aerobic zone and the transition zone, and an aerobic zone mud discharge pipe 10 is provided at the junction of the aerobic zone 2 and the bottom of the baffle plate 19 .

所述的过渡区3内置有流化床填料K1。过渡区3左侧通过挡板19与好氧区2分隔,但通过挡板19与组合斜板Ⅰ20之间的缝隙相通,通过组合斜板Ⅰ20与厌氧区4分隔,但通过组合斜板Ⅰ19与组合斜板Ⅱ21之间缝隙相通。The transition zone 3 is built with a fluidized bed filler K1. The left side of the transition zone 3 is separated from the aerobic zone 2 by the baffle 19, but communicates with the gap between the baffle 19 and the combined sloping plate I20, and is separated from the anaerobic zone 4 by the combined sloping plate I20, but communicates with the gap between the combined sloping plate I19 and the combined sloping plate II21.

所述的厌氧区4位于过渡区3与分离区6之间,通过组合斜板Ⅰ20与过渡区3分隔,但通过组合斜板Ⅰ20与组合斜板Ⅱ21底部之间缝隙与过渡区3相通;通过组合斜板Ⅱ21分别与导流区5、分离区6分隔,但通过组合斜板Ⅱ21与顶板之间的缝隙与导流区5相通;厌氧区4顶板上设有厌氧区排气管15,厌氧区4组合斜板Ⅰ20与组合斜板Ⅱ21底部之间缝隙处设有过渡区与厌氧区排泥管11。The anaerobic zone 4 is located between the transition zone 3 and the separation zone 6, and is separated from the transition zone 3 by the combined inclined plate I20, but communicates with the transition zone 3 through the gap between the combined inclined plate I20 and the bottom of the combined inclined plate II21; it is separated from the diversion zone 5 and the separation zone 6 by the combined inclined plate II21, but communicates with the diversion zone 5 through the gap between the combined inclined plate II21 and the top plate; The transition area and the anaerobic area mud discharge pipe 11 are provided at the gap between the 0 and the bottom of the combined sloping plate II 21.

所述的导流区5位于厌氧区4的右上侧,通过组合斜板Ⅱ21与厌氧区4分隔,但通过组合斜板Ⅱ21与顶板之间的缝隙与厌氧区4相通;通过斜板22与分离区6分隔,但通过斜板22与组合斜板Ⅱ21之间缝隙与分离区6相通。The diversion zone 5 is located on the upper right side of the anaerobic zone 4, and is separated from the anaerobic zone 4 by the combined sloping plate II 21, but communicates with the anaerobic zone 4 through the gap between the combined sloping plate II 21 and the top plate; it is separated from the separation zone 6 by the sloping plate 22, but communicates with the separation zone 6 through the gap between the sloping plate 22 and the combined sloping plate II 21.

所述的分离区6位于生物反应器主体1的最右侧,通过组合斜板Ⅱ21、斜板22分别与厌氧区4、导流区5分隔,但通过斜板22与组合斜板Ⅱ21之间缝隙与导流区5相通;分离区顶板上设有分离区排气管16,外侧设有出水槽17、出水管18、回流管13,分离区6通过狭缝与出水槽17连通;分离区6与组合斜板Ⅱ21底部结合处设有分离区排泥管12。The separation zone 6 is located on the far right side of the bioreactor main body 1, and is separated from the anaerobic zone 4 and the flow diversion zone 5 by the combined inclined plate II 21 and the inclined plate 22, but communicates with the diversion zone 5 through the gap between the inclined plate 22 and the combined inclined plate II 21; the separation zone exhaust pipe 16 is arranged on the top plate of the separation zone, and the water outlet tank 17, the water outlet pipe 18 and the return pipe 13 are arranged on the outside, and the separation zone 6 is communicated with the water outlet tank 17 through the slit; The joint is provided with a mud discharge pipe 12 in the separation zone.

其中,所述生物反应器主体1长(L)、宽(W)、高(H)比值为(4~6):1:(2~3),好氧区2、过渡区3、厌氧区4、分离区6体积比为3:1:2:1。所述隔室双侧布水器8长度与生物反应器主体1宽度相等,双侧板与反应器主体面形成封闭隔室,双侧板均开有圆孔阵,圆孔直径(D)为(0.05~0.015)L,双侧板的宽度均为0.03L。所述微孔曝气管9长度为好氧区2长度1/2,一端紧邻隔室双侧布水器8,沿生物反应器主体1长度方向布置,位于反应器主体1高度面一侧。所述挡板19位于反应器主体1/2L处并垂直设置,挡板19高度为(1/2~2/3)H。所述组合斜板Ⅰ20由纵向斜板201和横向斜板202组成,纵向斜板201与横向斜板202之间夹角为150°;纵向斜板201与反应器顶板接合,水平夹角为60°;横向斜板202水平夹角为30°。所述组合斜板Ⅱ21由纵向斜板211和横向斜板212组成,纵向斜板211与横向斜板212夹角为150°;纵向斜板211与反应器主体底部结合,水平夹角为60°,横向斜板212水平夹角为30°;组合斜板Ⅱ21与组合斜板Ⅰ20之间缝隙宽度为2~10cm,组合斜板Ⅱ21中横向斜板212上边缘高度低于出水管18高度3~15cm。所述斜板22与反应器主体1顶板接合,水平夹角60°;斜板22与组合斜板Ⅱ21之间缝隙宽度为2~10cm。所述出水槽17狭缝高度低于出水管18高度6~15cm。所述好氧区与过渡区排气管14、厌氧区排气管15、分离区排气管16均位于反应器主体顶板宽度1/2处,分别位于各功能区长度1/2处,排气管内径均为2~10cm。所述的好氧区2内置好氧反硝化絮体污泥,内置半软性纤维束填料体积占好氧区1体积的25%~45%;厌氧区4内置厌氧氨氧化颗粒污泥,过渡区3填充满流化填料K1,污泥种类由反应过程自动配置。Wherein, the ratio of the length (L), width (W) and height (H) of the bioreactor main body 1 is (4-6):1:(2-3), and the volume ratio of the aerobic zone 2, transition zone 3, anaerobic zone 4, and separation zone 6 is 3:1:2:1. The length of the water distributor 8 on both sides of the compartment is equal to the width of the main body of the bioreactor 1. The double side plates and the main body of the reactor form a closed compartment. Both side plates are opened with circular hole arrays. The diameter (D) of the round holes is (0.05 ~ 0.015) L, and the width of both side plates is 0.03L. The length of the microporous aeration pipe 9 is 1/2 of the length of the aerobic zone 2, and one end is adjacent to the double-sided water distributor 8 of the compartment, arranged along the length direction of the bioreactor body 1, and located on the side of the height plane of the reactor body 1. The baffle 19 is located at 1/2L of the main body of the reactor and arranged vertically, and the height of the baffle 19 is (1/2˜2/3)H. The combined inclined plate I20 is composed of a longitudinal inclined plate 201 and a transverse inclined plate 202. The angle between the longitudinal inclined plate 201 and the transverse inclined plate 202 is 150°; the longitudinal inclined plate 201 is connected to the top plate of the reactor, and the horizontal angle is 60°; the horizontal angle between the transverse inclined plate 202 is 30°. The combined inclined plate II 21 is composed of a longitudinal inclined plate 211 and a transverse inclined plate 212. The angle between the longitudinal inclined plate 211 and the transverse inclined plate 212 is 150°; the longitudinal inclined plate 211 is combined with the bottom of the reactor main body at a horizontal angle of 60°, and the horizontal inclined plate 212 is 30°; Water pipe 18 height 3~15cm. The sloping plate 22 is joined to the top plate of the reactor main body 1 with a horizontal angle of 60°; the gap between the sloping plate 22 and the combined sloping plate II 21 has a width of 2-10 cm. The slit height of the water outlet tank 17 is 6-15 cm lower than the height of the water outlet pipe 18 . The exhaust pipe 14 of the aerobic zone and the transition zone, the exhaust pipe 15 of the anaerobic zone, and the exhaust pipe 16 of the separation zone are all located at 1/2 of the width of the top plate of the reactor main body, and respectively located at 1/2 of the length of each functional zone, and the inner diameter of the exhaust pipe is 2 to 10 cm. The aerobic zone 2 is built with aerobic denitrification floc sludge, and the volume of the built-in semi-soft fiber bundle filler accounts for 25% to 45% of the volume of the aerobic zone 1; the anaerobic zone 4 is built with anammox granular sludge, and the transition zone 3 is filled with fluidized filler K1, and the sludge type is automatically configured by the reaction process.

本发明一体式部分亚硝化-厌氧氨氧化斜板强化生物反应器工作过程如下:含氨氮废水经进水管7进入隔室双侧布水器8,在隔室双侧布水器8中与回流管13的回流出水充分混匀后,经分布于隔室双侧布水器8中双侧板上的圆孔阵,从横、纵两方向均匀布水后进入好氧区2,在位于反应器主体1高度面一侧的微孔曝气管释放出空气的搅动与曝气作用下使污水在好氧区实现全混并进行一定程度充氧,污水在好氧区2进行部分亚硝化反应,部分氨氮转化为亚硝酸钠盐,污水流经好氧区后半段,因无微孔曝气管曝气,污水中氧气含量逐渐降低;污水继续经挡板19与组合斜板Ⅰ20之间缝隙进入过渡区3,若氧气浓度较高,为好氧或兼氧环境,则过渡区3行使好氧区2功能,以短程硝化反应为主,若氧气浓度较低,为缺氧或厌氧环境,则过渡区3行使厌氧区4功能,以厌氧氨氧化反应为主;污水从过渡区3经组合斜板Ⅰ20与组合斜板Ⅱ21之间的缝隙继续进入厌氧区4,污水在厌氧区4进行厌氧氨氧化反应,氮污染物最终生成氮气排出,附有气泡而上浮的厌氧氨氧化颗粒污泥经组合斜板Ⅱ21的阻留、分离作用可返回至厌氧区5;污水继续经由斜板22与组合斜板Ⅱ21之间缝隙由导流区5进入分离区6,因组合斜板Ⅱ21的设置可增大分离区表面积,从而降低污水表面流速,使泥水得到良好的分离;污水继续经分离区6中狭缝流入出水槽17经排水管18外排。The working process of the integrated partial nitrosation-anammox slanted plate enhanced bioreactor of the present invention is as follows: ammonia nitrogen-containing waste water enters the double-sided water distributor 8 of the compartment through the water inlet pipe 7, and after being fully mixed with the reflux outlet water of the return pipe 13 in the double-sided water distributor 8 of the compartment, the water is evenly distributed in the horizontal and vertical directions through the circular hole arrays on the double-side plates of the compartment double-sided water distributor 8, and then enters the aerobic zone 2. Under the action of agitation and aeration, the sewage is fully mixed and oxygenated to a certain extent in the aerobic zone. The sewage undergoes partial nitrosation in the aerobic zone 2, and part of the ammonia nitrogen is converted into sodium nitrite. The sewage flows through the second half of the aerobic zone. Because there is no microporous aeration tube for aeration, the oxygen content in the sewage gradually decreases; the sewage continues to enter the transition zone 3 through the gap between the baffle plate 19 and the combined inclined plate I20. If the oxygen concentration is high, it is an aerobic or facultative environment. The short-range nitrification reaction is the main one. If the oxygen concentration is low and it is an anoxic or anaerobic environment, the transition zone 3 will perform the function of the anaerobic zone 4, mainly anaerobic ammonium oxidation reaction; the sewage from the transition zone 3 will continue to enter the anaerobic zone 4 through the gap between the combined inclined plate I20 and the combined inclined plate II21. Zone 5: The sewage continues to enter the separation zone 6 from the diversion zone 5 through the gap between the sloping plate 22 and the combined sloping plate II 21. The setting of the combined sloping plate II 21 can increase the surface area of the separation zone, thereby reducing the surface velocity of the sewage and making the muddy water well separated; the sewage continues to flow into the outlet tank 17 through the slit in the separation zone 6 and is discharged through the drain pipe 18.

本说明书实施例所述的内容仅仅是对发明构思的实现形式的列举,本发明的保护范围不应当被视为仅限于实施例所陈述的具体形式,本发明的保护范围也包括本领域技术人员根据本发明构思所能够想到的等同技术手段。The content described in the embodiments of this specification is only an enumeration of the implementation forms of the inventive concept. The protection scope of the present invention should not be regarded as limited to the specific forms stated in the embodiments. The protection scope of the present invention also includes equivalent technical means that those skilled in the art can think of according to the present invention concept.

Claims (7)

1.一种一体式部分亚硝化-厌氧氨氧化斜板强化生物反应器,其特征在于:所述生物反应器主体结构为长方体,从左至右依次分为好氧区、过渡区、厌氧区、导流区、分离区,包括进水管、隔室双侧布水器、微孔曝气管、好氧区排泥管、过渡区与厌氧区排泥管、分离区排泥管、回流管、好氧区与过渡区排气管、厌氧区排气管、分离区排气管、出水槽、出水管、挡板、组合斜板Ⅰ、组合斜板Ⅱ、斜板;1. An integrated partial nitrosation-anammox slanted plate enhanced bioreactor, characterized in that: the main structure of the bioreactor is a cuboid, which is divided into aerobic zone, transition zone, anaerobic zone, diversion zone, and separation zone from left to right, including water inlet pipe, compartment double-sided water distributor, microporous aeration pipe, aerobic zone sludge discharge pipe, transition zone and anaerobic zone sludge discharge pipe, separation zone mud discharge pipe, return pipe, aerobic zone and transition zone exhaust pipe, anaerobic zone exhaust pipe, Separation area exhaust pipe, water outlet tank, outlet pipe, baffle, combined sloping plate I, combined sloping plate II, sloping plate; 所述的好氧区内置有半软性纤维束填料,所述好氧区通过挡板与其右侧的过渡区分隔,但通过挡板与组合斜板Ⅰ之间的缝隙相通;通过组合斜板Ⅰ与厌氧区分隔,所述好氧区最左侧底部从左至右分别设有隔室双侧布水器、微孔曝气管,所述隔室双侧布水器与进水管相连通,所述好氧区顶板上设有好氧区与过渡区排气管,好氧区与挡板底部结合处布有好氧区排泥管;The aerobic zone is built with semi-soft fiber bundle packing, and the aerobic zone is separated from the transition zone on the right side by a baffle, but communicated with the gap between the baffle and the combined sloping plate I; separated from the anaerobic zone by the combined sloping plate I, the leftmost bottom of the aerobic zone is provided with compartment double-sided water distributors and microporous aeration pipes from left to right, and the compartment bilateral water distributors are connected to the water inlet pipe. There are mud discharge pipes in the aerobic zone; 所述的过渡区内置有流化床填料K1,所述过渡区左侧通过挡板与好氧区分隔,但通过挡板与组合斜板Ⅰ之间的缝隙相通;通过组合斜板Ⅰ与厌氧区分隔,但通过组合斜板Ⅰ与组合斜板Ⅱ之间缝隙相通;The fluidized bed filler K1 is built in the transition zone, and the left side of the transition zone is separated from the aerobic zone by a baffle, but communicates with the gap between the baffle and the combined sloping plate I; it is separated from the anaerobic zone by the combined sloping plate I, but communicates through the gap between the combined sloping plate I and the combined sloping plate II; 所述的过渡区可在反应器实际运行中自主调整其所行使的功能,可在好氧半程硝化、厌氧氨氧化进行合理切换,可自调整好氧区、厌氧区之间配比,对运行参数的变动进行快速有效的响应,自主调节合理分配;若氧气浓度较高,为好氧或兼氧环境,则过渡区行使好氧区功能,以短程硝化反应为主,若氧气浓度较低,为缺氧或厌氧环境,则过渡区行使厌氧区功能,以厌氧氨氧化反应为主;The function of the transition zone can be adjusted independently during the actual operation of the reactor. It can be reasonably switched between aerobic half-stage nitrification and anaerobic ammonium oxidation. It can self-adjust the ratio between the aerobic zone and the anaerobic zone, respond quickly and effectively to changes in operating parameters, and independently adjust and distribute reasonably. If the oxygen concentration is high, it is an aerobic or facultative environment. Mainly anaerobic ammonium oxidation reaction; 所述的厌氧区位于过渡区与分离区之间,通过组合斜板Ⅰ与过渡区分隔,但通过组合斜板Ⅰ与组合斜板Ⅱ底部之间缝隙相通;通过组合斜板Ⅱ分别与导流区、分离区分隔,但通过组合斜板Ⅱ与顶板之间的缝隙与导流区相通;厌氧区顶板上布有厌氧区排气管,厌氧区组合斜板Ⅰ与组合斜板Ⅱ底部之间缝隙处设有过渡区与厌氧区排泥管。The anaerobic zone is located between the transition zone and the separation zone, and is separated from the transition zone by the combined sloping plate I, but communicates through the gap between the combined sloping plate I and the bottom of the combined sloping plate II; the combined sloping plate II is separated from the diversion zone and the separation zone, but communicates with the diversion zone through the gap between the combined sloping plate II and the top plate; 2.根据权利要求1所述生物反应器,其特征在于:所述的导流区位于厌氧区的右上侧,通过组合斜板Ⅱ与厌氧区分隔,但通过组合斜板Ⅱ与顶板之间的缝隙与厌氧区相通;通过斜板与分离区分隔,但通过斜板与组合斜板Ⅱ之间缝隙与分离区相通。2. The bioreactor according to claim 1, characterized in that: the diversion zone is located on the upper right side of the anaerobic zone, separated from the anaerobic zone by the combined inclined plate II, but communicated with the anaerobic zone through the gap between the combined inclined plate II and the top plate; separated from the separation zone by the inclined plate, but communicated with the separation zone through the gap between the inclined plate and the combined inclined plate II. 3.根据权利要求1所述生物反应器,其特征在于:所述的分离区位于生物反应器主体的最右侧,通过组合斜板Ⅱ、斜板分别与厌氧区、导流区分隔,但通过斜板与组合斜板Ⅱ之间缝隙与导流区相通;分离区顶板上设有分离区排气管,外侧设有出水槽、出水管、回流管,分离区通过出水槽狭缝与出水槽连通;分离区与组合斜板Ⅱ底部结合处布有分离区排泥管。3. The bioreactor according to claim 1, characterized in that: the separation zone is located at the far right of the main body of the bioreactor, and is separated from the anaerobic zone and the flow diversion zone by the combined sloping plate II and the sloping plate, but communicates with the flow diversion zone through the gap between the sloping plate and the combined sloping plate II; the separation zone exhaust pipe is arranged on the top plate of the separation zone, and the water outlet tank, the water outlet pipe, and the return pipe are arranged on the outside, and the separation zone communicates with the water outlet tank through the slit of the water outlet tank; . 4.根据权利要求1所述生物反应器,其特征在于:所述生物反应器主体长、宽、高比值为(4~6):1:(2~3),好氧区、过渡区、厌氧区、分离区体积比为3:1:2:1。4. The bioreactor according to claim 1, characterized in that: the ratio of the length, width, and height of the bioreactor body is (4-6):1:(2-3), and the volume ratio of the aerobic zone, transition zone, anaerobic zone, and separation zone is 3:1:2:1. 5.根据权利要求1所述生物反应器,其特征在于:所述隔室双侧布水器长度与生物反应器主体宽度相等,双侧板与反应器主体面形成封闭隔室,双侧板均开有圆孔阵,圆孔直径为反应器主体长度的0.05~0.015,双侧板的宽度为反应器主体长度的0.03。5. The bioreactor according to claim 1, characterized in that: the length of the water distributor on both sides of the compartment is equal to the width of the main body of the bioreactor, the double side plates form a closed compartment with the surface of the main body of the reactor, and both side plates are provided with circular hole arrays, the diameter of the round holes is 0.05 to 0.015 of the length of the main body of the reactor, and the width of the double side plates is 0.03 of the length of the main body of the reactor. 6.根据权利要求1所述生物反应器,其特征在于:所述微孔曝气管长度为好氧区长度1/2,一端紧邻隔室双侧布水器,沿生物反应器长度方向布置,位于反应器主体高度面一侧;6. The bioreactor according to claim 1, characterized in that: the length of the microporous aeration pipe is 1/2 of the length of the aerobic zone, and one end is adjacent to the water distributor on both sides of the compartment, arranged along the length direction of the bioreactor, and located on one side of the height surface of the reactor body; 其中,所述挡板位于反应器主体1/2长度处并垂直设置,挡板高度为(1/2~2/3) 反应器主体高度。Wherein, the baffle is located at 1/2 of the length of the reactor main body and arranged vertically, and the height of the baffle is (1/2-2/3) the height of the reactor main body. 7.根据权利要求1所述生物反应器,其特征在于:所述组合斜板Ⅰ由纵向斜板和横向斜板组成,纵向斜板与横向斜板之间夹角为150º;纵向斜板与反应器顶板接合,水平夹角为60º;横向斜板水平夹角为30º;7. The bioreactor according to claim 1, characterized in that: the combined inclined plate I is composed of a longitudinal inclined plate and a transverse inclined plate, and the angle between the longitudinal inclined plate and the transverse inclined plate is 150°; the longitudinal inclined plate is joined to the top plate of the reactor, and the horizontal angle is 60°; the horizontal angle between the transverse inclined plate is 30°; 其中,所述组合斜板Ⅱ由纵向斜板和横向斜板组成,纵向斜板与横向斜板夹角为150º;纵向斜板与反应器主体底部接合,水平夹角为60º,横向斜板水平夹角为30º;组合斜板Ⅱ与组合斜板Ⅰ之间缝隙宽度为2~10cm,组合斜板Ⅱ中横向斜板上边缘高度低于出水管高度3~15cm。Wherein, the combined inclined plate II is composed of a longitudinal inclined plate and a transverse inclined plate, and the angle between the longitudinal inclined plate and the transverse inclined plate is 150°; the longitudinal inclined plate is joined to the bottom of the reactor main body, the horizontal angle is 60°, and the horizontal inclined plate is 30°; the width of the gap between the combined inclined plate II and the combined inclined plate I is 2-10 cm, and the height of the edge of the transverse inclined plate in the combined inclined plate II is lower than the height of the outlet pipe by 3-15 cm.
CN201810418854.XA 2018-05-04 2018-05-04 Integrated Partial Nitrosation-ANAMMOX Inclined Plate Enhanced Bioreactor Active CN108298690B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810418854.XA CN108298690B (en) 2018-05-04 2018-05-04 Integrated Partial Nitrosation-ANAMMOX Inclined Plate Enhanced Bioreactor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810418854.XA CN108298690B (en) 2018-05-04 2018-05-04 Integrated Partial Nitrosation-ANAMMOX Inclined Plate Enhanced Bioreactor

Publications (2)

Publication Number Publication Date
CN108298690A CN108298690A (en) 2018-07-20
CN108298690B true CN108298690B (en) 2023-07-21

Family

ID=62846607

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810418854.XA Active CN108298690B (en) 2018-05-04 2018-05-04 Integrated Partial Nitrosation-ANAMMOX Inclined Plate Enhanced Bioreactor

Country Status (1)

Country Link
CN (1) CN108298690B (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111547852B (en) * 2020-05-22 2020-12-22 广西春晖环保工程有限责任公司 Control method of integrated shortcut nitrification-anaerobic ammonia oxidation denitrification process
CN114315037B (en) * 2021-12-30 2022-08-23 哈尔滨工业大学 Inversion A of external electric field 2 O-GDMBR (membrane bioreactor-membrane bioreactor) integrated village and town sewage treatment device and method
GB2619123A (en) * 2022-09-07 2023-11-29 Harbin Inst Technology Integrated inverted A2/O-GDMBR based on external electric field for village sewage treatment device and method

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CA2542894A1 (en) * 2006-04-04 2007-10-04 Laleh Yerushalmi Multi-environment wastewater treatment method
WO2017173708A1 (en) * 2016-04-05 2017-10-12 江南大学 Integrated reactor for biological treatment of livestock farm wastewater

Family Cites Families (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001179273A (en) * 1999-12-28 2001-07-03 Hitachi Chem Co Ltd Sludge storage tank and septic tank having the sludge storage tank
CN1239406C (en) * 2003-02-13 2006-02-01 上海达源环境科技工程有限公司 Biochemical reactor for treating sewage
CN201906487U (en) * 2010-11-25 2011-07-27 广州益方田园环保科技开发有限公司 Three-phase separator for sewage treatment
CN103508561B (en) * 2013-09-29 2014-12-31 浙江大学 Segmented oxygen supply self-circulation denitrification reactor
CN203582586U (en) * 2013-09-29 2014-05-07 浙江大学 Self-circulation denitrification reactor adopting sectional oxygen supply
CN103601293B (en) * 2013-10-10 2015-01-28 杭州师范大学 Tower-type bioreactor synchronously removing carbon, nitrogen and sulfur
CN103755026B (en) * 2013-12-30 2015-05-27 杭州师范大学 Integrated baffle plate internal circulation autotrophic nitrogen removal granular sludge reactor
CN104787889B (en) * 2015-04-29 2017-06-06 北京工业大学 The method for recovering municipal sewage short distance Anammox using the micro- exposure of hypoxemia and anoxia stirring
CN104986923B (en) * 2015-07-27 2017-06-06 北京工业大学 A kind of apparatus and method of the multistage A/O biological denitrificaions based on municipal sewage short distance nitration Anammox
CN105502663B (en) * 2016-02-18 2018-02-13 江西省科学院能源研究所 A kind of multifunctional bio denitrification reactor
CN106745737A (en) * 2016-12-17 2017-05-31 杭州师范大学 A kind of short distance nitration Anammox manifold type denitrification reactor
CN106904796B (en) * 2017-04-20 2020-11-10 成都孚华环保科技有限公司 Multistage diversion type SSMBBR sewage treatment system and treatment method
CN208454615U (en) * 2018-05-04 2019-02-01 中国海洋大学 Integrated partial nitrosation-anammox inclined plate bioreactor

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CA2542894A1 (en) * 2006-04-04 2007-10-04 Laleh Yerushalmi Multi-environment wastewater treatment method
WO2017173708A1 (en) * 2016-04-05 2017-10-12 江南大学 Integrated reactor for biological treatment of livestock farm wastewater

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
中试一体式部分亚硝化-厌氧氨氧化反应器的启动与区域特性;周正;王凡;林兴;董石语;朱强;李祥;黄勇;;环境科学(第03期) *

Also Published As

Publication number Publication date
CN108298690A (en) 2018-07-20

Similar Documents

Publication Publication Date Title
CN103936229B (en) A kind of municipal sewage improvement A2/ O intensified denitrification and dephosphorization processes device and technique
CN101514064B (en) Biological denitrification device of sequencing batch internal circulation biological denitrification process
CN201125187Y (en) A three-phase internal circulation biochemical reaction device
CN102276103B (en) Integrated in-situ denitrification aquaculture wastewater biological treatment device and treatment method
CN100469718C (en) Device and method for treating refractory wastewater by hydrolysis-composite membrane biology
CN102259980B (en) Biological aerated filter and sewage treatment process thereof
CN205170617U (en) Combined type treatment of domestic sewage integration equipment
CN104045156A (en) Integrated efficient autotrophic nitrogen removal reactor
CN102826715A (en) Sewage treatment method for nitrogen and phosphorus removal through combination of biofilm process and multilevel activated sludge process
CN103755026B (en) Integrated baffle plate internal circulation autotrophic nitrogen removal granular sludge reactor
CN108298690B (en) Integrated Partial Nitrosation-ANAMMOX Inclined Plate Enhanced Bioreactor
CN108383241B (en) Self-circulation autotrophic denitrification bioreactor
CN209226777U (en) A kind of reinforcing advanced nitrogen dephosphorization process sewage-treatment plant
CN207998522U (en) A kind of packing type country sewage integrated treatment unit
CN109502751A (en) A kind of green top partitioning type multistage AO integrated sewage disposal technique
CN101269879B (en) Zanjon type gas-lift stream-pull tridimensional circulation type inversion A<2>O integral co-construction oxidation ditch
CN203866153U (en) Improved reinforced A2/O denitrogenation and dephosphorization treating device for municipal sewage
CN107337270B (en) Bottom-inlet efficient denitrification aerobic granular sludge reactor with adjustable water inlet height and treatment process
CN101973630B (en) Pressure pipe type sewage treatment reactor
CN208454615U (en) Integrated partial nitrosation-anammox inclined plate bioreactor
CN104445616B (en) A kind of vertical Continuous Flow dephosphorization apparatus and method
CN214781014U (en) Rural single household sewage treatment plant
CN204874023U (en) Bury formula catalytic oxidation AO technology sewage treatment plant
CN201027190Y (en) Multi-chamber hydrolysis-composite membrane biological method for treating wastewater
CN204342500U (en) A kind of semi-open partition type alternating current raw water biological pretreatment reaction unit

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