CN100494104C - Helical self-circulating bioreactor - Google Patents
Helical self-circulating bioreactor Download PDFInfo
- Publication number
- CN100494104C CN100494104C CNB2007100682157A CN200710068215A CN100494104C CN 100494104 C CN100494104 C CN 100494104C CN B2007100682157 A CNB2007100682157 A CN B2007100682157A CN 200710068215 A CN200710068215 A CN 200710068215A CN 100494104 C CN100494104 C CN 100494104C
- Authority
- CN
- China
- Prior art keywords
- reaction chamber
- chamber
- pipe
- flow reaction
- plug flow
- 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.)
- Expired - Fee Related
Links
Images
Classifications
-
- Y02W10/12—
Landscapes
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
本发明公开了一种螺旋式自循环生物反应器。它具有反应器本体、支架,反应器本体设有平推流反应室、折流板沉淀室;平推流反应室底部和中心分别设有第一排泥管和回流管,以回流管为轴设有多层螺旋板,螺旋板底层设有进水管;折流板沉淀室下端为外圆筒渐扩管;折流板沉淀室中心为多片高低交错、垂直平行的折流板;折流板沉淀室入口为一气液提升管,气液提升管另一端连接平推流反应室顶端;折流板沉淀室出口设有溢流堰和出水管;折流板沉淀室上端为法兰盖,法兰盖中心设有排气管。本发明有效遏制了短流与气涌现象的产生;调节酸碱与基质平衡;提升了沉淀性能;具有很高的容积负荷、容积转化效率和容积产气效率,并具有抗基质和水力负荷冲击能力。
The invention discloses a spiral self-circulation bioreactor. It has a reactor body and a bracket. The reactor body is equipped with a plug flow reaction chamber and a baffle plate sedimentation chamber; the bottom and center of the plug flow reaction chamber are respectively equipped with a first mud discharge pipe and a return pipe, with the return pipe as the axis There are multi-layer spiral plates, and the bottom of the spiral plate is equipped with a water inlet pipe; the lower end of the baffle plate sedimentation chamber is an outer cylindrical expanding pipe; The inlet of the plate sedimentation chamber is a gas-liquid riser, and the other end of the gas-liquid riser is connected to the top of the push flow reaction chamber; the outlet of the baffle sedimentation chamber is provided with an overflow weir and an outlet pipe; the upper end of the baffle sedimentation chamber is a flange cover, An exhaust pipe is arranged in the center of the flange cover. The invention effectively curbs short flow and gas surge; adjusts acid-base and matrix balance; improves sedimentation performance; has high volume load, volume conversion efficiency and volume gas production efficiency, and has resistance to matrix and hydraulic load impact ability.
Description
技术领域 technical field
本发明涉及一种螺旋式自循环生物反应器。The invention relates to a spiral self-circulation bioreactor.
背景技术 Background technique
厌氧生物处理技术是在厌氧条件下,利用微生物的代谢作用,把有机污染物转化成沼气,从而使污水达到净化的过程。与好氧生物处理相比,厌氧生物处理具有耗能小,污泥产量低,且能回收清洁能源(沼气)的特点,是实现循环经济的有效手段之一,应用前景广阔。Anaerobic biological treatment technology is the process of converting organic pollutants into biogas by using the metabolism of microorganisms under anaerobic conditions, so as to purify sewage. Compared with aerobic biological treatment, anaerobic biological treatment has the characteristics of low energy consumption, low sludge output, and the ability to recover clean energy (biogas). It is one of the effective means to realize circular economy and has broad application prospects.
随着人们对厌氧生物过程认识的深入以及对厌氧生物处理技术应用的普及,厌氧生物反应器也得到了较好的开发。迄今,厌氧生物反应器已发展至以厌氧颗粒污泥膨胀床(EGSB)和厌氧内循环反应器(IC)为代表的第三代高效反应器。它们的特点是:污泥活性高,运行负荷高,泥水接触好,传质效果佳。然而,第三代反应器也有其固有的短流严重的缺点,限制了反应器转化效率和出水质量的进一步提高。由于高效反应器的容积负荷很高,其容积产气率也很大,所产沼气会对活性污泥(包括颗粒污泥)产生强烈搅动,致使活性污泥被大量洗出反应器。若污泥生长速度低于污泥流失速度,则反应器将最终失效。此外,高容积产气率还会产生大量短流,影响基质转化。With the deepening of people's understanding of anaerobic biological processes and the popularization of the application of anaerobic biological treatment technology, anaerobic bioreactors have also been better developed. So far, anaerobic bioreactors have been developed to the third generation of high-efficiency reactors represented by anaerobic granular sludge expanded bed (EGSB) and anaerobic internal circulation reactor (IC). Their characteristics are: high sludge activity, high operating load, good mud-water contact, and good mass transfer effect. However, the third-generation reactor also has its inherent serious shortcomings of short flow, which limits the further improvement of reactor conversion efficiency and effluent quality. Due to the high volume load of the high-efficiency reactor, its volumetric gas production rate is also high, and the biogas produced will strongly agitate the activated sludge (including granular sludge), resulting in a large amount of activated sludge being washed out of the reactor. If the sludge growth rate is lower than the sludge loss rate, the reactor will eventually fail. In addition, the high volumetric gas production rate will also generate a large number of short flows, which will affect the substrate conversion.
针对第三代厌氧生物反应器的上述缺陷,本发明试图通过设置螺旋板通道,延长流程,使泥水混合物沿此通道呈平推流式流动,强化反应器的处理效能,有效遏制短流现象;同时通过折流板沉淀、气液提升管与回流管的作用,使污泥强制回流,回收一部分碱度,中和产酸阶段形成的酸度,调节酸碱平衡。试验证明,据此开发的螺旋式自循环具有很好的厌氧处理效能,并具有很高的运行稳定性。Aiming at the above-mentioned defects of the third-generation anaerobic bioreactor, the present invention attempts to extend the process by setting a spiral plate channel, so that the mud-water mixture flows along the channel in a flat push-flow manner, strengthens the treatment efficiency of the reactor, and effectively curbs the short-flow phenomenon ; At the same time, through the action of baffle plate precipitation, gas-liquid riser and return pipe, the sludge is forced to reflux, recover part of the alkalinity, neutralize the acidity formed in the acid production stage, and adjust the acid-base balance. Tests have proved that the spiral self-circulation developed accordingly has good anaerobic treatment efficiency and high operation stability.
发明内容 Contents of the invention
本发明的目的是提供一种螺旋式自循环生物反应器。The purpose of the present invention is to provide a spiral self-circulation bioreactor.
它具有反应器本体、支架,反应器本体自下而上设有平推流反应室、折流板沉淀室;平推流反应室底部设有第一排泥管,平推流反应室顶端设有第二排泥管,平推流反应室中心设有回流管,以回流管为轴自下而上设有多层螺旋板,螺旋板底层设有进水管;折流板沉淀室下端为外圆筒渐扩管,外圆筒渐扩管中间设有第三排泥管,外圆筒渐扩管固定于反应室圆筒上端,外圆筒渐扩管底部与回流管顶端相连通;折流板沉淀室中心设有多片高低交错、垂直平行的折流板,在每块折流板间沿水位线设有第四排泥管;折流板沉淀室入口为气液提升管的一端,气液提升管另一端连接平推流反应室顶端;折流板沉淀室出口设有溢流堰和出水管;折流板沉淀室上端为法兰盖,法兰盖中心设有排气管。It has a reactor body and a bracket. The reactor body is equipped with a plug flow reaction chamber and a baffle plate sedimentation chamber from bottom to top; a first mud discharge pipe is provided at the bottom of the plug flow reaction chamber, and a There is a second row of mud pipes, a return pipe is provided in the center of the push flow reaction chamber, and a multi-layer spiral plate is arranged from bottom to top with the return pipe as the axis, and a water inlet pipe is provided at the bottom of the spiral plate; the lower end of the baffle plate sedimentation chamber is the outer Cylinder expander, the middle of the outer cylinder expander is provided with a third row of mud pipes, the outer cylinder expander is fixed on the upper end of the reaction chamber cylinder, the bottom of the outer cylinder expander is connected with the top of the return pipe; folding The center of the baffle settling chamber is equipped with a plurality of baffles staggered in height and vertically parallel, and a fourth mud discharge pipe is arranged between each baffle along the water level line; the entrance of the baffle settling chamber is one end of the gas-liquid riser , the other end of the gas-liquid riser is connected to the top of the push flow reaction chamber; the outlet of the baffle sedimentation chamber is provided with an overflow weir and an outlet pipe; the upper end of the baffle sedimentation chamber is a flange cover, and the center of the flange cover is provided with an exhaust pipe .
所述的平推流反应室呈圆筒状,平推流反应室高径比为4~10:1,平推流反应室直径与螺旋板螺距之比为1:2~5,平推流反应室横截面积S1与折流板沉淀室最大横截面积S2之比为1:1~4,平推流反应室与回流管横截面积之比为16~25:1,平推流反应室与气流提升管的横截面积S3之比为16~25:1。折流板沉淀室体积与反应器本体总体积之比为1~2:5,折流板数量为3-6片,奇数号折流板高出水位线5-20cm,偶数号折流板低于水位线深度为折流板沉淀室直径的10%-30%。外圆筒渐扩管与基准水平面的夹角α成50°~70°,气液提升管与基准水平面的夹角β为50°~70°。The plug flow reaction chamber is cylindrical, the height-to-diameter ratio of the plug flow reaction chamber is 4 to 10:1, the ratio of the diameter of the plug flow reaction chamber to the pitch of the spiral plate is 1:2 to 5, and the plug flow reaction chamber is 1:2 to 5. The ratio of the cross-sectional area S 1 of the reaction chamber to the maximum cross-sectional area S 2 of the baffle plate precipitation chamber is 1:1~4, and the ratio of the cross-sectional area of the plug flow reaction chamber to the return pipe is 16~25:1. The ratio of the cross-sectional area S3 of the flow reaction chamber to the flow riser is 16-25:1. The ratio of the volume of the baffle settling chamber to the total volume of the reactor body is 1-2:5, the number of baffles is 3-6 pieces, the odd-numbered baffles are 5-20cm higher than the water level line, and the even-numbered baffles are lower The depth at the water level is 10%-30% of the diameter of the baffle plate sedimentation chamber. The angle α between the expander of the outer cylinder and the reference horizontal plane is 50°-70°, and the angle β between the gas-liquid riser and the reference horizontal plane is 50°-70°.
本发明的优点:1)所置的螺旋板结构,一方面大大延长了反应室内的泥水流程(实现了有效高径比与实际反应器高径比分离),使其在所产沼气的作用下呈平推流式流动,有效地遏制了短流现象;另一方面起到了支撑上部污泥的作用,减轻了上下层污泥间的直接挤压,有助于沼气逸出,防止产生气涌现象;此外,由于污泥产气,螺旋板间存在垂直方向的气搅作用,促进了泥水间的传质,强化了基质降解。2)气液提升管与回流管贯通反应器的反应区和沉淀区,在所产沼气的作用下,对回流管底部产生负压抽吸作用,可加速回流管上部沉淀室内的泥水分离,还能强制液流循环。循环液流一方面可以调节反应室内的酸碱平衡,防止局部过酸或过碱,另一方面可以稀释进水基质浓度,具有较强的抗基质负荷冲击的能力。3)折流板沉淀区延长了泥水流程,增加了沉淀时间,同时,各块折板间互相的干扰较小,能缓冲水力波动,具有较强的抗水力负荷(流量)冲击的能力,使泥、水、气得到有效分离,保证出水质量。4)该反应器能承受很高的进水有机物浓度和很短的水力停留时间,具有很高的容积负荷、容积转化效率和容积产气效率(实验室小试运行,最高已达95%以上的容积转化率,100kgCOD/m3·d以上的容积负荷以及50m3/m3·d以上的容积产气率)。Advantages of the present invention: 1) The spiral plate structure, on the one hand, greatly prolongs the muddy water flow in the reaction chamber (realizing the separation of the effective height-to-diameter ratio and the actual reactor height-to-diameter ratio), making it under the action of the biogas produced It is a flat push flow, which effectively curbs the short flow phenomenon; on the other hand, it plays the role of supporting the upper sludge, reducing the direct extrusion between the upper and lower sludge, helping the escape of biogas and preventing gas surge In addition, due to the gas produced by the sludge, there is a vertical gas stirring effect between the spiral plates, which promotes the mass transfer between the mud and water and strengthens the degradation of the matrix. 2) The gas-liquid riser and the return pipe run through the reaction zone and the sedimentation zone of the reactor. Under the action of the biogas produced, negative pressure suction is generated on the bottom of the return pipe, which can accelerate the separation of mud and water in the sedimentation chamber at the upper part of the return pipe. Can force liquid circulation. On the one hand, the circulating liquid flow can adjust the acid-base balance in the reaction chamber to prevent local over-acid or over-alkaline; 3) The baffle plate settling area prolongs the muddy water flow and increases the settling time. At the same time, the mutual interference between the baffle plates is small, which can buffer hydraulic fluctuations and has a strong ability to resist hydraulic load (flow) impact, making Mud, water and gas are effectively separated to ensure the quality of the effluent. 4) The reactor can withstand a high concentration of influent organic matter and a short hydraulic retention time, and has a high volume load, volume conversion efficiency and volume gas production efficiency (laboratory small test operation, the highest has reached more than 95% The volume conversion rate, the volume load of 100kgCOD/m 3 ·d or more and the volume gas production rate of 50m 3 /m 3 ·d or more).
附图说明 Description of drawings
图1(a)是螺旋式自循环生物反应器结构示意图;Fig. 1 (a) is a structural representation of a spiral self-circulation bioreactor;
图1(b)是螺旋式自循环生物反应器A-A’截面图;Fig. 1 (b) is a spiral self-circulation bioreactor A-A ' sectional view;
图中:1.平推流反应室;2.折流板沉淀室;3.气液提升管;4.支架;5.第一排泥管;6.进水管;7.螺旋板;8.回流管;9.取样管;10.反应室圆筒;11.第二排泥管;12.第三排泥管;13.外圆筒渐扩管;14.出水管;15.第四排泥管;16.溢流堰;17.折流板;18.法兰盖;19.排气管;20.折流板沉淀室入口。In the figure: 1. Flat push flow reaction chamber; 2. Baffle plate sedimentation chamber; 3. Gas-liquid riser; 4. Support; 5. First mud discharge pipe; 6. Inlet pipe; 7. Spiral plate; 8. Return pipe; 9. Sampling pipe; 10. Reaction chamber cylinder; 11. Second mud discharge pipe; 12. Third mud discharge pipe; 13. Expanding pipe of outer cylinder; 14. Outlet pipe; 15. Fourth row Mud pipe; 16. Overflow weir; 17. Baffle; 18. Flange cover; 19. Exhaust pipe; 20. Inlet of baffle sedimentation chamber.
具体实施方式 Detailed ways
如附图所示,螺旋式自循环生物反应器具有反应器本体、支架4,反应器本体自下而上设有平推流反应室1、折流板沉淀室2;平推流反应室1底部设有第一排泥管5,平推流反应室1顶端设有第二排泥管11,平推流反应室1中心设有回流管8,以回流管8为轴自下而上设有多层螺旋板7,螺旋板7底层设有进水管6;折流板沉淀室2下端为外圆筒渐扩管13,外圆筒渐扩管13中间设有第三排泥管12,外圆筒渐扩管13固定于反应室圆筒16上端,外圆筒渐扩管13底部与回流管8顶端相连通;折流板沉淀室2中心设有多片高低交错、垂直平行的折流板17,在每块折流板17间沿水位线设有第四排泥管15;折流板沉淀室入口20为气液提升管3的一端,气液提升管3另一端连接平推流反应室1顶端;折流板沉淀室2出口设有溢流堰16和出水管14;折流板沉淀室2上端为法兰盖18,法兰盖18中心设有排气管19。As shown in the accompanying drawings, the spiral self-circulation bioreactor has a reactor body and a bracket 4, and the reactor body is provided with a plug flow reaction chamber 1 and a baffle plate precipitation chamber 2 from bottom to top; The bottom is provided with a first row of
平推流反应室1呈圆筒状,平推流反应室1高径比为4~10:1,平推流反应室1直径与螺旋板7螺距之比为1:2~5,平推流反应室1横截面积S1与折流板沉淀室2最大横截面积S2之比为1:1~4,平推流反应室1与回流管8横截面积之比为16~25:1,平推流反应室1与气流提升管3的横截面积S3之比为16~25:1。折流板沉淀室2体积与反应器本体总体积之比为1~2:5,折流板17数量为3-6片,奇数号折流板17高出水位线5-20cm,偶数号折流板17低于水位线深度为折流板沉淀室2直径的10%-30%,外圆筒渐扩管13与基准水平面的夹角α成50°~70°,气液提升管3与基准水平面的夹角β为50°~70°。The plug flow reaction chamber 1 is cylindrical, the height-to-diameter ratio of the plug flow reaction chamber 1 is 4-10:1, and the ratio of the diameter of the plug-flow reaction chamber 1 to the pitch of the spiral plate 7 is 1:2-5. The ratio of the cross-sectional area S1 of the flow reaction chamber 1 to the maximum cross-sectional area S2 of the baffle plate precipitation chamber 2 is 1:1-4, and the ratio of the cross-sectional area of the plug-flow reaction chamber 1 to the return pipe 8 is 16-25 :1, the ratio of the cross-sectional area S3 of the plug flow reaction chamber 1 to the airflow riser 3 is 16-25:1. The ratio of the volume of the baffle settling chamber 2 to the total volume of the reactor body is 1-2:5, the number of
螺旋式自循环生物反应器可由有机玻璃和钢板构建。接种污泥从折流沉淀室经回流管加入至反应室中。废水从反应室底部两螺旋板间的进水口进入,与回流的污泥混合后在反应室内发生反应,产生沼气。在沼气推动下,泥水呈平推流式流动。流至反应室上部的泥水混合物,在气体的推动下,共同进入沉淀室。在沉淀室中的每层折流板间,泥、水、气三相得到有效分离,污泥沉至沉淀室底部后,在沼气上升所致的负压抽吸作用下沿回流管返回至反应室底部,调节酸碱平衡,强化基质降解,并与后来的进水混合。分离后的废水经溢流堰由出水管排出,沼气体则由排气管引出。The spiral self-circulating bioreactor can be constructed of plexiglass and steel plate. Inoculation sludge is fed into the reaction chamber from the baffle sedimentation chamber through the return pipe. Waste water enters from the water inlet between the two spiral plates at the bottom of the reaction chamber, and reacts in the reaction chamber after mixing with the returning sludge to generate biogas. Driven by the biogas, the muddy water flows in a flat plug flow. The mud-water mixture flowing to the upper part of the reaction chamber, driven by the gas, enters the sedimentation chamber together. Between each layer of baffles in the sedimentation chamber, the three phases of mud, water, and gas are effectively separated. After the sludge sinks to the bottom of the sedimentation chamber, it returns to the reaction chamber along the return pipe under the action of negative pressure suction caused by the rise of biogas. At the bottom of the chamber, it adjusts the acid-base balance, strengthens the degradation of the matrix, and mixes with the subsequent influent. The separated waste water is discharged from the outlet pipe through the overflow weir, and the biogas is led out from the exhaust pipe.
Claims (10)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB2007100682157A CN100494104C (en) | 2007-04-24 | 2007-04-24 | Helical self-circulating bioreactor |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB2007100682157A CN100494104C (en) | 2007-04-24 | 2007-04-24 | Helical self-circulating bioreactor |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN101037269A CN101037269A (en) | 2007-09-19 |
| CN100494104C true CN100494104C (en) | 2009-06-03 |
Family
ID=38888474
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CNB2007100682157A Expired - Fee Related CN100494104C (en) | 2007-04-24 | 2007-04-24 | Helical self-circulating bioreactor |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN100494104C (en) |
Families Citing this family (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105906041B (en) * | 2016-06-07 | 2018-06-19 | 浙江大学 | From air supporting efficient anaerobe reactor and its method |
| CN106746387B (en) * | 2017-03-31 | 2020-05-12 | 河南工程学院 | A kind of decentralized sewage treatment method |
| CN109126680A (en) * | 2018-06-29 | 2019-01-04 | 平顶山金晶生物科技股份有限公司 | A kind of soluble soybean polysaccharide continuous extraction reactor |
| KR102098046B1 (en) * | 2019-12-16 | 2020-05-26 | (주)케이이씨시스템 | Vertical cylinder type anaerobic digestion apparatus for treating organic waste |
| CN118667627B (en) * | 2024-06-05 | 2025-10-24 | 山东大学 | A device and method for determining the toxicity of antibiotics in water and intermediate products thereof during treatment |
-
2007
- 2007-04-24 CN CNB2007100682157A patent/CN100494104C/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| CN101037269A (en) | 2007-09-19 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN100473616C (en) | Overlay sewage biochemical reactor | |
| CN101767875B (en) | Double-circulation biological membrane anaerobic ammonia oxidation reactor | |
| CN100491269C (en) | Efficient anaerobic ammoxidation reactor | |
| CN102603124B (en) | Two-phase two-period anaerobic organism reactor for processing wastewater | |
| CN102583731B (en) | Spiral symmetrical flow anaerobic reactor | |
| CN102249415B (en) | Air-lift internal circulation nitrogen and phosphorus removal bioreactor | |
| CN100436341C (en) | Spiral self-circulating anaerobic bioreactor | |
| CN201530770U (en) | A deep water combined biochemical treatment facility | |
| CN100448787C (en) | An air-lift self-circulating anaerobic bioreactor | |
| CN201190127Y (en) | Three-phase separator of anaerobic internal circulation reactor | |
| CN101269877A (en) | Two-stage anaerobic digestion cycle stripping system | |
| CN102774961B (en) | Multistage anaerobic wastewater treatment method and special device | |
| CN100494104C (en) | Helical self-circulating bioreactor | |
| CN100412007C (en) | Multiphase Internal Circulation Anaerobic Reactor | |
| CN101628754A (en) | Two-phase integrated anaerobic digestion reaction vessel | |
| CN202099166U (en) | Integrated circuit (IC) anaerobic reactor | |
| CN201999792U (en) | Internal circulation moving bed bioreactor | |
| CN106966490A (en) | A kind of high-efficiency aerobic reactor and sewage treatment process | |
| CN201049911Y (en) | Spiral self-circulating bioreactor | |
| CN202519088U (en) | Helical symmetrical flow anaerobic reactor | |
| CN100412008C (en) | Composite internal circulation anaerobic reactor | |
| CN202186922U (en) | An air-lift internal circulation nitrogen and phosphorus removal bioreactor | |
| CN111217446B (en) | High-efficient good oxygen biological fluidized bed reactor | |
| CN116199333B (en) | A sewage anaerobic treatment method with enhanced internal circulation | |
| CN205527987U (en) | Anaerobism inner loop hydrogen generation ware |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| C17 | Cessation of patent right | ||
| CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20090603 Termination date: 20100424 |
