CN1215993C - Batch type integrated membrane bioreactor - Google Patents
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- CN1215993C CN1215993C CN031335713A CN03133571A CN1215993C CN 1215993 C CN1215993 C CN 1215993C CN 031335713 A CN031335713 A CN 031335713A CN 03133571 A CN03133571 A CN 03133571A CN 1215993 C CN1215993 C CN 1215993C
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- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
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Abstract
Description
技术领域technical field
本发明属于环境工程技术领域,涉及污水处理及中水回用技术,特别涉及膜生物反应器工艺脱氮除磷功能实现的方法。The invention belongs to the technical field of environmental engineering, relates to sewage treatment and reclaimed water technology, in particular to a method for realizing the denitrification and dephosphorization functions of a membrane bioreactor process.
背景技术Background technique
我国是世界上13个贫水国之一,为节约宝贵的水资源,中水回用是有效途径之一。国内外的研究证明,将膜过滤和生物降解有机结合的膜生物反应器工艺是一种高效、实用的污水处理和中水回用技术,但是膜生物反应器脱氮除磷能力不足,无法满足日益严格的水质要求。my country is one of the 13 water-poor countries in the world. In order to save precious water resources, reuse of reclaimed water is one of the effective ways. Studies at home and abroad have proved that the membrane bioreactor process that combines membrane filtration and biodegradation is an efficient and practical technology for sewage treatment and reclaimed water reuse, but the membrane bioreactor has insufficient nitrogen and phosphorus removal capabilities to meet Increasingly stringent water quality requirements.
氮磷含量高的再生污水回用于工业冷却水、工业生产用水或市政杂用水时将造成以下主要危害:使受纳水体富营养化;导致输水管道、用水设备繁殖生物垢,从而造成堵塞或影响效率;增加消毒剂用量,提高制水成本的同时,降低水质的安全性。在《污水综合排放标准》(GB8978-1996)中对城镇污水二级处理厂出水水质提出了磷酸盐≤0.5mg/L,氨氮≤15mg/L的严格要求。Recycled sewage with high nitrogen and phosphorus content will cause the following main hazards when it is reused in industrial cooling water, industrial production water or municipal miscellaneous water: eutrophication of the receiving water body; lead to the propagation of biofouling in water pipelines and water equipment, resulting in blockage Or affect efficiency; increase the amount of disinfectant, while increasing the cost of water production, reduce the safety of water quality. In the "Comprehensive Wastewater Discharge Standard" (GB8978-1996), strict requirements for phosphate ≤ 0.5mg/L and ammonia nitrogen ≤ 15mg/L were put forward for the effluent quality of urban sewage secondary treatment plants.
传统的A2/O法同步脱氮除磷工艺需要厌氧池、缺氧池、好氧池及二沉池四个池体,好氧池出水需要由回流泵作用部分循环回到缺氧池,实现硝化液脱氮;二沉池含磷污泥需要由污泥泵作用部分循环回到厌氧池,实现聚磷菌充分放磷。此工艺流程复杂、能耗高、不易操作和控制,而且该工艺出水是二沉池的上清液,出水水质差,不能作为中水实现回用。The traditional A 2 /O synchronous nitrogen and phosphorus removal process requires four pools: anaerobic tank, anoxic tank, aerobic tank and secondary sedimentation tank. The effluent from the aerobic tank needs to be partially circulated back to the anoxic tank by the return pump. , to realize the denitrification of the nitrifying liquid; the phosphorus-containing sludge in the secondary sedimentation tank needs to be partially circulated back to the anaerobic tank by the action of the sludge pump, so as to realize the full release of phosphorus by the phosphorus-accumulating bacteria. This process is complex, high energy consumption, difficult to operate and control, and the effluent of this process is the supernatant of the secondary sedimentation tank, the effluent water quality is poor, and cannot be reused as reclaimed water.
发明内容Contents of the invention
本发明的目的是提供一种使膜生物反应器具有脱氮除磷功能的方法,其所需装置称为序批式一体化膜生物反应器。用该方法设计及建造膜生物反应器,将使其在保持原有优势的基础上,对氮磷污染物质能够充分有效地去除,而且操作简单、易于实现。The purpose of the present invention is to provide a method for making the membrane bioreactor have the function of denitrification and phosphorus removal, and the required device is called sequence batch integrated membrane bioreactor. Using this method to design and build a membrane bioreactor will enable it to fully and effectively remove nitrogen and phosphorus pollutants on the basis of maintaining the original advantages, and it is simple to operate and easy to implement.
实现本发明所述使膜生物反应器具有脱氮除磷功能方法的技术方案是:Realize the technical scheme that makes membrane bioreactor have denitrification and dephosphorization functional method described in the present invention is:
在膜生物反应器中增设搅拌机,利用液位控制器和时间继电器控制搅拌机、鼓风机、进水提升泵和出水抽吸泵四个设备的开停方式和运行时间,在同一个反应池中实现好氧、缺氧、厌氧三种环境。鼓风机曝气期间,由倒伞型中气泡曝气器产生气泡,在充分扰动膜丝、减缓膜污染的同时,向反应池中活性污泥提供充足的氧,使其处于好氧状态,从而异养菌降解有机污染物质,硝化细菌将氨氮氧化为硝酸盐,聚磷菌对磷进行过量吸收。鼓风机停止曝气时,抽吸泵停止,搅拌机开动,保证活性污泥处于悬浮状态,反应池内泥水混合均匀。同时提升泵以大流量进水,在尽量短的时间内,使反应池水位恢复至最高水位,由液位控制器控制提升泵停止。即提升泵的开泵由时间继电器控制,而停止是由液位控制器控制。在停止曝气后短时间内大量进水为反硝化提供了充足的电子供体,无须外加碳源;而且避免了反硝化菌和聚磷菌对有机底物的竞争,保证了良好的除磷效果;大量有机碳的进入,可使溶解氧迅速降低,保证反应池中足够的缺氧、厌氧时间。缺氧阶段反硝化菌以废水中含碳有机物为碳源使硝酸盐转化为氮气逸出,实现彻底的脱氮。硝酸盐浓度逐渐降低,进入厌氧阶段,聚磷菌充分放磷。在停止曝气后,由反硝化菌和聚磷菌作用,有机物也会得到进一步的去除。厌氧状态结束后,通过时间继电器控制,鼓风机开启,使反应池中活性污泥重新进入好氧状态。Add a mixer in the membrane bioreactor, use the liquid level controller and time relay to control the start-stop mode and running time of the four equipment of the mixer, the blower, the water inlet lift pump and the water outlet suction pump, and achieve good results in the same reaction tank. Oxygen, anoxic and anaerobic environments. During blower aeration, bubbles are generated by the inverted umbrella-type medium bubble aerator, which fully disturbs the membrane filaments and slows down membrane fouling, and at the same time provides sufficient oxygen to the activated sludge in the reaction tank to make it in an aerobic state, thereby reducing Bacteria cultivation degrades organic pollutants, nitrifying bacteria oxidize ammonia nitrogen to nitrate, and phosphorus accumulating bacteria absorb phosphorus excessively. When the blower stops aeration, the suction pump stops and the mixer starts to ensure that the activated sludge is in a suspended state and the mud and water in the reaction tank are evenly mixed. At the same time, the lifting pump feeds water with a large flow rate, and the water level of the reaction tank is restored to the highest water level in the shortest possible time, and the lifting pump is controlled by the liquid level controller to stop. That is, the opening of the lift pump is controlled by the time relay, while the stop is controlled by the liquid level controller. In a short period of time after the aeration is stopped, a large amount of water inflow provides sufficient electron donors for denitrification, without the need for additional carbon sources; and avoids the competition between denitrifying bacteria and phosphorus accumulating bacteria for organic substrates, ensuring good phosphorus removal Effect: The entry of a large amount of organic carbon can rapidly reduce dissolved oxygen and ensure sufficient anoxic and anaerobic time in the reaction tank. In the anoxic stage, denitrifying bacteria use carbon-containing organic matter in wastewater as a carbon source to convert nitrate into nitrogen and escape, thereby achieving complete denitrification. The concentration of nitrate gradually decreased and entered the anaerobic stage, and the phosphorus accumulating bacteria fully released phosphorus. After the aeration is stopped, organic matter will be further removed by denitrifying bacteria and phosphorus accumulating bacteria. After the anaerobic state is over, the blower is turned on through the time relay control, so that the activated sludge in the reaction tank enters the aerobic state again.
本方法能够强化膜生物反应器脱氮除磷功能的原因主要在于:采用序批式的运行方式,使微生物处于缺氧/厌氧/好氧交替的环境中;在停止曝气后短时间内集中进水,保证了足够的缺/厌氧时间;可以根据进水氮磷含量,就周期和交换比进行简单调节,灵活性高。The reason why this method can strengthen the denitrification and dephosphorization function of the membrane bioreactor mainly lies in: adopting the sequence batch operation mode, so that the microorganisms are in an anoxic/anaerobic/aerobic alternate environment; Concentrated water intake ensures sufficient anoxic/anaerobic time; the period and exchange ratio can be simply adjusted according to the nitrogen and phosphorus content of the influent, with high flexibility.
而且,本方法中停止曝气后,出水蠕动泵停止抽吸,使混合液中的物质向膜丝表面运动的作用力减弱,而同时搅拌机启动,对膜丝仍存在扰动作用,有利于膜丝表面附着物质向混合液方向扩散,从而可以减轻膜污染。Moreover, after the aeration is stopped in this method, the effluent peristaltic pump stops suction, so that the force of the substances in the mixed solution moving to the surface of the membrane filaments is weakened, and at the same time the mixer is started, which still has a disturbing effect on the membrane filaments, which is beneficial to the membrane filaments. Substances attached to the surface diffuse toward the mixed solution, thereby reducing membrane fouling.
反应池含磷剩余污泥由气提泵定期排至污泥浓缩池,使其浓缩、减容,上清液返回调节池进行再处理。鼓风机曝气阶段,只需打开支路上阀门,污泥就可以实现气提,不另外消耗电能。The excess phosphorus-containing sludge in the reaction tank is regularly discharged to the sludge thickening tank by the air lift pump to concentrate and reduce the volume, and the supernatant is returned to the regulating tank for reprocessing. In the aeration stage of the blower, only need to open the valve on the branch road, the sludge can be lifted by air, and no additional power consumption is required.
本发明的效果和益处是脱氮除磷能力强、流程简单、操作方便、能耗低,可用于处理高氮磷含量污水,对中水回用工程尤为适用。The effect and benefit of the present invention are strong denitrification and dephosphorization capabilities, simple process, convenient operation and low energy consumption, and can be used to treat sewage with high nitrogen and phosphorus content, especially suitable for reclaimed water reuse projects.
附图说明Description of drawings
附图是序批式一体化膜生物反应器工艺流程示意图。The accompanying drawing is a schematic diagram of the process flow of the sequencing batch integrated membrane bioreactor.
图中:(1)鼓风机;(2)提升泵;(3)搅拌机;(4)抽吸泵;(5)膜组件;(6)倒伞型中气泡曝气器;(7)气提泵;(8)阀门;(9)反应池;(10)调节池;(11)污泥浓缩池。In the figure: (1) blower; (2) lifting pump; (3) mixer; (4) suction pump; (5) membrane module; (6) inverted umbrella type medium bubble aerator; (7) air lift pump (8) valve; (9) reaction pool; (10) regulating pool; (11) sludge thickening pool.
具体实施方式Detailed ways
以下结合附图,详细说明本发明方法及装置的最佳实施例。The best embodiments of the method and device of the present invention will be described in detail below in conjunction with the accompanying drawings.
实施例Example
生活污水中C/N比通常在10∶1以上,此时设定时间继电器每1小时进行切换。若进水C/N比低于10∶1,则可延长循环周期中好氧阶段的时间,强化硝化作用;同时,提高好氧阶段的出水量,来增加缺/厌氧阶段的短时间内进入反应器的有机碳源量,强化反硝化效果。The C/N ratio in domestic sewage is usually above 10:1. At this time, the time relay is set to switch every hour. If the influent C/N ratio is lower than 10:1, the time of the aerobic stage in the cycle can be extended to strengthen nitrification; at the same time, the water output in the aerobic stage can be increased to increase the short-term time of the anoxic/anaerobic stage The amount of organic carbon source entering the reactor strengthens the denitrification effect.
工艺呈周期式运行,每个周期分为两个阶段,即好氧阶段和缺/厌氧阶段。鼓风机(1)与抽吸泵(4)同步启动,此阶段,只出水,不进水,反应池(9)水位下降,此为好氧阶段。1小时后,由时间继电器控制,鼓风机(1)与抽吸泵(4)停止运行,与此同时,提升泵(2)和搅拌机(3)同步启动。提升泵(2)以大流量进水,在尽量短的时间内,使反应池(9)水位恢复到最高水位,提升泵(2)的停止由液位控制器控制,此为缺/厌氧阶段。2小时后,搅拌机(3)由时间继电器控制停止,同时鼓风机(1)与抽吸泵(4)再启动,完成一个循环周期。鼓风机曝气时,定期打开阀门(8),含磷剩余污泥由气提泵(7)排至污泥浓缩池(11),污泥在池底浓缩,上清液返回调节池(10)再处理。本发明自控系统简单,易于实现,可使膜生物反应器具有极佳的脱氮除磷能力。The process runs in cycles, and each cycle is divided into two phases, namely the aerobic phase and the anoxic/anaerobic phase. The air blower (1) and the suction pump (4) start synchronously. At this stage, only water is discharged, and no water is taken in. The water level of the reaction tank (9) drops, which is an aerobic stage. After 1 hour, controlled by the time relay, the air blower (1) and the suction pump (4) stop running, and at the same time, the lifting pump (2) and the mixer (3) start synchronously. The lift pump (2) feeds water with a large flow rate, and the water level of the reaction tank (9) is restored to the highest water level in the shortest possible time. The stop of the lift pump (2) is controlled by the liquid level controller. This is anaerobic/anaerobic stage. After 2 hours, the mixer (3) is controlled by the time relay to stop, and simultaneously the blower (1) and the suction pump (4) are restarted to complete a cycle. When the blower is aerated, the valve (8) is opened regularly, and the excess sludge containing phosphorus is discharged to the sludge concentration tank (11) by the air lift pump (7), the sludge is concentrated at the bottom of the tank, and the supernatant is returned to the adjustment tank (10) reprocessing. The automatic control system of the invention is simple and easy to implement, and can make the membrane bioreactor have excellent nitrogen and phosphorus removal capabilities.
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| CN031335713A CN1215993C (en) | 2003-05-30 | 2003-05-30 | Batch type integrated membrane bioreactor |
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| CN1215993C true CN1215993C (en) | 2005-08-24 |
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Families Citing this family (14)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1304304C (en) * | 2005-09-08 | 2007-03-14 | 山东大学 | Process for two-step type bioreactor for sludge decrement |
| CN100384759C (en) * | 2006-05-12 | 2008-04-30 | 南京大学 | A kind of drinking water biological treatment method that realizes simultaneous nitrification and denitrification |
| CN101074141B (en) * | 2007-06-20 | 2010-05-19 | 大连春兴水处理科技发展有限公司 | Low-concentration organic wastewater regeneration and reuse process |
| CN101215045B (en) * | 2008-01-22 | 2010-06-09 | 天津工业大学 | Three-compartment submerged anaerobic membrane bioreactor |
| CN101250008B (en) * | 2008-03-25 | 2010-06-02 | 北京城市排水集团有限责任公司 | Device and method for developing interior carbon source of sewage treatment plant |
| CN101513590B (en) * | 2009-02-19 | 2011-02-16 | 北京科技大学 | Processing device of ammoniacal odor and spray liquid and operation method thereof |
| CN101885538B (en) * | 2009-05-15 | 2013-02-27 | 江西金达莱环保股份有限公司 | Membrane bioreactor process for removing phosphorus without mud discharge |
| CN101885537B (en) * | 2009-05-15 | 2011-12-07 | 江西金达莱环保研发中心有限公司 | Process for treating sewage with low sludge content |
| CN101973677A (en) * | 2010-10-29 | 2011-02-16 | 上海优博环境工程有限公司 | Sequencing batch submerged membrane bioreactor |
| CN104556550B (en) * | 2014-04-09 | 2016-06-29 | 高吁萍 | A kind of efficiently mental retardation lessening membrane fouling MBR devices and methods therefor |
| CN109110918A (en) * | 2018-09-18 | 2019-01-01 | 戚汝常 | A kind of novel SBR-MBR sewage disposal system and technique |
| CN111620521B (en) * | 2020-06-04 | 2025-06-24 | 湖南易净环保科技有限公司 | Sewage treatment system and sewage treatment method |
| CN111995077A (en) * | 2020-08-03 | 2020-11-27 | 优德太湖水务(苏州)有限公司 | Distributed sewage treatment automatic control device and method |
| CN117819704A (en) * | 2024-02-20 | 2024-04-05 | 中钢集团马鞍山矿山研究总院股份有限公司 | Domestic sewage treatment equipment and process adopting new control logic and layout |
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