CN112537845B - A system and method for anaerobic resource utilization of rural sewage - Google Patents

A system and method for anaerobic resource utilization of rural sewage Download PDF

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CN112537845B
CN112537845B CN202011392348.1A CN202011392348A CN112537845B CN 112537845 B CN112537845 B CN 112537845B CN 202011392348 A CN202011392348 A CN 202011392348A CN 112537845 B CN112537845 B CN 112537845B
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reaction zone
hydrolysis reaction
sewage
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CN112537845A (en
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刘建伟
冯文韬
陈欣玥
臧娜娜
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Beijing University of Civil Engineering and Architecture
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    • 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
    • C02F3/28Anaerobic digestion processes
    • C02F3/2853Anaerobic digestion processes using anaerobic membrane bioreactors
    • 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
    • C02F3/28Anaerobic digestion processes
    • C02F3/284Anaerobic digestion processes using anaerobic baffled reactors
    • 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
    • C02F3/28Anaerobic digestion processes
    • C02F3/286Anaerobic digestion processes including two or more steps
    • 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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

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Abstract

The invention discloses a rural sewage anaerobic resource utilization system and a method, the system comprises an anaerobic membrane biological reaction area, two sides of the anaerobic membrane biological reaction area are provided with anaerobic hydrolysis reaction areas communicated with the anaerobic membrane biological reaction area, the interior of the anaerobic hydrolysis reaction area is divided into at least two upflow reaction compartments by folded plates, two-phase separation fillers are transversely arranged in the upflow reaction compartments, a water distribution system and an aeration system are arranged below the anaerobic membrane biological reaction area and the anaerobic hydrolysis reaction area, and a sludge discharge port is arranged below the aeration system. The method comprises the following steps: after being distributed by a water distribution system, sewage flows into the anaerobic hydrolysis reaction area from bottom to top between the folded plates for primary treatment; and the sewage flows into the anaerobic membrane biological reaction zone for further treatment through the anaerobic hydrolysis reaction zone, the sludge is discharged from the sludge discharge port, and the purified water is discharged. The invention has simple structure, stable operation, high reaction efficiency, low energy consumption, low cost and easy start; simple operation and stable operation treatment effect.

Description

一种农村污水厌氧资源化利用系统及方法A system and method for anaerobic resource utilization of rural sewage

技术领域technical field

本发明涉及一种污水处理系统及方法,尤其涉及一种农村污水厌氧资源化利用系统及方法。The invention relates to a sewage treatment system and method, in particular to a system and method for anaerobic resource utilization of rural sewage.

背景技术Background technique

厌氧污水处理工艺在能源资源回收利用方面具有良好的应用前景。污水中的BOD5通过厌氧处理可以被转化为沼气等能源气体,污水中的有机氮通过厌氧处理转化为氨氮,经过厌氧处理的污水含有大量可供农作物生长的氮、磷元素,如果在去除其中的重金属离子、病原微生物等污染物指标的情况下,可以将出水回收利用。The anaerobic wastewater treatment process has good application prospects in the recovery and utilization of energy resources. BOD 5 in sewage can be converted into energy gas such as biogas through anaerobic treatment, and organic nitrogen in sewage can be converted into ammonia nitrogen through anaerobic treatment. In the case of removing heavy metal ions, pathogenic microorganisms and other pollutant indicators, the effluent can be recycled.

厌氧污水处理工艺高效运行的关键是厌氧微生物的截留和富集,因为厌氧微生物增殖缓慢,所以需要维持一定的生物量以保证反应效率。但传统的厌氧污水处理工艺普遍有启动时间长、厌氧污泥随着反应进行流失的问题,造成处理效率低,出水效果差,很难满足回收利用的需求。目前农村污水处理工艺多为厌氧加好氧工艺,重治理,轻利用,资源化利用程度不高。The key to the efficient operation of the anaerobic sewage treatment process is the retention and enrichment of anaerobic microorganisms. Because the proliferation of anaerobic microorganisms is slow, it is necessary to maintain a certain biomass to ensure the reaction efficiency. However, the traditional anaerobic sewage treatment process generally has the problems of long start-up time and loss of anaerobic sludge with the reaction, resulting in low treatment efficiency and poor effluent effect, and it is difficult to meet the needs of recycling. At present, the rural sewage treatment process is mostly anaerobic and aerobic process, which emphasizes treatment and neglects utilization, and the degree of resource utilization is not high.

目前传统的高效厌氧工艺主要通过形成厌氧颗粒污泥或在载体表面形成生物膜等方法实现厌氧微生物的截留和富集。传统的厌氧折板反应器在处理农村污水时有启动时间长、两相分离困难、处理效果不稳定等问题;厌氧生物滤池在处理农村污水时有填料易堵塞、处理效率低、不适合处理高有机负荷污水等问题。厌氧膜生物反应器尽管能够较达到较好的出水效果,但是膜污染问题依然制约着其发展推广。因此,传统厌氧工艺处理农村污水难以达到出水资源化利用的目的。At present, the traditional high-efficiency anaerobic process mainly realizes the retention and enrichment of anaerobic microorganisms by forming anaerobic granular sludge or forming biofilm on the surface of the carrier. The traditional anaerobic folded-plate reactor has problems such as long start-up time, difficulty in two-phase separation, and unstable treatment effect when treating rural sewage; anaerobic biological filter is easy to block with fillers, low treatment efficiency, and ineffective when treating rural sewage. It is suitable for dealing with high organic load sewage and other problems. Although the anaerobic membrane bioreactor can achieve better effluent effect, the problem of membrane fouling still restricts its development and promotion. Therefore, the traditional anaerobic process to treat rural sewage is difficult to achieve the purpose of water resource utilization.

发明内容SUMMARY OF THE INVENTION

发明目的:本发明的一个目的是提供一种反应高效、低能耗、低成本、操作空间少的农村污水厌氧资源化利用系统;Purpose of the invention: One purpose of the present invention is to provide a rural sewage anaerobic resource utilization system with high reaction efficiency, low energy consumption, low cost and less operation space;

本发明的另一个目的是提供一种利用农村污水厌氧资源化利用系统的方法。Another object of the present invention is to provide a method for utilizing the rural sewage anaerobic resource utilization system.

技术方案:本发明所述的农村污水厌氧资源化利用系统,包括厌氧膜生物反应区,所述厌氧膜生物反应区的两侧设置有与厌氧膜生物反应区相通的厌氧水解反应区,所述厌氧水解反应区内部通过折板分隔为至少两个上流式反应隔室,所述上流式反应隔室沿横向设置有将反应隔室上下分隔的两相分离填料,所述厌氧膜生物反应区和厌氧水解反应区下方设有配水系统和用于实现厌氧污泥在反应器内部的循环流动的曝气系统,所述曝气系统下方设有排泥口。Technical solution: The anaerobic resource utilization system for rural sewage according to the present invention includes an anaerobic membrane biological reaction zone, and two sides of the anaerobic membrane biological reaction zone are provided with anaerobic hydrolysis devices that communicate with the anaerobic membrane biological reaction zone. The reaction zone, the interior of the anaerobic hydrolysis reaction zone is divided into at least two up-flow reaction compartments by folded plates, and the up-flow reaction compartments are provided with two-phase separation fillers that separate the reaction compartments up and down along the transverse direction, and the The anaerobic membrane biological reaction zone and the anaerobic hydrolysis reaction zone are provided with a water distribution system and an aeration system for realizing the circulating flow of anaerobic sludge inside the reactor, and a sludge discharge port is provided below the aeration system.

优选地,本发明由折板构成的厌氧水解反应区改善了水力条件,强化了厌氧水解,提高了有机物处理效率;折板之间设置两相分离填料,将厌氧水解反应区分成上下两部分,每部分特定驯化了不同的微生物种群,从而使产酸相和产甲烷相进行分离。两相分离填料实现了两相分离,同时保留了氮、磷等营养物质,较传统厌氧污水处理工艺能获得更好的出水水质,经过处理后的水可回用于灌溉用水等,实现污水的资源化利用。Preferably, the anaerobic hydrolysis reaction zone composed of folded plates in the present invention improves hydraulic conditions, strengthens anaerobic hydrolysis, and improves the efficiency of organic matter treatment; two-phase separation fillers are arranged between the folded plates to divide the anaerobic hydrolysis reaction zone into upper and lower parts Two parts, each of which specifically domesticates a different microbial population, allowing for the separation of acidogenic and methanogenic phases. The two-phase separation packing realizes two-phase separation, while retaining nutrients such as nitrogen and phosphorus. Compared with the traditional anaerobic sewage treatment process, it can obtain better effluent quality. The treated water can be reused for irrigation water, etc., to realize sewage treatment. resource utilization.

优选地,所述两相分离填料上部的体积大于下部的体积。两相分离填料将厌氧水解反应区分为上下两部分,下部为产酸相,上部为产甲烷相,上部和下部体积比优选为2:1;两相分离填料采用立体网状填料,水流呈三维流动、不堵塞、不结团,孔隙率95%,下部采用玻璃钢网状支撑板,由于污水在折板之间曲折上升,更易与填料接触,使固液、气液更易分离,故填料可不倾斜布置。Preferably, the volume of the upper part of the two-phase separation packing is larger than the volume of the lower part. The two-phase separation packing divides the anaerobic hydrolysis reaction into upper and lower parts, the lower part is the acid-producing phase, the upper part is the methane-producing phase, and the volume ratio of the upper and lower parts is preferably 2:1; the two-phase separation packing adopts a three-dimensional mesh packing, and the water flow is Three-dimensional flow, no clogging, no agglomeration, 95% porosity, the lower part adopts glass fiber reinforced plastic mesh support plate, because the sewage rises in twists and turns between the folded plates, it is easier to contact the filler, so that the solid-liquid and gas-liquid are easier to separate, so the filler can not be used. Inclined arrangement.

优选地,所述厌氧膜生物反应区包括膜组件,所述膜组件的两侧设有用于对所述曝气系统产生的气体进行导流的导流板。膜组件选用中空纤维超滤膜,膜组件可以将厌氧微生物菌群截留在厌氧水解反应区,保证厌氧微生物的浓度,提高反应效率;膜组件还可将含有大分子有机物的污水截留,使其在厌氧水解反应区继续降解,通过膜组件的过滤作用,实现了水力停留时间和生物固体停留时间的分离,大大提高了系统的反应效率。与传统工艺相比,本发明的厌氧膜生物反应区减少了操作空间和单元操作数量,易于扩大规模及选择性回收、分离养分和资源。Preferably, the anaerobic membrane biological reaction zone includes a membrane module, and two sides of the membrane module are provided with guide plates for guiding the gas generated by the aeration system. The membrane module adopts hollow fiber ultrafiltration membrane, which can trap the anaerobic microbial flora in the anaerobic hydrolysis reaction zone to ensure the concentration of anaerobic microorganisms and improve the reaction efficiency; the membrane module can also trap the sewage containing macromolecular organic matter, It continues to degrade in the anaerobic hydrolysis reaction zone. Through the filtration of the membrane module, the separation of the hydraulic retention time and the biological solids retention time is realized, which greatly improves the reaction efficiency of the system. Compared with the traditional process, the anaerobic membrane biological reaction zone of the present invention reduces the operation space and the number of unit operations, and is easy to expand the scale and selectively recover and separate nutrients and resources.

优选地,所述折板、导流板和膜组件的顶部依次降低,所述折板、导流板和膜组件的厎部依次升高。本发明改变了传统厌氧折板的推流式进水,通过反应器底部均匀进水,使污水自下而上流动,独特的折板结构改善了水力条件,增强了厌氧污泥和污水在反应器内腔的循环流动,促进传质,降低了污水的有机负荷,有效缓解了膜污染的问题。Preferably, the tops of the folded plate, the deflector and the membrane assembly are lowered in sequence, and the cradles of the folded plate, the deflector and the membrane assembly are raised in sequence. The invention changes the push-flow water inflow of the traditional anaerobic folded plate, and the water is evenly fed through the bottom of the reactor, so that the sewage flows from bottom to top, the unique folded plate structure improves the hydraulic conditions, and strengthens the anaerobic sludge and sewage. The circulating flow in the inner cavity of the reactor promotes mass transfer, reduces the organic load of sewage, and effectively alleviates the problem of membrane fouling.

优选地,所述厌氧膜生物反应区连接出水口,所述出水口的一端与出水监测装置、出水加压泵连接,所述出水口的另一端与进水口连接用于实现水的循环。Preferably, the anaerobic membrane biological reaction zone is connected to a water outlet, one end of the water outlet is connected to the water outlet monitoring device and the outlet water pressurizing pump, and the other end of the water outlet is connected to the water inlet for realizing water circulation.

优选地,所述厌氧水解反应区的上方设有收集沼气的集气罩,所述集气罩上连接有排气管和放气阀。Preferably, a gas collecting hood for collecting biogas is arranged above the anaerobic hydrolysis reaction zone, and an exhaust pipe and a gas release valve are connected to the gas collecting hood.

优选地,所述集气罩上连接有沼气处理装置,所述沼气处理装置通过气体压缩机与曝气系统连接用于向曝气系统供气。反应器内腔中厌氧污泥将污水中的有机物分解为无机物,产生的沼气经过处理收集后通过系统底部的曝气装置进行曝气,既减缓了膜污染,又增强了厌氧污泥在反应器中的循环流动。Preferably, a biogas treatment device is connected to the gas collecting hood, and the biogas treatment device is connected to the aeration system through a gas compressor for supplying gas to the aeration system. The anaerobic sludge in the inner chamber of the reactor decomposes the organic matter in the sewage into inorganic matter, and the generated biogas is aerated through the aeration device at the bottom of the system after treatment and collection, which not only slows down the membrane pollution, but also enhances the anaerobic sludge. Circulation flow in the reactor.

优选地,所述配水系统与设置于厌氧水解反应区下方的进水口连接,所述进水口与进水监测装置及蠕动泵连接。污水从底部的配水系统配水可以使污水和厌氧污泥充分接触之后进入厌氧膜生物反应区,提高污水的降解效果,提高系统的抗冲击负荷能力,降低进入膜组件污水的有机负荷,减缓膜污染。Preferably, the water distribution system is connected to a water inlet arranged below the anaerobic hydrolysis reaction zone, and the water inlet is connected to a water inlet monitoring device and a peristaltic pump. The water distribution of sewage from the water distribution system at the bottom can make the sewage and anaerobic sludge fully contact and enter the anaerobic membrane biological reaction zone, improve the degradation effect of sewage, improve the anti-shock load capacity of the system, reduce the organic load of sewage entering the membrane module, slow down Membrane fouling.

优选地,所述厌氧水解反应区设有用于监测系统反应状态的多功能显示计。Preferably, the anaerobic hydrolysis reaction zone is provided with a multifunctional display meter for monitoring the reaction state of the system.

利用上述农村污水厌氧资源化利用系统的处理污水的方法,包括以下步骤:The method for treating sewage using the above-mentioned rural sewage anaerobic resource utilization system includes the following steps:

(S1)污水由配水系统布水后在折板之间自下向上流入厌氧水解反应区,进行初级处理;(S1) After the sewage is distributed by the water distribution system, it flows into the anaerobic hydrolysis reaction zone from bottom to top between the folded plates for primary treatment;

(S2)经由厌氧水解反应区的污水流入厌氧膜生物反应区进一步处理,污泥由排泥口排出,净化后的水排出。(S2) The sewage in the anaerobic hydrolysis reaction zone flows into the anaerobic membrane biological reaction zone for further treatment, the sludge is discharged from the sludge discharge port, and the purified water is discharged.

有益效果:本发明与现有技术相比,取得如下显著效果:1、构造简单,反应高效,低能耗、低成本、易启动,相对传统污水处理工艺,本发明装置减少了操作空间,更容易扩大规模以及对资源的选择性回收利用,更适合于处理污水。2、有机结合厌氧折流板反应器与厌氧膜生物反应器,采用一体化设计,发挥厌氧折流板技术和厌氧膜生物反应器的优势;3、本发明方法操作简单、运行处理效果稳定、高效。Beneficial effects: Compared with the prior art, the present invention achieves the following remarkable effects: 1. The structure is simple, the reaction is efficient, low energy consumption, low cost, and easy to start. Compared with the traditional sewage treatment process, the device of the present invention reduces the operating space and is easier to operate. Expanded scale and selective recycling of resources are more suitable for sewage treatment. 2. The anaerobic baffle plate reactor and the anaerobic membrane bioreactor are organically combined, and the integrated design is adopted to give full play to the advantages of the anaerobic baffle plate technology and the anaerobic membrane bioreactor; 3. The method of the present invention is simple and easy to operate. The treatment effect is stable and efficient.

附图说明Description of drawings

图1为本发明系统的结构示意图。FIG. 1 is a schematic structural diagram of the system of the present invention.

具体实施方式Detailed ways

下面结合说明书附图对本发明作进一步详细描述。The present invention will be described in further detail below with reference to the accompanying drawings.

如图1所示,本发明提供了一种农村污水厌氧资源化利用系统,包括厌氧膜生物反应区,在所述厌氧膜生物反应区的两侧设有与厌氧膜生物反应区相通的厌氧水解反应区。As shown in FIG. 1 , the present invention provides a rural sewage anaerobic resource utilization system, including an anaerobic membrane biological reaction zone, and two sides of the anaerobic membrane biological reaction zone are provided with an anaerobic membrane biological reaction zone. Connected anaerobic hydrolysis reaction zone.

厌氧水解反应区在竖直方向共设有8个完全相同的锯齿形折板5,以厌氧膜生物反应区为中心每侧分别布置4个折板5,每侧两折板5相互平行且等距离布置,如此设置使水流在折板5之间产生扰动,有利于污水与厌氧污泥充分接触。每侧两个折板5之间沿水平方向设置两相分离填料22,将厌氧水解反应区分为上下两部分,下部为产酸相,上部为产甲烷相,上部和下部体积比为2:1;两相分离填料22采用立体网状填料,水流呈三维流动、不堵塞、不结团,孔隙率95%,下部采用玻璃钢网状支撑板,由于污水在折板5之间曲折上升,更易与填料接触,使固液、气液更易分离,故填料可不倾斜布置。厌氧水解反应区安装多功能显示计7,用于监测系统反应状态,如pH、温度等,防止系统厌氧水解酸化导致pH过低。The anaerobic hydrolysis reaction zone is provided with 8 identical zigzag folded plates 5 in the vertical direction, and four folded plates 5 are arranged on each side with the anaerobic membrane biological reaction zone as the center, and the two folded plates 5 on each side are parallel to each other. And they are arranged at equal distances, so that the water flow is disturbed between the folded plates 5, which is conducive to the full contact between the sewage and the anaerobic sludge. Two-phase separation packing 22 is arranged between the two folded plates 5 on each side along the horizontal direction, and the anaerobic hydrolysis reaction is divided into upper and lower parts. 1; The two-phase separation packing 22 adopts three-dimensional mesh packing, the water flow is three-dimensional, does not block, does not agglomerate, the porosity is 95%, and the lower part adopts the glass fiber reinforced plastic mesh support plate. Contact with the packing makes it easier to separate solid-liquid and gas-liquid, so the packing can be arranged without tilting. A multi-function display meter 7 is installed in the anaerobic hydrolysis reaction area to monitor the reaction status of the system, such as pH, temperature, etc., to prevent the pH from being too low due to acidification of the system by anaerobic hydrolysis.

厌氧膜生物反应区包括膜组件4,膜组件4采用中空纤维超滤膜,膜孔径0.2μm,起始膜通量为60L/m2*h,沿竖直方向布置;膜组件4两侧安装导流板6,用于对曝气系统产生的气体进行导流。污水在经过厌氧水解反应区后,悬浮固体和大分子有机物含量大大降低,随后进入膜组件4进行高效的固液分离,将悬浮物和病原微生物等截留,使出水可直接回用,实现了污水的资源化;厌氧膜生物反应区设置在系统中心,两侧为厌氧水解反应区,一方面污水经过厌氧水解去除大分子有机物,随后进入膜组件4,能够起到降低膜污染的作用,保证较高的膜通量;另一方面提高系统的抗冲击负荷能力,保证系统的处理效果。折板5、导流板6和膜组件4的顶部依次降低,所述折板5、导流板6和膜组件4的厎部依次升高,如此设置形成导流梯度,有利于增强污水和厌氧污泥的扰动,促进污水和厌氧污泥在反应器内的循环流动。The anaerobic membrane biological reaction zone includes a membrane module 4. The membrane module 4 adopts a hollow fiber ultrafiltration membrane with a membrane pore size of 0.2 μm and an initial membrane flux of 60L/m 2 *h, which is arranged in the vertical direction; both sides of the membrane module 4 A deflector 6 is installed for guiding the gas generated by the aeration system. After the sewage passes through the anaerobic hydrolysis reaction zone, the content of suspended solids and macromolecular organic matter is greatly reduced, and then enters the membrane module 4 for efficient solid-liquid separation, and the suspended solids and pathogenic microorganisms are retained, so that the effluent can be directly reused. Recycling of sewage; the anaerobic membrane biological reaction zone is set in the center of the system, and the two sides are anaerobic hydrolysis reaction zones. On the one hand, the sewage undergoes anaerobic hydrolysis to remove macromolecular organic matter, and then enters the membrane module 4, which can reduce membrane pollution. It can ensure a higher membrane flux; on the other hand, it can improve the anti-shock load capacity of the system and ensure the treatment effect of the system. The tops of the folded plate 5, the deflector 6 and the membrane module 4 are lowered in turn, and the folds of the folded plate 5, the deflector 6 and the cubby of the membrane module 4 are raised in turn, so setting up a diversion gradient, which is conducive to enhancing sewage and pollution. The disturbance of anaerobic sludge promotes the circulating flow of sewage and anaerobic sludge in the reactor.

曝气系统包括微孔曝气头17和微孔曝气管18,设置于膜组件4和厌氧水解反应区下方,厌氧水解产生的沼气通过曝气系统对膜组件4进行冲刷,减缓膜污染,延长膜组件4使用寿命,对两相分离填料22冲刷,防止填料堵塞,加强水流扰动。The aeration system includes a microporous aeration head 17 and a microporous aeration pipe 18, which are arranged below the membrane module 4 and the anaerobic hydrolysis reaction zone. pollution, prolong the service life of the membrane module 4, wash the two-phase separation packing 22, prevent the packing from clogging, and strengthen the water flow disturbance.

系统下部侧壁设有进水口3,进水口3一端依次连接有进水监测装置2和进水蠕动泵1,另一端连接配水系统,配水系统包括设置于厌氧膜生物反应区和厌氧水解反应区下方的配水管19,配水管上均布有配水口20。膜组件通过负压管道连接出水口12,出水口12一端连接加压泵15和出水监测装置14,另一端与进水口3连接形成回流管路,回流管路上设置控制阀,以维持系统中有机负荷相对稳定。在厌氧膜生物反应区和厌氧水解反应区上方设有集气罩11,集气罩11上设有放气阀8和排气口9,排气管将气体排出。集气罩11上连接有沼气处理装置13,在沼气处理装置13与曝气系统之间设有气体压缩机16,将气体输送至微孔曝气管18内,通过微孔曝气头17向上曝气。在曝气系统和配水管19下方设有排泥口21,排泥口21两侧采用斜面布置,斜面与水平面成60°角,如此设置有利于防止污泥沉积,造成堵塞。The lower side wall of the system is provided with a water inlet 3. One end of the water inlet 3 is sequentially connected with a water inlet monitoring device 2 and a water inlet peristaltic pump 1, and the other end is connected with a water distribution system. The water distribution system includes an anaerobic membrane biological reaction zone and anaerobic hydrolysis. The water distribution pipes 19 below the reaction zone are uniformly distributed with water distribution ports 20 . The membrane module is connected to the water outlet 12 through a negative pressure pipeline. One end of the water outlet 12 is connected to the pressurizing pump 15 and the water outlet monitoring device 14, and the other end is connected to the water inlet 3 to form a return pipeline. A control valve is set on the return pipeline to maintain the organic flow in the system. The load is relatively stable. Above the anaerobic membrane biological reaction zone and the anaerobic hydrolysis reaction zone, a gas collecting hood 11 is provided. The gas collecting hood 11 is provided with a gas release valve 8 and an exhaust port 9, and the exhaust pipe discharges the gas. A biogas treatment device 13 is connected to the gas collecting hood 11, and a gas compressor 16 is arranged between the biogas treatment device 13 and the aeration system, and the gas is transported into the microporous aeration pipe 18, and the gas is passed upward through the microporous aeration head 17. Aeration. A mud discharge port 21 is provided under the aeration system and the water distribution pipe 19. The two sides of the mud discharge port 21 are arranged with inclined planes, and the inclined plane and the horizontal plane form an angle of 60°.

利用上述农村污水厌氧资源化利用系统的方法,包括以下步骤:The method for utilizing the above-mentioned rural sewage anaerobic resource utilization system includes the following steps:

(1)污水通过底部配水系统布水,配水管19贯穿整个反应器,污水从配水口自下而上均匀上升,起到均匀配水的效果,上流速度在0.5~1.5m/h,这是保证反应器平稳运行的关键环节;(1) The sewage is distributed through the bottom water distribution system. The water distribution pipe 19 runs through the entire reactor. The sewage rises evenly from the bottom to the top from the water distribution port, which has the effect of uniform water distribution. The key link for the smooth operation of the reactor;

(2)厌氧污泥接种于厌氧水解反应区,污水经厌氧水解反应区去除水中部分BOD5和悬浮固体;水流在两折板5之间螺旋上升,强化了污水与厌氧微生物的接触,保证了厌氧反应效果,提高了厌氧水解效率;横向穿过折板5设置两相分离填料22,将厌氧水解反应区分为上部和下部,污水在上部的停留时间大于下部,在厌氧水解反应区的水力停留时间为6~10h;(2) The anaerobic sludge is inoculated in the anaerobic hydrolysis reaction zone, and the sewage passes through the anaerobic hydrolysis reaction zone to remove part of the BOD5 and suspended solids in the water; the water flow spirals up between the two folded plates 5, which strengthens the contact between the sewage and the anaerobic microorganisms , to ensure the effect of anaerobic reaction and improve the efficiency of anaerobic hydrolysis; two-phase separation packing 22 is arranged transversely through the folded plate 5, and the anaerobic hydrolysis reaction is divided into upper and lower parts, and the residence time of sewage in the upper part is longer than that in the lower part, and the anaerobic hydrolysis reaction is divided into the upper part and the lower part. The hydraulic retention time of the oxygen hydrolysis reaction zone is 6-10h;

其中,在厌氧水解反应区上部产甲烷相污泥可添加少量蚝壳粉末,蚝壳粉含有钙、镁、铁等多种元素和多种氨基酸成分,能够促进产甲烷菌的生长,从而加快甲烷的生物合成;Among them, a small amount of oyster shell powder can be added to the methane-producing phase sludge in the upper part of the anaerobic hydrolysis reaction zone. The oyster shell powder contains calcium, magnesium, iron and other elements and various amino acid components, which can promote the growth of methanogens, thereby accelerating the methane biosynthesis;

污水在厌氧水解反应区产生的沼气进入集气罩11,集气罩11中的气体达到一定量后由排气管9输送到沼气处理装置13,随后通过气体压缩机16由气体循环管路送入曝气系统,微孔曝气头17对膜组件4和两相分离填料22进行曝气,微孔曝气强度为3-5L/m2*s,通过对沼气的回收利用既是对沼气的资源化利用,起到了节约能源的效果,又可缓解膜污染,起到延长膜组件寿命的效果;The biogas generated by the sewage in the anaerobic hydrolysis reaction zone enters the gas collecting hood 11. After the gas in the gas collecting hood 11 reaches a certain amount, it is transported to the biogas treatment device 13 by the exhaust pipe 9, and then passes through the gas compressor 16 through the gas circulation pipeline. It is sent to the aeration system, and the microporous aeration head 17 aerates the membrane module 4 and the two-phase separation packing 22, and the microporous aeration intensity is 3-5L/m 2 *s. The resource utilization of the membrane has the effect of saving energy, alleviating membrane pollution, and prolonging the life of the membrane module;

曝气系统采用间歇曝气,每10min的循环中,出水7~8min,曝气2~3min;经过曝气冲刷后,膜通量出现明显的恢复,冲洗后的膜通量可恢复至起始膜通量的85%~90%;The aeration system adopts intermittent aeration. In every 10min cycle, the effluent is 7-8min and the aeration is 2-3min; after the aeration flushing, the membrane flux is obviously recovered, and the membrane flux after flushing can be restored to the original 85% to 90% of membrane flux;

污水在厌氧水解过程产生的沼气一部分通过气体收集装置收集,一部分进入曝气系统作为曝气的气体来源,通过曝气系统的曝气作用,实现厌氧污泥在反应器内部的循环流动,促进传质,提高污水的降解率;Part of the biogas generated by the anaerobic hydrolysis of sewage is collected by the gas collection device, and part of it enters the aeration system as a gas source for aeration. Promote mass transfer and improve the degradation rate of sewage;

(3)经由厌氧水解反应区的污水流入厌氧膜生物反应区,通过膜组件4中超滤膜的截流作用去除绝大部分悬浮固体、大分子有机物以及病原微生物等;(3) The sewage in the anaerobic hydrolysis reaction zone flows into the anaerobic membrane biological reaction zone, and most of the suspended solids, macromolecular organic matter and pathogenic microorganisms are removed by the interception effect of the ultrafiltration membrane in the membrane module 4;

(4)污水在厌氧水解区产生的污泥通过反应器底部排泥口21排出,对污泥进行收集并进行资源化利用;(4) The sludge produced by the sewage in the anaerobic hydrolysis zone is discharged through the sludge discharge port 21 at the bottom of the reactor, and the sludge is collected and utilized for resource utilization;

污水经过厌氧膜生物反应区膜组件4的截流、过滤等作用实现对污水的高效净化并且达到资源化利用标准,通过出水加压泵15将水从膜组件4中抽吸出来,收集后进行农作物灌溉、景观用水等资源化利用;系统总水力停留时间8~12h,整个运行过程中,保持系统水温34~37℃;The sewage passes through the interception and filtration of the membrane module 4 in the anaerobic membrane biological reaction zone to achieve high-efficiency purification of the sewage and reach the standard of resource utilization. Resource utilization such as crop irrigation and landscape water; the total hydraulic retention time of the system is 8 to 12 hours, and the system water temperature is maintained at 34 to 37 °C during the entire operation process;

出水口12处安装的水质监测装置14检测水质,若COD负荷过高,膜组件4出水一部分通过出水口与进水口之间的循环管路回流至进水口,以保证进入系统的污水有机负荷相对稳定,减缓系统酸化,保证系统的稳定运行,当系统稳定出水浊度<0.6NTU、COD<80mg/L时,出水水质可达到回用标准。The water quality monitoring device 14 installed at the water outlet 12 detects the water quality. If the COD load is too high, part of the effluent from the membrane module 4 will return to the water inlet through the circulation pipeline between the water outlet and the water inlet to ensure that the organic load of the sewage entering the system is relatively high. Stable, slow down the acidification of the system and ensure the stable operation of the system. When the turbidity of the stable effluent of the system is less than 0.6NTU and COD is less than 80mg/L, the quality of the effluent can reach the reuse standard.

Claims (7)

1. The utility model provides a rural sewage anaerobism resource utilization system, its characterized in that, includes anaerobic membrane bioreaction district, anaerobic membrane bioreaction district's both sides are provided with the communicating anaerobic hydrolysis reaction zone with anaerobic membrane bioreaction district, anaerobic hydrolysis reaction district is inside to be separated for two at least upflow reaction compartments through folded plate (5), upflow reaction compartment is along transversely being provided with two-phase separation filler (22) with reaction compartment partition from top to bottom, and two-phase separation filler is upper and lower two parts with anaerobic hydrolysis reaction district, and the lower part is the acid production phase, and upper portion is the methane production phase, and upper portion and lower part volume ratio are 2: 1;
a water distribution system and an aeration system for realizing the circular flow of anaerobic sludge in the reactor are arranged below the anaerobic membrane biological reaction zone and the anaerobic hydrolysis reaction zone, and a sludge discharge port (21) is arranged below the aeration system;
the anaerobic membrane biological reaction zone comprises a membrane component (4), and guide plates (6) for guiding the flow of the gas generated by the aeration system are arranged on two sides of the membrane component (4); the tops of the folded plate (5), the guide plate (6) and the membrane assembly (4) are sequentially lowered, and the bottoms of the folded plate (5), the guide plate (6) and the membrane assembly (4) are sequentially raised.
2. The rural sewage anaerobic resource utilization system according to claim 1, wherein the anaerobic membrane biological reaction region is connected with a water outlet (12), one end of the water outlet (12) is connected with a water outlet monitoring device (14) and a water outlet pressure pump (15), and the other end of the water outlet (12) is connected with a water inlet (3) for realizing water circulation.
3. The rural sewage anaerobic resource utilization system of claim 1, wherein a gas collecting hood (11) for collecting biogas is arranged above the anaerobic hydrolysis reaction zone, and an exhaust pipe (9) and an air release valve (8) are connected to the gas collecting hood (11).
4. The rural sewage anaerobic resource utilization system according to claim 3, wherein a biogas treatment device (13) is connected to the gas collecting hood (11), and the biogas treatment device (13) is connected to the aeration system through a gas compressor (16) and used for supplying gas to the aeration system.
5. The rural sewage anaerobic resource utilization system of claim 1, wherein the water distribution system is connected with a water inlet (3) arranged below the anaerobic hydrolysis reaction zone, and the water inlet (3) is connected with a water inlet monitoring device (2) and a peristaltic pump (1).
6. The rural sewage anaerobic resource utilization system of claim 1, wherein the anaerobic hydrolysis reaction zone is provided with a multifunctional display meter (7) for monitoring the reaction state of the system.
7. A method for treating sewage by using the anaerobic resource utilization system for rural sewage of claim 1, which is characterized by comprising the following steps:
(S1) the sewage flows into the anaerobic hydrolysis reaction zone from bottom to top between the folded plates (5) after being distributed by a water distribution system for primary treatment;
(S2) the sewage flows into the anaerobic membrane biological reaction zone through the anaerobic hydrolysis reaction zone for further treatment, the sludge is discharged from a sludge discharge port, and the purified water is discharged.
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