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CN105368710B - Anaerobic digestion device for kitchen waste - Google Patents

Anaerobic digestion device for kitchen waste Download PDF

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CN105368710B
CN105368710B CN201510926206.1A CN201510926206A CN105368710B CN 105368710 B CN105368710 B CN 105368710B CN 201510926206 A CN201510926206 A CN 201510926206A CN 105368710 B CN105368710 B CN 105368710B
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孔峰
张晓叶
程洁红
姜翠萍
路娟娟
高永�
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Abstract

本发明公开了一种餐厨垃圾的厌氧消化装置,厌氧消化装置的反应器主体内设置固相反应区和液相反应区,反应器顶部设置出气口、回流水进水口,和测温口,回流水进水口下部设置喷淋头,液相反应区下设置出水口,反应器底部设置进水口和排泥管。在对餐厨垃圾进行厌氧消化时,通过浸没式厌氧消化和淋滤反应交替运行的方式,可以使得餐厨垃圾的固相残渣和液相废液都得以充分厌氧消化反应,以最大程度使得餐厨垃圾得以处理,实现最大程度的资源化处理。

The invention discloses an anaerobic digestion device for kitchen waste. A solid-phase reaction zone and a liquid-phase reaction zone are arranged in a reactor main body of the anaerobic digestion device, and an air outlet, a return water inlet, and a temperature measuring device are arranged on the top of the reactor. A sprinkler head is set at the lower part of the return water inlet, a water outlet is set under the liquid phase reaction zone, and a water inlet and a sludge discharge pipe are set at the bottom of the reactor. When anaerobic digestion of food waste is carried out, through the alternate operation of submerged anaerobic digestion and leaching reaction, the solid phase residue and liquid phase waste liquid of food waste can be fully anaerobic digestion reaction, with the maximum The degree enables the kitchen waste to be treated and realizes the maximum resource treatment.

Description

餐厨垃圾的厌氧消化装置Anaerobic digestion device for food waste

本申请是申请号为201410178288.1,申请日为2014年4月29日,发明创造名称为“餐厨垃圾的厌氧消化装置和消化方法”的发明专利申请的分案申请。This application is a divisional application of the invention patent application with the application number 201410178288.1 and the application date of April 29, 2014, and the invention name is "anaerobic digestion device and digestion method for kitchen waste".

技术领域technical field

本发明涉及一种厌氧消化系统,具体涉及一种餐厨垃圾的厌氧消化装置。The invention relates to an anaerobic digestion system, in particular to an anaerobic digestion device for kitchen waste.

背景技术Background technique

餐厨垃圾是指家庭、学校、机关、公共食堂以及餐饮行业的食物废料、餐饮剩余物、食品加工废料及不可再食用的动植物油脂和各类油水混合物,是城市生活垃圾的一部分。目前国内厨余垃圾处理方式主要是以和生活垃圾一起填埋、焚烧处理为主,填埋处理方式会降低填埋场的使用年限,而对于焚烧处理方式,我国仅有深圳等少数发达城市采用了垃圾焚烧技术,且对焚烧所产生的二恶英、氮氧化物、二氧化硫等有害气体、粉尘、废水等还未能有效控制。为了实现资源的可持续发展,必须寻找更有效的处理方式,实现厨余垃圾的有效资源化,对我国的经济与环境发展产生重大的意义。Food waste refers to food waste, catering leftovers, food processing waste and non-edible animal and vegetable oils and various oil-water mixtures from families, schools, institutions, public canteens and catering industries. It is part of urban domestic waste. At present, domestic kitchen waste treatment methods are mainly landfill and incineration together with domestic waste. The landfill treatment method will reduce the service life of the landfill. As for the incineration treatment method, only a few developed cities such as Shenzhen have adopted it. Waste incineration technology has been adopted, and the harmful gases, dust, waste water, etc. produced by incineration such as dioxin, nitrogen oxides, and sulfur dioxide have not been effectively controlled. In order to realize the sustainable development of resources, it is necessary to find a more effective treatment method to realize the effective recycling of kitchen waste, which is of great significance to the economic and environmental development of our country.

厌氧消化是微生物在不存在氧气的情况下分解生物可降解材料的一系列过程。生物可降解材料包括废纸、餐厨垃圾、高浓度有机废水、动物排泄物和液体废物等。厌氧消化适合于处理湿润的有机材料,被广泛用于有机废物的处理。Anaerobic digestion is a series of processes in which microorganisms break down biodegradable materials in the absence of oxygen. Biodegradable materials include waste paper, kitchen waste, high-concentration organic wastewater, animal excrement and liquid waste, etc. Anaerobic digestion is suitable for the treatment of wet organic materials and is widely used in the treatment of organic waste.

例如中国专利文献CN 102939369 A(申请号 201080063847.4)公开了一种厌氧反应器,反应器为罐的形式,通过实心部件被分开成分离的室。每个室包括进料分配系统、填充床以及用于生物气和液体排放的装置。使用时,进料分配系统将进料基本均匀地分配通过每个室的基部。每个堆叠的反应室优选的包括混合空间,其含有或适合于含有进料管线或进料分配系统。进料分配系统是可操作的以将进料递送并分配至室的基部并将其与厌氧细菌混合。在混合空间的上方,通常设置具有上填充格栅和下填充格栅的填充床。填充床包括填充介质和厌氧细菌。通过室内所包括的厌氧细菌将混合空间内的进料主要转换为挥发性脂肪酸、氢和二氧化碳。任何适合的填充介质均可在填充床中使用。为了为产甲烷细菌提供适合的环境,填充介质具有高表面积体积比。但是该厌氧反应器结构较复杂,运行时物料的流进流出控制繁琐。For example, Chinese patent document CN 102939369 A (application number 201080063847.4) discloses an anaerobic reactor in the form of a tank, which is divided into separate chambers by solid components. Each chamber includes feed distribution systems, packed beds, and devices for biogas and liquid discharge. In use, the feed distribution system distributes feed substantially evenly across the base of each chamber. Each stacked reaction chamber preferably includes a mixing space containing or adapted to contain feed lines or a feed distribution system. The feed distribution system is operable to deliver and distribute feed to the base of the chamber and mix it with the anaerobic bacteria. Above the mixing space, a packed bed with an upper packing grid and a lower packing grid is usually arranged. Packed beds include packing media and anaerobic bacteria. The feed in the mixing space is primarily converted to volatile fatty acids, hydrogen and carbon dioxide by anaerobic bacteria included in the chamber. Any suitable packing media can be used in the packed bed. In order to provide a suitable environment for methanogenic bacteria, the packing medium has a high surface area to volume ratio. However, the structure of the anaerobic reactor is relatively complicated, and the inflow and outflow control of materials during operation is cumbersome.

发明内容Contents of the invention

本发明所要解决的技术问题是提供一种结构简单、消化程度高的餐厨垃圾的厌氧消化装置。The technical problem to be solved by the invention is to provide an anaerobic digestion device for kitchen waste with simple structure and high degree of digestion.

实现本发明目的的技术方案是一种餐厨垃圾的厌氧消化装置,包括反应器主体、上盖、循环泵、输水管路、回水管路、控制阀和原水池;循环泵为双向循环泵;上盖设置在反应器主体的顶部,密封反应器主体内部的空腔;循环泵通过输水管路将原水池中的废液输送至反应器主体底部的进水口,循环泵通过回水管路将反应器主体内部的反应液从上方回流送入反应器内部。The technical solution for realizing the purpose of the present invention is an anaerobic digestion device for kitchen waste, comprising a reactor main body, an upper cover, a circulation pump, a water delivery pipeline, a return water pipeline, a control valve and a raw water pool; the circulation pump is a two-way circulation pump The upper cover is arranged on the top of the reactor main body to seal the cavity inside the reactor main body; the circulation pump transports the waste liquid in the raw water tank to the water inlet at the bottom of the reactor main body through the water delivery pipeline, and the circulation pump transports the waste liquid in the raw water tank to the water inlet at the bottom of the reactor main body through the water return pipeline The reaction liquid in the main body of the reactor is fed back into the reactor from above.

反应器主体的内部设有固相反应区和液相反应区,反应器主体的底部设有底部排泥口;液相反应区包括上、下筛网和两个筛网之间的填料;固相反应区位于的上筛网的上方,固相反应区的底部设有排泥口。The interior of the reactor body is provided with a solid phase reaction zone and a liquid phase reaction zone, and the bottom of the reactor body is provided with a bottom sludge outlet; the liquid phase reaction zone includes upper and lower screens and packing between the two screens; The phase reaction zone is located above the upper screen, and the bottom of the solid phase reaction zone is provided with a sludge discharge port.

上述上盖上设有出气口、回流进水口和测温口;出气口与出气管相连通,出气管与气体储罐相连;回流进水口与回水管路的出水口相连通;测温口内设置用于检测反应器主体内部的温度的测温探头。The upper cover is provided with a gas outlet, a return water inlet and a temperature measuring port; the gas outlet is connected to the gas outlet pipe, and the gas outlet pipe is connected to the gas storage tank; the return water inlet is connected to the water outlet of the return water pipeline; the temperature measuring port is set Temperature probe for detecting the temperature inside the reactor body.

所述输水管路按照液体的流向依次包括第一管道、第二管道、第三管道、第四管道和进水管;第一管道的进水口位于原水池内的液面下方,第一管道的出水口与第一三通的右接口相连,第一三通的左接口与第二管道的进水端相连,第二管道的出水端与循环泵的右侧端口相连,循环泵的左侧端口与第三管道的进水端相连,第三管道的出水端与第二三通的右接口的相连,第二三通的上接口与第四管道的进水端相连,第四管道的出水端与进水管的进水端相连,进水管的出水端从反应器主体的底部伸入反应器主体内,进水管的出水端连接布水器。The water delivery pipeline includes a first pipeline, a second pipeline, a third pipeline, a fourth pipeline and a water inlet pipe in sequence according to the flow direction of the liquid; the water inlet of the first pipeline is located below the liquid level in the raw water pool, and the water outlet of the first pipeline It is connected with the right port of the first tee, the left port of the first tee is connected with the water inlet of the second pipe, the water outlet of the second pipe is connected with the right port of the circulation pump, and the left port of the circulation pump is connected with the water inlet of the second pipe. The water inlet of the third pipe is connected, the water outlet of the third pipe is connected with the right port of the second tee, the upper port of the second tee is connected with the water inlet of the fourth pipe, and the water outlet of the fourth pipe is connected with the water inlet. The water inlet ends of the water pipes are connected, the water outlet ends of the water inlet pipes extend into the reactor body from the bottom of the reactor body, and the water outlet ends of the water inlet pipes are connected to the water distributor.

所述回水管路按照液体的流向依次包括出水管、第五管道、第六管道、第七管道和第八管道;出水管的进水端口位于液相反应区的下端,出水管的出水口与第五管道的进水口相连,第五管道的出水口与第三三通的左接口相连,第三三通的右接口与第六管道相连,第六管道的出水口接储液罐;第三三通的下接口与第七管道的进水口相连,第七管道的出水口与第二三通的左接口的相连,第七管道通过第二三通、输水管路的第三管道与循环泵的左侧端口相连,循环泵的右侧端口通过输水管路的第二管道和第一三通与第八管道的进水口相连,第八管道的出水口与回流进水管的进水端相连,回流进水管的出水端从上盖伸入反应器主体内。The return pipeline includes an outlet pipe, a fifth pipe, a sixth pipe, a seventh pipe, and an eighth pipe in sequence according to the flow direction of the liquid; The water inlet of the fifth pipe is connected, the water outlet of the fifth pipe is connected with the left port of the third tee, the right port of the third tee is connected with the sixth pipe, and the water outlet of the sixth pipe is connected with the liquid storage tank; The lower interface of the tee is connected to the water inlet of the seventh pipe, the water outlet of the seventh pipe is connected to the left interface of the second tee, and the seventh pipe passes through the second tee, the third pipe of the water delivery pipeline and the circulation pump The left port of the circulating pump is connected with the water inlet of the eighth pipe through the second pipe and the first tee of the water delivery pipeline, and the water outlet of the eighth pipe is connected with the water inlet end of the return water inlet pipe. The water outlet end of the return water inlet pipe extends into the reactor main body from the upper cover.

一种如上所述的餐厨垃圾的厌氧消化装置对餐厨垃圾进行厌氧消化方法,包括以下步骤:A method for anaerobic digestion of kitchen waste by an anaerobic digestion device for food waste as described above, comprising the following steps:

①菌种的驯化,驯化后的菌种附着在填料上。① Domestication of the strains, the domesticated strains are attached to the filler.

②餐厨垃圾的固液分离,将餐厨垃圾进行固液分离,分离得到的固相垃圾的含固率为70%~80%,储放在原泥池;液相垃圾即废液储放在原水池中待处理。② Solid-liquid separation of kitchen waste, solid-liquid separation of kitchen waste, the solid content of the separated solid phase waste is 70% to 80%, and stored in the original mud pool; liquid phase waste, that is, waste liquid, is stored in the original In the pool to be treated.

③物料的装填,打开反应器主体顶部的上盖,将液相反应区的上、下筛网之间填充满步骤①的填料,厌氧菌种附着在填料内部;然后将原泥池中的固相垃圾转移至上筛网上方,固相垃圾的放置高度为反应器主体高度的1/5~2/5,固相垃圾装填完毕后盖上上盖。③Material loading, open the upper cover on the top of the reactor main body, fill the space between the upper and lower screens in the liquid phase reaction zone with the filler of step ①, and anaerobic bacteria adhere to the inside of the filler; The solid phase waste is transferred to the top of the upper screen, and the height of the solid phase waste is 1/5 to 2/5 of the height of the main body of the reactor. After the solid phase waste is filled, the upper cover is closed.

④餐厨垃圾的厌氧消化,厨垃圾的厌氧消化过程总耗时为24~42天,由3~5个消化周期组成,每一个消化周期依次包括浸没式厌氧消化过程和淋滤反应过程;浸没式厌氧消化过程中废液浸没固相垃圾;淋滤反应过程中液相反应区中的反应液通过回水管路输送至反应器主体的顶部,反应液喷淋在固相反应区的固体垃圾上方;3~5个消化周期结束后完成餐厨垃圾的厌氧消化过程。④ Anaerobic digestion of food waste. The anaerobic digestion process of kitchen waste takes 24 to 42 days in total and consists of 3 to 5 digestion cycles. Each digestion cycle includes submerged anaerobic digestion process and leaching reaction in turn. process; in the submerged anaerobic digestion process, the waste liquid is submerged in the solid phase garbage; in the leaching reaction process, the reaction liquid in the liquid phase reaction zone is transported to the top of the reactor main body through the return pipe, and the reaction liquid is sprayed in the solid phase reaction area Above the solid waste; after 3 to 5 digestion cycles, the anaerobic digestion process of kitchen waste is completed.

上述步骤①驯化菌种时,取含固率为5%~7%的城市污水处理厂的厌氧池中的原泥装入培养池中,培养池中放入填料,培养池中的原泥浸没填料,驯化菌种时,向培养池中加入营养液,在33℃~37℃下菌种驯化10~15d。The above steps 1. When domesticating the strains, take the raw mud in the anaerobic tank of the urban sewage treatment plant with a solid content rate of 5% to 7% and put it into the culture tank, put fillers in the culture tank, and put the raw mud in the culture tank When submerging the filler and acclimating the strains, add nutrient solution into the culture tank, and acclimatize the strains at 33°C to 37°C for 10 to 15 days.

上述步骤④餐厨垃圾厌氧消化时,进行第一个消化周期的浸没式厌氧消化过程时,打开输水管路上的控制阀,关闭回水管路上的控制阀;打开循环泵,循环泵将原水池中的废液从反应器主体底部的进水管送入反应器主体内,待液面浸没固相反应区的固体垃圾的顶部,关闭循环泵,开始浸没式厌氧处理,浸没式厌氧处理持续4~7天;In the above step 4, during the anaerobic digestion of food waste, when performing the submerged anaerobic digestion process of the first digestion cycle, open the control valve on the water delivery pipeline and close the control valve on the return water pipeline; turn on the circulation pump, and the circulation pump will convert the original The waste liquid in the pool is sent into the main body of the reactor from the water inlet pipe at the bottom of the main body of the reactor, and when the liquid surface is immersed in the top of the solid waste in the solid phase reaction area, the circulating pump is turned off, and the submerged anaerobic treatment starts. last for 4 to 7 days;

待浸没式厌氧消化过程结束后,关闭输水管路上的控制阀,打开回水管路上的控制阀;打开循环泵,循环泵将液相反应区中的反应液通过回水管路输送至反应器主体的顶部,反应液喷淋在固相反应区的固体垃圾上方,固相反应区的固体垃圾进行淋滤反应4~7天,完成厌氧消化的第一个周期;After the submerged anaerobic digestion process is over, close the control valve on the water delivery pipeline, open the control valve on the return water pipeline; turn on the circulation pump, and the circulation pump will transport the reaction liquid in the liquid phase reaction zone to the main body of the reactor through the return water pipeline The reaction solution is sprayed on top of the solid waste in the solid-phase reaction zone, and the solid waste in the solid-phase reaction zone undergoes a leaching reaction for 4 to 7 days to complete the first cycle of anaerobic digestion;

进行第二个消化周期的浸没式厌氧消化过程时,关闭循环泵和回水管路上的第三控制阀和第五控制阀;反应器主体内的污泥进行浸没式厌氧处理,持续4~7天;When carrying out the submerged anaerobic digestion process of the second digestion cycle, close the third control valve and the fifth control valve on the circulation pump and the return water pipeline; the sludge in the reactor main body is subjected to submerged anaerobic treatment for 4~ 7 days;

待第二个消化周期的浸没式厌氧消化过程结束后,打开回水管路上的第三控制阀和第五控制阀;打开循环泵,循环泵将液相反应区中的反应液通过回水管路输送至反应器主体的顶部,反应液喷淋在固相反应区的固体垃圾上方,固相反应区的固体垃圾进行淋滤反应4~7天,从而完成餐厨垃圾的第二个周期的厌氧消化过程;After the submerged anaerobic digestion process of the second digestion cycle is over, open the third control valve and the fifth control valve on the return water pipeline; turn on the circulation pump, and the circulation pump will pass the reaction liquid in the liquid phase reaction zone through the return water pipeline Transported to the top of the main body of the reactor, the reaction liquid is sprayed over the solid waste in the solid phase reaction area, and the solid waste in the solid phase reaction area undergoes a leaching reaction for 4 to 7 days, thus completing the second cycle of depletion of kitchen waste. Oxygen digestion process;

第三个消化周期至第五个消化周期的步骤与第二个消化周期相同。The steps from the third digestion cycle to the fifth digestion cycle are the same as the second digestion cycle.

本发明具有积极的效果:(1)本发明的消化装置通过设置双向循环泵,在厌氧消化的初始阶段将待处理的餐厨垃圾中的液体从反应器主体的底部进水口送入反应器主体内部,待厌氧消化一段时间后,将反应器主体内部的液体从反应器主体下部的出水管抽出,然后输送至反应器的顶部,从反应器的顶部向反应器主体内部的固相反应区喷淋。一台双向循环泵完成了反应体系的液体输送,整个反应装置结构简单,施工方便并且操作方便。The present invention has positive effects: (1) The digestion device of the present invention sends the liquid in the food waste to be treated into the reactor from the bottom water inlet of the reactor main body in the initial stage of anaerobic digestion by setting a bidirectional circulation pump Inside the main body, after anaerobic digestion for a period of time, the liquid inside the reactor main body is drawn out from the outlet pipe at the lower part of the reactor main body, and then transported to the top of the reactor, from the top of the reactor to the solid phase reaction inside the main body of the reactor Area spraying. A two-way circulation pump completes the liquid delivery of the reaction system, and the whole reaction device has a simple structure, convenient construction and easy operation.

(2)本发明的餐厨垃圾的厌氧消化方法在对餐厨垃圾进行厌氧消化时,首先将餐厨垃圾进行固液相分离,将固相垃圾储放在原泥池,液相垃圾即废液储放在原水池中;待处理的固相垃圾预先转移至消化装置的反应器主体的固体反应区,原水池中的废液由循环泵输送至反应器主体内部浸没固体反应区的固相垃圾,厌氧消化一段时间后,再将反应器主体中的反应液从反应器主体下部抽出从上部喷淋在固相反应区,通过浸没式厌氧消化和淋滤反应交替运行的方式,可以使得餐厨垃圾的固相残渣和液相废液都得以充分厌氧消化反应,以最大程度使得餐厨垃圾得以处理,实现最大程度的资源化处理。同时此装置和方法除了处理餐厨垃圾外,也能够处理鸡粪、城市污泥等有机固体废弃物。(2) In the anaerobic digestion method of kitchen waste of the present invention, when the kitchen waste is anaerobically digested, the kitchen waste is firstly separated from the solid-liquid phase, and the solid-phase waste is stored in the raw mud pond, and the liquid-phase waste is The waste liquid is stored in the raw water pool; the solid waste to be treated is transferred to the solid reaction area of the reactor body of the digestion unit in advance, and the waste liquid in the raw water pool is transported by the circulating pump to the solid phase of the submerged solid reaction area inside the reactor body Garbage, after anaerobic digestion for a period of time, the reaction liquid in the reactor main body is pumped out from the lower part of the reactor main body and sprayed on the solid phase reaction area from the upper part. Through the alternate operation of submerged anaerobic digestion and leaching reaction, it can The solid-phase residue and liquid-phase waste liquid of the kitchen waste can be fully anaerobically digested, so that the kitchen waste can be treated to the greatest extent, and the resource treatment can be realized to the greatest extent. At the same time, in addition to processing kitchen waste, the device and method can also process organic solid waste such as chicken manure and urban sludge.

附图说明Description of drawings

图1为本发明的厌氧消化装置的结构示意图;Fig. 1 is the structural representation of anaerobic digestion device of the present invention;

上述附图中的标记如下:反应器主体1,固相反应区11,排泥口11-1,液相反应区12,筛网12-1,填料12-2,底部排泥口13;The marks in the above drawings are as follows: reactor main body 1, solid phase reaction zone 11, sludge discharge port 11-1, liquid phase reaction zone 12, screen mesh 12-1, filler 12-2, bottom sludge discharge port 13;

上盖2,出气管21,回流进水管22,喷淋头23,测温探头24;Upper cover 2, air outlet pipe 21, return water inlet pipe 22, spray head 23, temperature measuring probe 24;

循环泵3;circulation pump 3;

输水管路4,第一管道41,第二管道42,第三管道43,第四管道44;进水管45,布水器45-1,Water pipeline 4, first pipeline 41, second pipeline 42, third pipeline 43, fourth pipeline 44; water inlet pipe 45, water distributor 45-1,

回水管路5,出水管51,第五管道52,第六管道53,第七管道54,第八管道55;Return water pipeline 5, outlet pipe 51, fifth pipeline 52, sixth pipeline 53, seventh pipeline 54, eighth pipeline 55;

第一控制阀61,第二控制阀62,第三控制阀63,第四控制阀64,第五控制阀65;The first control valve 61, the second control valve 62, the third control valve 63, the fourth control valve 64, and the fifth control valve 65;

原水池7。Raw water pool 7.

具体实施方式Detailed ways

(实施例1、餐厨垃圾的厌氧消化装置)(Example 1, anaerobic digestion device for kitchen waste)

见图1,本实施例的餐厨垃圾的厌氧消化装置包括反应器主体1、上盖2、循环泵3、输水管路4、回水管路5、控制阀和原水池7。上盖2设置在反应器主体1的顶部,密封反应器主体1内部的空腔。循环泵3通过输水管路4将原水池7中的废液输送至反应器主体1的进水口,循环泵3通过回水管路5将反应器主体1内部的反应液从反应器上方回流送入反应器1内部。Referring to FIG. 1 , the anaerobic digestion device for kitchen waste in this embodiment includes a reactor main body 1 , an upper cover 2 , a circulating pump 3 , a water delivery pipeline 4 , a return water pipeline 5 , a control valve and a raw water pool 7 . The upper cover 2 is arranged on the top of the reactor main body 1 to seal the cavity inside the reactor main body 1 . The circulation pump 3 transports the waste liquid in the raw water tank 7 to the water inlet of the reactor main body 1 through the water delivery pipeline 4, and the circulation pump 3 sends the reaction liquid inside the reactor main body 1 back from the top of the reactor through the return water pipeline 5. Inside Reactor 1.

反应器主体1的内部设有固相反应区11和液相反应区12,反应器主体1的底部设有底部排泥口13。所述液相反应区12设置在反应器主体1的内部空腔的下部,固相反应区11位于液相反应区12的上方。The interior of the reactor main body 1 is provided with a solid phase reaction zone 11 and a liquid phase reaction zone 12 , and a bottom sludge outlet 13 is provided at the bottom of the reactor main body 1 . The liquid phase reaction zone 12 is arranged at the lower part of the inner cavity of the reactor main body 1 , and the solid phase reaction zone 11 is located above the liquid phase reaction zone 12 .

液相反应区12包括上、下筛网12-1和两个筛网之间的填料12-2。下筛网12-1距离反应器主体1底部的距离为反应器主体1高度的1/10~1/5。上筛网与下筛网之间的距离为反应器主体1高度的2/5~3/5。上筛网与下筛网均采用304不锈钢材料制成,上筛网与下筛网的目数均为500目。The liquid phase reaction zone 12 includes upper and lower screens 12-1 and packing 12-2 between the two screens. The distance between the lower screen 12 - 1 and the bottom of the reactor body 1 is 1/10-1/5 of the height of the reactor body 1 . The distance between the upper screen and the lower screen is 2/5-3/5 of the height of the reactor main body 1 . Both the upper screen and the lower screen are made of 304 stainless steel, and the mesh numbers of the upper screen and the lower screen are both 500 mesh.

填料12-2填充满上、下筛网12-1之间的空间。填料12-2上附着生物膜,填料中包含厌氧菌种,为了给厌氧菌种提供适合的生长环境,填料12-2所选用的材质具有高表面积/体积比。本实施例所选用的填料12-2购自宜兴市高塍恒光环保设备厂的生物挂膜组合填料,填料由半软性高分子聚合物和软性醛化维纶丝组成,软性醛化维纶丝被压制在半软性高分子聚合物内圈上。所述生物膜是经过培养驯化后,附着于填料上的微生物膜,填料上开始挂膜时从边缘的软性填料醛化维纶上开始挂膜,一周后,生物膜就会延伸至内圈半软性填料上,使软性和半软性皆产生效果,最终达到较好的处理效果。Filler 12-2 fills up the space between upper and lower screen cloth 12-1. Biofilm is attached to the filler 12-2, and the filler contains anaerobic bacteria. In order to provide a suitable growth environment for the anaerobic bacteria, the material selected for the filler 12-2 has a high surface area/volume ratio. The filler 12-2 used in this example was purchased from Yixing Gaocheng Hengguang Environmental Protection Equipment Factory. The silk is pressed onto a semi-soft polymer inner ring. The biofilm is a microbial film attached to the filler after being cultivated and acclimated. When the filler starts to form a film, it starts to form a film from the soft filler at the edge of the vinylon, and after a week, the biofilm will extend to the inner circle. On the soft filler, both softness and semi-softness can produce effects, and finally achieve a better treatment effect.

上筛网12-1通过反应器主体1的内壁上等间距设置的4个或4个以上的挂钩固定在反应器主体1的内部,下筛网12-1的固定方式与上筛网12-1相同。The upper screen 12-1 is fixed inside the reactor main body 1 through 4 or more hooks arranged at equal intervals on the inner wall of the reactor main body 1, and the fixing method of the lower screen 12-1 is the same as that of the upper screen 12-1. 1 is the same.

固相反应区11位于上筛网12-1的上方。固相反应区11的高度为反应器主体1高度的1/5~2/5。固相反应区11的底部设有排泥口11-1,排泥口11-1位于上筛网12-1的上方。The solid phase reaction zone 11 is located above the upper screen 12-1. The height of the solid phase reaction zone 11 is 1/5-2/5 of the height of the reactor main body 1 . A sludge discharge port 11-1 is provided at the bottom of the solid phase reaction zone 11, and the sludge discharge port 11-1 is located above the upper screen 12-1.

上盖2上设有出气口、回流进水口和测温口。出气口与出气管21相连通,出气管21与气体储罐相连。回流进水口与回流进水管22相连通,回流进水管22的出水口设置喷淋头23。测温口内设置测温探头24,用于检测反应器主体1内部的温度。The upper cover 2 is provided with an air outlet, a return water inlet and a temperature measuring port. The gas outlet is connected with the gas outlet pipe 21, and the gas outlet pipe 21 is connected with the gas storage tank. The backflow water inlet is connected with the backflow water inlet pipe 22 , and the water outlet of the backflow water inlet pipe 22 is provided with a spray head 23 . A temperature measuring probe 24 is arranged in the temperature measuring port for detecting the temperature inside the reactor main body 1 .

循环泵3为双向循环泵,本实施例中所用的双向循环泵为保定兰格恒流泵有限公司的JL350-2J型号的双向循环泵。The circulation pump 3 is a bidirectional circulation pump, and the bidirectional circulation pump used in this embodiment is a model JL350-2J bidirectional circulation pump of Baoding Lange Constant Flow Pump Co., Ltd.

所述输水管路4按照液体的流向依次包括第一管道41、第二管道42、第三管道43、第四管道44和进水管45。第一管道41的进水口位于原水池7内的液面下方,第一管道41的出水口与第一三通的右接口相连,第一三通的左接口与第二管道42的进水端相连,第二管道42的出水端与循环泵3的右侧端口相连,循环泵3的左侧端口与第三管道43的进水端相连,第三管道43的出水端与第二三通的右接口的相连,第二三通的上接口与第四管道44的进水端相连,第四管道44的出水端与进水管45的进水端相连,进水管45的出水端从反应器主体1的底部伸入反应器主体1内,进水管45的出水端连接布水器45-1。The water delivery pipeline 4 sequentially includes a first pipeline 41 , a second pipeline 42 , a third pipeline 43 , a fourth pipeline 44 and a water inlet pipe 45 according to the flow direction of the liquid. The water inlet of the first pipeline 41 is located below the liquid level in the raw water pool 7, the water outlet of the first pipeline 41 is connected with the right interface of the first tee, and the left interface of the first tee is connected with the water inlet of the second pipeline 42 The outlet end of the second pipeline 42 is connected with the right port of the circulation pump 3, the left port of the circulation pump 3 is connected with the water inlet end of the third pipeline 43, and the water outlet end of the third pipeline 43 is connected with the second three-way port. The right interface is connected, the upper interface of the second tee is connected with the water inlet end of the fourth pipeline 44, the water outlet end of the fourth pipeline 44 is connected with the water inlet end of the water inlet pipe 45, and the water outlet end of the water inlet pipe 45 is connected from the reactor main body The bottom of 1 extends into the reactor main body 1, and the water outlet end of the water inlet pipe 45 is connected to the water distributor 45-1.

所述回水管路5按照液体的流向依次包括出水管51、第五管道52、第六管道53、第七管道54和第八管道55。出水管51的进水端口位于液相反应区12的下端,出水管51的出水口与第五管道52的进水口相连,第五管道52的出水口与第三三通的左接口相连,第三三通的右接口与第六管道53相连,第六管道53的出水口接储液罐;第三三通的下接口与第七管道54的进水口相连,第七管道54的出水口与第二三通的左接口的相连,第七管道54通过第二三通、输水管路4的第三管道43与循环泵3的左侧端口相连,循环泵3的右侧端口通过输水管路4的第二管道42和第一三通与第八管道55的进水口相连,第八管道55的出水口与回流进水管22的进水端相连,回流进水管22的出水端从上盖2伸入反应器主体1内。The return water pipeline 5 includes an outlet pipe 51 , a fifth pipeline 52 , a sixth pipeline 53 , a seventh pipeline 54 and an eighth pipeline 55 in sequence according to the flow direction of the liquid. The water inlet port of the water outlet pipe 51 is located at the lower end of the liquid phase reaction zone 12, and the water outlet of the water outlet pipe 51 is connected with the water inlet of the fifth pipe 52, and the water outlet of the fifth pipe 52 is connected with the left interface of the third tee. The right interface of three three links links to each other with the sixth pipeline 53, and the water outlet of the sixth pipeline 53 connects liquid storage tank; The lower interface of the third three links links to each other with the water inlet of the seventh pipeline 54, and the water outlet of the seventh pipeline 54 is connected with The left interface of the second tee is connected, the seventh pipeline 54 is connected with the left port of the circulation pump 3 through the second tee, the third pipeline 43 of the water delivery pipeline 4, and the right side port of the circulation pump 3 is passed through the water delivery pipeline The second pipe 42 of 4 and the first tee are connected with the water inlet of the eighth pipe 55, and the water outlet of the eighth pipe 55 is connected with the water inlet end of the return water inlet pipe 22, and the water outlet end of the backflow water inlet pipe 22 is connected from the upper cover 2 into the reactor main body 1.

回水管路5与输水管路4共用一段管路,可以简化管道设计,节省基建投资。The return water pipeline 5 and the water delivery pipeline 4 share a section of pipeline, which can simplify pipeline design and save infrastructure investment.

控制阀包括第一控制阀61、第二控制阀62、第三控制阀63、第四控制阀64和第五控制阀65,分别设置在对应的管道上。其中第一控制阀61设置在输水管路4的第一管道41上,第二控制阀62设置在输水管路4的进水管45上,第三控制阀63设置在回水管路5的出水管51上,第四控制阀64设置在回水管路5的第六管道53上,第五控制阀65设置在回水管路5的第八管道55上。The control valves include a first control valve 61 , a second control valve 62 , a third control valve 63 , a fourth control valve 64 and a fifth control valve 65 , which are respectively arranged on corresponding pipelines. Wherein the first control valve 61 is arranged on the first pipe 41 of the water delivery pipeline 4, the second control valve 62 is arranged on the water inlet pipe 45 of the water delivery pipeline 4, and the third control valve 63 is arranged on the water outlet pipe of the return water pipeline 5 51 , the fourth control valve 64 is set on the sixth pipe 53 of the return water line 5 , and the fifth control valve 65 is set on the eighth line 55 of the return water line 5 .

本发明的消化装置通过设置双向循环泵,在厌氧消化的初始阶段可以将待处理的餐厨垃圾中的液体从反应器主体的底部进水口送入反应器主体内部,待厌氧消化一段时间后,再将反应器主体内部的液体从反应器主体下部的出水管抽出,然后输送至反应器的顶部,从反应器的顶部向反应器主体内部的固相反应区喷淋。一台双向循环泵完成了反应体系的液体输送,整个反应装置管道设计简洁,结构简单,施工方便并且操作方便。The digestion device of the present invention is provided with a two-way circulation pump, and in the initial stage of anaerobic digestion, the liquid in the food waste to be treated can be sent from the bottom water inlet of the reactor body into the interior of the reactor body, and wait for anaerobic digestion for a period of time Finally, the liquid inside the reactor body is drawn out from the outlet pipe at the lower part of the reactor body, and then transported to the top of the reactor, and sprayed from the top of the reactor to the solid phase reaction area inside the reactor body. A two-way circulating pump completes the liquid delivery of the reaction system. The entire reaction device has a simple pipeline design, a simple structure, and is convenient for construction and operation.

本发明的消化装置在反应器主体1的内部分隔设置固相反应区11和液相反应区12,而不是将餐厨垃圾与菌种混合后直接在反应器主体1内部厌氧消化,使得液相废弃物具有更高的消化效率,同时固相废弃物也能得到充分消化,以提高废弃物整体消化产气率,同时具有固相液相易分离,反应彻底的优点。The digestion device of the present invention separates the solid-phase reaction zone 11 and the liquid-phase reaction zone 12 in the interior of the reactor main body 1, instead of directly anaerobic digestion inside the reactor main body 1 after mixing the food waste and bacteria, so that the liquid Phase waste has higher digestion efficiency, and solid phase waste can also be fully digested to improve the overall gas production rate of waste digestion. At the same time, it has the advantages of easy separation of solid phase and liquid phase and thorough reaction.

(实施例2、餐厨垃圾的厌氧消化方法)(Example 2, the anaerobic digestion method of kitchen waste)

本实施例的餐厨垃圾的厌氧消化方法所用的装置为实施例1所述的厌氧消化装置。The device used in the anaerobic digestion method of kitchen waste in this example is the anaerobic digestion device described in Example 1.

本实施例的餐厨垃圾的厌氧消化方法包括以下步骤:The anaerobic digestion method of the kitchen waste of the present embodiment comprises the following steps:

①菌种的驯化。取含固率为5%~7%的城市污水处理厂的厌氧池中的原泥装入培养池中,培养池中放入填料12-2,培养池中的原泥浸没填料12-2,驯化菌种时,为满足培养池内微生物生长的需求,向培养池中加入营养元素葡萄糖、N、P及微量元素Fe、Co、Ni配制成的营养液,每1kg原泥中加入10L的培养液;在中温(35±2℃)条件下菌种驯化10~15d。驯化结束后填料12-2上附着驯化后得到的厌氧菌种。① Domestication of strains. Take the raw mud in the anaerobic tank of the urban sewage treatment plant with a solid content of 5% to 7% and put it into the cultivation tank, put the filler 12-2 in the cultivation tank, and submerge the raw mud in the cultivation tank with the filler 12-2 , when acclimating the strains, in order to meet the needs of microbial growth in the culture tank, add nutrients glucose, N, P and trace elements Fe, Co, Ni to the culture tank, add 10L of culture solution; the strains were acclimatized for 10-15 days at medium temperature (35±2°C). After the acclimatization is completed, the anaerobic strain obtained after acclimatization is attached to the filler 12-2.

所述培养液中,每1L培养液含有1.03g葡萄糖、1g碳酸氢钠氮、0.26g氯化铵、45mg硫酸镁、30mg磷酸氢二钾、25mg柠檬酸钠、15mg氯化钙、1mg硫酸镍、4mg三氯化铁等。In the culture solution, every 1L culture solution contains 1.03g glucose, 1g sodium bicarbonate nitrogen, 0.26g ammonium chloride, 45mg magnesium sulfate, 30mg dipotassium hydrogen phosphate, 25mg sodium citrate, 15mg calcium chloride, 1mg nickel sulfate , 4mg ferric chloride, etc.

②餐厨垃圾的固液分离。将家庭、学校、机关、公共食堂以及餐饮行业的食物废料、餐饮剩余物、食品加工废料及不可再食用的动植物油脂和各类油水混合物送入三相螺旋挤压脱水机中进行固液分离,分离得到的固相垃圾的含固率为70%~80%,储放在原泥池;液相垃圾即废液储放在原水池7中待处理。② Solid-liquid separation of kitchen waste. Send food waste, catering leftovers, food processing waste, non-edible animal and vegetable oils and various oil-water mixtures from families, schools, institutions, public canteens and catering industries into the three-phase screw extrusion dehydrator for solid-liquid separation , the solid-phase garbage obtained by separation has a solid content rate of 70% to 80%, and is stored in the raw mud pool; liquid-phase garbage, that is, waste liquid, is stored in the raw water pool 7 to be treated.

步骤①和步骤②时间上无先后之分。Step ① and step ② are in no particular order in time.

③物料的装填。打开反应器主体1顶部的上盖2,将液相反应区12的上、下筛网之间填充满从步骤①的培养池中取出的填料12-2,厌氧菌种附着在填料12-2内部;然后将原泥池中的固相垃圾转移至上筛网上方,固相垃圾的放置高度为反应器主体1高度的1/5~2/5。固相垃圾装填完毕后盖上上盖2。③ Loading of materials. Open the upper cover 2 on the top of the reactor main body 1, and fill the upper and lower screens of the liquid phase reaction zone 12 with the filler 12-2 taken out from the culture tank in step ①, and the anaerobic bacteria adhere to the filler 12-2. 2 inside; then transfer the solid-phase garbage in the raw mud tank to the top of the upper screen, and the height of the solid-phase garbage is 1/5 to 2/5 of the height of the reactor main body 1. Cover the upper cover 2 after the solid-phase garbage has been loaded.

④餐厨垃圾的厌氧消化。餐厨垃圾的厌氧消化过程总耗时为24~42天,由3~5个消化周期组成,每一个周期依次包括浸没式厌氧消化过程和淋滤反应过程。也即厌氧消化过程中,浸没式厌氧消化过程和淋滤反应过程交替进行。④ Anaerobic digestion of food waste. The anaerobic digestion process of food waste takes 24 to 42 days in total and consists of 3 to 5 digestion cycles, and each cycle includes an immersion anaerobic digestion process and a leaching reaction process in sequence. That is, in the anaerobic digestion process, the submerged anaerobic digestion process and the leaching reaction process are carried out alternately.

进行第一个消化周期的浸没式厌氧消化过程时,打开输水管路4上的第一控制阀61和第二控制阀62,关闭回水管路5上的第三控制阀63、第四控制阀64和第五控制阀65;打开循环泵3,循环泵3将原水池7中的废液从反应器主体1底部的进水管45送入反应器主体1内,待液面浸没固相反应区11的固体垃圾的顶部,开始餐厨垃圾的浸没式厌氧消化过程,浸没式厌氧处理持续4~7天(本实施例中为5天)。浸没式厌氧消化过程中,氧化还原电位ORP为-200~-350mv,厌氧消化温度为35~40℃。待浸没式厌氧消化过程结束后,关闭输水管路4上的第一控制阀61和第二控制阀62,打开回水管路5上的第三控制阀63和第五控制阀65;打开循环泵3,循环泵3将液相反应区12中的反应液通过回水管路5输送至反应器主体1的顶部,反应液喷淋在固相反应区11的固体垃圾上方,固相反应区11的固体垃圾进行淋滤反应4~7天(本实施例中为5天),从而完成餐厨垃圾的第一个周期的厌氧消化过程。淋滤过程中,氧化还原电位ORP为-200~-350mv,固体垃圾的温度为35~40℃。When carrying out the submerged anaerobic digestion process of the first digestion cycle, open the first control valve 61 and the second control valve 62 on the water delivery pipeline 4, close the third control valve 63 and the fourth control valve on the return water pipeline 5 Valve 64 and fifth control valve 65; turn on the circulating pump 3, and the circulating pump 3 sends the waste liquid in the raw water pool 7 from the water inlet pipe 45 at the bottom of the reactor main body 1 into the reactor main body 1, and wait for the liquid surface to be immersed in the solid phase reaction On the top of the solid waste in zone 11, the submerged anaerobic digestion process of kitchen waste starts, and the submerged anaerobic treatment lasts for 4-7 days (5 days in this embodiment). In the submerged anaerobic digestion process, the oxidation reduction potential ORP is -200~-350mv, and the anaerobic digestion temperature is 35~40°C. After the submerged anaerobic digestion process ends, close the first control valve 61 and the second control valve 62 on the water delivery pipeline 4, open the third control valve 63 and the fifth control valve 65 on the return water pipeline 5; open the cycle The pump 3 and the circulating pump 3 transport the reaction liquid in the liquid phase reaction zone 12 to the top of the reactor main body 1 through the return pipe 5, and the reaction liquid is sprayed on the solid waste in the solid phase reaction zone 11, and the solid phase reaction zone 11 The solid waste is subjected to leaching reaction for 4-7 days (5 days in this embodiment), so as to complete the anaerobic digestion process of the first cycle of the kitchen waste. During the leaching process, the oxidation-reduction potential ORP is -200~-350mv, and the temperature of solid waste is 35~40°C.

进行第二个消化周期的浸没式厌氧消化过程时,关闭循环泵3和回水管路5上的第三控制阀63和第五控制阀65;反应器主体1内的污泥进行浸没式厌氧处理持续4~7天(本实施例中为5天)。When carrying out the submerged anaerobic digestion process of the second digestion cycle, close the third control valve 63 and the fifth control valve 65 on the circulation pump 3 and the return water pipeline 5; The oxygen treatment was continued for 4-7 days (5 days in this example).

待第二个消化周期的浸没式厌氧消化过程结束后,打开回水管路5上的第三控制阀63和第五控制阀65;打开循环泵3,循环泵3将液相反应区12中的反应液通过回水管路5输送至反应器主体1的顶部,反应液喷淋在固相反应区11的固体垃圾上方,固相反应区11的固体垃圾进行淋滤反应4~7天(本实施例中为5天),从而完成餐厨垃圾的第二个周期的厌氧消化过程。After the submerged anaerobic digestion process of the second digestion cycle ends, open the third control valve 63 and the fifth control valve 65 on the return water pipeline 5; The reaction liquid is transported to the top of the reactor main body 1 through the return water pipeline 5, and the reaction liquid is sprayed on the solid waste in the solid phase reaction area 11, and the solid waste in the solid phase reaction area 11 undergoes a leaching reaction for 4 to 7 days (this In the embodiment, it is 5 days), so as to complete the anaerobic digestion process of the second cycle of the kitchen waste.

第三个消化周期至第五个消化周期的步骤与第二个消化周期相同。本实施例中包括三个消化周期。The steps from the third digestion cycle to the fifth digestion cycle are the same as the second digestion cycle. Three digestion cycles were included in this example.

餐厨垃圾的厌氧消化结束后,关闭循环泵3,打开固相反应区11下方的排泥口11-1将消化后的固体垃圾排出,消化后的固体垃圾经过杀灭病原菌后可用于景观、林地和农业用肥。打开回水管路5上的第三控制阀63和第四控制阀64,将反应液排出反应器主体,消化后的反应液有机物浓度大大降低,进入厂区污水处理设施进一步处理后,可排入污水管道,进入污水处理厂统一处理。After the anaerobic digestion of the kitchen waste is completed, the circulating pump 3 is turned off, and the mud outlet 11-1 below the solid phase reaction zone 11 is opened to discharge the digested solid waste, which can be used for landscape after killing pathogenic bacteria , forest land and agricultural fertilizers. Open the third control valve 63 and the fourth control valve 64 on the return line 5 to discharge the reaction liquid out of the main body of the reactor. The concentration of organic matter in the digested reaction liquid is greatly reduced, and after entering the sewage treatment facility in the factory area for further treatment, it can be discharged into sewage Pipeline, into the sewage treatment plant for unified treatment.

厌氧消化过程中产生的甲烷从出气管21排出后,收集在气体储罐中。The methane produced in the anaerobic digestion process is discharged from the outlet pipe 21 and collected in the gas storage tank.

本实施例通过浸没式厌氧消化和淋滤反应的方式,使餐厨垃圾的厌氧条件下通过微生物作用将餐厨垃圾泥通过厌氧发酵转为清洁能源——甲烷,不仅可解决餐厨垃圾的处置问题,也可在一定程度上减少对化石燃料的依赖,进而减少由于使用化石燃料所造成的环境污染问题。能为社会带来显著的经济和环境生态效益,在倡导绿色化学、清洁化工的21世纪具有极其诱人的应用前景。In this example, through submerged anaerobic digestion and leaching reaction, under the anaerobic condition of the kitchen waste, the kitchen waste sludge can be converted into clean energy through anaerobic fermentation—methane through the action of microorganisms, which can not only solve the problem of kitchen waste Disposal of garbage can also reduce dependence on fossil fuels to a certain extent, thereby reducing environmental pollution caused by the use of fossil fuels. It can bring significant economic and environmental ecological benefits to the society, and has an extremely attractive application prospect in the 21st century when green chemistry and clean chemistry are advocated.

(应用例1)(Application example 1)

取学校食堂的餐厨垃圾,未进行厌氧消化处理前,检测液相废液COD值为120000mg/L;按照实施例2的方法进行厌氧消化处理后,废液的COD值下降至6000~8000mg/L,消化后的固体垃圾减重88%以上。收集得到甲烷562.21L。Take the kitchen waste from the school canteen, before the anaerobic digestion treatment, the COD value of the liquid phase waste liquid is 120000mg/L; after the anaerobic digestion treatment according to the method of Example 2, the COD value of the waste liquid drops to 6000~ 8000mg/L, the digested solid waste loses more than 88% of its weight. Collect 562.21L of methane.

作为对比的,同样取学校食堂的餐厨垃圾1kg,未进行厌氧消化处理前,液相废液COD值为120000mg/L。进行厌氧消化时,将餐厨垃圾直接与驯化后的污泥0.3kg直接混合,污泥的驯化方法与实施例2的步骤①相同。厌氧消化30天后,废液的COD值下降至10000~13000mg/L。收集得到甲烷489.12L。As a comparison, 1 kg of kitchen waste from the school canteen was also taken. Before anaerobic digestion treatment, the COD value of the liquid phase waste liquid was 120,000 mg/L. When carrying out anaerobic digestion, the kitchen waste is directly mixed with 0.3 kg of domesticated sludge, and the sludge domestication method is the same as step ① in Example 2. After 30 days of anaerobic digestion, the COD value of the waste liquid dropped to 10000-13000mg/L. Collect 489.12L of methane.

因此本发明的消化装置和方法使得餐厨垃圾固液分离得到的液相废弃物具有更高的消化效率,同时固相废弃物也能得到充分消化,废弃物整体消化产气量提高。Therefore, the digestion device and method of the present invention make the liquid-phase waste obtained by the solid-liquid separation of kitchen waste have higher digestion efficiency, and at the same time, the solid-phase waste can also be fully digested, and the overall gas production of the waste is improved.

Claims (1)

  1. A kind of 1. anaerobic digestion device of kitchen garbage, it is characterised in that:Including reactor body(1), upper cover(2), circulating pump (3), hydraulic pipeline(4), water return pipeline(5), control valve and former pond(7);Circulating pump(3)For bidirectional circulating pump;
    Upper cover(2)It is arranged on reactor body(1)Top, seal reactor body(1)Internal cavity;Upper cover(2)On set There are gas outlet, reflux water inlet and temperature-measuring port;Gas outlet and air outlet pipe(21)It is connected, air outlet pipe(21)With gas reservoir phase Even;Flow back water inlet and water return pipeline(5)Water outlet be connected;Set in temperature-measuring port and be used to detect reactor body(1)It is interior The temperature probe of the temperature in portion(24);
    Circulating pump(3)Pass through hydraulic pipeline(4)By former pond(7)In waste liquid be delivered to reactor body(1)The water inlet of bottom Mouthful, circulating pump(3)Pass through water return pipeline(5)By reactor body(1)Internal reaction solution flows back from top and is sent into reactor(1) It is internal;
    Reactor body(1)Be internally provided with solid phase reaction area(11)With liquid phase reactor area(12), reactor body(1)Bottom Equipped with bottom mud discharging mouth(13);Liquid phase reactor area(12)Including upper and lower sieve(12-1)Filler between two sieves(12- 2);Solid phase reaction area(11)The top for the upper screen cloth being located at, solid phase reaction area(11)Bottom be equipped with mud discharging mouth(11-1);
    The hydraulic pipeline(4)Include the first pipeline successively according to the flow direction of liquid(41), second pipe(42), the 3rd pipeline (43), the 4th pipeline(44)And water inlet pipe(45);First pipeline(41)Water inlet be located at former pond(7)Below interior liquid level, First pipeline(41)Water outlet be connected with the right interface of the first threeway, the left interface and second pipe of the first threeway(42)Into Water end (W.E.) is connected, second pipe(42)Water outlet and circulating pump(3)Right side port be connected, circulating pump(3)Left side port with 3rd pipeline(43)Water inlet end be connected, the 3rd pipeline(43)Water outlet and the right interface of the second threeway be connected, the two or three Logical upper interface and the 4th pipeline(44)Water inlet end be connected, the 4th pipeline(44)Water outlet and water inlet pipe(45)Water inlet end It is connected, water inlet pipe(45)Water outlet from reactor body(1)Bottom stretch into reactor body(1)It is interior, water inlet pipe(45)'s Water outlet connects water distributor(45-1);
    The water return pipeline(5)Include outlet pipe successively according to the flow direction of liquid(51), the 5th pipeline(52), the 6th pipeline (53), the 7th pipeline(54)With the 8th pipeline(55);Outlet pipe(51)Water inlet port be located at liquid phase reactor area(12)Lower end, Outlet pipe(51)Water outlet and the 5th pipeline(52)Water inlet be connected, the 5th pipeline(52)Water outlet and the 3rd threeway Left interface is connected, the right interface and the 6th pipeline of the 3rd threeway(53)It is connected, the 6th pipeline(53)Water outlet connect fluid reservoir;The The lower interface of three threeways and the 7th pipeline(54)Water inlet be connected, the 7th pipeline(54)Water outlet and a left side for the second threeway connect Mouth is connected, the 7th pipeline(54)Pass through the second threeway, hydraulic pipeline(4)The 3rd pipeline(43)With circulating pump(3)Left side Port is connected, circulating pump(3)Right side port pass through hydraulic pipeline(4)Second pipe(42)With the first threeway and the 8th pipeline (55)Water inlet be connected, the 8th pipeline(55)Water outlet with reflux water inlet pipe(22)Water inlet end be connected, flow back water inlet pipe (22)Water outlet from upper cover(2)Stretch into reactor body(1)It is interior.
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