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CN108723067A - A kind of integrated form domestic garbage resource processing system and its processing method - Google Patents

A kind of integrated form domestic garbage resource processing system and its processing method Download PDF

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CN108723067A
CN108723067A CN201810763117.3A CN201810763117A CN108723067A CN 108723067 A CN108723067 A CN 108723067A CN 201810763117 A CN201810763117 A CN 201810763117A CN 108723067 A CN108723067 A CN 108723067A
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biogas
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张虎成
焦婕
田靓
文天放
肖拓
唐小龙
肖国俊
赵颖
刘更生
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China City Environment Protection Engineering Ltd
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/40Destroying solid waste or transforming solid waste into something useful or harmless involving thermal treatment, e.g. evaporation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B1/00Dumping solid waste
    • B09B1/004Covering of dumping sites
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B5/00Operations not covered by a single other subclass or by a single other group in this subclass
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    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

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Abstract

本发明属于生活垃圾处理技术领域,具体涉及一种集成式生活垃圾资源化处理系统,垃圾储存单元、破碎筛分单元、磁选单元和发酵单元依次连接;发酵单元的出气口分别连接有厌氧沼气管路和好氧沼气管路,厌氧沼气管路上依次设有第一阀门、沼气预处理单元和沼气发电单元;好氧沼气管路上依次设有第二阀门、沼气净化单元和沼气燃烧单元。本发明还提供一种集成式生活垃圾资源化处理方法,1)将生活垃圾暂存;2)生活垃圾经破碎、筛分后除去石块;再磁选除去金属杂物;3)生活垃圾进行厌氧发酵;4)注入空气,生活垃圾开始进行好氧发酵;5)生活垃圾转至卫生填埋场进行填埋。本发明的处理系统和方法工艺简单,资源化利用率高、污染排放少。

The invention belongs to the technical field of domestic waste treatment, and specifically relates to an integrated domestic waste resource treatment system, in which a waste storage unit, a crushing and screening unit, a magnetic separation unit and a fermentation unit are sequentially connected; the gas outlets of the fermentation units are respectively connected with anaerobic Biogas pipeline and aerobic biogas pipeline, the anaerobic biogas pipeline is provided with the first valve, biogas pretreatment unit and biogas power generation unit in sequence; the aerobic biogas pipeline is provided with the second valve, biogas purification unit and biogas combustion unit in sequence . The present invention also provides an integrated domestic waste resource treatment method, 1) temporarily storing domestic waste; 2) removing stones after the domestic waste is crushed and sieved; then removing metal impurities by magnetic separation; 3) carrying out domestic waste Anaerobic fermentation; 4) Air is injected, and aerobic fermentation of domestic waste begins; 5) Domestic waste is transferred to a sanitary landfill for landfill. The processing system and method of the present invention have simple process, high resource utilization rate and less pollution discharge.

Description

一种集成式生活垃圾资源化处理系统及其处理方法An integrated domestic waste resource treatment system and its treatment method

技术领域technical field

本发明属于生活垃圾处理技术领域,具体涉及一种集成式生活垃圾资源化处理系统及其处理方法。The invention belongs to the technical field of domestic waste treatment, and in particular relates to an integrated domestic waste resource treatment system and a treatment method thereof.

背景技术Background technique

随着我国社会经济的快速发展和城市化进程的加快,城市生活生产过程中产生的废弃物也日益增多。城市生活垃圾成分复杂,含水率高,有机物含量高,随意堆放或处理不当,都将对周边大气、土壤以及水等造成二次污染。With the rapid development of my country's social economy and the acceleration of urbanization, the waste generated in the process of urban life and production is also increasing. Municipal solid waste has complex components, high moisture content, and high organic matter content. Random stacking or improper disposal will cause secondary pollution to the surrounding air, soil, and water.

目前国内城市生活垃圾主要的处理方法是垃圾填埋和垃圾焚烧发电。垃圾填埋并没有进行无害化处理,填埋垃圾中残留着大量的细菌病毒,填埋的垃圾需要多年的自然降解方能达到稳定状态,未稳定的垃圾会长时间的产生大量的沼气和渗滤液,对地下水和周围环境有着严重隐患。生活垃圾热值低,垃圾焚烧发电成本高昂,会产生大量有毒有害气体和飞灰,此外,垃圾焚烧厂建设较难解决“邻避效应”。At present, the main treatment methods of municipal solid waste in China are landfill and waste incineration for power generation. The landfill does not carry out harmless treatment. There are a large number of bacteria and viruses in the landfill waste. The landfill waste needs many years of natural degradation to reach a stable state. Unstabilized waste will produce a large amount of methane and gas for a long time. Leachate has serious hidden dangers to groundwater and the surrounding environment. The calorific value of domestic waste is low, and the cost of waste incineration for power generation is high, which will produce a large amount of toxic and harmful gases and fly ash. In addition, it is difficult to solve the "NIMBY effect" in the construction of waste incineration plants.

因此有必要设计一种新的集成式生活垃圾资源化处理系统及其处理方法,以克服上述问题。Therefore, it is necessary to design a new integrated domestic waste resource treatment system and its treatment method to overcome the above problems.

发明内容Contents of the invention

为了克服上述现有技术存在的不足,本发明的目的是提供一种集成式生活垃圾资源化处理系统及其处理方法,能够实现生活垃圾的环境污染最小化和资源利用最大化目标。In order to overcome the deficiencies of the above-mentioned prior art, the object of the present invention is to provide an integrated household garbage resource treatment system and its treatment method, which can realize the goals of minimizing environmental pollution of household garbage and maximizing resource utilization.

为实现上述目的,本发明的技术方案为一种集成式生活垃圾资源化处理系统,包括垃圾储存单元、破碎筛分单元、磁选单元、发酵单元、沼气预处理单元、沼气净化单元、沼气发电单元和沼气燃烧单元;所述垃圾储存单元、所述破碎筛分单元、所述磁选单元和所述发酵单元依次连接;所述发酵单元的出气口分别连接有厌氧沼气管路和好氧沼气管路,所述厌氧沼气管路上依次设有第一阀门、所述沼气预处理单元和所述沼气发电单元;所述好氧沼气管路上依次设有第二阀门、所述沼气净化单元和所述沼气燃烧单元。In order to achieve the above purpose, the technical solution of the present invention is an integrated domestic waste resource treatment system, including a waste storage unit, a crushing and screening unit, a magnetic separation unit, a fermentation unit, a biogas pretreatment unit, a biogas purification unit, and a biogas power generation unit. unit and biogas combustion unit; the garbage storage unit, the crushing and screening unit, the magnetic separation unit and the fermentation unit are sequentially connected; the gas outlet of the fermentation unit is respectively connected with an anaerobic biogas pipeline and an aerobic A biogas pipeline, the anaerobic biogas pipeline is sequentially provided with a first valve, the biogas pretreatment unit and the biogas power generation unit; the aerobic biogas pipeline is sequentially provided with a second valve, the biogas purification unit and the biogas combustion unit.

进一步地,所述发酵单元的出液口连接有渗滤液管路,所述渗滤液管路上设有渗滤液处理单元,所述渗滤液管路上连接有一支渗滤液循环回灌旁路且所述渗滤液循环回灌旁路出口端连接至所述发酵单元,于所述渗滤液循环回灌旁路上设有旁通阀。Further, the liquid outlet of the fermentation unit is connected with a leachate pipeline, and a leachate treatment unit is provided on the leachate pipeline, and a leachate circulation and refill bypass is connected to the leachate pipeline, and the The outlet port of the leachate circulation backfill bypass is connected to the fermentation unit, and a bypass valve is arranged on the leachate circulation backfill bypass.

进一步地,所述垃圾储存单元包括用于临时存储生活垃圾的垃圾仓,所述垃圾仓内设有用于监测臭气浓度的臭气监测器和用于喷淋臭气抑制剂的自动喷淋装置,所述臭气监测器与自动喷淋装置连接。Further, the garbage storage unit includes a garbage bin for temporarily storing domestic garbage, and the garbage bin is provided with an odor monitor for monitoring the odor concentration and an automatic spraying device for spraying odor inhibitors , the odor monitor is connected with an automatic sprinkler.

进一步地,所述破碎筛分单元包括依次连接的用于破碎垃圾的破碎装置、用于传输垃圾的螺旋推进器和用于筛分垃圾的筛分装置;所述磁选单元包括用于磁选除去金属杂物的永磁辊式磁选机;所述永磁辊式磁选机的进料口与所述筛分装置的出料口相连,所述永磁辊式磁选机的出料口与所述发酵单元相连。Further, the crushing and screening unit includes a crushing device for crushing garbage, a screw propeller for transporting garbage, and a screening device for screening garbage connected in sequence; the magnetic separation unit includes A permanent magnet roller magnetic separator for removing metal impurities; the feed inlet of the permanent magnet roller magnetic separator is connected with the discharge port of the screening device, and the discharge of the permanent magnet roller magnetic separator is The port is connected to the fermentation unit.

进一步地,所述发酵单元包括用于发酵生活垃圾的发酵罐体,所述发酵罐体的出气口分别与所述厌氧沼气管路的进气口和所述好氧沼气管路的进气口连接;所述发酵罐体的出液口与所述渗滤液管路的进液口相连;所述发酵罐体内设有用于向垃圾堆体内注入空气的通风管道。Further, the fermentation unit includes a fermenter body for fermenting domestic waste, and the gas outlet of the fermenter body is connected to the air inlet of the anaerobic biogas pipeline and the air inlet of the aerobic biogas pipeline respectively. The liquid outlet of the fermentation tank is connected with the liquid inlet of the leachate pipeline; the fermentation tank is provided with a ventilation pipe for injecting air into the garbage dump.

更进一步地,所述通风管道为特氟龙不锈钢管,所述特氟龙不锈钢管上均匀设置若干通风孔,所述特氟龙不锈钢管的表面缠绕有短纤针刺土工布。Furthermore, the ventilation pipe is a Teflon stainless steel pipe, and several ventilation holes are evenly arranged on the Teflon stainless steel pipe, and the surface of the Teflon stainless steel pipe is wound with short-fiber needle-punched geotextiles.

进一步地,所述渗滤液处理单元包括用于对所述发酵单元产生的渗透液进行处理的两级DTRO装置和用于对两级DTRO装置产生的浓水进行处理的MVR蒸发器,所述两级DTRO装置的进液口与所述发酵单元相连,所述两级DTRO装置的浓水出口与所述MVR蒸发器相连。Further, the leachate treatment unit includes a two-stage DTRO device for treating the permeate produced by the fermentation unit and an MVR evaporator for treating the concentrated water produced by the two-stage DTRO device, the two The liquid inlet of the two-stage DTRO device is connected with the fermentation unit, and the concentrated water outlet of the two-stage DTRO device is connected with the MVR evaporator.

进一步地,所述沼气预处理单元包括依次连接的用于脱水的第一塔式沼气脱水器、用于脱硫的第一生物脱硫设备和用于脱碳的膜法沼气脱碳净化设备,所述沼气发电单元包括储气罐、沼气锅炉和沼气发电机组;所述第一塔式沼气脱水器与第一阀门连接,所述膜法沼气脱碳净化设备与所述储气罐连接,所述储气罐分别与所述沼气锅炉和所述沼气发电机组连接。Further, the biogas pretreatment unit includes a first tower biogas dehydrator for dehydration, a first biological desulfurization device for desulfurization, and a membrane biogas decarbonization purification device for decarbonization, which are connected in sequence. The biogas power generation unit includes a gas storage tank, a biogas boiler and a biogas generator set; the first tower biogas dehydrator is connected to the first valve, the membrane method biogas decarbonization purification equipment is connected to the gas storage tank, the storage The gas tank is respectively connected with the biogas boiler and the biogas generating set.

进一步地,所述沼气净化单元包括依次连接的用于脱水的第二塔式沼气脱水器和用于脱硫的第二生物脱硫设备,所述沼气燃烧单元包括用于燃烧净化后沼气的内燃式沼气火炬;所述第二塔式沼气脱水器与第二阀门连接,所述第二生物脱硫设备与所述内燃式沼气火炬连接。Further, the biogas purification unit includes a second tower-type biogas dehydrator for dehydration and a second biological desulfurization device for desulfurization connected in sequence, and the biogas combustion unit includes an internal combustion biogas dehydrator for burning purified biogas Flare; the second tower biogas dehydrator is connected to the second valve, and the second biological desulfurization equipment is connected to the internal combustion biogas torch.

本发明还提供一种集成式生活垃圾资源化处理方法,该方法包括如下步骤:The present invention also provides an integrated domestic waste resource treatment method, which includes the following steps:

1)将生活垃圾置于垃圾储存单元暂存;1) Put domestic garbage in the garbage storage unit for temporary storage;

2)将生活垃圾运输至破碎筛分单元,经破碎、筛分后除去生活垃圾中的石块;再经磁选单元磁选除去金属杂物;2) Transport the domestic waste to the crushing and screening unit, and remove the stones in the domestic waste after crushing and screening; then remove metal debris by magnetic separation through the magnetic separation unit;

3)关闭第二阀门和旁通阀,打开第一阀门,生活垃圾进入发酵单元的发酵罐体中进行厌氧发酵,厌氧发酵产生的沼气进入沼气预处理单元中依次进行脱水、脱硫和脱碳处理,预处理后沼气进入沼气发电单元进行发电;厌氧反应产生的渗滤液通过管道进入渗滤液处理单元处理达标后排放或回用;3) Close the second valve and bypass valve, open the first valve, domestic waste enters the fermentation tank of the fermentation unit for anaerobic fermentation, and the biogas generated by anaerobic fermentation enters the biogas pretreatment unit for dehydration, desulfurization and desulfurization in sequence Carbon treatment, after pretreatment, the biogas enters the biogas power generation unit for power generation; the leachate generated by the anaerobic reaction enters the leachate treatment unit through the pipeline and is discharged or reused after reaching the standard;

4)当检测到发酵罐体内的生活垃圾的BDM值小于6%时,则认为生活垃圾处于厌氧反应后期;当生活垃圾处于厌氧反应后期时,打开第二阀门和旁通阀,关闭第一阀门,打开风机向发酵罐体内的垃圾堆体中注入空气,生活垃圾开始进行好氧发酵,好氧发酵产生的沼气进入沼气净化单元中依次进行脱水和脱硫处理,净化后的沼气进入沼气燃烧单元中安全燃烧;好氧发酵产生的渗滤液部分回灌至发酵单元中,其余渗滤液通过管道进入渗滤液处理单元处理达标后排放或回用;4) When the BDM value of domestic waste in the fermenter is detected to be less than 6%, it is considered that the domestic waste is in the late stage of anaerobic reaction; when the domestic waste is in the late stage of anaerobic reaction, open the second valve and bypass valve, and close the first One valve, open the fan to inject air into the garbage dump in the fermentation tank, the domestic garbage starts to undergo aerobic fermentation, and the biogas generated by aerobic fermentation enters the biogas purification unit for dehydration and desulfurization in turn, and the purified biogas enters the biogas combustion Safe combustion in the unit; part of the leachate produced by aerobic fermentation is refilled into the fermentation unit, and the rest of the leachate enters the leachate treatment unit through the pipeline for treatment and discharge or reuse after reaching the standard;

5)生活垃圾在发酵单元中依次经过厌氧发酵和好氧发酵后,达到基本稳定状态,转至卫生填埋场进行填埋。5) The domestic waste is transferred to the sanitary landfill for landfill after anaerobic fermentation and aerobic fermentation in the fermentation unit to reach a basic stable state.

与现有技术相比,本发明具有以下有益效果:Compared with the prior art, the present invention has the following beneficial effects:

(1)本发明提供的集成式生活垃圾资源化处理系统及其处理方法可以妥善处理好生活垃圾,并将其充分的资源化利用;工艺简单、资源化利用率高、机械化程度高、经济效益好、污染排放少;(1) The integrated domestic waste resource treatment system and its treatment method provided by the present invention can properly handle domestic waste and fully utilize it as a resource; the process is simple, the resource utilization rate is high, the degree of mechanization is high, and the economic benefit Good, less pollution discharge;

(2)本发明提供的集成式生活垃圾资源化处理系统将厌氧发酵产生的高浓度沼气经过沼气预处理单元处理后用于发电,将好氧发酵产生的低浓度沼气经过沼气净化单元处理后安全燃烧,实现沼气的高资源化利用;(2) The integrated domestic waste resource treatment system provided by the present invention uses the high-concentration biogas produced by anaerobic fermentation to be treated by the biogas pretreatment unit for power generation, and the low-concentration biogas produced by aerobic fermentation is treated by the biogas purification unit Safe combustion to realize high resource utilization of biogas;

(3)本发明提供的集成式生活垃圾资源化处理系统中发酵单元中垃圾好氧发酵产生的渗透液部分回灌至发酵单元垃圾中,可调节垃圾堆体内湿度,给微生物降解垃圾过程提供必要的水分补充,改善了微生物的生存环境;此外,渗滤液中含有大量降解垃圾的优势菌,大大提高其降解仓内垃圾的效率,缩短系统运行周期;(3) In the integrated domestic waste resource treatment system provided by the present invention, part of the permeate produced by the aerobic fermentation of the waste in the fermentation unit is refilled into the waste in the fermentation unit, which can adjust the humidity in the waste pile and provide the necessary for the process of microbial degradation of waste. The water replenishment improves the living environment of microorganisms; in addition, the leachate contains a large number of dominant bacteria that degrade garbage, which greatly improves the efficiency of degrading garbage in the warehouse and shortens the system operation cycle;

(4)本发明提供的集成式生活垃圾资源化处理方法通过先将垃圾厌氧发酵,再好氧发酵后,即达到基本稳定状态,垃圾最后转至卫生填埋场进行规范填埋,沼气利用经济效益高,污染排放少。(4) The integrated domestic waste resource treatment method provided by the present invention firstly anaerobically ferments the waste, and then aerobically ferments the waste to reach a basically stable state, and finally transfers the waste to a sanitary landfill for standardized landfill, and biogas utilization High economic benefit, less pollution discharge.

附图说明Description of drawings

为了更清楚地说明本发明实施例或现有技术中的技术方案,下面将对实施例或现有技术描述中所需要使用的附图作简单地介绍,显而易见地,下面描述中的附图仅仅是本发明的一些实施例,对于本领域普通技术人员来讲,在不付出创造性劳动的前提下,还可以根据这些附图获得其它的附图。In order to more clearly illustrate the technical solutions in the embodiments of the present invention or the prior art, the following will briefly introduce the drawings that need to be used in the description of the embodiments or the prior art. Obviously, the accompanying drawings in the following description are only These are some embodiments of the present invention. Those skilled in the art can also obtain other drawings based on these drawings without creative work.

图1为本发明实施例提供的集成式生活垃圾资源化处理系统的工艺流程图;Fig. 1 is the process flow diagram of the integrated domestic waste resource treatment system provided by the embodiment of the present invention;

图中:1、垃圾储存单元,2、破碎筛分单元,3、磁选单元,4、发酵单元,5、第一阀门,6、第二阀门,7、旁通阀,8、风机,9、沼气预处理单元,10、沼气发电单元,11、沼气净化单元,12、沼气燃烧单元,13、渗滤液处理单元。In the figure: 1. Garbage storage unit, 2. Crushing and screening unit, 3. Magnetic separation unit, 4. Fermentation unit, 5. First valve, 6. Second valve, 7. Bypass valve, 8. Fan, 9 1. Biogas pretreatment unit, 10. Biogas power generation unit, 11. Biogas purification unit, 12. Biogas combustion unit, 13. Leachate treatment unit.

具体实施方式Detailed ways

下面将结合本发明实施例中的附图,对本发明实施例中的技术方案进行清楚、完整地描述,显然,所描述的实施例仅仅是本发明一部分实施例,而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员在没有做出创造性劳动前提下所获得的所有其它实施例,都属于本发明保护的范围。The following will clearly and completely describe the technical solutions in the embodiments of the present invention with reference to the accompanying drawings in the embodiments of the present invention. Obviously, the described embodiments are only some, not all, embodiments of the present invention. Based on the embodiments of the present invention, all other embodiments obtained by persons of ordinary skill in the art without making creative efforts belong to the protection scope of the present invention.

如图1所示,本发明实施例提供一种集成式生活垃圾资源化处理系统,包括垃圾储存单元1、破碎筛分单元2、磁选单元3、发酵单元4、沼气预处理单元9、沼气净化单元11、沼气发电单元10和沼气燃烧单元12;其中,垃圾储存单元1、破碎筛分单元2、磁选单元3和发酵单元4依次连接;发酵单元4的出气口分别连接有厌氧沼气管路和好氧沼气管路,所述厌氧沼气管路上依次设有第一阀门5、所述沼气预处理单元9和所述沼气发电单元10;所述好氧沼气管路上依次设有第二阀门6、所述沼气净化单元11和所述沼气燃烧单元12。本实施例中发酵单元4的发酵罐体顶部设有沼气传输管道,沼气传输管道可在厌氧沼气管路和好氧沼气管路之间自动切换,当发酵单元4内垃圾处于厌氧发酵时,沼气传输管道与沼气预处理单元9连接,沼气进入沼气发电单元10发电;当发酵单元4内切换成好氧反应模式时,沼气传输管道对应的切换成与沼气净化单位11连接,沼气进入沼气燃烧单元12燃烧;发酵单元4内垃圾依次经过厌氧发酵和好氧发酵过程后,即达到基本稳定状态,垃圾最后转至卫生填埋场进行规范填埋。本实施例提供的集成式生活垃圾资源化处理系统及其处理方法可以妥善处理好生活垃圾,并将其充分的资源化利用;工艺简单、资源化利用率高、机械化程度高、经济效益好、污染排放少。As shown in Figure 1, the embodiment of the present invention provides an integrated domestic waste resource treatment system, including a waste storage unit 1, a crushing and screening unit 2, a magnetic separation unit 3, a fermentation unit 4, a biogas pretreatment unit 9, a biogas Purification unit 11, biogas power generation unit 10 and biogas combustion unit 12; wherein, garbage storage unit 1, crushing and screening unit 2, magnetic separation unit 3 and fermentation unit 4 are connected in sequence; the gas outlets of fermentation unit 4 are respectively connected with anaerobic biogas Pipeline and aerobic biogas pipeline, the first valve 5, the biogas pretreatment unit 9 and the biogas power generation unit 10 are sequentially arranged on the anaerobic biogas pipeline; Two valves 6 , the biogas purification unit 11 and the biogas combustion unit 12 . In this embodiment, the top of the fermentation tank of fermentation unit 4 is provided with a biogas transmission pipeline, which can automatically switch between anaerobic biogas pipeline and aerobic biogas pipeline. When the garbage in fermentation unit 4 is in anaerobic fermentation , the biogas transmission pipeline is connected to the biogas pretreatment unit 9, and the biogas enters the biogas power generation unit 10 to generate electricity; when the fermentation unit 4 is switched to the aerobic reaction mode, the biogas transmission pipeline is correspondingly switched to be connected to the biogas purification unit 11, and the biogas enters the biogas The combustion unit 12 burns; the garbage in the fermentation unit 4 undergoes anaerobic fermentation and aerobic fermentation in sequence, and then reaches a basically stable state, and the garbage is finally transferred to a sanitary landfill for standardized landfill. The integrated domestic waste resource treatment system and its treatment method provided in this embodiment can properly handle domestic waste and fully utilize it as a resource; the process is simple, the resource utilization rate is high, the degree of mechanization is high, and the economic benefit is good. Less pollution discharge.

进一步地,发酵单元4的出液口连接有渗滤液管路,所述渗滤液管路上设有渗滤液处理单元13,所述渗滤液管路上连接有一支渗滤液循环回灌旁路且所述渗滤液循环回灌旁路出口端连接至所述发酵单元4,于所述渗滤液循环回灌旁路上设有旁通阀7。本实施例中发酵单元4的发酵罐体底部设有渗滤液循环回灌旁路,渗滤液循环回灌旁路上设有旁通阀7;当发酵单元4中垃圾处于厌氧发酵时,旁通阀7关闭,渗滤液全部进入后续渗滤液处理单元13;当发酵单元4内切换成好氧反应模式时,旁通阀7自动打开,部分渗滤液循环回灌至发酵罐体垃圾堆体内,其他渗滤液进入后续渗滤液处理单元13。好氧发酵时部分渗滤液回灌至发酵单元4的垃圾中,可调节垃圾堆体内湿度,给微生物降解垃圾过程提供必要的水分补充,大大提高其降解仓内垃圾的效率,缩短系统运行周期。Further, the liquid outlet of the fermentation unit 4 is connected with a leachate pipeline, and the leachate treatment unit 13 is arranged on the leachate pipeline, and a leachate circulation and refill bypass is connected on the leachate pipeline, and the The outlet port of the leachate circulation backfill bypass is connected to the fermentation unit 4, and a bypass valve 7 is provided on the leachate circulation backfill bypass. In this embodiment, the bottom of the fermentation tank of the fermentation unit 4 is provided with a leachate circulation and refill bypass, and a bypass valve 7 is provided on the leachate circulation and refill bypass; when the garbage in the fermentation unit 4 is in anaerobic fermentation, the bypass When the valve 7 is closed, all the leachate enters the subsequent leachate treatment unit 13; when the fermentation unit 4 is switched to the aerobic reaction mode, the bypass valve 7 is automatically opened, and part of the leachate is circulated and refilled into the garbage dump of the fermentation tank. The leachate enters the subsequent leachate treatment unit 13 . During aerobic fermentation, part of the leachate is refilled into the garbage in the fermentation unit 4, which can adjust the humidity in the garbage pile, provide the necessary water supplement for the microbial degradation of garbage, greatly improve the efficiency of its degradation of garbage in the bin, and shorten the system operation cycle.

进一步地,垃圾储存单元1包括用于临时存储生活垃圾的垃圾仓,垃圾仓内设有用于监测臭气浓度的臭气监测器和用于喷淋臭气抑制剂的自动喷淋装置,臭气监测器与自动喷淋装置连接。本实施例中的垃圾仓为微负压密封式垃圾仓,仓内配有电动液压抓斗;当仓内臭气浓度超过设定浓度后,臭气监测器可将启动信号传递至自动喷淋装置,触发自动喷淋臭气抑制剂;臭气抑制剂可以是一种复合型微生物制剂,该复合型微生物制剂为天津健农园生物科技有限公司生产的BM微生物制剂,在消除恶臭的同时还可抑制苍蝇蚊虫的滋生,整个系统运行环境较好。Further, the garbage storage unit 1 includes a garbage bin for temporary storage of domestic garbage, and the garbage bin is provided with an odor monitor for monitoring the concentration of the odor and an automatic spray device for spraying odor inhibitors. The monitor is connected to the automatic sprinkler. The garbage bin in this embodiment is a micro-negative pressure sealed garbage bin, and the bin is equipped with an electro-hydraulic grab bucket; when the odor concentration in the bin exceeds the set concentration, the odor monitor can transmit the start signal to the automatic sprayer device to trigger automatic spraying of odor inhibitors; odor inhibitors can be a compound microbial preparation, which is a BM microbial preparation produced by Tianjin Jiannongyuan Biotechnology Co., Ltd. It can inhibit the breeding of flies and mosquitoes, and the whole system has a better operating environment.

进一步地,破碎筛分单元2包括依次连接的用于破碎垃圾的破碎装置、用于传输垃圾的螺旋推进器和用于筛分垃圾的筛分装置;硬度小的垃圾组分在破碎装置中得到破碎后,通过螺旋推进器传输至筛分装置,筛分装置把垃圾按颗粒大小进行分选,可将筛选出的石块等剔除。磁选单元3包括用于磁选除去金属杂物的永磁辊式磁选机;永磁辊式磁选机的进料口与筛分装置的出料口相连,永磁辊式磁选机的出料口与发酵单元4相连。生活垃圾中金属类物件被永磁辊式磁选机吸着后落入金属收集箱中回收利用,其他垃圾不受磁力影响,进入后续处理单元。Further, the crushing and screening unit 2 includes a crushing device for crushing rubbish, a screw propeller for transporting rubbish, and a screening device for screening rubbish connected in sequence; the rubbish components with low hardness are obtained in the crushing device After crushing, it is transported to the screening device by the screw propeller. The screening device sorts the garbage according to the size of the particles, and can remove the screened stones. Magnetic separation unit 3 comprises the permanent magnet roller magnetic separator that is used for magnetic separation to remove metal debris; The outlet of the outlet is connected with the fermentation unit 4. The metal objects in the domestic garbage are attracted by the permanent magnet roller magnetic separator and then fall into the metal collection box for recycling. Other garbage is not affected by the magnetic force and enters the subsequent processing unit.

进一步地,发酵单元4包括用于发酵生活垃圾的发酵罐体,发酵罐体顶部的出气口分别与厌氧沼气管路的进气口和好氧沼气管路的进气口连接,发酵罐体底部的出液口与渗滤液管路的进液口相连;发酵罐体内设有多个传感器和用于向垃圾堆体内注入空气的通风管道,多个传感器分别用于监测垃圾堆体温度以及发酵罐体内压力、沼气浓度、氧气浓度和二氧化碳浓度,通风管道与一风机8相连,通风管道可贯穿于垃圾堆体,向发酵罐体内的垃圾注入空气,实现好氧环境中垃圾快速发酵。作为一种实施方式,发酵罐体为立式柱形发酵罐体,罐体内安装的多个传感器可对垃圾堆体温度、压力、沼气浓度、氧气浓度和二氧化碳浓度等参数自动测定,由配套的PLC记录并发送至终端,终端可根据持续监测的数据判断发酵罐内垃圾的发酵状态。本实施例中的PLC控制器仅对发酵罐体中的各个参数进行监控,不涉及对PLC程序的改进。本实施例中的发酵罐体可满足垃圾在仓内的好氧发酵或厌氧发酵需求;当发酵仓处于密封环境,仓内垃圾即进行厌氧发酵,反应一段时间后,根据仓内多个传感器的数据记录可判断出垃圾所处厌氧反应周期,当判断出垃圾所处厌氧反应后期时,可切换成好氧反应模式,此时,风机启动,并通过通风管道向仓内垃圾注入空气,即实现仓内好氧环境。Further, the fermentation unit 4 includes a fermenter body for fermenting domestic waste, and the gas outlets on the top of the fermenter body are respectively connected to the air inlet of the anaerobic biogas pipeline and the air inlet of the aerobic biogas pipeline, and the fermenter body The liquid outlet at the bottom is connected to the liquid inlet of the leachate pipeline; the fermentation tank is equipped with multiple sensors and ventilation pipes for injecting air into the garbage dump, and the multiple sensors are used to monitor the temperature of the garbage dump and the fermentation process. The pressure in the tank, the biogas concentration, the oxygen concentration and the carbon dioxide concentration, the ventilation pipe is connected with a fan 8, the ventilation pipe can run through the garbage dump, inject air into the garbage in the fermentation tank, and realize the rapid fermentation of garbage in an aerobic environment. As an embodiment, the fermentation tank is a vertical columnar fermentation tank, and multiple sensors installed in the tank can automatically measure parameters such as the temperature, pressure, biogas concentration, oxygen concentration, and carbon dioxide concentration of the garbage dump. The PLC records and sends to the terminal, and the terminal can judge the fermentation status of the garbage in the fermentation tank according to the continuous monitoring data. The PLC controller in this embodiment only monitors various parameters in the fermentation tank, and does not involve improvement of the PLC program. The fermentation tank in this embodiment can meet the requirements of aerobic fermentation or anaerobic fermentation of garbage in the warehouse; when the fermentation warehouse is in a sealed environment, the garbage in the warehouse will undergo anaerobic fermentation. The data records of the sensor can determine the anaerobic reaction cycle of the garbage. When it is judged that the garbage is in the late stage of the anaerobic reaction, it can switch to the aerobic reaction mode. At this time, the fan starts and injects the garbage into the warehouse through the ventilation duct. Air, that is, to achieve an aerobic environment in the warehouse.

更进一步地,通风管道为耐腐蚀且强度高的特氟龙不锈钢管,特氟龙不锈钢管上均匀设置若干通风孔,以便向垃圾中注入空气,特氟龙不锈钢管的表面紧密缠绕有短纤针刺土工布,防止细小垃圾堵塞通风孔。Furthermore, the ventilation pipe is a corrosion-resistant and high-strength Teflon stainless steel tube. A number of ventilation holes are evenly arranged on the Teflon stainless steel tube to inject air into the garbage. The surface of the Teflon stainless steel tube is tightly wound with short fibers. Needle-punched geotextiles prevent fine debris from clogging ventilation holes.

进一步地,渗滤液处理单元13包括用于对发酵单元4产生的渗透液进行处理的两级DTRO(碟管式反渗透)装置和用于对两级DTRO装置产生的浓水进行处理的MVR蒸发器,两级DTRO装置的进液口与发酵单元4相连,两级DTRO装置的浓水出口与MVR蒸发器相连,渗滤液处理达标后可排放或回用。发酵单元4产生的渗透液经过两级DTRO装置进行反渗透处理,得到的反渗透浓缩液再经过MVR蒸发器进行蒸发结晶,产生的混合废盐作为危废装袋处理,两级DTRO装置和MVR蒸发器的产水经过消毒后进入回用水池。Further, the leachate treatment unit 13 includes a two-stage DTRO (disk tube reverse osmosis) device for treating the permeate generated by the fermentation unit 4 and an MVR evaporation device for treating the concentrated water generated by the two-stage DTRO device. The liquid inlet of the two-stage DTRO device is connected to the fermentation unit 4, the concentrated water outlet of the two-stage DTRO device is connected to the MVR evaporator, and the leachate can be discharged or reused after the treatment reaches the standard. The permeate produced by fermentation unit 4 is subjected to reverse osmosis treatment through a two-stage DTRO device, and the obtained reverse osmosis concentrate is evaporated and crystallized through an MVR evaporator, and the mixed waste salt generated is treated as hazardous waste in bags. The two-stage DTRO device and MVR The water produced by the evaporator is disinfected and then enters the reuse water tank.

进一步地,沼气预处理单元9包括依次连接的用于脱水的第一塔式沼气脱水器、用于脱硫的第一生物脱硫设备和用于脱碳的膜法沼气脱碳净化设备;沼气发电单元10包括储气罐、沼气锅炉和沼气发电机组;第一塔式沼气脱水器与第一阀门5连接,膜法沼气脱碳净化设备与储气罐连接,储气罐分别与沼气锅炉和沼气发电机组连接。厌氧发酵产生的高浓度沼气进入沼气预处理单元9依次进行脱水、脱硫和脱碳处理,后进入沼气发电单元10进行发电利用。Further, the biogas pretreatment unit 9 includes a first tower biogas dehydrator for dehydration, a first biological desulfurization device for desulfurization, and a membrane biogas decarbonization purification device for decarbonization connected in sequence; the biogas power generation unit 10 includes a gas storage tank, a biogas boiler and a biogas generator set; the first tower biogas dehydrator is connected to the first valve 5, the membrane method biogas decarbonization purification equipment is connected to the gas storage tank, and the gas storage tank is respectively connected to the biogas boiler and biogas power generation Unit connection. The high-concentration biogas produced by anaerobic fermentation enters the biogas pretreatment unit 9 for dehydration, desulfurization and decarbonization in sequence, and then enters the biogas power generation unit 10 for power generation and utilization.

进一步地,沼气净化单元11包括依次连接的用于脱水的第二塔式沼气脱水器和用于脱硫的第二生物脱硫设备,沼气燃烧单元12包括用于燃烧净化后沼气的内燃式沼气火炬,沼气在火炬中与空气混合后燃烧,经排气筒排入大气;第二塔式沼气脱水器与第二阀门6连接,第二生物脱硫设备与内燃式沼气火炬连接。好氧发酵产生的低浓度沼气进入沼气净化单元11依次进行脱水、脱硫处理,后进入内燃式沼气火炬中进行安全燃烧。Further, the biogas purification unit 11 includes a second tower biogas dehydrator for dehydration and a second biological desulfurization device for desulfurization connected in sequence, and the biogas combustion unit 12 includes an internal combustion biogas torch for burning purified biogas, The biogas is mixed with air in the torch and burned, and discharged into the atmosphere through the exhaust pipe; the second tower biogas dehydrator is connected to the second valve 6, and the second biological desulfurization equipment is connected to the internal combustion biogas torch. The low-concentration biogas produced by aerobic fermentation enters the biogas purification unit 11 for dehydration and desulfurization in turn, and then enters the internal combustion biogas torch for safe combustion.

如图1所示,本发明实施例还提供一种集成式生活垃圾资源化处理方法,该方法包括如下步骤:As shown in Figure 1, the embodiment of the present invention also provides an integrated domestic waste resource treatment method, which includes the following steps:

1)将生活垃圾置于垃圾储存单元1的垃圾仓中暂存;当仓内臭气浓度超过设定浓度后,臭气监测器可将启动信号传递至自动喷淋装置,触发自动喷淋臭气抑制剂,在消除恶臭的同时还可抑制苍蝇蚊虫的滋生;1) Put domestic garbage in the garbage bin of garbage storage unit 1 for temporary storage; when the odor concentration in the bin exceeds the set concentration, the odor monitor can transmit the start signal to the automatic spray device to trigger the automatic spray odor Gas inhibitor, while eliminating the stench, it can also inhibit the breeding of flies and mosquitoes;

2)将生活垃圾运输至破碎筛分单元2,经破碎装置破碎,由螺旋推进器传输至筛分装置,筛分除去生活垃圾中的石块后,筛选后的垃圾传输至磁选单元3,经永磁辊式磁选机磁选除去金属杂物;2) Transport the domestic waste to the crushing and screening unit 2, crush it through the crushing device, and transfer it to the screening device by the screw propeller. After screening and removing the stones in the domestic waste, the screened waste is transferred to the magnetic separation unit 3, Remove metal impurities by magnetic separation with permanent magnet roller magnetic separator;

3)关闭第二阀门6和旁通阀7,打开第一阀门5,磁选后的生活垃圾进入发酵单元4的发酵罐体中进行厌氧发酵,厌氧发酵产生的沼气进入沼气预处理单元9中依次进行脱水、脱硫和脱碳处理,预处理后沼气进入沼气发电单元10进行发电;厌氧反应产生的渗滤液通过管道进入渗滤液处理单元13中,经过两级DTRO装置和MVR蒸发器处理达标后排放或回用;3) Close the second valve 6 and the bypass valve 7, open the first valve 5, the domestic garbage after magnetic separation enters the fermentation tank of the fermentation unit 4 for anaerobic fermentation, and the biogas generated by anaerobic fermentation enters the biogas pretreatment unit In 9, dehydration, desulfurization and decarbonization are carried out sequentially. After pretreatment, the biogas enters the biogas power generation unit 10 for power generation; the leachate generated by the anaerobic reaction enters the leachate treatment unit 13 through the pipeline, and passes through the two-stage DTRO device and the MVR evaporator Discharge or reuse after treatment reaches the standard;

4)根据发酵罐体内的传感器检测的垃圾堆体温度和发酵罐体内压力、沼气浓度、氧气浓度和二氧化碳浓度判断垃圾所处厌氧反应周期;当检测到发酵罐体内的生活垃圾的BDM(生物降解率)值小于6%时,则认为生活垃圾处于厌氧反应后期;当生活垃圾处于厌氧反应后期时,打开第二阀门6和旁通阀7,关闭第一阀门5,打开风机8向发酵罐体内的垃圾堆体中注入空气,生活垃圾开始进行好氧发酵,好氧发酵产生的沼气进入沼气净化单元11中依次进行脱水和脱硫处理,净化后的沼气进入沼气燃烧单元12中安全燃烧;好氧发酵产生的渗滤液部分回灌至发酵单元4中,其余渗滤液通过管道进入渗滤液处理单元13处理达标后排放或回用;好氧发酵时部分渗滤液回灌至发酵仓垃圾中,可调节垃圾堆体内湿度,给微生物降解垃圾过程提供必要的水分补充,改善了微生物的生存环境。此外,渗滤液中含有大量降解垃圾的优势菌,回灌即是给垃圾堆体中微生物补充优势菌的过程,可显著提高垃圾堆体中微生物的活性,大大提高其降解仓内垃圾的效率,缩短系统运行周期;4) Judging the anaerobic reaction cycle of the garbage according to the temperature of the garbage dump detected by the sensor in the fermentation tank, the pressure in the fermentation tank, the concentration of methane, the concentration of oxygen and the concentration of carbon dioxide; when the BDM (biological When the value is less than 6%, it is considered that the domestic waste is in the late stage of anaerobic reaction; when the domestic waste is in the late stage of anaerobic reaction, open the second valve 6 and the bypass valve 7, close the first valve 5, and turn on the fan 8 Air is injected into the garbage pile in the fermentation tank, and the domestic garbage starts to undergo aerobic fermentation. The biogas generated by aerobic fermentation enters the biogas purification unit 11 for dehydration and desulfurization in turn, and the purified biogas enters the biogas combustion unit 12 for safe combustion. Part of the leachate produced by aerobic fermentation is refilled into the fermentation unit 4, and the rest of the leachate enters the leachate treatment unit 13 through the pipeline and is discharged or reused after reaching the standard; during aerobic fermentation, part of the leachate is refilled into the fermentation bin garbage , can adjust the humidity inside the garbage dump, provide the necessary water supplement for the process of microbial degradation of garbage, and improve the living environment of microorganisms. In addition, the leachate contains a large number of dominant bacteria that degrade garbage. Reinjection is the process of supplementing the dominant bacteria in the microorganisms in the garbage dump, which can significantly improve the activity of the microorganisms in the garbage dump, and greatly improve its efficiency in degrading the garbage in the bin. Shorten the system operation cycle;

5)生活垃圾在发酵单元4中依次经过厌氧发酵和好氧发酵后,达到基本稳定状态,转至卫生填埋场进行填埋。5) Household wastes undergo anaerobic fermentation and aerobic fermentation successively in the fermentation unit 4, and reach a basic stable state, and are transferred to sanitary landfills for landfill.

本实施例提供的集成式生活垃圾资源化处理系统中垃圾在发酵罐体内发生厌氧反应和好氧反应,反应条件可监控可调节,在最适条件下垃圾可充分发酵,且反应速度相比自然条件大大缩短;将垃圾在厌氧阶段产生的高浓度沼气予以发电,在好氧阶段产生的低浓度沼气予以燃烧,系统可根据监控结果自动完成切换操作,配置合理,沼气利用经济效益高。In the integrated domestic waste resource treatment system provided in this example, the waste undergoes anaerobic and aerobic reactions in the fermentation tank, the reaction conditions can be monitored and adjusted, and the waste can be fully fermented under optimal conditions, and the reaction speed is compared The natural conditions are greatly shortened; the high-concentration biogas generated by the garbage in the anaerobic stage is used for power generation, and the low-concentration biogas generated in the aerobic stage is burned. The system can automatically complete the switching operation according to the monitoring results. The configuration is reasonable and the economic benefits of biogas utilization are high.

本实施例提供的集成式生活垃圾资源化处理工艺合理,能够实现生活垃圾的环境污染最小化和资源利用最大化目标,污染排放少,且经济效益好。The integrated domestic waste resource treatment process provided in this embodiment is reasonable, can realize the goal of minimizing environmental pollution of domestic waste and maximizing resource utilization, with less pollution discharge and good economic benefits.

以上所述仅为本发明的较佳实施例而已,并不用以限制本发明,凡在本发明的精神和原则之内,所作的任何修改、等同替换、改进等,均应包含在本发明的保护范围之内。The above descriptions are only preferred embodiments of the present invention, and are not intended to limit the present invention. Any modifications, equivalent replacements, improvements, etc. made within the spirit and principles of the present invention shall be included in the scope of the present invention. within the scope of protection.

Claims (10)

1. a kind of integrated form domestic garbage resource processing system, it is characterised in that:Including rubbish storage unit(1), broken sieve Subdivision(2), magnetic separating unit(3), fermentation unit(4), biogas pretreatment unit(9), marsh gas purifying unit(11), marsh gas power generation Unit(10)With biogas combustion unit(12);The rubbish storage unit(1), the crushing and screening unit(2), the magnetic separation list Member(3)With the fermentation unit(4)It is sequentially connected;The fermentation unit(4)Gas outlet be connected separately with anaerobic methane pipeline With aerobic methane pipeline, the first valve is equipped on the anaerobic methane pipeline successively(5), the biogas pretreatment unit(9)With The marsh gas power generation unit(10);The second valve is equipped on the aerobic methane pipeline successively(6), the marsh gas purifying unit (11)With the biogas combustion unit(12).
2. a kind of integrated form domestic garbage resource processing system as described in claim 1, it is characterised in that:The fermentation is single Member(4)Liquid outlet be connected with diafiltration liquid pipeline, the diafiltration liquid pipeline is equipped with percolate processing unit(13), the diafiltration Be connected with leachate tail water recharge bypass on liquid pipeline and the leachate tail water recharge bypass outlet end be connected to it is described Fermentation unit(4), by-passing valve is equipped in leachate tail water recharge bypass(7).
3. a kind of integrated form domestic garbage resource processing system as described in claim 1, it is characterised in that:The garbage storing Memory cell(1)Include the trash repository for interim storage house refuse, is equipped in the trash repository for monitoring odor concentration Foul smell monitor and automatic spraying device for spraying odor inhibitor, the foul smell monitor connect with automatic spraying device It connects.
4. a kind of integrated form domestic garbage resource processing system as described in claim 1, it is characterised in that:The broken sieve Subdivision(2)Including sequentially connected breaker for shredding refuse, it is used for transmission the spiral propeller of rubbish and is used for Sieve the screening plant of rubbish;The magnetic separating unit(3)It include the permanent magnetic roll type magnetic separator that metal sundries are removed for magnetic separation;Institute The feed inlet for stating permanent magnetic roll type magnetic separator is connected with the discharge port of the screening plant, the discharge port of the permanent magnetic roll type magnetic separator With the fermentation unit(4)It is connected.
5. a kind of integrated form domestic garbage resource processing system as claimed in claim 2, it is characterised in that:The fermentation is single Member(4)Include the fermentation tank for house refuse of fermenting, the gas outlet of the fermentation tank respectively with the anaerobic methane pipe The air inlet on road is connected with the air inlet of the aerobic methane pipeline;The liquid outlet of the fermentation tank and the diafiltration liquid pipeline Inlet be connected;The ventilation shaft for injecting air into junk-heap body is equipped in the fermentation tank.
6. a kind of integrated form domestic garbage resource processing system as claimed in claim 5, it is characterised in that:The ventilation duct Road is Teflon stainless steel tube, and several ventilation holes, the Teflon stainless steel tube are uniformly arranged on the Teflon stainless steel tube Surface wrap have chopped fiber needle-punched geotextiles.
7. a kind of integrated form domestic garbage resource processing system as claimed in claim 2, it is characterised in that:The percolate Processing unit(13)Including being used for the fermentation unit(4)The two-stage DTRO devices and be used for that the penetrating fluid of generation is handled To the MVR evaporators that the concentrated water that two-stage DTRO devices generate is handled, inlet and the hair of the two-stage DTRO devices Ferment unit(4)It is connected, the concentrated water outlet of the two-stage DTRO devices is connected with the MVR evaporators.
8. a kind of integrated form domestic garbage resource processing system as described in claim 1, it is characterised in that:The biogas is pre- Processing unit(9)Including sequentially connected the first tower methane dehydrator for being used for dehydration, for the first biological desulphurization of desulfurization Equipment and embrane method Methane decarbonization cleaning equipment for decarburization, the marsh gas power generation unit(10)Including air accumulator, methane boiler And Biogas Generator Set;The first tower methane dehydrator and the first valve(5)Connection, the embrane method Methane decarbonization purification are set Standby to be connect with the air accumulator, the air accumulator is connect with the methane boiler and the Biogas Generator Set respectively.
9. a kind of integrated form domestic garbage resource processing system as described in claim 1, it is characterised in that:The biogas is net Change unit(11)Including sequentially connected the second tower methane dehydrator for dehydration and for the second biological desulphurization of desulfurization Equipment, the biogas combustion unit(12)It include the internal-combustion biogas torch for biogas after purification of burning;Described second is tower Methane dehydrator and the second valve(6)Connection, second biological desulfurization apparatus are connect with the internal-combustion biogas torch.
10. a kind of integrated form domestic garbage resource processing method, which is characterized in that this method comprises the following steps:
1)House refuse is placed in rubbish storage unit(1)It is temporary;
2)House refuse is transported to crushing and screening unit(2), through stone broken, after screening in removing house refuse;It passes through again Magnetic separating unit(3)Magnetic separation removes metal sundries;
3)Close the second valve(6)And by-passing valve(7), open the first valve(5), house refuse enters fermentation unit(4)Hair Anaerobic fermentation is carried out in fermentation tank body, the biogas that anaerobic fermentation generates enters biogas pretreatment unit(9)In be dehydrated, taken off successively Sulphur and carbonization treatment, biogas enters marsh gas power generation unit after pretreatment(10)It generates electricity;The percolate that anaerobic reaction generates is logical Piping enters percolate processing unit(13)Handle rear discharge or reuse up to standard;
4)When detecting that the BDM values of the house refuse in fermentation tank are less than 6%, then it is assumed that house refuse is in anaerobic reaction Later stage;When house refuse is in the anaerobic reaction later stage, the second valve is opened(6)And by-passing valve(7), close the first valve(5), Open wind turbine(8)Air is injected in junk-heap body into fermentation tank, house refuse proceeds by aerobic fermentation, aerobic fermentation The biogas of generation enters marsh gas purifying unit(11)In carry out successively dehydration and desulfurization process, purified biogas enter biogas combustion Burn unit(12)Middle safe combustion;The percolate part recharge that aerobic fermentation generates is to fermentation unit(4)In, remaining percolate is logical Piping enters percolate processing unit(13)Handle rear discharge or reuse up to standard;
5)House refuse is in fermentation unit(4)In successively after anaerobic fermentation and aerobic fermentation, reach basicly stable state, turn It is filled to sanitary filling field.
CN201810763117.3A 2018-07-12 2018-07-12 A kind of integrated form domestic garbage resource processing system and its processing method Pending CN108723067A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109266543A (en) * 2018-11-20 2019-01-25 黄冬艳 A kind of methane production device of automatic adjustment
CN111196999A (en) * 2020-01-13 2020-05-26 中国科学院青岛生物能源与过程研究所 Biomass garbage batch type microbial fermentation treatment system and treatment method
CN113441510A (en) * 2021-07-01 2021-09-28 格尔木弘钜环保科技有限公司 Landfill method for treating waste by waste through treating aluminum ash with industrial waste acid

Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1923382A (en) * 2006-07-07 2007-03-07 华中科技大学 Domestic refuse anaerobic-aerobic reactor circulating operation landfill method
CN102476959A (en) * 2010-11-30 2012-05-30 中国环境科学研究院 Anaerobic quick start and anaerobic-aerobic integrated fermentation method under low temperature condition
CN102527701A (en) * 2012-01-06 2012-07-04 北京昊海天际科技有限公司 Comprehensive treating system for domestic wastes
CN102615092A (en) * 2012-04-10 2012-08-01 苏州天荣能源环境科技有限公司 Municipal refuse treatment device and method
CN102643118A (en) * 2012-04-26 2012-08-22 杨军 Method and device for harmless and recycled disposal of domestic garbage
CN202595137U (en) * 2012-06-01 2012-12-12 江苏雪枫环保科技有限公司 Methane collection power generation system
CN104438289A (en) * 2014-11-21 2015-03-25 广东源盛生态环保科技有限公司 Zero waste emission power generation method
CN205188273U (en) * 2015-11-30 2016-04-27 中国天楹股份有限公司 Anaerobic fermentation system is united with excrement and urine to district rubbish from cooking
CN106140780A (en) * 2015-04-13 2016-11-23 樊军 One way of life refuse disposal system
CN106881337A (en) * 2017-04-19 2017-06-23 江苏雪枫环保科技有限公司 A kind of many output formula biologic garbage processing equipments
CN207057247U (en) * 2017-02-15 2018-03-02 唐山绿航机械制造有限公司 A kind of small towns consumer waste innocent comprehensive treatment equipment
CN208695922U (en) * 2018-07-12 2019-04-05 武汉都市环保工程技术股份有限公司 A kind of integrated form domestic garbage resource processing system

Patent Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1923382A (en) * 2006-07-07 2007-03-07 华中科技大学 Domestic refuse anaerobic-aerobic reactor circulating operation landfill method
CN102476959A (en) * 2010-11-30 2012-05-30 中国环境科学研究院 Anaerobic quick start and anaerobic-aerobic integrated fermentation method under low temperature condition
CN102527701A (en) * 2012-01-06 2012-07-04 北京昊海天际科技有限公司 Comprehensive treating system for domestic wastes
CN102615092A (en) * 2012-04-10 2012-08-01 苏州天荣能源环境科技有限公司 Municipal refuse treatment device and method
CN102643118A (en) * 2012-04-26 2012-08-22 杨军 Method and device for harmless and recycled disposal of domestic garbage
CN202595137U (en) * 2012-06-01 2012-12-12 江苏雪枫环保科技有限公司 Methane collection power generation system
CN104438289A (en) * 2014-11-21 2015-03-25 广东源盛生态环保科技有限公司 Zero waste emission power generation method
CN106140780A (en) * 2015-04-13 2016-11-23 樊军 One way of life refuse disposal system
CN205188273U (en) * 2015-11-30 2016-04-27 中国天楹股份有限公司 Anaerobic fermentation system is united with excrement and urine to district rubbish from cooking
CN207057247U (en) * 2017-02-15 2018-03-02 唐山绿航机械制造有限公司 A kind of small towns consumer waste innocent comprehensive treatment equipment
CN106881337A (en) * 2017-04-19 2017-06-23 江苏雪枫环保科技有限公司 A kind of many output formula biologic garbage processing equipments
CN208695922U (en) * 2018-07-12 2019-04-05 武汉都市环保工程技术股份有限公司 A kind of integrated form domestic garbage resource processing system

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109266543A (en) * 2018-11-20 2019-01-25 黄冬艳 A kind of methane production device of automatic adjustment
CN111196999A (en) * 2020-01-13 2020-05-26 中国科学院青岛生物能源与过程研究所 Biomass garbage batch type microbial fermentation treatment system and treatment method
CN113441510A (en) * 2021-07-01 2021-09-28 格尔木弘钜环保科技有限公司 Landfill method for treating waste by waste through treating aluminum ash with industrial waste acid

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