CN111872048A - A kind of wet garbage humidity control fermentation power generation system and process - Google Patents
A kind of wet garbage humidity control fermentation power generation system and process Download PDFInfo
- Publication number
- CN111872048A CN111872048A CN202010754015.2A CN202010754015A CN111872048A CN 111872048 A CN111872048 A CN 111872048A CN 202010754015 A CN202010754015 A CN 202010754015A CN 111872048 A CN111872048 A CN 111872048A
- Authority
- CN
- China
- Prior art keywords
- wet
- flue gas
- power generation
- fermentation
- humidity
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 238000000855 fermentation Methods 0.000 title claims abstract description 131
- 239000010813 municipal solid waste Substances 0.000 title claims abstract description 88
- 238000010248 power generation Methods 0.000 title claims abstract description 62
- 230000004151 fermentation Effects 0.000 title claims abstract description 52
- 238000000034 method Methods 0.000 title claims abstract description 22
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims abstract description 87
- 239000003546 flue gas Substances 0.000 claims abstract description 87
- 239000000446 fuel Substances 0.000 claims abstract description 11
- 230000005611 electricity Effects 0.000 claims abstract description 9
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 8
- 239000002699 waste material Substances 0.000 claims description 82
- 230000003750 conditioning effect Effects 0.000 claims description 33
- 239000002002 slurry Substances 0.000 claims description 22
- 239000003337 fertilizer Substances 0.000 claims description 18
- 239000002918 waste heat Substances 0.000 claims description 13
- 238000002360 preparation method Methods 0.000 claims description 12
- 239000007789 gas Substances 0.000 claims description 7
- 239000002994 raw material Substances 0.000 claims description 7
- 239000000779 smoke Substances 0.000 claims description 7
- 238000004519 manufacturing process Methods 0.000 claims description 4
- 230000001143 conditioned effect Effects 0.000 claims 1
- 238000010438 heat treatment Methods 0.000 abstract 1
- 241000894006 Bacteria Species 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 235000013305 food Nutrition 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 235000019645 odor Nutrition 0.000 description 2
- 238000003860 storage Methods 0.000 description 2
- 241000219112 Cucumis Species 0.000 description 1
- 235000015510 Cucumis melo subsp melo Nutrition 0.000 description 1
- 241000238631 Hexapoda Species 0.000 description 1
- 241001464837 Viridiplantae Species 0.000 description 1
- 241000607479 Yersinia pestis Species 0.000 description 1
- FJJCIZWZNKZHII-UHFFFAOYSA-N [4,6-bis(cyanoamino)-1,3,5-triazin-2-yl]cyanamide Chemical compound N#CNC1=NC(NC#N)=NC(NC#N)=N1 FJJCIZWZNKZHII-UHFFFAOYSA-N 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000007791 dehumidification Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 201000010099 disease Diseases 0.000 description 1
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 description 1
- 239000010791 domestic waste Substances 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 235000006694 eating habits Nutrition 0.000 description 1
- 235000013399 edible fruits Nutrition 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000010794 food waste Substances 0.000 description 1
- 231100001261 hazardous Toxicity 0.000 description 1
- 239000010806 kitchen waste Substances 0.000 description 1
- 235000021190 leftovers Nutrition 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 239000010815 organic waste Substances 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000004056 waste incineration Methods 0.000 description 1
Images
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/40—Destroying solid waste or transforming solid waste into something useful or harmless involving thermal treatment, e.g. evaporation
Landscapes
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Physics & Mathematics (AREA)
- Thermal Sciences (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
本发明公开了一种湿垃圾调湿发酵发电系统及工艺,系统包括湿垃圾调湿设备、厌氧发酵设备及焚烧发电锅炉;湿垃圾调湿设备的湿垃圾空间连接湿垃圾源,湿垃圾调湿设备的垃圾出口连接厌氧发酵设备的垃圾进口,厌氧发酵设备的沼气出口连接焚烧发电锅炉的燃料进口,焚烧发电锅炉烟气出口连接湿垃圾调湿设备的烟气进口,湿垃圾调湿设备的烟气出口连接厌氧发酵设备的烟气进口。工艺为:将湿垃圾进行加热调湿去除湿垃圾中的部分水,再将调湿后的湿垃圾进行厌氧发酵,将厌氧发酵后的沼气进行焚烧发电,焚烧发电的烟气对湿垃圾进行加热调湿,采用调湿后的烟气调节厌氧发酵的温度。
The invention discloses a wet garbage humidity control fermentation power generation system and a process. The system includes wet garbage humidity control equipment, anaerobic fermentation equipment and an incineration power generation boiler; the wet garbage space of the wet garbage humidity control equipment is connected to the wet garbage source, and the wet garbage adjustment The garbage outlet of the wet equipment is connected to the garbage inlet of the anaerobic fermentation equipment, the biogas outlet of the anaerobic fermentation equipment is connected to the fuel inlet of the incineration power generation boiler, the flue gas outlet of the incineration power generation boiler is connected to the flue gas inlet of the wet garbage humidity control equipment, and the wet garbage humidity control The flue gas outlet of the equipment is connected to the flue gas inlet of the anaerobic fermentation equipment. The process is: heating the wet garbage to adjust the humidity to remove part of the water in the wet garbage, then anaerobic fermentation of the wet garbage after humidity adjustment, incineration of the biogas after anaerobic fermentation to generate electricity, and the flue gas of the incineration power generation to the wet garbage. The temperature of anaerobic fermentation is adjusted by using the flue gas after humidity adjustment.
Description
技术领域technical field
本发明涉及湿垃圾处理技术领域,具体涉及一种湿垃圾调湿发酵发电系统及工艺。The invention relates to the technical field of wet garbage disposal, in particular to a wet garbage humidity control fermentation power generation system and process.
背景技术Background technique
公开该背景技术部分的信息仅仅旨在增加对本发明的总体背景的理解,而不必然被视为承认或以任何形式暗示该信息构成已经成为本领域一般技术人员所公知的现有技术。The information disclosed in this Background section is only for enhancement of understanding of the general background of the invention and should not necessarily be taken as an acknowledgement or any form of suggestion that this information forms the prior art already known to a person of ordinary skill in the art.
我国人口众多,而且饮食习惯复杂,产生的垃圾量巨大而且垃圾的含水量也很大。随着我国垃圾分类的实施,垃圾分为可回收垃圾、干垃圾、湿垃圾及有害垃圾。其中,湿垃圾是指又称为厨余垃圾、有机垃圾,即易腐垃圾,指食材废料、剩菜剩饭、过期食品、瓜皮果核、花卉绿植、中药药渣等易腐的生物质生活废弃物。目前,湿垃圾以家庭厨房、餐厅、饭店、食堂、市场及其他与食品加工有关的行业作为主要来源,根据本发明的发明人研究发现,这种被分类出来的湿垃圾含水量更是大。湿垃圾数量巨大,如果不及时处理,会产生严重的异味,还会滋生细菌,最终污染环境。处理大量湿垃圾最快的方式就是焚烧。然而,经过本发明的发明人进一步研究发现,利用这类湿垃圾焚烧发电时,含水量大会限制锅炉的利用效率和发电量。my country has a large population and complex eating habits. The amount of garbage generated is huge and the water content of the garbage is also very large. With the implementation of garbage classification in my country, garbage is divided into recyclable garbage, dry garbage, wet garbage and hazardous garbage. Among them, wet waste refers to also known as kitchen waste, organic waste, or perishable waste, which refers to food waste, leftovers, expired food, melon peel and fruit pits, flowers and green plants, traditional Chinese medicine dregs and other perishable raw materials. Material domestic waste. At present, household kitchens, restaurants, restaurants, canteens, markets and other industries related to food processing are the main sources of wet waste. According to the research of the inventors of the present invention, it is found that the classified wet waste has a higher water content. The amount of wet garbage is huge. If it is not disposed of in time, it will produce serious odors, breed bacteria, and eventually pollute the environment. The fastest way to dispose of large amounts of wet waste is incineration. However, through further research by the inventors of the present invention, it is found that when such wet waste is used for incineration to generate electricity, the water content will limit the utilization efficiency and power generation of the boiler.
发明内容SUMMARY OF THE INVENTION
为了解决现有技术的不足,本发明的目的是提供一种湿垃圾调湿发酵发电系统及工艺,能够避免湿垃圾焚烧发电存在的限制锅炉的利用效率和发电量的问题,具有节能高效环保、能量利用率高等特点。In order to solve the deficiencies of the prior art, the purpose of the present invention is to provide a wet waste humidity control fermentation power generation system and process, which can avoid the problem of limiting the utilization efficiency and power generation of the boiler existing in the wet waste incineration power generation, and has the advantages of energy saving, high efficiency, environmental protection, High energy utilization characteristics.
为了实现上述目的,本发明的技术方案为:In order to achieve the above object, the technical scheme of the present invention is:
一方面,一种湿垃圾调湿发酵发电系统,包括湿垃圾调湿设备、厌氧发酵设备及焚烧发电锅炉;On the one hand, a wet waste humidity control and fermentation power generation system includes wet waste humidity control equipment, anaerobic fermentation equipment and an incineration power generation boiler;
所述湿垃圾调湿设备设有烟气通道和湿垃圾空间,烟气通道和湿垃圾空间使得烟气与湿垃圾间接接触,实现利用烟气的高温余热调节湿垃圾的湿度;The wet garbage humidity conditioning equipment is provided with a flue gas channel and a wet garbage space, and the flue gas channel and the wet garbage space make the flue gas indirectly contact with the wet garbage, so that the high temperature waste heat of the flue gas can be used to adjust the humidity of the wet garbage;
厌氧发酵设备设有烟气通道和发酵空间,烟气通道和发酵空间使得烟气与发酵原料间接接触,实现利用烟气的低温余热调节发酵温度;The anaerobic fermentation equipment is provided with a flue gas channel and a fermentation space. The flue gas channel and the fermentation space make the flue gas indirectly contact with the fermentation raw materials, and realize the use of the low-temperature waste heat of the flue gas to adjust the fermentation temperature;
湿垃圾调湿设备的湿垃圾空间连接湿垃圾源,湿垃圾调湿设备的垃圾出口连接厌氧发酵设备的垃圾进口,厌氧发酵设备的沼气出口连接焚烧发电锅炉的燃料进口,焚烧发电锅炉烟气出口连接湿垃圾调湿设备的烟气进口,湿垃圾调湿设备的烟气出口连接厌氧发酵设备的烟气进口。The wet waste space of the wet waste humidity conditioning equipment is connected to the wet waste source, the waste outlet of the wet waste humidity conditioning equipment is connected to the waste inlet of the anaerobic fermentation equipment, the biogas outlet of the anaerobic fermentation equipment is connected to the fuel inlet of the incineration power generation boiler, and the smoke of the incineration power generation boiler is connected. The gas outlet is connected to the flue gas inlet of the wet waste humidity conditioning device, and the flue gas outlet of the wet waste humidity conditioning device is connected to the flue gas inlet of the anaerobic fermentation device.
另一方面,一种湿垃圾调湿发酵发电工艺,将湿垃圾进行加热调湿去除湿垃圾中的部分水,再将调湿后的湿垃圾进行厌氧发酵,将厌氧发酵后的沼气进行焚烧发电,焚烧发电的烟气对湿垃圾进行加热调湿,采用调湿后的烟气调节厌氧发酵的温度。On the other hand, a wet waste conditioning and fermentation power generation process, the wet waste is heated and humidified to remove part of the water in the wet waste, and then the wet waste after humidity conditioning is subjected to anaerobic fermentation, and the biogas after anaerobic fermentation is subjected to anaerobic fermentation. Incineration power generation, the flue gas of incineration power generation is used to heat the wet garbage and adjust the humidity, and the flue gas after humidity adjustment is used to adjust the temperature of anaerobic fermentation.
本发明的有益效果为:The beneficial effects of the present invention are:
1.本发明利用高温烟气调节湿垃圾湿度,使湿垃圾的湿度可以达到厌氧发酵最适合的湿度,用低温烟气促进厌氧发酵,缩短发酵时间,增加发酵产物。充分利用了烟气的余热,大大提高了能量的利用率。1. The present invention utilizes high-temperature flue gas to adjust the humidity of wet garbage, so that the humidity of wet garbage can reach the most suitable humidity for anaerobic fermentation, and uses low-temperature flue gas to promote anaerobic fermentation, shorten fermentation time, and increase fermentation products. The waste heat of the flue gas is fully utilized, which greatly improves the utilization rate of energy.
2.本发明利用垃圾厌氧发酵的沼气和沼渣焚烧发电,环保节能高效。2. The present invention utilizes the biogas and biogas residues from the anaerobic fermentation of garbage to generate electricity, which is environmentally friendly, energy-saving and efficient.
3.本发明通过调湿设备可以调节垃圾的湿度,使湿度最适合垃圾细菌发酵。3. In the present invention, the humidity of garbage can be adjusted through the humidity control device, so that the humidity is most suitable for the fermentation of garbage bacteria.
4.本发明可以厌氧发酵产生的沼液被收集,用做肥料、饲料,防治病虫害等。4. In the present invention, the biogas slurry produced by anaerobic fermentation can be collected and used as fertilizer, feed, and control of diseases and insect pests.
5.本发明厌氧发酵产生的沼渣既可以去锅炉焚烧发电,也可以作为化肥使用。5. The biogas residue produced by the anaerobic fermentation of the present invention can not only be used for incineration in boilers to generate electricity, but also can be used as chemical fertilizer.
6.本发明湿垃圾除湿后不直接焚烧发电,用其发酵产生品质更好的沼气,有利于提高资源利用率。6. The wet garbage of the present invention does not directly incinerate to generate electricity after dehumidification, and uses it to ferment to produce biogas with better quality, which is beneficial to improve resource utilization.
附图说明Description of drawings
构成本发明的一部分的说明书附图用来提供对本发明的进一步理解,本发明的示意性实施例及其说明用于解释本发明,并不构成对本发明的不当限定。The accompanying drawings forming a part of the present invention are used to provide further understanding of the present invention, and the exemplary embodiments of the present invention and their descriptions are used to explain the present invention, and do not constitute an improper limitation of the present invention.
图1为本发明的湿垃圾调湿发酵发电的工艺流程图;Fig. 1 is the process flow diagram of the wet garbage humidity control fermentation power generation of the present invention;
其中,1、湿垃圾库,2、湿垃圾调湿设备,3、湿度合适的垃圾,4、厌氧发酵设备,5、沼气,6、焚烧锅炉,7、高温烟气,8、低温烟气,9、烟气,10、沼液,11、沼渣。Among them, 1. Wet garbage storage, 2. Wet garbage humidity control equipment, 3. Garbage with suitable humidity, 4. Anaerobic fermentation equipment, 5. Biogas, 6. Incineration boiler, 7. High temperature flue gas, 8. Low temperature flue gas , 9, flue gas, 10, biogas slurry, 11, biogas residue.
具体实施方式Detailed ways
应该指出,以下详细说明都是示例性的,旨在对本发明提供进一步的说明。除非另有指明,本文使用的所有技术和科学术语具有与本发明所属技术领域的普通技术人员通常理解的相同含义。It should be noted that the following detailed description is exemplary and intended to provide further explanation of the invention. Unless otherwise defined, all technical and scientific terms used herein have the same meaning as commonly understood by one of ordinary skill in the art to which this invention belongs.
需要注意的是,这里所使用的术语仅是为了描述具体实施方式,而非意图限制根据本发明的示例性实施方式。如在这里所使用的,除非上下文另外明确指出,否则单数形式也意图包括复数形式,此外,还应当理解的是,当在本说明书中使用术语“包含”和/或“包括”时,其指明存在特征、步骤、操作、器件、组件和/或它们的组合。It should be noted that the terminology used herein is for the purpose of describing specific embodiments only, and is not intended to limit the exemplary embodiments according to the present invention. As used herein, unless the context clearly dictates otherwise, the singular is intended to include the plural as well, furthermore, it is to be understood that when the terms "comprising" and/or "including" are used in this specification, it indicates that There are features, steps, operations, devices, components and/or combinations thereof.
鉴于湿垃圾直接焚烧发电存在锅炉的利用效率和发电量低的问题,本发明提出了一种湿垃圾调湿发酵发电系统及工艺。In view of the problems of low utilization efficiency and low power generation of boilers caused by direct incineration of wet waste for power generation, the present invention proposes a system and process for power generation by humidity control and fermentation of wet waste.
本发明的一种典型实施方式,提供了一种湿垃圾调湿发酵发电系统,包括湿垃圾调湿设备、厌氧发酵设备及焚烧发电锅炉;A typical embodiment of the present invention provides a wet waste humidity control and fermentation power generation system, including wet waste humidity control equipment, anaerobic fermentation equipment and an incineration power generation boiler;
所述湿垃圾调湿设备设有烟气通道和湿垃圾空间,烟气通道和湿垃圾空间使得烟气与湿垃圾间接接触,实现利用烟气的高温余热调节湿垃圾的湿度,同时避免了烟气混入水蒸气和垃圾臭味;The wet garbage humidity conditioning equipment is provided with a flue gas channel and a wet garbage space. The flue gas channel and the wet garbage space make the flue gas indirectly contact with the wet garbage, so that the high temperature waste heat of the flue gas can be used to adjust the humidity of the wet garbage, and the smoke is avoided at the same time. Gas mixed with water vapor and garbage odor;
厌氧发酵设备设有烟气通道和发酵空间,烟气通道和发酵空间使得烟气与发酵原料间接接触,实现利用烟气的低温余热调节发酵温度;The anaerobic fermentation equipment is provided with a flue gas channel and a fermentation space. The flue gas channel and the fermentation space make the flue gas indirectly contact with the fermentation raw materials, and realize the use of the low-temperature waste heat of the flue gas to adjust the fermentation temperature;
湿垃圾调湿设备的湿垃圾空间连接湿垃圾源,湿垃圾调湿设备的垃圾出口连接厌氧发酵设备的垃圾进口,厌氧发酵设备的沼气出口连接焚烧发电锅炉的燃料进口,焚烧发电锅炉烟气出口连接湿垃圾调湿设备的烟气进口,湿垃圾调湿设备的烟气出口连接厌氧发酵设备的烟气进口。The wet waste space of the wet waste humidity conditioning equipment is connected to the wet waste source, the waste outlet of the wet waste humidity conditioning equipment is connected to the waste inlet of the anaerobic fermentation equipment, the biogas outlet of the anaerobic fermentation equipment is connected to the fuel inlet of the incineration power generation boiler, and the smoke of the incineration power generation boiler is connected. The gas outlet is connected to the flue gas inlet of the wet waste humidity conditioning device, and the flue gas outlet of the wet waste humidity conditioning device is connected to the flue gas inlet of the anaerobic fermentation device.
该实施方式的一种或多种实施例中,厌氧发酵设备的沼渣出口连接焚烧发电锅炉的燃料进口。In one or more examples of this embodiment, the biogas residue outlet of the anaerobic fermentation equipment is connected to the fuel inlet of the incineration power generation boiler.
该实施方式的一种或多种实施例中,包括沼液收集罐,厌氧发酵设备的沼液出口连接沼液收集罐。In one or more examples of this embodiment, a biogas slurry collection tank is included, and the biogas slurry outlet of the anaerobic fermentation equipment is connected to the biogas slurry collection tank.
该实施方式的一种或多种实施例中,包括化肥制备装置,厌氧发酵设备的沼液出口连接化肥制备装置。In one or more examples of this embodiment, a fertilizer preparation device is included, and the biogas slurry outlet of the anaerobic fermentation equipment is connected to the fertilizer preparation device.
该实施方式的一种或多种实施例中,包括化肥制备装置,厌氧发酵设备的沼渣出口连接化肥制备装置。In one or more examples of this embodiment, a fertilizer preparation device is included, and the biogas residue outlet of the anaerobic fermentation equipment is connected to the fertilizer preparation device.
本发明的另一种实施方式,提供了一种湿垃圾调湿发酵发电工艺,将湿垃圾进行加热调湿去除湿垃圾中的部分水,再将调湿后的湿垃圾进行厌氧发酵,将厌氧发酵后的沼气进行焚烧发电,焚烧发电的烟气对湿垃圾进行加热调湿,采用调湿后的烟气调节厌氧发酵的温度。Another embodiment of the present invention provides a process for generating electricity by humidity control and fermentation of wet waste. The wet waste is heated and humidified to remove part of the water in the wet waste. The biogas after anaerobic fermentation is incinerated for power generation, the flue gas from incineration and power generation is used to heat the wet garbage and adjust the humidity, and the flue gas after humidity adjustment is used to adjust the temperature of anaerobic fermentation.
该实施方式的一种或多种实施例中,湿垃圾调湿至24~40%进行厌氧发酵。In one or more examples of this embodiment, the wet garbage is adjusted to a humidity of 24-40% for anaerobic fermentation.
该实施方式的一种或多种实施例中,厌氧发酵后的沼渣进行焚烧发电。In one or more embodiments of this embodiment, the biogas residue after anaerobic fermentation is incinerated to generate electricity.
该实施方式的一种或多种实施例中,厌氧发酵后的沼渣进行制肥。In one or more embodiments of this embodiment, the anaerobic fermentation of the digestate is used for fertilizer production.
该实施方式的一种或多种实施例中,厌氧发酵后的沼液进行制肥。In one or more examples of this embodiment, the biogas slurry after anaerobic fermentation is used for fertilizer production.
为了使得本领域技术人员能够更加清楚地了解本发明的技术方案,以下将结合具体的实施例详细说明本发明的技术方案。In order to enable those skilled in the art to understand the technical solutions of the present invention more clearly, the technical solutions of the present invention will be described in detail below with reference to specific embodiments.
实施例1Example 1
一种湿垃圾调湿发酵发电系统,包括湿垃圾调湿设备、厌氧发酵设备、焚烧发电锅炉、沼液收集罐。A wet garbage humidity control fermentation power generation system includes wet garbage humidity control equipment, anaerobic fermentation equipment, an incineration power generation boiler, and a biogas slurry collection tank.
湿垃圾调湿设备设有烟气通道和湿垃圾空间,烟气通道和湿垃圾空间使得烟气与湿垃圾间接接触,实现利用烟气的高温余热调节湿垃圾的湿度。The wet garbage humidity conditioning equipment is provided with a flue gas channel and a wet garbage space. The flue gas channel and the wet garbage space make the flue gas come into indirect contact with the wet garbage, so that the high temperature waste heat of the flue gas can be used to adjust the humidity of the wet garbage.
厌氧发酵设备设有烟气通道和发酵空间,烟气通道和发酵空间使得烟气与发酵原料间接接触,实现利用烟气的低温余热调节发酵温度。The anaerobic fermentation equipment is provided with a flue gas channel and a fermentation space. The flue gas channel and the fermentation space make the flue gas come into indirect contact with the fermentation raw materials, so that the low-temperature waste heat of the flue gas can be used to adjust the fermentation temperature.
湿垃圾调湿设备的湿垃圾空间连接湿垃圾源,湿垃圾调湿设备的垃圾出口连接厌氧发酵设备的垃圾进口,厌氧发酵设备的沼气出口连接焚烧发电锅炉的燃料进口,焚烧发电锅炉烟气出口连接湿垃圾调湿设备的烟气进口,湿垃圾调湿设备的烟气出口连接厌氧发酵设备的烟气进口。The wet waste space of the wet waste humidity conditioning equipment is connected to the wet waste source, the waste outlet of the wet waste humidity conditioning equipment is connected to the waste inlet of the anaerobic fermentation equipment, the biogas outlet of the anaerobic fermentation equipment is connected to the fuel inlet of the incineration power generation boiler, and the smoke of the incineration power generation boiler is connected. The gas outlet is connected to the flue gas inlet of the wet waste humidity conditioning device, and the flue gas outlet of the wet waste humidity conditioning device is connected to the flue gas inlet of the anaerobic fermentation device.
厌氧发酵设备的沼渣出口连接焚烧发电锅炉的燃料进口。The biogas residue outlet of the anaerobic fermentation equipment is connected to the fuel inlet of the incineration power generation boiler.
厌氧发酵设备的沼液出口连接沼液收集罐。The biogas slurry outlet of the anaerobic fermentation equipment is connected to the biogas slurry collection tank.
湿垃圾调湿发酵发电工艺,如图1所示,流程包括:The wet waste humidity control fermentation power generation process, as shown in Figure 1, the process includes:
1.垃圾流程:垃圾车运送来的湿垃圾先储存在湿垃圾库1中,然后运送到湿垃圾调湿设备2,调节温度至60℃进行湿度调节,再将湿度合适(24~40%)的垃圾输送至厌氧发酵设备4进行厌氧发酵。1. Garbage process: the wet garbage transported by the garbage truck is first stored in the
2.沼气流程:厌氧发酵4产生的沼气5被收集,然后进入焚烧锅炉6进行焚烧发电。2. Biogas process: The
3.沼渣流程:厌氧发酵4产生的沼渣11送入焚烧锅炉6进行焚烧发电。3. Biogas residue process: The
4.沼液流程:厌氧发酵4产生的沼液10被收集再利用。4. Biogas slurry process: The
5.烟气流程:锅炉焚烧发电6产生的高温烟气7(~200℃)进入湿垃圾调湿设备,降温后变为低温烟气8(~100℃),然后进入垃圾库促进垃圾进行厌氧发酵。5. Flue gas process: The high temperature flue gas 7 (~200℃) generated by the boiler
实施例2Example 2
一种湿垃圾调湿发酵发电系统,包括湿垃圾调湿设备、厌氧发酵设备、焚烧发电锅炉、沼液收集罐、化肥制备装置。A wet garbage humidity control fermentation power generation system includes wet garbage humidity control equipment, anaerobic fermentation equipment, an incineration power generation boiler, a biogas slurry collection tank, and a fertilizer preparation device.
湿垃圾调湿设备设有烟气通道和湿垃圾空间,烟气通道和湿垃圾空间使得烟气与湿垃圾间接接触,实现利用烟气的高温余热调节湿垃圾的湿度。The wet garbage humidity conditioning equipment is provided with a flue gas channel and a wet garbage space. The flue gas channel and the wet garbage space make the flue gas come into indirect contact with the wet garbage, so that the high temperature waste heat of the flue gas can be used to adjust the humidity of the wet garbage.
厌氧发酵设备设有烟气通道和发酵空间,烟气通道和发酵空间使得烟气与发酵原料间接接触,实现利用烟气的低温余热调节发酵温度。The anaerobic fermentation equipment is provided with a flue gas channel and a fermentation space. The flue gas channel and the fermentation space make the flue gas come into indirect contact with the fermentation raw materials, so that the low-temperature waste heat of the flue gas can be used to adjust the fermentation temperature.
湿垃圾调湿设备的湿垃圾空间连接湿垃圾源,湿垃圾调湿设备的垃圾出口连接厌氧发酵设备的垃圾进口,厌氧发酵设备的沼气出口连接焚烧发电锅炉的燃料进口,焚烧发电锅炉烟气出口连接湿垃圾调湿设备的烟气进口,湿垃圾调湿设备的烟气出口连接厌氧发酵设备的烟气进口。The wet waste space of the wet waste humidity conditioning equipment is connected to the wet waste source, the waste outlet of the wet waste humidity conditioning equipment is connected to the waste inlet of the anaerobic fermentation equipment, the biogas outlet of the anaerobic fermentation equipment is connected to the fuel inlet of the incineration power generation boiler, and the smoke of the incineration power generation boiler is connected. The gas outlet is connected to the flue gas inlet of the wet waste humidity conditioning device, and the flue gas outlet of the wet waste humidity conditioning device is connected to the flue gas inlet of the anaerobic fermentation device.
厌氧发酵设备的沼渣出口连接化肥制备装置。The biogas residue outlet of the anaerobic fermentation equipment is connected to the fertilizer preparation device.
厌氧发酵设备的沼液出口连接沼液收集罐。The biogas slurry outlet of the anaerobic fermentation equipment is connected to the biogas slurry collection tank.
实施例3Example 3
一种湿垃圾调湿发酵发电系统,包括湿垃圾调湿设备、厌氧发酵设备、焚烧发电锅炉、沼液收集罐、化肥制备装置。A wet garbage humidity control fermentation power generation system includes wet garbage humidity control equipment, anaerobic fermentation equipment, an incineration power generation boiler, a biogas slurry collection tank, and a fertilizer preparation device.
湿垃圾调湿设备设有烟气通道和湿垃圾空间,烟气通道和湿垃圾空间使得烟气与湿垃圾间接接触,实现利用烟气的高温余热调节湿垃圾的湿度。The wet garbage humidity conditioning equipment is provided with a flue gas channel and a wet garbage space. The flue gas channel and the wet garbage space make the flue gas come into indirect contact with the wet garbage, so that the high temperature waste heat of the flue gas can be used to adjust the humidity of the wet garbage.
厌氧发酵设备设有烟气通道和发酵空间,烟气通道和发酵空间使得烟气与发酵原料间接接触,实现利用烟气的低温余热调节发酵温度。The anaerobic fermentation equipment is provided with a flue gas channel and a fermentation space. The flue gas channel and the fermentation space make the flue gas come into indirect contact with the fermentation raw materials, so that the low-temperature waste heat of the flue gas can be used to adjust the fermentation temperature.
湿垃圾调湿设备的湿垃圾空间连接湿垃圾源,湿垃圾调湿设备的垃圾出口连接厌氧发酵设备的垃圾进口,厌氧发酵设备的沼气出口连接焚烧发电锅炉的燃料进口,焚烧发电锅炉烟气出口连接湿垃圾调湿设备的烟气进口,湿垃圾调湿设备的烟气出口连接厌氧发酵设备的烟气进口。The wet waste space of the wet waste humidity conditioning equipment is connected to the wet waste source, the waste outlet of the wet waste humidity conditioning equipment is connected to the waste inlet of the anaerobic fermentation equipment, the biogas outlet of the anaerobic fermentation equipment is connected to the fuel inlet of the incineration power generation boiler, and the smoke of the incineration power generation boiler is connected. The gas outlet is connected to the flue gas inlet of the wet waste humidity conditioning device, and the flue gas outlet of the wet waste humidity conditioning device is connected to the flue gas inlet of the anaerobic fermentation device.
厌氧发酵设备的沼渣出口连接焚烧发电锅炉的燃料进口。The biogas residue outlet of the anaerobic fermentation equipment is connected to the fuel inlet of the incineration power generation boiler.
厌氧发酵设备的沼液出口连接化肥制备装置。The biogas slurry outlet of the anaerobic fermentation equipment is connected to the fertilizer preparation device.
以上所述仅为本发明的优选实施例而已,并不用于限制本发明,对于本领域的技术人员来说,本发明可以有各种更改和变化。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. For those skilled in the art, the present invention may have various modifications and changes. Any modification, equivalent replacement, improvement, etc. made within the spirit and principle of the present invention shall be included within the protection scope of the present invention.
Claims (10)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202010754015.2A CN111872048A (en) | 2020-07-30 | 2020-07-30 | A kind of wet garbage humidity control fermentation power generation system and process |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202010754015.2A CN111872048A (en) | 2020-07-30 | 2020-07-30 | A kind of wet garbage humidity control fermentation power generation system and process |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN111872048A true CN111872048A (en) | 2020-11-03 |
Family
ID=73205791
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN202010754015.2A Pending CN111872048A (en) | 2020-07-30 | 2020-07-30 | A kind of wet garbage humidity control fermentation power generation system and process |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN111872048A (en) |
Citations (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1502421A (en) * | 2002-11-23 | 2004-06-09 | 伟 才 | Environment protective method for systemacally treating urban domestic refuse |
| JP2005270778A (en) * | 2004-03-24 | 2005-10-06 | Ebara Corp | Digestion gas usage and equipment |
| CN102500604A (en) * | 2011-11-28 | 2012-06-20 | 辽宁科技大学 | Household solid garbage recycling and renewable biological carbon circulating technology |
| CN203936118U (en) * | 2014-06-20 | 2014-11-12 | 黑龙江龙能伟业燃气股份有限公司 | A kind of resource reutilization system |
| CN104651218A (en) * | 2015-01-27 | 2015-05-27 | 深圳市海吉星环保有限责任公司 | Coupling utilization system and method of anaerobic fermentation of fruit and vegetable wastes and afterheat of bio-gas generator |
| CN206262969U (en) * | 2016-10-28 | 2017-06-20 | 深圳市海源能源科技有限公司 | A kind of kitchen garbage, sludge and green garbage cooperative disposal system |
| CN109010056A (en) * | 2018-07-25 | 2018-12-18 | 山东鑫蓝新能源科技有限公司 | It is a kind of can self energizing Chinese medicine production system |
| CN110822438A (en) * | 2019-11-07 | 2020-02-21 | 光大环保技术研究院(南京)有限公司 | Waste incineration power generation system and method |
| CN110976472A (en) * | 2019-11-14 | 2020-04-10 | 武汉龙净环保工程有限公司 | Kitchen waste and household waste co-processing method |
-
2020
- 2020-07-30 CN CN202010754015.2A patent/CN111872048A/en active Pending
Patent Citations (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1502421A (en) * | 2002-11-23 | 2004-06-09 | 伟 才 | Environment protective method for systemacally treating urban domestic refuse |
| JP2005270778A (en) * | 2004-03-24 | 2005-10-06 | Ebara Corp | Digestion gas usage and equipment |
| CN102500604A (en) * | 2011-11-28 | 2012-06-20 | 辽宁科技大学 | Household solid garbage recycling and renewable biological carbon circulating technology |
| CN203936118U (en) * | 2014-06-20 | 2014-11-12 | 黑龙江龙能伟业燃气股份有限公司 | A kind of resource reutilization system |
| CN104651218A (en) * | 2015-01-27 | 2015-05-27 | 深圳市海吉星环保有限责任公司 | Coupling utilization system and method of anaerobic fermentation of fruit and vegetable wastes and afterheat of bio-gas generator |
| CN206262969U (en) * | 2016-10-28 | 2017-06-20 | 深圳市海源能源科技有限公司 | A kind of kitchen garbage, sludge and green garbage cooperative disposal system |
| CN109010056A (en) * | 2018-07-25 | 2018-12-18 | 山东鑫蓝新能源科技有限公司 | It is a kind of can self energizing Chinese medicine production system |
| CN110822438A (en) * | 2019-11-07 | 2020-02-21 | 光大环保技术研究院(南京)有限公司 | Waste incineration power generation system and method |
| CN110976472A (en) * | 2019-11-14 | 2020-04-10 | 武汉龙净环保工程有限公司 | Kitchen waste and household waste co-processing method |
Non-Patent Citations (4)
| Title |
|---|
| 夏征农等: "《大辞海 能源科学卷》", 31 December 2013, 上海辞书出版社 * |
| 张蕾主编: "《固体废弃物处理与资源化利用》", 31 December 2017, 中国矿业大学出版社 * |
| 时君友等: "《可再生能源概述》", 30 June 2017, 电子科技大学出版社 * |
| 赵由才等: "《生活垃圾处理与资源化技术手册》", 31 May 2007, 冶金工业出版社 * |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN102746035B (en) | Residential kitchen garbage on-site reduction method | |
| CN102500604B (en) | Household solid garbage recycling and renewable biological carbon circulating technology | |
| CN103264038B (en) | The dead poultry treating apparatus of a kind of epidemic disease | |
| CN203487151U (en) | Internal thermal garage solid state anaerobic fermentation device | |
| CN108911802A (en) | Household composting device | |
| CN105948454A (en) | Treatment method for industrial sludge and heat pump-solar coupling system implementing method | |
| CN102716894A (en) | Method and system for drying aerobic organisms in urban raw garbage by aid of hot air | |
| CN214348577U (en) | Kitchen waste aerobic treatment equipment | |
| CN106007285A (en) | Municipal sludge treatment method and heat pump and solar energy coupling system for implementing method | |
| CN208907086U (en) | home composting device | |
| CN104893745B (en) | A kind of biomass carbonizing furnace smoke waste heat utilization system | |
| CN210907370U (en) | Organic refuse treatment waste heat recovery device | |
| CN110773549A (en) | Efficient energy-saving system of organic garbage biological treatment machine | |
| CN202244953U (en) | Solar automatic drying garbage can | |
| CN108585971A (en) | A kind of market town formula house refuse aerobic compost treatment process and its device | |
| CN210304995U (en) | A kind of kitchen and kitchen waste drying treatment device | |
| CN108380639A (en) | A kind of cooperative disposal method of rubbish from cooking and green garbage | |
| CN208562172U (en) | A kind of market town formula house refuse aerobic compost processing unit | |
| CN220034352U (en) | Device for composting household garbage and generating methane by utilizing medium-temperature flue gas | |
| CN202717682U (en) | Solar sludge drying system | |
| CN214949073U (en) | Energy comprehensive utilization system of kitchen waste treatment plant | |
| CN110375306A (en) | A kind of organic matter rubbish method of thermal cracking | |
| CN103088072B (en) | Method for automatic treatment of organic household garbage | |
| CN203159595U (en) | Zymocyte culture apparatus for household garbage pretreatment | |
| CN2659569Y (en) | Organic refuse processor |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PB01 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| RJ01 | Rejection of invention patent application after publication | ||
| RJ01 | Rejection of invention patent application after publication |
Application publication date: 20201103 |
