CN204026685U - One way of life high temperature garbage anaerobism pyrolysis system - Google Patents
One way of life high temperature garbage anaerobism pyrolysis system Download PDFInfo
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- CN204026685U CN204026685U CN201420515455.2U CN201420515455U CN204026685U CN 204026685 U CN204026685 U CN 204026685U CN 201420515455 U CN201420515455 U CN 201420515455U CN 204026685 U CN204026685 U CN 204026685U
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- refuse
- flue gas
- high temperature
- refuse pyrolysis
- pyrolysis
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Abstract
The utility model relates to one way of life high temperature garbage anaerobism pyrolysis system, include the body of cylindrical shape, described body is provided with charging aperture, at least one flue gas discharge opening, refuse pyrolysis room is provided with in described body, the below of described refuse pyrolysis room is provided with after-flame carburization zone, be provided with interlayer between described body and described refuse pyrolysis room, described interlayer communicates with described refuse pyrolysis room; Described refuse pyrolysis indoor are provided with flue gas secondary combustion section, and described flue gas discharge opening connects flue-gas purification equipment.The utility model by being provided with refuse pyrolysis room in body, and between body and described refuse pyrolysis room, be provided with interlayer, described interlayer communicates with refuse pyrolysis room; Refuse pyrolysis indoor are provided with flue gas secondary combustion section, connect flue-gas purification equipment at flue gas discharge opening, by refuse pyrolysis, flue gas secondary combustion through gas cleaning, avoid the generation of pernicious gas, ensure that smokeless, tasteless, qualified discharge.
Description
Technical field
The utility model relates to a kind of garbage waste material treating apparatus, particularly relates to one way of life high temperature garbage anaerobism pyrolysis system.
Background technology
As the inevitable outcome of industrialzation and urbanization process, it is tired that the growth rapidly of house refuse becomes environment already.How to stop city finally to be engulfed by rubbish, become unavoidable problem in environmental improvement.A large amount of rubbish is land occupation, influence ecological environment, contaminated air not only, and harmful substance wherein also can jeopardize the health of the mankind.Simultaneously in vast rural area, along with rural economy constantly increases, while farmer's income level improves constantly, the house refuse problem in rural area is but more and more serious.Not only have impact on the looks of new rural village, the more important thing is and direct threat is caused to the living environment of peasant and health.
People in the countryside are sparsely populated lacks fixing dumping place and special refuse collection, transport, treatment system.Major part villages and small towns dumping point is mixed and disorderly, and disorderly phenomenon is serious for rubbish.Dispersion pollution is only made to change concentrated contaminated water into.There is concentrated collection ground some areas, but treatment facility is simple and crude, causes secondary pollution serious.
At present, by the processing method of house refuse and device varied, processing method generally includes the multiple processing methods such as compacting, fragmentation, sorting, solidification, burning, biological treatment, and method step is complicated, and requirement is high.Wherein incinerating method is comparatively general, so the many employings of existing device are burned, burns pyrolysis discarded object, and burning pyrolysis is by organic matter high temperature (500-1000C) heating under anaerobic or anoxia condition, makes it to be decomposed into gas, liquid, solid three class product.Make solid waste pyrolytic and deep oxidation by burning pyrolysis like this, benefit is that a large amount of harmful scrap digestion is become harmless material.Because in house refuse, the ratio of combustible increases gradually, adopt incinerating method process house refuse, utilize the development trend that its heat energy has become inevitable.With this kind of processing method house refuse, take up an area few, treating capacity is large, in protection of the environment, provides in the energy etc. and can obtain good effect.European countries comparatively early adopt incinerating method process solid waste, and incineration plant is located at the big city of more than 100,000 populations more, and is provided with energy-recuperation system.The heat energy that burning process obtains may be used for generating.Utilize the heat that incinerator occurs, can be used for resident to warm oneself, for maintaining greenhouse room temperature etc., but burn and also have shortcoming, such as, invest larger, burning process smoke evacuation causes secondary pollution, and equipment corrosion phenomena is serious, and solid waste can not be made in burning to decompose completely.
The incinerator of main use is both at home and abroad as Martin furnace, Circulation fluidized-bed furnace and high-temperature gasification pyrolysis oven now, its ubiquitous problem is that specific investment cost is high, per unit makes an investment in 60-75 more than ten thousand yuan, other incinerator technical matters complexity is not easy to operate above, fume treatment is wasted a large amount of funds and the energy, and discharge standard always instability be the problem existing for all incinerators, and have potential safety hazard, operating cost is high, and a large amount of coal, gas, oil or electric power supply need be had to run well.
Utility model content
The purpose of this utility model is to avoid the deficiencies in the prior art to provide one way of life high temperature garbage anaerobism pyrolysis system, it carries out high temperature pyrolysis process by high temperature anaerobic pyrolysis to discarded object, and pass through smoke eliminator, can not produce the composition of atmosphere pollution after ensure that process, emission gases reaches safe standard.
For achieving the above object, the technical scheme taked of the utility model is as follows:
One way of life high temperature garbage anaerobism pyrolysis system, include the body of cylindrical shape, described body is provided with charging aperture, at least one flue gas discharge opening, refuse pyrolysis room is provided with in described body, the below of described refuse pyrolysis room is provided with after-flame carburization zone, be provided with interlayer between described body and described refuse pyrolysis room, described interlayer communicates with described refuse pyrolysis room; Described refuse pyrolysis indoor are provided with flue gas secondary combustion section, and described flue gas discharge opening connects flue-gas purification equipment.
Described flue gas discharge opening is located at the top of described body, and described flue gas discharge opening is communicated with described interlayer.
Described flue-gas purification equipment includes the atomizing spray cooler, low efficient filter, static electric field process device, media adsorbs layer and the photocatalysis apparatus that connect successively.
Described charging aperture is connected with shaftless screw conveying batcher, and described shaftless screw conveying batcher is provided with hopper.
Grid is provided with between described refuse pyrolysis room and described after-flame carburization zone.
The below of described after-flame carburization zone is provided with fire grate device.
Described body is provided with access hole and observation panel.
The utility model life refuse high temperature anaerobism pyrolysis system, by being provided with refuse pyrolysis room in body, is provided with after-flame carburization zone in the below of refuse pyrolysis room, and between body and described refuse pyrolysis room, be provided with interlayer, described interlayer communicates with refuse pyrolysis room; Refuse pyrolysis indoor are provided with flue gas secondary combustion section, connect flue-gas purification equipment at flue gas discharge opening, by refuse pyrolysis, flue gas secondary combustion through gas cleaning, avoid the generation of pernicious gas, ensure that smokeless, tasteless, qualified discharge.
Accompanying drawing explanation
Figure 1 shows that the structural representation of the one way of life high temperature garbage anaerobism pyrolysis system that the utility model embodiment provides;
Figure 2 shows that the schematic diagram of flue-gas purification equipment.
Detailed description of the invention
Below, in conjunction with example, substantive distinguishing features of the present utility model and advantage are further described, but the utility model is not limited to listed embodiment.
Shown in Figure 1, the figure shows the structure of the one way of life high temperature garbage anaerobism pyrolysis system that the utility model embodiment provides.For convenience of explanation, illustrate only the part relevant with the utility model embodiment.
Refer to Fig. 1-2, one way of life high temperature garbage anaerobism pyrolysis system, include the body 1 of cylindrical shape, described body is provided with charging aperture, at least one flue gas discharge opening 6, refuse pyrolysis room 2 is provided with in described body, the below of described refuse pyrolysis room 2 is provided with after-flame carburization zone 10, is provided with interlayer 3 between described body and described refuse pyrolysis room, and described interlayer 3 communicates with described refuse pyrolysis room 2; Be provided with flue gas secondary combustion section 4 in described refuse pyrolysis room 2, described flue gas discharge opening 6 connects flue-gas purification equipment 30.
Wherein, described flue gas discharge opening 6 is located at the top of described body 1, and described flue gas discharge opening 6 is communicated with described interlayer 3.
Described interlayer 3 having air inlet port or hole, being used for air for inwardly carrying decomposition combustion.
Described flue gas secondary combustion section 4 comprises multiple skewed combustion tube arranged in a crossed manner, and this combustion tube has smoke entrance.
Shown in Figure 2, described flue-gas purification equipment 30 includes the low efficient filter 31, static electric field process device 32, media adsorbs layer 33 and the photocatalysis apparatus 34 that connect successively, the front end of described flue-gas purification equipment 30 is provided with atomizing spray heat sink 20, carries out level Four purified treatment for high-temperature flue gas is undertaken being sent to described flue-gas purification equipment 30 after cooling processes by atomizing spray water smoke.
Described low efficient filter is used for filtration and is greater than 10 μm of materials such as particle and hair fiber, it is charged that described static electric field process device is used for making to be less than 0.01 μm of colloidal sol by electrostatic field, and the electricity that reaches capacity, the cation of high concentration, high strength has the effect infiltrating bacterium and microorganism, described media adsorbs layer can complex media adsorption layer under prior art, for removing pernicious gas and catching charged particle, described photocatalysis apparatus comprises ultraviolet light disinfector, discharges after carrying out virus killing process for pernicious gases such as Dui bioxin.By above-mentioned level Four gas purification disinfection process, carry out the process of gas, ensure that smokeless, tasteless, qualified discharge.
It should be noted that, described low efficient filter 31, static electric field process device 32, media adsorbs layer 33 and photocatalysis apparatus 34 can adopt shaped device in prior art to assemble.
Traditional waste incineration can produce a large amount of flue gas, causes dispute and the opposition of plant area's nearby residents, and through the flue gas that above-mentioned level Four purifies, plasma anaerobism garbage disposer ensure that discharge is the transparent gas of gas colorless and odorless, namely reaches smokeless emission.
Further, described charging aperture is connected with shaftless screw conveying batcher 11, and described shaftless screw conveying batcher is provided with hopper 12.
Further, grid 9 is provided with between described refuse pyrolysis room 2 and described after-flame carburization zone 10.
Further, the below of described after-flame carburization zone 10 is provided with fire grate device 8.
Further, described body 1 is provided with access hole 5 and observation panel 7.
The utility model plasma anaerobism garbage disposer can process following organic matter: comprise the rubber-like refuses such as damaged tire, clinical waste (syringe, infusion bag, transfusion bags, plastic glove, diaper etc.), the various building waste wood such as wallpaper, petroleum product (plastics, vinyl, foamed glue, plastic lunch box etc.), waste household appliances/refuse battery (metallic member remains in superfine ashes), animal wastes etc., the dead bones of the body of animal, culled wood, litter decoration, various friperie, the lignocellulosic wastes such as old quilt, vinasse, soybean residue, the residual meal leftovers etc. in kitchen, nearly all organic waste.
For not accessible inorganic matter, when processing also without the need to prior go-no-go, the above-mentioned inorganic matter be mingled in organic waste can process simultaneously, does again and process respectively after plasma machine process.
The utility model can suppress the generation of bioxin to greatest extent, by controlling the supply of oxygen, prevent 2 phenyl ring as Er Evil class foundation to be combined by oxygen, by the dividing processing of plasma in stove, another prevents the generation of phenyl ring itself.
The utility model can process all organic wastes, by poisonous and harmful substance by isoionic segmentation, makes handled thing volume reduce to minimum, controls the generation of harmful and noxious substance to greatest extent.
Solid-state fluorescence material can reasonably be processed in the very first time, the first place by the utility model, the energy makes full use of, be that the domestic waste of energy-saving and emission-reducing is innoxious, minimizing, recycling treatment new technology, be the new technology of recycling economy and sustainable development.
The utility model life refuse high temperature anaerobism pyrolysis system, by being provided with refuse pyrolysis room in body, is provided with after-flame carburization zone in the below of refuse pyrolysis room, and between body and described refuse pyrolysis room, be provided with interlayer, described interlayer communicates with refuse pyrolysis room; Refuse pyrolysis indoor are provided with flue gas secondary combustion section, connect flue-gas purification equipment at flue gas discharge opening, by refuse pyrolysis, flue gas secondary combustion through gas cleaning, avoid the generation of pernicious gas, ensure that smokeless, tasteless, qualified discharge.
The above is only preferred embodiment of the present utility model; it should be pointed out that for those skilled in the art, under the prerequisite not departing from the utility model principle; can also make some improvements and modifications, these improvements and modifications also should be considered as protection domain of the present utility model.
Claims (7)
1. one way of life high temperature garbage anaerobism pyrolysis system, it is characterized in that, include the body of cylindrical shape, described body is provided with charging aperture, at least one flue gas discharge opening, refuse pyrolysis room is provided with in described body, the below of described refuse pyrolysis room is provided with after-flame carburization zone, is provided with interlayer between described body and described refuse pyrolysis room, and described interlayer communicates with described refuse pyrolysis room; Described refuse pyrolysis indoor are provided with flue gas secondary combustion section, and described flue gas discharge opening connects flue-gas purification equipment.
2. life refuse high temperature anaerobism pyrolysis system as claimed in claim 1, it is characterized in that, described flue gas discharge opening is located at the top of described body, and described flue gas discharge opening is communicated with described interlayer.
3. life refuse high temperature anaerobism pyrolysis system as claimed in claim 2, it is characterized in that, described flue-gas purification equipment includes the atomizing spray cooler, low efficient filter, static electric field process device, media adsorbs layer and the photocatalysis apparatus that connect successively.
4. life refuse high temperature anaerobism pyrolysis system as claimed in claim 3, is characterized in that, described charging aperture is connected with shaftless screw conveying batcher, and described shaftless screw conveying batcher is provided with hopper.
5. the life refuse high temperature anaerobism pyrolysis system as described in any one of claim 1-4, is characterized in that, is provided with grid between described refuse pyrolysis room and described after-flame carburization zone.
6. life refuse high temperature anaerobism pyrolysis system as claimed in claim 5, it is characterized in that, the below of described after-flame carburization zone is provided with fire grate device.
7. the life refuse high temperature anaerobism pyrolysis system as described in claim 1 or 6, it is characterized in that, described body is provided with access hole and observation panel.
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CN201420515455.2U CN204026685U (en) | 2014-09-10 | 2014-09-10 | One way of life high temperature garbage anaerobism pyrolysis system |
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CN201420515455.2U CN204026685U (en) | 2014-09-10 | 2014-09-10 | One way of life high temperature garbage anaerobism pyrolysis system |
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Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104696967A (en) * | 2015-03-05 | 2015-06-10 | 中国人民解放军总后勤部建筑工程研究所 | Downward smoke discharging type household garbage pyrolysis furnace and pyrolysis method |
CN105805758A (en) * | 2014-12-30 | 2016-07-27 | 湖南金卫环保设备科技有限公司 | Garbage progressive grading pyrolysis device capable of preventing generation of dioxin |
CN107023837A (en) * | 2017-03-01 | 2017-08-08 | 沃邦环保有限公司 | Processing method for application of city life garbage |
-
2014
- 2014-09-10 CN CN201420515455.2U patent/CN204026685U/en not_active Expired - Fee Related
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105805758A (en) * | 2014-12-30 | 2016-07-27 | 湖南金卫环保设备科技有限公司 | Garbage progressive grading pyrolysis device capable of preventing generation of dioxin |
CN104696967A (en) * | 2015-03-05 | 2015-06-10 | 中国人民解放军总后勤部建筑工程研究所 | Downward smoke discharging type household garbage pyrolysis furnace and pyrolysis method |
CN107023837A (en) * | 2017-03-01 | 2017-08-08 | 沃邦环保有限公司 | Processing method for application of city life garbage |
CN107023837B (en) * | 2017-03-01 | 2019-04-26 | 沃邦环保有限公司 | Processing method for application of city life garbage |
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CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20141217 Termination date: 20150910 |
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EXPY | Termination of patent right or utility model |