CN2697475Y - Screened pyrolyzing treatment furnace for domestic refuse - Google Patents

Screened pyrolyzing treatment furnace for domestic refuse Download PDF

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CN2697475Y
CN2697475Y CN 200420028437 CN200420028437U CN2697475Y CN 2697475 Y CN2697475 Y CN 2697475Y CN 200420028437 CN200420028437 CN 200420028437 CN 200420028437 U CN200420028437 U CN 200420028437U CN 2697475 Y CN2697475 Y CN 2697475Y
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pyrolysis
furnace body
inner furnace
stove
garbage
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张于峰
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Tianjin University
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Abstract

本实用新型具体涉及一种采用热解气化处理生活垃圾的装置。生活垃圾筛上物热解气化处理炉采用了内炉体外加保温层,并在内外炉体间设置螺旋烟气夹层的结构设计,并且对内炉体内送风供水加热器和外炉体底部燃烧系统同时进行加热,达到对垃圾筛上物快速升温的技术要求,内设的搅拌系统可使垃圾物料膨料层破碎,确保热解气化过程的连续性。本实用新型除热解炉自身消耗部分热量维持热解外,剩余热量以燃气的方式输出,作为清洁能源使用。每吨垃圾的燃气产量可达到300立方米,排出5~10%的垃圾灰。由于热解过程是在缺氧的800℃高温条件下运行,因此无二恶英的产生条件,可实现无害化处理,同时也达到资源化和减量化的处理要求。

Figure 200420028437

The utility model specifically relates to a device for treating domestic garbage by pyrolysis and gasification. The pyrolysis and gasification treatment furnace for household garbage sieve adopts the structure design of inner furnace body plus insulation layer, and a spiral flue gas interlayer is set between the inner and outer furnace bodies, and the air supply and water supply heater in the inner furnace body and the bottom of the outer furnace body The combustion system is heated at the same time to meet the technical requirements for rapid heating of the waste on the sieve. The built-in stirring system can break the expanded material layer of the waste material to ensure the continuity of the pyrolysis and gasification process. In the utility model, except that the pyrolysis furnace itself consumes part of the heat to maintain pyrolysis, the remaining heat is output in the form of gas and used as clean energy. The gas output per ton of garbage can reach 300 cubic meters, and 5-10% of garbage ash is discharged. Since the pyrolysis process operates under the high-temperature condition of 800°C in the absence of oxygen, there are no conditions for the generation of dioxins, which can realize harmless treatment, and also meet the treatment requirements of resource utilization and reduction.

Figure 200420028437

Description

生活垃圾筛上物热解处理炉Pyrolysis treatment furnace for domestic waste oversize

                              技术领域Technical field

本实用新型属于生活垃圾处理技术,具体涉及一种采用热解气化处理生活垃圾的装置。The utility model belongs to the domestic garbage treatment technology, in particular to a device for treating domestic garbage by adopting pyrolysis and gasification.

                              背景技术 Background technique

从环境保护和资源回收利用的角度考虑,城市生活垃圾理想的处理方式是采用综合治理技术。堆肥技术通过微生物作用消除垃圾,但是对垃圾的成分要求严格,非食物链的垃圾成分处理起来较为困难,可以采用机械筛进行垃圾的简单筛选,筛下物作为堆肥的原始物料,这种方式的堆肥技术已经成熟,但是筛上物的处理长期没有得到解决,导致大量筛上物的囤积,造成周围环境的严重污染,而且占用了大量土地。利用热解气化技术是较为理想的垃圾筛上物的处理方式,无需再对筛上物垃圾进行分类,处理过程中无污染物的排放,且可回收有用资源。筛上物在热解气化过程中需要快速的加热温度,同时亦需要防止物料的膨料层出现。因此如何快速提高炉膛温度是垃圾热解气化技术研究的重点和难点,它直接关系到对城市生活垃圾理想处理设备的推广和应用。From the perspective of environmental protection and resource recycling, the ideal way to deal with municipal solid waste is to adopt comprehensive treatment technology. Composting technology eliminates garbage through the action of microorganisms, but it has strict requirements on the composition of garbage, and it is difficult to deal with non-food chain garbage components. Mechanical sieves can be used for simple screening of garbage, and the sieve is used as the original material of compost. The technology has matured, but the treatment of oversize has not been solved for a long time, resulting in the accumulation of a large amount of oversize, causing serious pollution of the surrounding environment, and occupying a large amount of land. The use of pyrolysis and gasification technology is an ideal way to treat the oversize garbage. There is no need to classify the oversize garbage, no pollutants are discharged during the treatment process, and useful resources can be recovered. The oversize needs rapid heating temperature during the pyrolysis and gasification process, and at the same time, it is also necessary to prevent the appearance of the swelling layer of the material. Therefore, how to quickly increase the furnace temperature is the focus and difficulty in the research of waste pyrolysis gasification technology, which is directly related to the promotion and application of ideal treatment equipment for municipal solid waste.

                              发明内容Contents of Invention

本实用新型的目的是将生活垃圾的筛上物热解气化成为可燃气体而具体提供的一种处理装置。The purpose of the utility model is to specifically provide a treatment device for pyrolyzing and gasifying the oversize of domestic garbage into combustible gas.

参照附图,生活垃圾筛上物热解气化处理炉主要由热解气化主炉1、冷凝器4、引风机5和尾气处理器6等组成。热解气化主炉1是由内炉体2、外炉保温体3及螺旋烟气夹层7构成。内炉体2设计为圆形,内炉体内送风供水加热系统采用电加热,外炉保温体3底部采用燃气燃烧,同时对内炉体内物料进行加热。热解主炉的内炉体2经过集气器19与冷凝器4连接。引风机5的进口与冷凝器4出口连接,冷凝器4排出的是燃气,出口接于燃烧喷嘴10进行燃烧。除灰器12设置在外炉保温体3外底部并与内炉体2连通,由此可避免高温除灰对金属材质的特殊要求和方便的运行操作。尾气处理器6与螺旋烟气夹层7连接,出口与大气相通。垃圾物料从主炉的进料口13进入800℃高温的主炉内炉体2,在极度缺氧的状态下,通过垂直下移与自下而上高温气流的作用,逐步完成垃圾预热、水分蒸发和有机物质热解等过程,而后形成垃圾炭层。产生的热解气化湿燃气在引风机5的作用下,经过集气器19过滤后通过燃气管道进入冷凝器4冷凝,并排出冷凝水。燃气一部分经过阀门8送出,另一部分分别经阀门18送入内炉体2和在阀门9的控制下进入燃烧喷嘴10。燃气在外炉体内燃烧产生高温烟气,进入螺旋夹层烟道7加热内炉体2的周壁,而后排出主炉进入尾气处理装置6,经处理达标后排入大气。其中另有一部分烟气经控制阀门14进入送风供水加热装置11,再与内炉体2内的垃圾炭反应,生成气化燃气使其垃圾炭逐渐形成垃圾灰,在除灰器12的推动下排出主炉体。在热解气化主炉1炉体的中心有搅拌轴16,搅拌轴通过电机15驱动炉体内的搅拌叶17,对炉内物料进行搅拌,同时起到均匀内炉膛的温度作用。启动热解气化过程的初始热量来自于外部燃料在外炉保温体3内底部的燃烧层,内炉体2产生的燃气由回流管道经阀门18回到内炉膛中,其作用是加快提升内炉膛的温度。燃烧稳定过程中所产生的多余燃气在阀门8的控制下,提供其他用能设备使用。Referring to the accompanying drawings, the domestic garbage oversize pyrolysis gasification furnace is mainly composed of a pyrolysis gasification main furnace 1, a condenser 4, an induced draft fan 5, and a tail gas processor 6. The pyrolysis and gasification main furnace 1 is composed of an inner furnace body 2, an outer furnace insulation body 3 and a spiral flue gas interlayer 7. The inner furnace body 2 is designed to be circular, the air supply and water supply heating system in the inner furnace body adopts electric heating, and the bottom of the outer furnace insulation body 3 adopts gas combustion to heat the materials in the inner furnace body at the same time. The inner furnace body 2 of the pyrolysis main furnace is connected with the condenser 4 through the gas collector 19 . The inlet of the induced draft fan 5 is connected with the outlet of the condenser 4, and what the condenser 4 discharges is gas, and the outlet is connected to the combustion nozzle 10 for combustion. The ash remover 12 is arranged on the outer bottom of the outer furnace insulation body 3 and communicates with the inner furnace body 2, thereby avoiding the special requirements of high-temperature ash removal for metal materials and convenient operation. The exhaust processor 6 is connected with the spiral flue gas interlayer 7, and the outlet communicates with the atmosphere. Garbage materials enter the furnace body 2 of the 800°C high-temperature main furnace from the feed port 13 of the main furnace. In the state of extreme oxygen deficiency, the garbage preheating, Processes such as water evaporation and pyrolysis of organic matter, and then the formation of a garbage charcoal layer. Under the action of the induced draft fan 5, the generated pyrolysis gasification wet gas is filtered by the gas collector 19 and enters the condenser 4 through the gas pipeline to condense, and the condensed water is discharged. A part of the gas is sent out through the valve 8, and the other part is sent into the inner furnace body 2 through the valve 18 and enters the combustion nozzle 10 under the control of the valve 9. The gas burns in the outer furnace body to produce high-temperature flue gas, which enters the spiral interlayer flue 7 to heat the surrounding wall of the inner furnace body 2, and then exits the main furnace and enters the tail gas treatment device 6, and is discharged into the atmosphere after being treated up to the standard. Another part of the flue gas enters the air supply and water supply heating device 11 through the control valve 14, and then reacts with the garbage charcoal in the inner furnace body 2 to generate gasification gas so that the garbage charcoal gradually forms garbage ash. Discharge the main furnace body. There is a stirring shaft 16 in the center of the pyrolysis gasification main furnace 1 furnace body, and the stirring shaft drives the stirring blade 17 in the furnace body through the motor 15 to stir the materials in the furnace, and at the same time play a role in uniforming the temperature of the inner furnace. The initial heat for starting the pyrolysis gasification process comes from the combustion layer of the external fuel at the bottom of the outer furnace insulation body 3, and the gas generated by the inner furnace body 2 returns to the inner furnace through the return pipe through the valve 18, and its function is to accelerate the lifting of the inner furnace temperature. Under the control of the valve 8, the excess gas generated during the combustion stabilization process is provided to other energy-consuming equipment for use.

本实用新型采用了内炉体外加保温层,并在内外炉体间设置螺旋烟气夹层的结构设计,并且对内炉体内送风供水加热器和外炉体底部燃烧系统同时进行加热,达到对垃圾筛上物快速升温的技术要求,内设的搅拌系统可使垃圾物料膨料层破碎,确保热解气化过程的连续性。设置的燃气回流管可在设备启动过程中实现缺氧,加快物料的加热过程。The utility model adopts the structural design of adding an insulation layer outside the inner furnace body and setting a spiral flue gas interlayer between the inner and outer furnace bodies, and simultaneously heats the air supply and water supply heater in the inner furnace body and the combustion system at the bottom of the outer furnace body to achieve The technical requirements for the rapid heating of the waste oversize, the built-in stirring system can break the expanded material layer of the waste material to ensure the continuity of the pyrolysis and gasification process. The set gas return pipe can realize the lack of oxygen during the start-up process of the equipment, and accelerate the heating process of the material.

本实用新型的有益效果是生活垃圾筛上物经由热解气化装置处理后,除热解炉自身消耗部分热量维持热解外,剩余热量以燃气的方式输出,作为清洁能源使用。每吨垃圾的燃气产量可达到300立方米,燃值约为3000~5000大卡/立方米,排出5~10%的垃圾灰经简单筛选,除去金属、玻璃等可回收物质后,可作为花草养殖土。整个热解过程无需外来能源,如果垃圾含炭量满足,除燃气和垃圾灰外无其它对外排放物。由于热解过程是在缺氧的800℃高温条件下运行,因此无二恶英的产生条件,可实现无害化处理,同时也达到资源化和减量化的处理要求,产生的燃气还可获得一定的经济效益。The beneficial effect of the utility model is that after the domestic garbage sieve is processed by the pyrolysis gasification device, in addition to the pyrolysis furnace itself consuming part of the heat to maintain pyrolysis, the remaining heat is output in the form of gas and used as clean energy. The gas output per ton of garbage can reach 300 cubic meters, the fuel value is about 3000-5000 kcal/cubic meter, and 5-10% of the garbage ash discharged can be used as flowers and plants after simple screening to remove metal, glass and other recyclable materials Breeding soil. The entire pyrolysis process does not require external energy. If the carbon content of the garbage is sufficient, there will be no other external emissions except gas and garbage ash. Since the pyrolysis process operates under the high-temperature condition of 800°C in the absence of oxygen, there are no conditions for the generation of dioxins, which can realize harmless treatment, and also meet the treatment requirements of resource utilization and reduction, and the gas produced can also be recycled. obtain certain economic benefits.

                              附图说明Description of drawings

附图为本实用新型的结构原理图。Accompanying drawing is the structural principle diagram of the utility model.

                            具体实施方式 Detailed ways

城市生活垃圾进入垃圾堆放场地后,在设备的启动过程中,首先通过机械筛进行筛分,筛上物垃圾由进料推进器将其送入主炉进料口13炉体内,搅拌器将物料层搅拌均匀。装料量约计3/4炉内体积,重量约计200公斤。待物料装入内炉体后,在外炉体底部加入燃料燃烧,同时开启送风供水加热器11,加热内炉体2使其内部的物料升温,此时热解产生的非燃气体经过集气器19排出,燃烧产生的烟气经尾气处理器排入大气。为加快升温速度,可将脱水后的部分无氧非燃气通过阀门18重新送入内炉体,强化内部的气流的循环,其余部分由阀门8控制排出炉体。当炉内物料达到热解温度500℃后,开始产生湿燃气,经过冷凝器脱水,成为可燃气体,此时关闭阀门18。将可燃燃气的一部分由阀门9控制进入燃烧器10喷射燃烧,提供热解气化需要的热量,替代外炉体内的燃料热。烟气依然通过螺旋夹层7进入尾气处理器6。当炉内温度达到气化温度800℃后,热解后的垃圾炭形成,控制阀门14输送部分烟气和水进入炉内,使垃圾炭进行气化,进一步生成可燃气体,与热解形成的可燃气体一同进入冷凝器脱水,继续完成前述的气体流程。冷凝器为水冷式,冷凝温度为90℃,冷却的燃气量约计300m3。尾气处理装置为半湿式XD型锅炉烟气脱硫装置,采用石灰水循环喷淋过滤烟气,达到除尘脱硫的目的。物料的流程是自上而下的过程,垃圾开始正常生产燃气后,新进入的物料将在高温环境下快速升温进行热解,随后产生的垃圾炭与回流烟气进行气化反应,最后形成垃圾灰。由于圆形的炉体结构,物料在重力的作用下均匀下沉,为新物料的进入留下空间,而内炉内的搅拌器将定时转动,破坏可能形成的结层,促使物料下沉进入除灰器定时排出炉外。处理炉稳定运行后每间隔半小时上料100公斤,每小时热解气化垃圾200公斤,产生燃气约计300m3,热值约2000Kcal/kg,产生垃圾灰约计15kg,冷凝循环水量约计1吨/时,消耗电能约计4kW。After the municipal solid waste enters the waste dump site, it is screened through a mechanical sieve during the start-up process of the equipment, and the waste on the screen is sent into the furnace body of the main furnace feed port 13 by the feed propeller, and the agitator puts the material into the furnace body. Layers are stirred well. The amount of charge is about 3/4 of the furnace volume, and the weight is about 200 kg. After the material is loaded into the inner furnace body, fuel is added to the bottom of the outer furnace body for combustion, and at the same time, the air supply and water supply heater 11 is turned on to heat the inner furnace body 2 to heat up the material inside. At this time, the non-combustible gas generated by pyrolysis passes through the gas collection 19, and the flue gas generated by combustion is discharged into the atmosphere through the exhaust processor. In order to speed up the temperature rise, part of the dehydrated oxygen-free non-gas can be re-sent into the inner furnace body through the valve 18 to strengthen the circulation of the internal air flow, and the rest is controlled by the valve 8 to be discharged out of the furnace body. When the material in the furnace reaches the pyrolysis temperature of 500°C, wet gas starts to be produced, and after being dehydrated by the condenser, it becomes combustible gas. At this time, the valve 18 is closed. Part of the combustible gas is controlled by the valve 9 into the burner 10 for injection and combustion, providing the heat required for pyrolysis and gasification, and replacing the fuel heat in the outer furnace body. The flue gas still enters the exhaust processor 6 through the spiral interlayer 7 . When the temperature in the furnace reaches the gasification temperature of 800°C, pyrolyzed garbage charcoal is formed, and the control valve 14 sends part of the flue gas and water into the furnace to gasify the garbage charcoal and further generate combustible gas, which is combined with the pyrolyzed waste charcoal. The combustible gas enters the condenser together for dehydration, and continues to complete the aforementioned gas flow. The condenser is water-cooled, the condensing temperature is 90°C, and the cooling gas volume is about 300m 3 . The tail gas treatment device is a semi-wet XD boiler flue gas desulfurization device, which uses lime water circulation spraying to filter the flue gas to achieve the purpose of dust removal and desulfurization. The flow of materials is a top-down process. After the garbage starts to produce gas normally, the newly entered materials will rapidly heat up in a high temperature environment for pyrolysis, and then the generated garbage charcoal will undergo gasification reaction with the return flue gas, and finally form garbage Ash. Due to the circular furnace body structure, the material sinks evenly under the action of gravity, leaving space for the entry of new materials, and the stirrer in the inner furnace will rotate regularly to destroy the possible formation of knots and promote the material to sink into the The ash remover is discharged out of the furnace at regular intervals. After the treatment furnace runs stably, 100 kg of material is fed every half an hour, 200 kg of waste is pyrolyzed and gasified per hour, and the gas generated is about 300m 3 , the calorific value is about 2000Kcal/kg, the garbage ash is about 15kg, and the condensing and circulating water is about 1 ton/kg , the power consumption is about 4kW.

Claims (3)

1. house refuse oversize pyrolysis processing stove, mainly by pyrolytic gasification master stove (1), condenser (4), air-introduced machine (5) and exhaust gas treating device compositions such as (6), it is characterized in that pyrolytic gasification master stove (1) is by inner furnace body (2), outer stove thermal insulator (3) and spiral flue gas interlayer (7) constitute, inner furnace body (2) is designed to circle, air-supply water supply heating system adopts electrical heating in the inner furnace body, fuel gas buring is adopted in outer stove thermal insulator (3) bottom, simultaneously material in the inner furnace body is heated, the inner furnace body (2) of pyrolysis master stove is connected with condenser (4) through gas collector (19), the import of air-introduced machine (5) is connected with condenser (4) outlet, outlet is connected to burner noz(zle) (10), soot blower (12) is arranged on outer stove thermal insulator (3) outer bottom and is communicated with inner furnace body (2), exhaust gas treating device (6) is connected with flue gas interlayer (7), and outlet communicates with atmosphere.
2. house refuse oversize pyrolysis processing stove according to claim 1 is characterized in that at the center of pyrolytic gasification master stove (1) body of heater shaft (16) being arranged, and shaft drives the interior paddle (17) of body of heater by motor (15).
3. house refuse oversize pyrolysis processing stove according to claim 1 and 2 is characterized in that being provided with air-supply feed-water heater (11) in inner furnace body, and as the support of shaft in the body of heater (16).
CN 200420028437 2004-03-01 2004-03-01 Screened pyrolyzing treatment furnace for domestic refuse Expired - Fee Related CN2697475Y (en)

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CN101786095A (en) * 2010-04-06 2010-07-28 杨成志 Energy recovery type household waste disposer
CN104862016A (en) * 2015-03-31 2015-08-26 张家港天源生物能源科技有限公司 Gas recycling and cooling system of biomass carbonization furnace
CN105674294A (en) * 2016-03-21 2016-06-15 安徽未名生物环保有限公司 Waste combustion furnace capable of discharging solid-liquid-gas three-phase products in classified mode
CN105716083A (en) * 2016-03-21 2016-06-29 安徽未名生物环保有限公司 Air inlet control system of low-energy-consumption pyrolyzing furnace
CN105737166A (en) * 2016-03-21 2016-07-06 安徽未名生物环保有限公司 Circulation control system for pyrolysis gasifier
CN105728439A (en) * 2016-04-06 2016-07-06 北京神雾环境能源科技集团股份有限公司 System and method for treating organic waste
CN106765133A (en) * 2017-01-23 2017-05-31 广西威荣环保科技有限公司 Residents in rural community indirect heating method carbonization kiln
CN106813245A (en) * 2017-01-13 2017-06-09 安徽未名鼎和环保有限公司 A kind of auxiliary heating type refuse treatment plant
CN106871132A (en) * 2017-03-31 2017-06-20 溆浦农达科技有限公司 A kind of dry type refuse gasification boiler
CN108117889A (en) * 2018-02-12 2018-06-05 玉溪市圣力环保科技有限公司 A kind of pressurization reverse-flow type organic waste gasification furnace
CN110836375A (en) * 2019-10-24 2020-02-25 周序妹 A multi-triggered environmentally friendly waste incineration equipment
CN111561700A (en) * 2020-04-01 2020-08-21 华北电力大学 Rotary rake type organic solid waste pyrolysis device and pyrolysis method
CN119436146A (en) * 2024-11-19 2025-02-14 山东科技大学 One-piece domestic waste gasification energy supply device

Cited By (17)

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CN101786095A (en) * 2010-04-06 2010-07-28 杨成志 Energy recovery type household waste disposer
CN104862016B (en) * 2015-03-31 2017-07-11 张家港天源生物能源科技有限公司 Gas reuse cooling system in biomass carbonization stove
CN104862016A (en) * 2015-03-31 2015-08-26 张家港天源生物能源科技有限公司 Gas recycling and cooling system of biomass carbonization furnace
CN105674294A (en) * 2016-03-21 2016-06-15 安徽未名生物环保有限公司 Waste combustion furnace capable of discharging solid-liquid-gas three-phase products in classified mode
CN105716083A (en) * 2016-03-21 2016-06-29 安徽未名生物环保有限公司 Air inlet control system of low-energy-consumption pyrolyzing furnace
CN105737166A (en) * 2016-03-21 2016-07-06 安徽未名生物环保有限公司 Circulation control system for pyrolysis gasifier
CN105728439A (en) * 2016-04-06 2016-07-06 北京神雾环境能源科技集团股份有限公司 System and method for treating organic waste
CN105728439B (en) * 2016-04-06 2018-03-23 神雾科技集团股份有限公司 The system and method for handling organic waste
CN106813245B (en) * 2017-01-13 2019-05-07 安徽未名鼎和环保有限公司 A kind of auxiliary heating type refuse treatment plant
CN106813245A (en) * 2017-01-13 2017-06-09 安徽未名鼎和环保有限公司 A kind of auxiliary heating type refuse treatment plant
CN106765133A (en) * 2017-01-23 2017-05-31 广西威荣环保科技有限公司 Residents in rural community indirect heating method carbonization kiln
CN106871132A (en) * 2017-03-31 2017-06-20 溆浦农达科技有限公司 A kind of dry type refuse gasification boiler
CN108117889A (en) * 2018-02-12 2018-06-05 玉溪市圣力环保科技有限公司 A kind of pressurization reverse-flow type organic waste gasification furnace
CN110836375A (en) * 2019-10-24 2020-02-25 周序妹 A multi-triggered environmentally friendly waste incineration equipment
CN110836375B (en) * 2019-10-24 2021-08-17 宝泽工程科技有限公司 A multi-triggered environmentally friendly waste incineration equipment
CN111561700A (en) * 2020-04-01 2020-08-21 华北电力大学 Rotary rake type organic solid waste pyrolysis device and pyrolysis method
CN119436146A (en) * 2024-11-19 2025-02-14 山东科技大学 One-piece domestic waste gasification energy supply device

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