WO2007009399A1 - A dry distillation garbage incinerator - Google Patents

A dry distillation garbage incinerator Download PDF

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Publication number
WO2007009399A1
WO2007009399A1 PCT/CN2006/001813 CN2006001813W WO2007009399A1 WO 2007009399 A1 WO2007009399 A1 WO 2007009399A1 CN 2006001813 W CN2006001813 W CN 2006001813W WO 2007009399 A1 WO2007009399 A1 WO 2007009399A1
Authority
WO
WIPO (PCT)
Prior art keywords
tunnel
incineration
garbage
dry distillation
drying zone
Prior art date
Application number
PCT/CN2006/001813
Other languages
French (fr)
Chinese (zh)
Inventor
Shizheng Yu
Original Assignee
Shizheng Yu
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Shizheng Yu filed Critical Shizheng Yu
Publication of WO2007009399A1 publication Critical patent/WO2007009399A1/en

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Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23JREMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES 
    • F23J1/00Removing ash, clinker, or slag from combustion chambers
    • F23J1/06Mechanically-operated devices, e.g. clinker pushers
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/02Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
    • F23G5/027Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage
    • F23G5/0276Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage using direct heating
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/44Details; Accessories
    • F23G5/442Waste feed arrangements
    • F23G5/444Waste feed arrangements for solid waste
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/44Details; Accessories
    • F23G5/46Recuperation of heat
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2201/00Pretreatment
    • F23G2201/10Drying by heat
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2203/00Furnace arrangements
    • F23G2203/80Furnaces with other means for moving the waste through the combustion zone
    • F23G2203/801Furnaces with other means for moving the waste through the combustion zone using conveyors
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2206/00Waste heat recuperation
    • F23G2206/10Waste heat recuperation reintroducing the heat in the same process, e.g. for predrying

Definitions

  • the present invention relates to a waste incinerator, and more particularly to a high temperature dry waste incinerator which utilizes high temperature to dry the waste in an anoxic state.
  • waste incinerators In the past, waste incinerators generally used garbage to be directly burned on the grate. This type of combustion is technically mature, but the garbage is not fully burned. It is often necessary to add a combustion improver to help the garbage burn, and the investment is large and the operating cost is high. High, and later there was a pyrolysis and gasification incineration method.
  • the waste gas was pyrolyzed and gasified by a combustion chamber of a rotary kiln, a fluidized bed or a gas-controlled incinerator, and then the combustible gas was burned in the second combustion chamber. Pyrolysis and gasification incineration can produce high calorific value combustible gas.
  • the combustion temperature in the second combustion chamber is high, and the garbage can be fully burned out.
  • the waste incineration must be divided into a combustion chamber and a second combustion chamber, and must be controlled in a combustion chamber.
  • the supply of air can cause the waste to be pyrolyzed and vaporized, the air supply is insufficient, the garbage cannot be burned normally, and the combustion temperature is low.
  • the secondary pollution caused by low-temperature combustion, especially the production of strong carcinogen dioxin, is a problem that cannot be ignored.
  • the garbage supplied to the rotary kiln and the fluidized bed needs to be selected and crushed, small in scale, large in investment, and low in operating cost. High, complex equipment, and many faults. At present, pyrolysis and gasification incineration methods are not yet mature in technology, and they are still in a perfect stage. Summary of the invention
  • the object of the present invention is to overcome the deficiencies of the prior incinerators and to provide a high-temperature dry distillation waste incinerator having a simple structure, low secondary pollution, low investment cost, low operating cost, low maintenance cost, and large processing capacity.
  • the high-temperature dry distillation waste incinerator of the present invention comprises two front and rear incineration tunnels of the same structure and opposite ends, and two driving tracks respectively disposed at the bottom of the front and rear incineration tunnels, a plurality of garbage incinerators having multi-layer grate on the road track, a driving device for driving the garbage incinerator, and an exhaust gas emission III and an exhaust gas washing device, wherein the incineration tunnel sequentially forms a drying zone and a dry distillation from the inlet to the outlet.
  • a garbage feeding port is arranged at the top of the tunnel behind the tunnel entrance;
  • the drying zone is provided with an exhaust gas exhaust pipe in the drying zone, and a waste heat inlet is arranged on the tunnel side wall of the drying zone to ignite
  • a waste heat outlet is provided on the side wall of the tunnel at the reclamation area;
  • the waste heat outlet of the former incineration tunnel is connected with the waste heat inlet of the post-incineration tunnel;
  • the waste heat inlet of the former incineration tunnel is connected with the waste heat outlet of the post-incineration tunnel;
  • the exhaust gas exhaust pipe of the post-burning tunnel drying zone is passed to the dry distillation combustion zone, and the exhaust gas of the post-incineration tunnel drying zone is passed through the exhaust gas exhaust pipe of the pre-incineration tunnel to the dry distillation combustion zone.
  • the top wall of the tunnel in the upper part of the drying zone is provided with a plurality of suction pipes, and a plurality of suction pipe air channels are collected in the gas collecting pipes, wherein the gas collecting pipes of one incineration tunnel are connected with the exhaust gas exhaust pipes of the drying zone of another incineration tunnel.
  • An auxiliary induced draft fan is provided on the pipeline.
  • the top wall of the tunnel in the upper portion of the dry distillation combustion zone is provided with a plurality of exhaust pipes, the plurality of exhaust pipes are collected in the collecting pipe, the collecting pipe is connected with the exhaust connecting pipe, the exhaust connecting pipe is provided with an exhaust fan, and the exhaust connecting pipe is smoke. Gas is introduced into the exhaust gas scrubbing device.
  • the front incineration tunnel and the post-incineration tunnel are placed side by side, and the waste heat inlet and the waste heat outlet are located on the same side wall of the front incineration tunnel or the post-incineration tunnel.
  • the drying is divided into a pre-drying zone and a post-drying zone.
  • the top wall of the tunnel in the pre-drying zone is straight, 0.2-0.8 m from the top of the garbage incineration vehicle, and the top wall of the tunnel in the post-drying zone is arched.
  • the top of the tunnel is increased by 0.2-0.8 m relative to the top wall of the tunnel in the front of the drying zone.
  • the exhaust duct is disposed in the post-drying zone, and the dome of the tunnel of the dry distillation combustion zone is increased by 0.2-0.8 m relative to the dome of the tunnel in the post-drying zone.
  • the top wall of the tunnel in the burning zone is the same height as the top wall of the tunnel in the pre-drying zone.
  • the grate in the garbage incineration vehicle is divided into three layers: upper, middle and lower.
  • Each grate is composed of several grate bars, wherein the grate spacing of the upper grate is greater than the grate spacing of the middle grate, and the middle grate is The spacing of the grate bars is greater than the spacing of the grate bars of the lower grate, and venting holes are provided on both sides of the garbage incineration vehicle.
  • the exhaust gas washing device includes an exhaust gas washing pool, a water pump and a circulation pipeline thereof.
  • the exhaust gas washing tank is provided with lime water added with alum and a freshener, and a plurality of water spray pipes are arranged above the exhaust gas washing tank, and each spray water pipe has enough water spray ports, and one end of the circulation pipe of the water pump and the water spray pipe Connected, the other end is connected to the lime water in the exhaust scrubber.
  • the respective ends of the two road tracks are connected by a lateral movement mechanism or a circular arc track.
  • It also includes an ash discharge device that is driven by a hydraulic cylinder at the exit of the tunnel.
  • the driving device of the incinerator is a hydraulic cylinder.
  • the lateral movement mechanism includes two traverse rails perpendicularly intersecting the traveling rail, a traverse bracket located above the traverse rail, and a bracket driving mechanism.
  • the bracket driving mechanism comprises a driving motor mounted on the traverse bracket, a driving sprocket mounted on the output shaft of the driving motor, a chain parallel to the traverse rail and engaging with the driving sprocket, and a chain mounted on the traverse bracket. Two guiding sprockets.
  • the advantages and positive effects of the high-temperature dry distillation waste incinerator of the present invention are as follows:
  • the use of high-temperature dry distillation technology that is, the use of garbage in the upper portion of the garbage incineration vehicle, causing the dry distillation conditions of the garbage anoxic, and utilizing the internal use of the garbage incineration vehicle
  • the improvement of the furnace bar and the furnace causes the combustion of the internal combustion of the garbage incineration vehicle and the combustion of the combustible gas generated by the dry distillation in the furnace to fully supply oxygen, and skillfully solve the contradiction between the oxygen supply of the waste distillation and the garbage combustion, and can burn out the grate furnace.
  • Unburnable plastic bags and other non-burning garbage no need to sort the garbage into the furnace; and because of the unique design of the incinerator, it has the function of "automatic ignition", no need to set the ignition device, the whole incinerator mainly includes the former
  • the latter two incineration tunnels with the same structure do not need to reciprocate, no need for wastewater treatment, so the structure is simple; high-temperature dry distillation technology makes the garbage fully burn, completely utilizes the heat of waste combustion, without adding any combustion improver, so its running cost is low; Due to the residual heat inlet of the drying zone of the former incineration tunnel and the burning zone of the post-burning tunnel The outlet is connected, and the waste heat inlet of the drying zone of the post-incineration tunnel is connected with the waste heat outlet of the burning zone of the former incineration tunnel.
  • the residual heat of the post-burning tunnel burning zone can be extracted by the auxiliary induced draft fan to dry and heat the front incineration tunnel.
  • the waste of the furnace, the waste heat from the burning zone in the front burning tunnel After drying, heating, incinerating the garbage that has just entered the tunnel, making full use of the waste heat in the burning zone, even if the water content of the garbage is large, it can be stably burned, and the adaptability is strong; in particular, in the present invention, the drying zone is discharged.
  • the moisture in the waste gas and garbage is sent to another dry burning zone of the incineration tunnel for secondary combustion, so that the high temperature of the combustible gas in the dry distillation combustion zone burns off the strong carcinogens such as dioxins produced by the low-temperature combustion of the garbage, and eliminates The secondary pollution solves the current world problem of excessive dioxin emission caused by waste drying and gasification.
  • the equipment is simple, and the incinerator is convenient to replace, so the equipment is easy to manufacture, the maintenance is simple, and the maintenance cost is low.
  • FIG. 1A is a schematic structural view of a high-temperature dry distillation waste incinerator of the present invention
  • Figure 1B is a cross-sectional view taken along line A-A of Figure 1A;
  • FIG. 2A is a schematic structural view of a garbage incinerator according to the present invention.
  • Figure 2B is a side elevational view of Figure 2A;
  • FIG. 3 is a schematic structural view of an exhaust gas washing device in the present invention.
  • Figure 4A is a schematic view showing the structure of a lateral moving mechanism at both ends of a high-temperature dry distillation waste incinerator
  • Figure 4B is an enlarged cross-sectional view of the P-P of Figure 4A;
  • Figure 5 is a schematic view showing the structure of an ash discharging apparatus in the present invention.
  • Exhaust gas induced draft fan 33.
  • Sprinkler pipe 34.
  • Exhaust gas exhaust chimney 35. Washing pool, 40.
  • Waste heat inlet 41, traverse bracket, 42, traverse track, 43, chain, 46, ash drain, 47, guide sprocket, 48, drive motor, 49, drive sprocket, 50, ash discharge Pressure cylinder, 51, limiter, 52, hydraulic cylinder block shaft.
  • the high-temperature dry distillation waste incinerator of the present invention comprises two front and rear incineration tunnels of identical construction except that their inlets and outlets are opposite, and a refractory layer 6 is provided at the top of the incineration tunnel.
  • Each incineration tunnel is divided into three zones. • Drying zone 3. Dry distillation burning zone 7 and burning zone 11.
  • the drying zone 3 is further divided into a pre-drying zone and a post-drying zone.
  • the entrance is a pre-drying zone, the top of the furnace is straight, the garbage incineration vehicle is filled with garbage and the smoke is blocked, and the top of the furnace is away from the garbage incineration vehicle. 0.5 m at the top, equipped with dry distillation garbage.
  • the distance is feasible within the range of 0.2-0.8 m.
  • the top wall of the tunnel in the post-drying area is arched.
  • the shape of the dome is increased by 0.5 m relative to the top wall of the tunnel in the pre-drying zone, and the distance is in the range of 0.2-0.8 m.
  • the zone is provided with an exhaust pipe 4, a dry distillation zone 7 and an upper arch of the tunnel.
  • the top is increased by 0.2-0.8 m relative to the tunnel arch in the post-drying zone to form a combustion furnace for the full combustion of the combustible gas.
  • the height of the top of the burning zone 11 is the same as that of the pre-drying zone.
  • the garbage incineration vehicle 18 enters from the inlet 1 and is slowly pushed into the incineration tunnel by the hydraulic cylinder 20.
  • the garbage inlet 2 is provided above the tunnel, and the garbage is filled with the garbage incineration vehicle 18 from the top inlet.
  • the drying zone 3 of the former incineration tunnel is just adjacent to the burning zone 11 of the post-incineration tunnel, and the drying zone 3 of the post-incineration tunnel is just adjacent to the burning zone 11 of the former incineration tunnel, and the auxiliary induced draft fan is used to burn the tunnel burning zone 11
  • the hot air is heated through the waste heat outlet 14 of the burning zone and the waste heat inlet 40 of the drying zone of the former incineration tunnel to heat the garbage that has just entered the incineration tunnel, so that even if the garbage having a large moisture content is dried, it can be stably incinerated.
  • the garbage incineration vehicle 18 near the dry distillation combustion zone 7 starts to burn, further drying and heating the waste in the upper part of the garbage incineration vehicle 18, and the waste gas and garbage discharged from the front incineration tunnel auxiliary draft fan.
  • the water vapor in the exhaust gas is sent to the dry distillation combustion zone 7 of the post-incineration tunnel through the exhaust gas exhaust pipe 10 for secondary combustion, and the post-incineration tunnel assists the exhaust gas discharged from the induced draft fan and the water vapor in the garbage to be sent to the front incineration through the exhaust gas exhaust pipe 10.
  • the retorting combustion zone 7 of the tunnel is subjected to secondary combustion to completely burn off strong carcinogens such as dioxins, and to solve the current drying and gasification at low temperatures.
  • the air extracted by the exhaust fan causes the garbage in the incinerator to burn rapidly, and the high temperature generated by the flammable gas generated by the retorting in the furnace, causing the garbage in the upper part of the garbage incinerator 18 and the garbage inside the incinerator to be sharp.
  • the garbage incinerator 18 of the present invention is made of heat-resistant steel and is made of heat-resistant steel.
  • the garbage incinerator is placed close to the side wall of the incineration tunnel, and the top of the garbage incineration is densely packed with 0.5 m thick garbage, causing anoxic state for dry distillation.
  • the upper grate is welded with four grate 22, the middle grate is welded with 9 intermediate grate 23, and the lower grate is welded with 18 lower grate 24, which are three-layer grate
  • the garbage is racked up, so that the volume of the dry distillation waste in the upper part of the incineration vehicle is reduced and the volume is reduced, and the upper layer of the grate is burned and burned; the upper grate is burned and dried, and the volume is reduced, and the inner grate is continuously burned; the middle layer garbage After combustion and retorting, the volume is reduced and falls to the lower grate to continue burning.
  • the garbage is dropped to expose the internal garbage, and it can continue to burn and dry distillation.
  • the base 27 of the incinerator is welded by channel steel, and the upper bottom plate 25 is provided thereon, and four wheels 26 are mounted on the lower side to slide on the traveling rails 21.
  • a groove of channel steel is welded on top of the base 27, the bottom layer of the furnace bar 24 is supported, four columns 28 are welded on the channel steels on both sides, and the intermediate grate 23 is supported by two channels of steel, and 8 pieces are used thereon.
  • the column supports the top layer of the furnace strip 22, and the inner wall 29 of the steel plate is welded on the upper and lower sides of the channel steel.
  • the two sides of the incinerator are corresponding to the interval between each two bars, which are venting holes 30, and the air can enter from the venting holes 30 on both sides.
  • the internal garbage of the incineration vehicle is fully burned, and the purpose of completely burning the garbage is achieved.
  • the entire incineration tunnel can be loaded with many incinerators.
  • each incineration tunnel is 60 meters long and can accommodate 30 incinerators at the same time. After the incinerator is ignited, it can work continuously for a long time without adding a combustion-supporting agent. The incinerator should be replaced with a burning vehicle without stopping the operation of the incinerator.
  • the exhaust gas induced draft fan 32 draws the exhaust gas of the combustion waste from the collecting flue gas pipe 9 of the dry distillation combustion zone 7 through the connecting pipe 31, and sends it to the exhaust gas washing tank 35. Since the cross-sectional area of the exhaust gas scrubbing tank 35 is much larger than the cross-sectional area of the exhaust gas intake pipe, the velocity of the exhaust gas entering the exhaust gas scrubbing tank is greatly reduced, and the suspended soot is dropped into the exhaust gas scrubbing tank.
  • the washing tank is filled with lime water with alum and freshener, and a plurality of water spray pipes 23 are arranged above, and the water spray pipe 23 has enough water spray ports, and the water pump extracts the washing liquid from the washing pool through the spray pipe from top to bottom.
  • the multi-layer water curtain is formed, and the exhaust gas is washed by a plurality of water curtains to remove the smoke and odor from the exhaust gas and neutralize harmful substances such as HC1, NOx, SOx and COx in the exhaust gas, and the exhaust gas meets or exceeds the exhaust emission standard, and passes through the chimney row. Go into the sky.
  • the two rails 21 in the front and rear incineration tunnels can be connected by circular arc tracks at the ends of the two incineration tunnels to form a closed rail, and can also be connected by a lateral moving mechanism.
  • the lateral movement mechanism in the present invention includes two traverse rails 42 perpendicularly intersecting the traveling rail 21, a traverse bracket 41 located above the traverse rail 42, and a bracket driving mechanism.
  • the carriage drive mechanism includes a forward and reverse drive motor 48 mounted on the traverse bracket 41, a drive sprocket 49 mounted on the output shaft of the drive motor 48, a chain 43 parallel to the traverse rail 42 and cooperating with the drive sprocket 49, And two guide sprockets 47 mounted on the traverse bracket 41.
  • the hydraulic cylinder 20 pushes the garbage incinerator 18 that has been sent to the incineration tunnel, and starts to enter another incineration tunnel to load the garbage. After the garbage is filled, the traverse bracket 41 returns to the original incinerator outlet under the reversal action of the driving motor 48. position. The entire course of action can be automatically controlled by the computer.
  • the dust discharging device of the present invention is a rotatable hydraulic cylinder 50 and an incinerator stopper 51.
  • Ash discharge process When the discharged garbage incinerator 18 is pushed up by the traverse bracket 41, the ash discharge is first started. The ash discharge operation is driven by a hydraulic cylinder 50 mounted below the incinerator. The cylinder of the hydraulic cylinder can be rotated about the shaft 52. The piston rod of the hydraulic cylinder is supported by the shaft of the rear wheel of the garbage incinerator, and the front wheel is stopped by the stopper 51 of the bracket, and the whole garbage incinerator is tilted to 50. - At 70 °, the non-combustible ash in the incineration vehicle is discharged to the ash discharge tank 46, then the hydraulic cylinder is dropped, and the garbage incineration vehicle is returned to the horizontal position for traverse. The ash poured into the ash discharge tank 46 is sieved and sent to the ash storage.

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  • Engineering & Computer Science (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The present invention provides a tunnel type garbage incinerator. It includes a first and a second incineration tunnel the structures of which are the same, end to end tracks, some bogies for incinerating garbage, a driver, a chimney for exhausting the gas and a smoke washing device. The incineration tunnel is divided into a drying section, a dry distilling and combusting section and a burning out section from inlet to outlet. There is a garbage inlet on the top of the tunnel behind the inlet of the tunnel. The drying section is furnished with an gas exhausting tube. There is a waste heat inlet on the sidewall of the tunnel in the drying section and a waste heat outlet on the sidewall of the tunnel in the burning out section. The waste heat outlet of the first tunnel is connecting with the waste heat inlet of the second tunnel. The garbage is dry distilling under an anoxic condition at high temperature and a lot of combustible gas is obtained and is supplied for the dry distillation of the garbage of another tunnel. The garbage is incinerated effectively without combustion promoter and the structure of the incinerator is simple.

Description

高温干馏垃圾焚烧炉  High temperature dry distillation waste incinerator
技术领域 Technical field
本发明涉及一种垃圾焚烧炉,特别是一种利用高温把处于缺氧状 态下的垃圾干馏的高温干镏垃圾焚烧炉。 背景技术  The present invention relates to a waste incinerator, and more particularly to a high temperature dry waste incinerator which utilizes high temperature to dry the waste in an anoxic state. Background technique
以往的垃圾焚烧炉普遍使用把垃圾放在炉排上直接燃烧,这种燃 烧方式在技术上已经成熟, 但垃圾燃烧不够充分, 往往还需要添加助 燃剂来帮助垃圾燃烧, 而且投资大, 运行成本高, 后来出现了热解、 气化焚烧方式, 先用回转窑、流化床或控气式焚烧炉的一燃室使垃圾 热解、 气化, 然后在二燃室燃烧可燃气体。 热解、 气化焚烧方式能产 生高热值的可燃气体, 在二燃室燃烧温度高, 能把垃圾充分燃尽, 但 垃圾焚烧必须分成一燃室和二燃室,在一燃室还必须控制空气的供给 量才能使垃圾热解、 气化, 空气供给不充分, 垃圾不能正常燃烧, 燃 烧温度低。低温燃烧引起的二次污染, 特别是强致癌物二恶英等的产 生是一个不容忽视的问题,其次,供给回转窑和流化床的垃圾需要挑 选、 破碎, 规模小, 投资大, 运行成本高, 设备复杂, 故障也多。 目 前,热解、气化焚烧方式在技术上还没有真正成熟, 尚处于完善阶段。 发明内容  In the past, waste incinerators generally used garbage to be directly burned on the grate. This type of combustion is technically mature, but the garbage is not fully burned. It is often necessary to add a combustion improver to help the garbage burn, and the investment is large and the operating cost is high. High, and later there was a pyrolysis and gasification incineration method. The waste gas was pyrolyzed and gasified by a combustion chamber of a rotary kiln, a fluidized bed or a gas-controlled incinerator, and then the combustible gas was burned in the second combustion chamber. Pyrolysis and gasification incineration can produce high calorific value combustible gas. The combustion temperature in the second combustion chamber is high, and the garbage can be fully burned out. However, the waste incineration must be divided into a combustion chamber and a second combustion chamber, and must be controlled in a combustion chamber. The supply of air can cause the waste to be pyrolyzed and vaporized, the air supply is insufficient, the garbage cannot be burned normally, and the combustion temperature is low. The secondary pollution caused by low-temperature combustion, especially the production of strong carcinogen dioxin, is a problem that cannot be ignored. Secondly, the garbage supplied to the rotary kiln and the fluidized bed needs to be selected and crushed, small in scale, large in investment, and low in operating cost. High, complex equipment, and many faults. At present, pyrolysis and gasification incineration methods are not yet mature in technology, and they are still in a perfect stage. Summary of the invention
(一)要解决的技术问题  (1) Technical problems to be solved
本发明的目的在于克服以往焚烧炉的不足, 提供一种结构简单、 二次污染小、 投资成本低、 运行成本低、 维护成本低、 处理能力大的 高温干馏垃圾焚烧炉。  The object of the present invention is to overcome the deficiencies of the prior incinerators and to provide a high-temperature dry distillation waste incinerator having a simple structure, low secondary pollution, low investment cost, low operating cost, low maintenance cost, and large processing capacity.
(二)技术方案  (2) Technical plan
为实现上述目的, 本发明釆用如下技术方案:  In order to achieve the above object, the present invention uses the following technical solutions:
本发明的高温干馏垃圾焚烧炉,其中包括结构相同而首尾相反的 前、 后焚烧隧道、 分别设置在前、 后焚烧隧道底部的两条行车轨道、 位于行车轨道上的若干辆具有多层炉排的垃圾焚烧车、用于驱动垃圾 焚烧车的驱动装置以及废气排放烟 III和废气洗涤装置,其中焚烧隧道 从入口至出口依次形成烘干区、 干馏燃烧区和燃烬区, 在隧道入口后 面隧道顶部设有垃圾进料口; 所述烘干区设有烘干区废气排气管, 在 烘干区的隧道侧壁上设有余热入口,燃烬区处的隧道侧壁上设有余热 出口; 前焚烧隧道的余热出口与后焚烧隧道余热入口连通, 前焚烧隧 道的余热入口与后焚烧隧道余热出口连通;前焚烧隧道烘干区的废气 经后焚烧隧道烘干区废气排气管通入到的干馏燃烧区,后焚烧隧道烘 干区的废气经前焚烧隧道的烘干区废气排气管通入到干馏燃烧区。 The high-temperature dry distillation waste incinerator of the present invention comprises two front and rear incineration tunnels of the same structure and opposite ends, and two driving tracks respectively disposed at the bottom of the front and rear incineration tunnels, a plurality of garbage incinerators having multi-layer grate on the road track, a driving device for driving the garbage incinerator, and an exhaust gas emission III and an exhaust gas washing device, wherein the incineration tunnel sequentially forms a drying zone and a dry distillation from the inlet to the outlet. In the burning zone and the burning zone, a garbage feeding port is arranged at the top of the tunnel behind the tunnel entrance; the drying zone is provided with an exhaust gas exhaust pipe in the drying zone, and a waste heat inlet is arranged on the tunnel side wall of the drying zone to ignite A waste heat outlet is provided on the side wall of the tunnel at the reclamation area; the waste heat outlet of the former incineration tunnel is connected with the waste heat inlet of the post-incineration tunnel; the waste heat inlet of the former incineration tunnel is connected with the waste heat outlet of the post-incineration tunnel; The exhaust gas exhaust pipe of the post-burning tunnel drying zone is passed to the dry distillation combustion zone, and the exhaust gas of the post-incineration tunnel drying zone is passed through the exhaust gas exhaust pipe of the pre-incineration tunnel to the dry distillation combustion zone.
其中烘干区上部的隧道顶壁设有若干抽气管道,若干抽管气道汇 集于集气管道,其中一焚烧隧道的集气管道与另一焚烧隧道的烘干区 废气排气管连通, 管路上设有辅助引风机。  The top wall of the tunnel in the upper part of the drying zone is provided with a plurality of suction pipes, and a plurality of suction pipe air channels are collected in the gas collecting pipes, wherein the gas collecting pipes of one incineration tunnel are connected with the exhaust gas exhaust pipes of the drying zone of another incineration tunnel. An auxiliary induced draft fan is provided on the pipeline.
其中干馏燃烧区上部的隧道顶壁设有若干排烟管道,若干排烟 管道汇集于集烟管道, 集烟管道连通有废气连接管, 废气连接管上安 装有废气引风机, 废气连接管将烟气通入所述废气洗涤装置。  The top wall of the tunnel in the upper portion of the dry distillation combustion zone is provided with a plurality of exhaust pipes, the plurality of exhaust pipes are collected in the collecting pipe, the collecting pipe is connected with the exhaust connecting pipe, the exhaust connecting pipe is provided with an exhaust fan, and the exhaust connecting pipe is smoke. Gas is introduced into the exhaust gas scrubbing device.
其中所述前焚烧隧道和后焚烧隧道并排放置,所述余热入口和余 热出口位于前焚烧隧道或后焚烧隧道的同一侧壁上。  The front incineration tunnel and the post-incineration tunnel are placed side by side, and the waste heat inlet and the waste heat outlet are located on the same side wall of the front incineration tunnel or the post-incineration tunnel.
其中烘干区分为烘干前区和烘干后区, 烘干前区的隧道顶壁平 直, 距离垃圾焚烧车顶部 0.2-0.8米, 烘干后区的隧道顶壁呈拱形, 其拱顶相对烘干前区的隧道顶壁提高 0.2-0.8米, 所述抽风风道设置 在该烘干后区,干馏燃烧区隧道的拱顶相对烘干后区隧道的拱顶提高 0.2-0.8米; 燃烬区隧道的顶壁与烘干前区的隧道顶壁高度相同。  The drying is divided into a pre-drying zone and a post-drying zone. The top wall of the tunnel in the pre-drying zone is straight, 0.2-0.8 m from the top of the garbage incineration vehicle, and the top wall of the tunnel in the post-drying zone is arched. The top of the tunnel is increased by 0.2-0.8 m relative to the top wall of the tunnel in the front of the drying zone. The exhaust duct is disposed in the post-drying zone, and the dome of the tunnel of the dry distillation combustion zone is increased by 0.2-0.8 m relative to the dome of the tunnel in the post-drying zone. The top wall of the tunnel in the burning zone is the same height as the top wall of the tunnel in the pre-drying zone.
其中垃圾焚烧车内的炉排分为上、 中、 下三层, 每层炉排由若干 根炉条组成, 其中上层炉排的炉条间距大于中层炉排的炉条间距, 中 层炉排的炉条间距大于下层炉排的炉条间距,垃圾焚烧车两侧设有透 气孔。  The grate in the garbage incineration vehicle is divided into three layers: upper, middle and lower. Each grate is composed of several grate bars, wherein the grate spacing of the upper grate is greater than the grate spacing of the middle grate, and the middle grate is The spacing of the grate bars is greater than the spacing of the grate bars of the lower grate, and venting holes are provided on both sides of the garbage incineration vehicle.
其中所述废气洗涤装置包括废气洗涤池、 抽水机及其循环管路, 其中废气洗涤池内装有加入明矾和清香剂的石灰水,废气洗涤池上方 设有若干喷水管, 每根喷水管上具有足够多的喷水口, 抽水机的循环 管路一端与喷水管连通, 另一端接入到废气洗涤池的石灰水内。 The exhaust gas washing device includes an exhaust gas washing pool, a water pump and a circulation pipeline thereof. The exhaust gas washing tank is provided with lime water added with alum and a freshener, and a plurality of water spray pipes are arranged above the exhaust gas washing tank, and each spray water pipe has enough water spray ports, and one end of the circulation pipe of the water pump and the water spray pipe Connected, the other end is connected to the lime water in the exhaust scrubber.
其中两条行车轨道的相应端部由横向移动机构或圆弧轨道连接 在一起。  The respective ends of the two road tracks are connected by a lateral movement mechanism or a circular arc track.
其中还包括设置在隧道出口处由液压缸驱动的卸灰装置。  It also includes an ash discharge device that is driven by a hydraulic cylinder at the exit of the tunnel.
其中所述焚烧车的驱动装置是液压缸。  The driving device of the incinerator is a hydraulic cylinder.
其中所述横向移动机构包括与行车轨道垂直相交的两条横移轨 道、 位于横移轨道上面的横移支架及支架驱动机构。  The lateral movement mechanism includes two traverse rails perpendicularly intersecting the traveling rail, a traverse bracket located above the traverse rail, and a bracket driving mechanism.
其中所述支架驱动机构包括安装在横移支架上的驱动电机、安装 在驱动电机输出轴上的主动链轮、平行于横移轨道并与主动链轮配合 的链条, 以及安装在横移支架的两个导向链轮。  Wherein the bracket driving mechanism comprises a driving motor mounted on the traverse bracket, a driving sprocket mounted on the output shaft of the driving motor, a chain parallel to the traverse rail and engaging with the driving sprocket, and a chain mounted on the traverse bracket. Two guiding sprockets.
(三)有益效果  (3) Beneficial effects
本发明的高温干馏垃圾焚烧炉的优点和积极效果是: 本发明中, 由于利用高温干馏技术, 即利用垃圾焚烧车上部垃圾密集装载, 造成 垃圾缺氧的干馏条件,又利用垃圾焚烧车内部用炉条架起和炉膛的提 高,造成垃圾焚烧车内部垃圾燃烧和干馏产生的可燃气体在炉膛燃烧 充分供氧的条件, 巧妙地解决垃圾干馏和垃圾燃烧的供氧矛盾, 可以 燃尽炉排炉难以燃尽的塑料袋等不好烧的垃圾, 入炉垃圾无需分选; 又由于焚烧车的独特设计, 起到 "自动拨火" 的功能, 无需设置拨火 装置, 整个焚烧炉主要包括前、 后两条结构相同的焚烧隧道, 无需往 复动作, 无需废水处理, 所以结构简单; 高温干馏技术使垃圾充分燃 烧, 完全利用垃圾燃烧的热量, 无需添加任何助燃剂, 所以其运行成 本低;又由于前焚烧隧道的烘干区余热入口与后焚烧隧道的燃烬区余 热出口连通,后焚烧隧道的烘干区余热入口与前焚烧隧道的燃烬区余 热出口连通,所以可以通过辅助引风机把后焚烧隧道燃烬区的余热抽 来烘干、加热前焚烧隧道刚进炉的垃圾, 把前焚烧隧道燃烬区的余热 抽来烘干、 加热后焚烧隧道刚进炉的垃圾, 充分利用燃烬区的余热, 即使垃圾的含水量大也能够稳定燃烧, 适应性强; 特别是本发明中, 其中烘干区排出的废气和垃圾中的水分被送入另一条焚烧隧道干镏 燃烧区进行二次燃烧,让干馏燃烧区可燃气体燃烧的高温烧掉了垃圾 低温燃烧所产生的二恶英等强致癌物质, 消灭了二次污染, 解决了目 前垃圾烘干和气化产生二恶英排放超标的世界难题; 另外, 在本发明 中设备简单, 焚烧车更换方便, 所以设备制造容易, 维护简单, 维护 费用低。 附图说明 The advantages and positive effects of the high-temperature dry distillation waste incinerator of the present invention are as follows: In the present invention, the use of high-temperature dry distillation technology, that is, the use of garbage in the upper portion of the garbage incineration vehicle, causing the dry distillation conditions of the garbage anoxic, and utilizing the internal use of the garbage incineration vehicle The improvement of the furnace bar and the furnace causes the combustion of the internal combustion of the garbage incineration vehicle and the combustion of the combustible gas generated by the dry distillation in the furnace to fully supply oxygen, and skillfully solve the contradiction between the oxygen supply of the waste distillation and the garbage combustion, and can burn out the grate furnace. Unburnable plastic bags and other non-burning garbage, no need to sort the garbage into the furnace; and because of the unique design of the incinerator, it has the function of "automatic ignition", no need to set the ignition device, the whole incinerator mainly includes the former The latter two incineration tunnels with the same structure do not need to reciprocate, no need for wastewater treatment, so the structure is simple; high-temperature dry distillation technology makes the garbage fully burn, completely utilizes the heat of waste combustion, without adding any combustion improver, so its running cost is low; Due to the residual heat inlet of the drying zone of the former incineration tunnel and the burning zone of the post-burning tunnel The outlet is connected, and the waste heat inlet of the drying zone of the post-incineration tunnel is connected with the waste heat outlet of the burning zone of the former incineration tunnel. Therefore, the residual heat of the post-burning tunnel burning zone can be extracted by the auxiliary induced draft fan to dry and heat the front incineration tunnel. The waste of the furnace, the waste heat from the burning zone in the front burning tunnel After drying, heating, incinerating the garbage that has just entered the tunnel, making full use of the waste heat in the burning zone, even if the water content of the garbage is large, it can be stably burned, and the adaptability is strong; in particular, in the present invention, the drying zone is discharged. The moisture in the waste gas and garbage is sent to another dry burning zone of the incineration tunnel for secondary combustion, so that the high temperature of the combustible gas in the dry distillation combustion zone burns off the strong carcinogens such as dioxins produced by the low-temperature combustion of the garbage, and eliminates The secondary pollution solves the current world problem of excessive dioxin emission caused by waste drying and gasification. In addition, in the present invention, the equipment is simple, and the incinerator is convenient to replace, so the equipment is easy to manufacture, the maintenance is simple, and the maintenance cost is low. DRAWINGS
图 1A是本发明的高温干馏垃圾焚烧炉的结构示意图;  1A is a schematic structural view of a high-temperature dry distillation waste incinerator of the present invention;
图 1B是图 1A的 A-A剖视图;  Figure 1B is a cross-sectional view taken along line A-A of Figure 1A;
图 2A是本发明中的垃圾焚烧车的结构示意图;  2A is a schematic structural view of a garbage incinerator according to the present invention;
图 2B是图 2A的侧面视图;  Figure 2B is a side elevational view of Figure 2A;
图 3是本发明中的废气洗涤装置的结构示意图;  Figure 3 is a schematic structural view of an exhaust gas washing device in the present invention;
图 4A是高温干馏垃圾焚烧炉两端的横向移动机构的结构示意 图;  Figure 4A is a schematic view showing the structure of a lateral moving mechanism at both ends of a high-temperature dry distillation waste incinerator;
图 4B是图 4A的 P-P剖视放大图;  Figure 4B is an enlarged cross-sectional view of the P-P of Figure 4A;
图 5是本发明中的卸灰装置的结构示意图。  Figure 5 is a schematic view showing the structure of an ash discharging apparatus in the present invention.
图中: 1.焚烧隧道入口, 2.垃圾进料口, 3.烘干区, 4.抽气道, 5. 烘干区集气管, 6.耐火层, 7.干馏燃烧区, 8.抽烟道, 9.干馏燃烧区集 烟管, 10.烘干区废气排气管, 11.燃烬区, 12.焚烧隧道出口, 13.燃烬 焚烧车, 14.燃烬区余热出口, 18.垃圾焚烧车, 20.液压缸驱动装置, 21.行车轨导, 22.顶层炉条, 23.中间炉条, 24.底层炉条, 25.盛灰底 板, 26.车轮, 27.槽钢底座, 28.立柱, 29.耐热钢内壁, 30.透气孔, 31.连接管, 32.废气引风机, 33.喷水管, 34.废气排放烟囱, 35.洗涤 池, 40.余热入口, 41、 横移支架, 42、 横移轨道, 43、 链条, 46、 卸灰池, 47、 导向链轮, 48、 驱动电机, 49、 主动链轮, 50、 卸灰液 压缸, 51、 限位器, 52、 液压缸缸体转轴。 具体实施方式 In the picture: 1. Incineration tunnel entrance, 2. Garbage feed inlet, 3. Drying zone, 4. Air extraction duct, 5. Drying zone gas collecting pipe, 6. Refractory layer, 7. Dry distillation burning zone, 8. Smoking Road, 9. Dry distillation zone collecting pipe, 10. Drying zone exhaust pipe, 11. Burning zone, 12. Incineration tunnel exit, 13. Burning and burning car, 14. Burning zone waste heat outlet, 18. Garbage incineration vehicle, 20. Hydraulic cylinder drive, 21. Driving rail guide, 22. Top furnace strip, 23. Intermediate grate, 24. Bottom grate, 25. Ash floor, 26. Wheel, 27. Channel base , 28. Column, 29. Heat-resistant steel inner wall, 30. Vented hole, 31. Connecting pipe, 32. Exhaust gas induced draft fan, 33. Sprinkler pipe, 34. Exhaust gas exhaust chimney, 35. Washing pool, 40. Waste heat inlet, 41, traverse bracket, 42, traverse track, 43, chain, 46, ash drain, 47, guide sprocket, 48, drive motor, 49, drive sprocket, 50, ash discharge Pressure cylinder, 51, limiter, 52, hydraulic cylinder block shaft. detailed description
参见图 1A和图 1B。本发明的高温干馏垃圾焚烧炉包括前、后两 条结构完全相同的焚烧隧道, 只是它们的入口和出口相反而已, 焚烧 隧道顶部设耐火层 6。 每条焚烧隧道分为三个区 ·. 烘干区 3、 干馏燃 烧区 7和燃烬区 11。 烘干区 3又分为烘干前区和烘干后区, 入口处 为烘干前区, 炉顶平直, 垃圾焚烧车装满垃圾并封堵烟尘外冒, 炉顶 距离垃圾焚烧车 18顶部 0.5米, 装干馏垃圾, 根据不同的要求, 该 距离在 0.2-0.8米范围内均是可行的, 隔两辆垃圾焚烧车后为烘干后 区, 烘干后区的隧道顶壁呈拱形, 其拱顶相对于烘干前区的隧道顶壁 提高 0.5米,该距离在 0.2-0.8米范围内均是可行的,该区设有抽气管 道 4, 干馏燃烧区 7 隧道上部的拱顶相对烘干后区隧道拱顶提高 0.2-0.8米形成燃烧炉膛, 供可燃气体充分燃烧, 燃烬区 11炉顶高度 和烘干前区相同。  See Figure 1A and Figure 1B. The high-temperature dry distillation waste incinerator of the present invention comprises two front and rear incineration tunnels of identical construction except that their inlets and outlets are opposite, and a refractory layer 6 is provided at the top of the incineration tunnel. Each incineration tunnel is divided into three zones. • Drying zone 3. Dry distillation burning zone 7 and burning zone 11. The drying zone 3 is further divided into a pre-drying zone and a post-drying zone. The entrance is a pre-drying zone, the top of the furnace is straight, the garbage incineration vehicle is filled with garbage and the smoke is blocked, and the top of the furnace is away from the garbage incineration vehicle. 0.5 m at the top, equipped with dry distillation garbage. According to different requirements, the distance is feasible within the range of 0.2-0.8 m. After the two garbage incineration vehicles are the drying area, the top wall of the tunnel in the post-drying area is arched. The shape of the dome is increased by 0.5 m relative to the top wall of the tunnel in the pre-drying zone, and the distance is in the range of 0.2-0.8 m. The zone is provided with an exhaust pipe 4, a dry distillation zone 7 and an upper arch of the tunnel. The top is increased by 0.2-0.8 m relative to the tunnel arch in the post-drying zone to form a combustion furnace for the full combustion of the combustible gas. The height of the top of the burning zone 11 is the same as that of the pre-drying zone.
垃圾焚烧车 18从入口 1进入, 用液压缸 20慢慢推入焚烧隧道, 隧道上方设有垃圾进料口 2, 垃圾从顶部的进料口装满垃圾焚烧车 18。 前焚烧隧道的烘干区 3正好紧邻后焚烧隧道的燃烬区 11, 后焚 烧隧道的烘干区 3正好紧邻前焚烧隧道的燃烬区 11, 辅助引风机把 后焚烧隧道燃烬区 11的热空气通过燃烬区余热出口 14和前焚烧隧道 的烘干区余热入口 40, 抽来加热刚进焚烧隧道的垃圾, 这样即使水 分含量大的垃圾经烘干以后也可以稳定焚烧。 同时, 在辅助引风机的 抽吸下, 靠近干馏燃烧区 7的垃圾焚烧车 18开始着火燃烧, 进一步 烘干、 加热垃圾焚烧车 18上部干馏的垃圾, 前焚烧隧道辅助引风机 排出的废气和垃圾中的水汽经废气排气管 10被送入后焚烧隧道的干 馏燃烧区 7进行二次燃烧,后焚烧隧道辅助引风机排出的废气和垃圾 中的水汽经废气排气管 10被送入前焚烧隧道的干馏燃烧区 7进行二 次燃烧, 彻底烧掉二恶英等强致癌物质, 解决目前烘干、 气化低温下 产生二恶英排放超标的世界难题。在干馏燃烧区 7废气引风机抽进来 的空气使焚烧车里垃圾急剧燃烧,和炉膛里干馏产生的可燃气体猛烈 燃烧产生的高温, 使这里的垃圾焚烧车 18上部的垃圾和焚烧车内部 垃圾急剧干镏, 迅速分解, 产生大量的可燃气体从垃圾内部逸出, 源 源不断地供给可燃气体在炉膛猛烈燃烧, 直至垃圾完全燃尽。在燃烬 区 11, 垃圾焚烧车 18上的垃圾已经干馏或燃烧, 留下碳化物的残烬 继续烧烧, 使这里的空气保持相当高的温度, 通过燃烬区余热出口 14、 烘干区余热入口 40被后焚烧隧道的辅助引风机抽过去烘干并加 热后焚烧隧道内刚进炉的垃圾,焚烧车上残留的不可燃物质温度逐渐 降低, 最后由出口 12被推出炉外进行卸灰。 The garbage incineration vehicle 18 enters from the inlet 1 and is slowly pushed into the incineration tunnel by the hydraulic cylinder 20. The garbage inlet 2 is provided above the tunnel, and the garbage is filled with the garbage incineration vehicle 18 from the top inlet. The drying zone 3 of the former incineration tunnel is just adjacent to the burning zone 11 of the post-incineration tunnel, and the drying zone 3 of the post-incineration tunnel is just adjacent to the burning zone 11 of the former incineration tunnel, and the auxiliary induced draft fan is used to burn the tunnel burning zone 11 The hot air is heated through the waste heat outlet 14 of the burning zone and the waste heat inlet 40 of the drying zone of the former incineration tunnel to heat the garbage that has just entered the incineration tunnel, so that even if the garbage having a large moisture content is dried, it can be stably incinerated. At the same time, under the suction of the auxiliary induced draft fan, the garbage incineration vehicle 18 near the dry distillation combustion zone 7 starts to burn, further drying and heating the waste in the upper part of the garbage incineration vehicle 18, and the waste gas and garbage discharged from the front incineration tunnel auxiliary draft fan. The water vapor in the exhaust gas is sent to the dry distillation combustion zone 7 of the post-incineration tunnel through the exhaust gas exhaust pipe 10 for secondary combustion, and the post-incineration tunnel assists the exhaust gas discharged from the induced draft fan and the water vapor in the garbage to be sent to the front incineration through the exhaust gas exhaust pipe 10. The retorting combustion zone 7 of the tunnel is subjected to secondary combustion to completely burn off strong carcinogens such as dioxins, and to solve the current drying and gasification at low temperatures. A world problem that produces excessive levels of dioxin emissions. In the dry distillation combustion zone, the air extracted by the exhaust fan causes the garbage in the incinerator to burn rapidly, and the high temperature generated by the flammable gas generated by the retorting in the furnace, causing the garbage in the upper part of the garbage incinerator 18 and the garbage inside the incinerator to be sharp. Drying, rapid decomposition, a large amount of flammable gas is released from the inside of the garbage, and the combustible gas is continuously supplied to the furnace to burn violently until the garbage is completely burned out. In the burning zone 11, the garbage on the garbage incineration vehicle 18 has been retorted or burned, leaving the residue of carbides to continue to burn, so that the air here maintains a relatively high temperature, through the waste heat outlet 14 of the burning zone, the drying zone The waste heat inlet 40 is sucked by the auxiliary induced draft fan of the post-incineration tunnel to dry and heat, and then incinerate the garbage newly entered into the tunnel. The temperature of the incombustible material remaining on the incinerator is gradually lowered, and finally the outlet 12 is pushed out of the furnace for unloading. .
参见图 2。 本发明中的垃圾焚烧车 18长 2米釆用耐热钢制成, 垃圾焚烧车紧贴焚烧隧道侧壁, 其顶部密集装载 0.5米厚的垃圾, 造 成缺氧状态用于干馏, 其内部设有上、 中、 下三层炉排, 上层炉排焊 接四根炉条 22, 中层间炉排焊接 9根中间炉条 23, 下层炉排焊接 18 根底层炉条 24, 这三层炉排把垃圾架起, 使焚烧车上部干馏垃圾燃 烧和干馏后体积减小, 掉到上层炉排继续燃烧; 上层炉排垃圾燃烧和 干镏后体积减小,掉到中层炉排继续燃烧; 中层垃圾燃烧和干馏后体 积减小, 掉到下层炉排继续燃烧。 垃圾掉落使内部垃圾外露, 得以继 续燃烧和干馏, 即使原来垃圾密集装载也能够烧透,起到 "自动拨火" 的功能, 垃圾得以彻底燃尽。 焚烧车的底座 27釆用槽钢焊接而成, 上面设盛灰底板 25,下面安装四个轮子 26,可在行车导轨 21上滑行。 在底座 27的上方再焊接一圈槽钢, 架住底层炉条 24, 在两侧的槽钢 上面各焊接四根立柱 28, 利用两根槽钢架住中间炉条 23, 上面再用 8根立柱架住顶层炉条 22, 在槽钢上、 下方焊接钢板内壁 29, 焚烧 车的两侧面相应于每两根炉条之间的间隔为透气孔 30, 空气可以从 两侧的透气孔 30进入, 使焚烧车内部垃圾充分燃烧, 达到把垃圾彻 底燃尽的目的。 根据焚烧炉的大小, 整个焚烧隧道可以装入许多焚烧车。作为实 实施例子,每条焚烧隧道全长 60米,内部可以同时容纳 30辆焚烧车。 焚烧炉点火以后无需添加助燃剂就可以长时间连续工作,焚烧车检修 只要更换一辆焚烧车, 无需暂停焚烧炉的运行。 See Figure 2. The garbage incinerator 18 of the present invention is made of heat-resistant steel and is made of heat-resistant steel. The garbage incinerator is placed close to the side wall of the incineration tunnel, and the top of the garbage incineration is densely packed with 0.5 m thick garbage, causing anoxic state for dry distillation. There are three upper, middle and lower grate, the upper grate is welded with four grate 22, the middle grate is welded with 9 intermediate grate 23, and the lower grate is welded with 18 lower grate 24, which are three-layer grate The garbage is racked up, so that the volume of the dry distillation waste in the upper part of the incineration vehicle is reduced and the volume is reduced, and the upper layer of the grate is burned and burned; the upper grate is burned and dried, and the volume is reduced, and the inner grate is continuously burned; the middle layer garbage After combustion and retorting, the volume is reduced and falls to the lower grate to continue burning. The garbage is dropped to expose the internal garbage, and it can continue to burn and dry distillation. Even if the original garbage is densely loaded, it can be burnt through, and the function of "automatic ignition" can be completely burned out. The base 27 of the incinerator is welded by channel steel, and the upper bottom plate 25 is provided thereon, and four wheels 26 are mounted on the lower side to slide on the traveling rails 21. A groove of channel steel is welded on top of the base 27, the bottom layer of the furnace bar 24 is supported, four columns 28 are welded on the channel steels on both sides, and the intermediate grate 23 is supported by two channels of steel, and 8 pieces are used thereon. The column supports the top layer of the furnace strip 22, and the inner wall 29 of the steel plate is welded on the upper and lower sides of the channel steel. The two sides of the incinerator are corresponding to the interval between each two bars, which are venting holes 30, and the air can enter from the venting holes 30 on both sides. , the internal garbage of the incineration vehicle is fully burned, and the purpose of completely burning the garbage is achieved. Depending on the size of the incinerator, the entire incineration tunnel can be loaded with many incinerators. As a practical example, each incineration tunnel is 60 meters long and can accommodate 30 incinerators at the same time. After the incinerator is ignited, it can work continuously for a long time without adding a combustion-supporting agent. The incinerator should be replaced with a burning vehicle without stopping the operation of the incinerator.
参见图 3。 本发明中, 废气引风机 32从干馏燃烧区 7的集烟气 管 9, 经连接管 31把燃烧垃圾的废气抽过来, 送入废气洗涤池 35。 由于废气洗涤池 35的截面积比废气进气管的截面积大许多, 废气进 入废气洗涤池后速度大大降低, 悬浮的烟尘就掉到废气洗涤池里。 洗 涤池里是加入明矾和清香剂的石灰水, 上方分布许多喷水管 23, 喷 水管 23开有足够多的喷水口, 抽水机从洗涤池抽出洗涤液经喷水管 自上而下喷出, 形成多层水幕, 废气经过许多水幕洗涤, 除去废气中 的烟尘、 恶臭并中和废气中的 HC1、 NOx、 SOx和 COx等有害物质 以后废气达到或超过废气排放标准, 经烟囱排入高空。  See Figure 3. In the present invention, the exhaust gas induced draft fan 32 draws the exhaust gas of the combustion waste from the collecting flue gas pipe 9 of the dry distillation combustion zone 7 through the connecting pipe 31, and sends it to the exhaust gas washing tank 35. Since the cross-sectional area of the exhaust gas scrubbing tank 35 is much larger than the cross-sectional area of the exhaust gas intake pipe, the velocity of the exhaust gas entering the exhaust gas scrubbing tank is greatly reduced, and the suspended soot is dropped into the exhaust gas scrubbing tank. The washing tank is filled with lime water with alum and freshener, and a plurality of water spray pipes 23 are arranged above, and the water spray pipe 23 has enough water spray ports, and the water pump extracts the washing liquid from the washing pool through the spray pipe from top to bottom. The multi-layer water curtain is formed, and the exhaust gas is washed by a plurality of water curtains to remove the smoke and odor from the exhaust gas and neutralize harmful substances such as HC1, NOx, SOx and COx in the exhaust gas, and the exhaust gas meets or exceeds the exhaust emission standard, and passes through the chimney row. Go into the sky.
本发明中, 前、后两条焚烧隧道中的两行车轨道 21的连接方式, 可以在两条焚烧隧道的端部由圆弧轨道连接在一起形成闭合轨道,还 可以由横向移动机构实现连接。  In the present invention, the two rails 21 in the front and rear incineration tunnels can be connected by circular arc tracks at the ends of the two incineration tunnels to form a closed rail, and can also be connected by a lateral moving mechanism.
参看图 5。 本发明中的横向移动机构包括与行车轨道 21垂直相 交的两条横移轨道 42、 位于横移轨道 42上面的横移支架 41及支架 驱动机构。 支架驱动机构包括安装在横移支架 41上的正反转驱动电 机 48、 安装在驱动电机 48输出轴上的主动链轮 49、平行于横移轨道 42并与主动链轮 49配合的链条 43, 以及安装在横移支架 41上的两 个导向链轮 47。  See Figure 5. The lateral movement mechanism in the present invention includes two traverse rails 42 perpendicularly intersecting the traveling rail 21, a traverse bracket 41 located above the traverse rail 42, and a bracket driving mechanism. The carriage drive mechanism includes a forward and reverse drive motor 48 mounted on the traverse bracket 41, a drive sprocket 49 mounted on the output shaft of the drive motor 48, a chain 43 parallel to the traverse rail 42 and cooperating with the drive sprocket 49, And two guide sprockets 47 mounted on the traverse bracket 41.
当垃圾焚烧车 18在该条焚烧隧道的驱动装置作用下, 从其中一 条焚烧隧道的出口 12移出后, 便移到横移轨道 42上。 横移支架有 4 个轮子, 可以在横移轨道上滑行。 链条两端是固定的, 只需通过两个 导向链轮 47绕到驱动电机 48的主动链轮 49上。 当启动电机, 主动 链轮 49转动, 便带动横移支架 41沿着横移轨道 42滑行, 到另一条 焚烧隧道的入口 1处停止, 此时, 焚烧车 18下的轨道已和另一条焚 烧隧道内的行车轨道 21相衔接, 如图 3的虛线所示。 液压缸 20把送 过来的垃圾焚烧车 18推入焚烧隧道, 开始进入另一条焚烧隧道装载 垃圾,垃圾装满后横移支架 41在驱动电机 48的反转作用下又回到原 始焚烧炉出口的位置。 整个动作过程可由计算机自动控制。 When the garbage incinerator 18 is removed from the outlet 12 of one of the incineration tunnels by the driving means of the incineration tunnel, it is moved to the traverse rail 42. The traverse bracket has 4 wheels that can slide on the traverse track. The ends of the chain are fixed and are simply wound by two guide sprockets 47 onto the drive sprocket 49 of the drive motor 48. When the motor is started, the drive sprocket 49 rotates, and the traverse bracket 41 is driven to slide along the traverse track 42 to another The entrance to the incineration tunnel is stopped. At this time, the track under the incinerator 18 has been engaged with the carriage track 21 in the other incineration tunnel, as shown by the dashed line in FIG. The hydraulic cylinder 20 pushes the garbage incinerator 18 that has been sent to the incineration tunnel, and starts to enter another incineration tunnel to load the garbage. After the garbage is filled, the traverse bracket 41 returns to the original incinerator outlet under the reversal action of the driving motor 48. position. The entire course of action can be automatically controlled by the computer.
参见图 5, 本发明中的卸灰装置是可转动的液压缸 50和焚烧车 限位器 51。  Referring to Fig. 5, the dust discharging device of the present invention is a rotatable hydraulic cylinder 50 and an incinerator stopper 51.
卸灰过程-. 当出炉的垃圾焚烧车 18被推上横移支架 41时, 首先 开始卸灰。 卸灰动作是由安装在焚烧车下方的液压缸 50驱动的。 液 压缸的缸体可以绕轴 52旋转, 液压缸的活塞杆托住垃圾焚烧车的后 车轮的轴往上抬, 而前车轮被支架的限位器 51止住, 整个垃圾焚烧 车倾斜到 50 - 70° 时, 焚烧车车里不可燃的炉灰便卸到卸灰池 46, 然后液压缸下落, 垃圾焚烧车回到水平位置, 进行横移。 倒入卸灰池 46中的灰渣, 经过筛后送入灰库。  Ash discharge process - When the discharged garbage incinerator 18 is pushed up by the traverse bracket 41, the ash discharge is first started. The ash discharge operation is driven by a hydraulic cylinder 50 mounted below the incinerator. The cylinder of the hydraulic cylinder can be rotated about the shaft 52. The piston rod of the hydraulic cylinder is supported by the shaft of the rear wheel of the garbage incinerator, and the front wheel is stopped by the stopper 51 of the bracket, and the whole garbage incinerator is tilted to 50. - At 70 °, the non-combustible ash in the incineration vehicle is discharged to the ash discharge tank 46, then the hydraulic cylinder is dropped, and the garbage incineration vehicle is returned to the horizontal position for traverse. The ash poured into the ash discharge tank 46 is sieved and sent to the ash storage.
本发明的的焚烧工艺只要求焚烧炉在开始运行时第一、二辆焚烧 车三层炉条上都装入木材, 第三、 四辆焚烧车里装入两层木材, 上层 装入垃圾, 此后每辆焚烧车只在底层炉条上装入木材, 上面全部装入 垃圾, 焚烧车从入口排满到焚烧炉的熄火区, 用少许柴油浇到第一辆 焚烧车上点燃木材进行燃烧, 烘烤焚烧隧道, 以后装满垃圾的焚烧车 不断进入, 无需添加任何助燃剂, 焚烧过程就可以长时间连续进行, 大大降低垃圾处理的成本, 方便、 省力、 节能。 工业适用性  The incineration process of the present invention only requires that the incinerator be loaded with wood on the three layers of the first and second incinerators at the beginning of operation, and the third and fourth incinerators are loaded with two layers of wood, and the upper layer is filled with garbage. After that, each incinerator only put wood on the bottom layer of the furnace, and all of it was filled with garbage. The incinerator was filled from the entrance to the extinguishing area of the incinerator, and a little diesel was poured into the first incinerator to ignite the wood for combustion. The incineration tunnel is baked, and the incinerators filled with garbage are continuously entered. No need to add any combustion improver, the incineration process can be carried out continuously for a long time, which greatly reduces the cost of garbage disposal, and is convenient, labor-saving and energy-saving. Industrial applicability
本焚烧炉由于利用高温干馏技术,同时利用燃尽区的余热烘干刚 进入焚烧隧道的垃圾, 所以适应性强, 能够焚烧炉排炉难以焚烧的塑 料袋等垃圾, 也能够焚烧含水量大的垃圾, 完全适合我国的国情, 也 适合其他国家的垃圾焚烧。  The incinerator uses the high-temperature dry distillation technology and uses the waste heat from the burnout zone to dry the garbage that has just entered the incineration tunnel. Therefore, it is highly adaptable, and it can incinerate garbage such as plastic bags that are difficult to be incinerated in the grate furnace, and can also incinerate water with a large amount of water. Garbage is completely suitable for China's national conditions and is also suitable for waste incineration in other countries.
高温干馏技术的应用, 大大降低了垃圾焚烧炉的投资成本、运行 成本和维修成本。 和目前曰本最先进的垃圾焚烧技术(以下简称 "曰 本技术")相比, 具有巨大的优越性: 本发明可以焚烧原生垃圾曰本 技术只能焚烧可燃垃圾; 本发明垃圾从入炉到燃尽一气呵成, 日本技 术需要经过分选、 破碎、 烘干、 气化等等工艺, 费时费力; 本发明每 日处理 1吨垃圾的投资不到 20万元, 日本技术超过 100万元; 本发 明处理 1吨垃圾的运行成本只要几十元, 日本技术则需 400 - 500元; 本发明单炉的日处理能力可达 500 - 600吨, 日本技术只有 160吨; 特别是本发明把烘干区的废气引入干馏燃烧区进行二次燃烧,可以烧 尽二恶英等强致癌物质, 曰本技术只是在燃烧残余的碳化物时温度烧 到 130CTC , 但在垃圾烘干、 气化时温度低, 无法烧尽二恶英等强致 癌物质, 二恶英排放自然超标。' The application of high temperature retorting technology greatly reduces the investment cost and operation of waste incinerator Cost and maintenance costs. Compared with the current state-of-the-art waste incineration technology (hereinafter referred to as "Sakamoto technology"), the present invention has enormous advantages: the invention can incinerate raw garbage, the technology can only incinerate combustible garbage; the garbage of the invention is from the furnace to the furnace Burning out in one go, Japanese technology needs to be sorted, crushed, dried, gasified, etc., which is time-consuming and laborious; the invention has less than 200,000 yuan of daily processing of 1 ton of garbage, and Japanese technology exceeds 1 million yuan; The operating cost of processing 1 ton of garbage is only tens of yuan, and the Japanese technology requires 400-500 yuan; the daily processing capacity of the single furnace of the invention can reach 500-600 tons, and the Japanese technology is only 160 tons; in particular, the drying zone of the present invention The exhaust gas is introduced into the dry distillation combustion zone for secondary combustion, and can burn out strong carcinogens such as dioxins. The technique is only to burn 130CTC when burning residual carbides, but the temperature is low when the garbage is dried and vaporized. It is impossible to burn out strong carcinogens such as dioxins, and dioxin emissions naturally exceed the standard. '

Claims

1.一种高温干馏垃圾焚烧炉, 其特征是包括结构相同的前、 后焚 烧隧道、 分别设置在前、 后焚烧隧道底部的两条行车轨道(21)、 位 于行车轨道(21)上的若干辆具有多层炉排的垃圾焚烧车 (18)、 用 于驱动垃圾焚烧车 (18) 的驱动装置(20) 以及废气排放烟囱 (34) 和废气洗涤装置, 其中焚烧隧道从入口 (1) 至出口 (12)依次形成 权 A high-temperature dry distillation waste incinerator characterized by comprising the same front and rear incineration tunnels, two running rails (21) respectively disposed at the bottom of the front and rear incineration tunnels, and a plurality of running rails (21) a waste incineration vehicle (18) with a multi-layer grate, a drive unit (20) for driving the waste incineration vehicle (18), an exhaust gas exhaust stack (34) and an exhaust gas scrubbing device, wherein the incineration tunnel is from the inlet (1) to Export (12) sequentially forms the right
烘干区 (3)、 干馏燃烧区 (7)和燃烬区 (11), 在隧道入口 (1)后 面隧道顶部设有垃圾进料口 (2); 所述烘干区 (3)设有烘干区废气 排气管 (10), 在烘干区 (3) 的隧道侧壁上设有余热入口 (40), 燃 烬区 (11) 处的隧道侧壁上设有余热出口 (14); 前焚烧隧道的余热 出口 (14)与后焚烧隧道余热入口 (40)连通, 前焚烧隧道的余热入 书 a drying zone (3), a dry distillation combustion zone (7) and a burning zone (11), a garbage inlet (2) is arranged at the top of the tunnel behind the tunnel entrance (1); the drying zone (3) is provided a waste gas exhaust pipe (10) in the drying zone, a waste heat inlet (40) on the tunnel side wall of the drying zone (3), and a waste heat outlet (14) on the tunnel side wall in the burning zone (11) The waste heat outlet (14) of the former incineration tunnel is connected to the waste heat inlet (40) of the post-incineration tunnel, and the waste heat from the former incineration tunnel is entered into the book.
口 (40)与后焚烧隧道余热出口 (14)连通; 前焚烧隧道烘干区的废 气经后焚烧隧道烘干区排废气管(10)通入到的干镏燃烧区(7), 后 焚烧隧道烘干区的废气经前焚烧隧道的烘干区排废气管( 10 )通入到 干馏燃烧区 (7)。 The mouth (40) is connected to the waste heat outlet (14) of the post-incineration tunnel; the exhaust gas in the drying zone of the former incineration tunnel is passed through the dry combustion zone (7) of the exhaust pipe (10) in the drying zone of the post-incineration tunnel, and is incinerated. The exhaust gas in the tunnel drying zone is passed to the dry distillation combustion zone (7) through the drying zone exhaust pipe (10) of the pre-incineration tunnel.
2.根据杈利要求 1所述的高温干馏垃圾焚烧炉, 其特征是烘干区 (3)上部的隧道顶壁设有若干抽气管道(4), 若干抽气管道(4)汇 集于集气管 (5), 其中一焚烧隧道的集气管 (5) 与另一焚烧隧道的 烘干区废气排气管 (10)连通, 管路上设有辅助引风机。  2. The high-temperature dry distillation waste incinerator according to claim 1, characterized in that the top wall of the tunnel in the upper part of the drying zone (3) is provided with a plurality of suction pipes (4), and a plurality of suction pipes (4) are collected in the set. The air pipe (5), wherein the gas collecting pipe (5) of one incineration tunnel is connected with the exhaust gas exhaust pipe (10) of the drying zone of another incineration tunnel, and an auxiliary induced draft fan is arranged on the pipeline.
3.根据权利要求 1或 2所述的高温干馏垃圾焚烧炉, 其特征是干 馏燃烧区 (7)上部的隧道顶壁设有若干排烟管道(8), 若干排烟管 道( 8 )汇集于集烟管道( 9 ), 集烟管道( 9 )连通有废气连接管( 31 ), 废气连接管 (31)上安装有废气引风机(32), 废气连接管 (31)将 烟气通入所述废气洗涤装置。  The high-temperature dry distillation waste incinerator according to claim 1 or 2, characterized in that the top wall of the tunnel in the upper portion of the dry distillation combustion zone (7) is provided with a plurality of exhaust pipes (8), and a plurality of exhaust pipes (8) are collected The collecting pipe (9), the collecting pipe (9) is connected with an exhaust pipe (31), the exhaust connecting pipe (31) is provided with an exhaust fan (32), and the exhaust connecting pipe (31) is used to pass the flue gas into the pipe. Exhaust gas washing device.
4.根据权利要求 1或 2所述的高温干馏垃圾焚烧炉, 其特征是所 述前焚烧隧道和后焚烧隧道并排放置, 所述余热入口 (40)和余热出 口 (14)位于前焚烧隧道或后焚烧隧道的同一侧壁上。 The high-temperature dry distillation waste incinerator according to claim 1 or 2, wherein the front incineration tunnel and the post-incineration tunnel are placed side by side, and the waste heat inlet (40) and the waste heat outlet (14) are located in a front incineration tunnel or After burning the same side wall of the tunnel.
5.根据杈利要求 3所述的高温干馏垃圾焚烧炉, 其特征是烘干区 (3)分为烘干前区和烘干后区, 烘干前区的隧道顶壁平直, 距离垃 圾焚烧车 (18)顶部 0.2-0.8米, 洪干后区的隧道顶壁呈拱形, 其拱 顶相对烘干前区的隧道顶壁提高 0.2-0.8米, 所述抽气管道(4)设置 在烘干后区, 干馏燃烧区 (7)上部的隧道拱顶相对烘干后区隧道拱 顶提高 0.2-0.8米; 燃烬区 (11)上部的隧道顶壁与烘干前区的隧道 顶壁高度相同。 5. The high-temperature dry distillation waste incinerator according to claim 3, characterized in that the drying zone (3) is divided into a pre-drying zone and a post-drying zone, and the top wall of the tunnel in the pre-drying zone is straight, away from the garbage. The top of the incinerator (18) is 0.2-0.8 m. The top wall of the tunnel in the trunk area is arched, and the dome is raised by 0.2-0.8 m from the top wall of the tunnel in the front of the drying zone. The exhaust pipe (4) is set. In the post-drying zone, the tunnel vault in the upper part of the dry distillation combustion zone (7) is increased by 0.2-0.8 m relative to the tunnel arch in the post-drying zone; the top of the tunnel in the upper part of the burning zone (11) and the tunnel top in the pre-drying zone The wall height is the same.
6.根据权利要求 5所述的高温干镏垃圾焚烧炉, 其特征是垃圾焚 烧车(18) 内的炉排分为上、 中、 下三层, 每层炉排由若干根炉条组 成, 其中上层炉排的炉条间距大于中层炉排的炉条间距, 中层炉排的 炉条间距大于下层炉排的炉条间距, 垃圾焚烧车(18)两侧设有透气 孔 (30)。  6. The high temperature dry waste incinerator according to claim 5, characterized in that the grate in the garbage incineration vehicle (18) is divided into upper, middle and lower layers, and each grate is composed of a plurality of grate bars. The spacing of the upper strips of the upper grate is greater than the spacing of the grate of the middle grate, the spacing of the grate of the middle grate is greater than the spacing of the grate of the lower grate, and the venting holes (30) are provided on both sides of the garbage incineration vehicle (18).
7.根据杈利要求 6所述的高温干馏垃圾焚烧炉, 其特征是所述废 气洗涤装置包括废气洗涤池 (35)、 抽水机及其循环管路, 其中废气 洗涤池 (35) 内装有加入明矾和清香剂的石灰水, 废气洗涤池 (35) 上面设有若干喷水管 (33), 每根喷水管 (33) 上具有若干喷水口, 抽水机的循环管路一端与喷水管(33)连通, 另一端接入到废气洗涤 池 (35) 的石灰水内。  7. The high-temperature dry distillation waste incinerator according to claim 6, characterized in that the exhaust gas washing device comprises an exhaust gas washing tank (35), a water pump and a circulation line thereof, wherein the exhaust gas washing pool (35) is filled with alum And the lime water of the freshener, the exhaust gas washing pool (35) is provided with a plurality of water spray pipes (33), each spray pipe (33) has a plurality of water spray ports, and one end of the circulation pipe of the water pump and the water spray pipe ( 33) Connected, the other end is connected to the lime water of the exhaust scrubber (35).
8.根据杈利要求 1或 2所述的高温干馏垃圾焚烧炉, 其特征是两 条行车轨道( 21 )的相应端部由横向移动机构或圆弧轨道连接在一起。  8. The high-temperature dry distillation waste incinerator according to claim 1 or 2, characterized in that the respective ends of the two running rails (21) are connected by a lateral moving mechanism or a circular arc track.
9.根据杈利要求 1或 2所述的高温干馏垃圾焚烧炉, 其特征是还 包括设置在隧道出口 (12) 处的卸灰装置。  9. The high temperature dry distillation waste incinerator according to claim 1 or 2, further comprising an ash discharge device disposed at the tunnel outlet (12).
10.根据杈利要求 7所述的高温干馏垃圾焚烧炉, 其特征是所述 垃圾焚烧车的驱动装置(20)是液压缸。  10. The high temperature dry distillation waste incinerator according to claim 7, characterized in that the driving device (20) of the garbage incineration vehicle is a hydraulic cylinder.
11.根据杈利要求 8所述的高温干馏垃圾焚烧炉, 其特征是所述 横向移动机构包括与行车轨道(21)垂直相交的两条横移轨道(42)、 位于横移轨道(42)上面的横移支架 (41)及支架驱动机构。 11. The high temperature dry distillation waste incinerator according to claim 8, wherein the lateral movement mechanism comprises two traverse rails (42) perpendicular to the roadway (21), and a traverse rail (42) The upper traverse bracket (41) and the bracket drive mechanism.
12.根据杈利要求 11所述的高温干馏垃圾焚烧炉, 其特征是所述 支架驱动机构包括安装在横移支架 (41)上的驱动电机 (48)、 安装 在驱动电机(48)输出轴上的主动链轮(49)、 平行于横移轨道(42) 并与主动链轮 (49) 配合的链条(43), 以及安装在横移支架 (41) 上的两个导向链轮 (47)。 12. The high temperature dry distillation waste incinerator according to claim 11, wherein the bracket drive mechanism comprises a drive motor (48) mounted on the traverse bracket (41) and mounted on the output shaft of the drive motor (48) The upper drive sprocket (49), the chain (43) parallel to the traverse track (42) and cooperates with the drive sprocket (49), and the two guide sprocket mounted on the traverse bracket (41) (47) ).
13.根据权利要求 12所述的高温干馏垃圾焚烧炉, 其特征是所述 驱动电机 (48)是正反转电机。  A high temperature dry distillation waste incinerator according to claim 12, wherein said drive motor (48) is a forward and reverse motor.
PCT/CN2006/001813 2005-07-22 2006-07-24 A dry distillation garbage incinerator WO2007009399A1 (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104942954A (en) * 2015-05-27 2015-09-30 台山市合利生物质科技有限公司 Gas retort for wood waste

Families Citing this family (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101556046B (en) * 2009-03-30 2011-06-08 赵健强 Waste incineration processing system
CN102878568B (en) * 2012-11-05 2016-03-02 刘贡友 The tunnel-type kiln of many temperature rank incineration treatment of garbage and method
CN103604127B (en) * 2013-12-02 2016-06-22 陈凤仪 Double-deck Horizontal band interlayer residual heat drying incinerator
CN104140851B (en) * 2014-08-12 2017-10-31 余式正 It is a kind of Wu bioxin and the vertical negative-pressure rubbish dry-distillation incineration stove of non-exhaust emission
CN107649485B (en) * 2017-09-20 2019-11-05 许春桂 A kind of rubbish and dense smoke integrated conduct method
CN111720837A (en) * 2020-06-22 2020-09-29 鲁西化工集团股份有限公司硅化工分公司 Organic silicon cracking slag incineration system, method and application
CN112268283A (en) * 2020-11-17 2021-01-26 佛山市华艺真空科技有限公司 Pyrolysis incineration device

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US2912941A (en) * 1956-10-15 1959-11-17 Charles W Hughes Continuous incinerator structures
US4836777A (en) * 1986-11-29 1989-06-06 Acme Marls Limited Kiln cars
US4944236A (en) * 1989-08-24 1990-07-31 Sheen Chao Chin Tunnel type garbage incinerator
JPH08159426A (en) * 1994-12-01 1996-06-21 Masao Ishii Incinerator for garbage
JPH09159128A (en) * 1995-12-05 1997-06-20 Daito:Kk Incinerator and combustion for incinerator
JPH11351545A (en) * 1998-06-09 1999-12-24 Yoshihiko Kamimura Sootless slagging incinerator

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US2912941A (en) * 1956-10-15 1959-11-17 Charles W Hughes Continuous incinerator structures
US4836777A (en) * 1986-11-29 1989-06-06 Acme Marls Limited Kiln cars
US4944236A (en) * 1989-08-24 1990-07-31 Sheen Chao Chin Tunnel type garbage incinerator
JPH08159426A (en) * 1994-12-01 1996-06-21 Masao Ishii Incinerator for garbage
JPH09159128A (en) * 1995-12-05 1997-06-20 Daito:Kk Incinerator and combustion for incinerator
JPH11351545A (en) * 1998-06-09 1999-12-24 Yoshihiko Kamimura Sootless slagging incinerator

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104942954A (en) * 2015-05-27 2015-09-30 台山市合利生物质科技有限公司 Gas retort for wood waste

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